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Rules and Regulations of the State of Georgia
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Subject 391-3-5 RULES FOR SAFE DRINKING WATER

Rule 391-3-5-.01 Purpose

The purpose of these Rules is to establish policies, procedures, requirements and standards to implement the Georgia Safe Drinking Water Act of 1977 (Act No. 231 O.C.G.A. Section 12-5-170et seq., as amended), and to carry out the purposes and requirements of the Federal Safe Drinking Water Act ( PL 93-523 ). These Rules are promulgated so that the citizens of the State of Georgia shall be assured adequate, safe drinking water of the highest quality. Any reference in these Rules to standards, procedures and requirements in other sources is a specific adoption and incorporation by reference of that source for such standard, procedure, or requirement for purposes of these rules.

Rule 391-3-5-.02 Definitions

All terms used in these rules shall be interpreted in accordance with the definitions as set forth in the Georgia Safe Drinking Water Act of 1977 or as herein defined:

(1) "Act" means the Georgia Safe Drinking Water Act of 1977, as amended.
(2) "Action Level" means the concentration of a contaminant, which if exceeded, triggers treatment or other requirements which a water system must follow.
(3) "Aquifer" means any stratum or zone of rock beneath the surface of the earth capable of containing water or producing water from a well.
(4) "Aquifer Testing" means a controlled pumping test of a well lasting at least 24 continuous hours in which the water level and the pumping rate are monitored at closely spaced intervals and the water level is monitored for at least as long a time following the test as the duration of the test.
(5) "Backflow" means the reverse flow of contaminated water, other liquid, gas, or substance into the distribution system of a potable water supply.
(6) "Back pressure" means a condition in which the pressure in a non-potable system is greater than the pressure in the potable distribution system and can cause contaminants to backflow into the potable system.
(7) "Backsiphonage" means a form of backflow caused by a negative or below atmospheric pressure within the potable water system.
(8) "Bag filters" are pressure-driven separation devices that remove particulate matter larger than 1 micrometer using an engineered porous filtration media. They are typically constructed of a non-rigid, fabric filtration media housed in a pressure vessel in which the direction of flow is from the inside of the bag to outside.
(9) "Bank filtration" is a water treatment process that uses a well to recover surface water that has naturally infiltrated into ground water through a river bed or bank(s). Infiltration is typically enhanced by the hydraulic gradient imposed by a nearby pumping water supply or other well(s).
(10) "Business plan" means a written plan which is prepared to demonstrate a public water system's managerial and financial capacity to comply with all drinking water regulations in effect, or likely to be in effect. The business plan is to be prepared in conformance with Appendix A of the Division's "Minimum Standards for Public Water Systems", latest edition. The business plan shall be updated at intervals determined by the Director.
(11) "Best Available Technology" or "BAT" means the best technology, treatment techniques, or other means promulgated by EPA and adopted by the Division. In promulgating BAT the EPA examines the efficacy under field conditions and not solely under laboratory conditions, and takes costs into consideration when determining what technology or treatment technique is available.
(12) "CFR" means the Code of Federal Regulations, Title 40. The Code of Federal Regulations is a codification of the general and permanent rules published in the Federal Register by the executive departments and agencies of the federal government.
(13) "Capacity" means the overall capability of a water system to reliably produce and deliver water meeting all national primary drinking water regulations in effect, or likely to be in effect. Capacity encompasses the technical, managerial, and financial capabilities, as described in the latest edition of EPD's "Minimum Standards for Public Water Systems" and will enable a water system to plan for, achieve, and maintain compliance with applicable drinking water standards.
(14) "Cartridge filters" are pressure-driven separation devices that remove particulate matter larger than 1 micrometer using an engineered porous filtration media. They are typically constructed as rigid or semi-rigid, self-supporting filter elements housed in pressure vessels in which flow is from the outside of the cartridge to the inside.
(15) "Casing" means the tubular material used to shut off or exclude a stratum or strata and to protect against entrance of contaminants during the expected life of the well.
(16) "Clean compliance history" is, for the purposes of the Revised Total Coliform Rule, 391-3-5-.55, a record of: no MCL violations under Rule 391-3-5-.18(4)(a)-(c) or Rule 391-3-5-.55; no monitoring violations under Rule 391-3-5-.23 or Rule 391-3-5-.55; and no coliform treatment technique trigger exceedances or treatment technique violations under Rule 391-3-5-.55.
(17) "Coagulation" means a process using coagulant chemicals and mixing by which colloidal and suspended materials are destabilized and agglomerated into flocs.
(18) "Combined distribution system" is the interconnected distribution system consisting of the distribution systems of wholesale systems and of the consecutive systems that receive finished water.
(19) "Community water system" or "CWS" means a public water system, which serves at least 15 service connections, used by year-round residents or regularly serves at least 25 year-round residents.
(20) "Compliance cycle" means the nine-year calendar year cycle during which public water systems must monitor. Each compliance cycle consists of three-year compliance periods. The first compliance cycle begins January 1, 1993.
(21) "Compliance period" means a three-year calendar year period within a compliance cycle. Each compliance cycle has three-year compliance periods.
(22) "Comprehensive performance evaluation" or "CPE" means a thorough review and analysis of a treatment plant's performance-based capabilities and associated administrative, operation and maintenance practices. It is conducted to identify factors that may be adversely impacting a plant's capability to achieve compliance and emphasizes approaches that can be implemented without significant capital improvements. For purpose of compliance with subparts P and T of 40 CFR Part 141, the CPE shall consist of at least the following components: Assessment of plant performance; evaluation of major unit processes; identification and prioritization of performance limiting factors; assessment of the applicability of comprehensive technical assistance; and preparation of a CPE report.
(23) "Confirmation Sample" means a sample analysis or analyses taken to verify the results of an original analysis. Each sample for the analysis shall be taken or measured at the same location in the water system as the original sample. The results of the confirmation samples shall be averaged with the original sample to determine compliance.
(24) "Confined Aquifer" means an aquifer which is separated from the land surface by a significant zone of low permeability which prevents surface recharge or pollutants from readily reaching the aquifer.
(25) "Confluent growth" means a continuous bacterial growth covering the entire filtration area of a membrane filter, or a portion thereof, in which bacterial colonies are not discrete.
(26) "Consecutive system" is a public water system that receives some or all of its finished water from one or more wholesale systems. Delivery may be through a direct connection or through the distribution system of one or more consecutive systems.
(27) "Consumer Confidence Report" means an annual report that community water systems must deliver to their customers which, as a minimum, contains information on the quality of the water delivered by the system and characterizes the risks (if any) from exposure to contaminants detected in the drinking water in an accurate and understandable manner.
(28) "Contaminant" means any physical, chemical, biological, or radiological substance or matter in water.
(29) "Conventional filtration treatment" means a series of processes including coagulation flocculation, sedimentation, and filtration resulting in substantial particulate removal.
(30) "Corrosion Inhibitor" means a substance capable of reducing the corrosivity of water toward metal plumbing materials, especially lead and copper, by forming a protective film on the interior surface of those materials.
(31) "Cross-connection" means any physical arrangement whereby a public water supply is connected, directly or indirectly, with any other water supply system, sewer, drain, conduit, pool, storage reservoir, plumbing fixture, or other device which contains or may contain contaminated water, sewage or other waste, or liquid of unknown or unsafe quality which may be capable of imparting contamination to the public water supply as the result of backflow. By-pass arrangements, jumper connections, removable sections, swivel or changeable devices, and other temporary or permanent devices through which or because of which backflow could occur are considered to be cross-connections.
(32) "CT" is the product of "residual disinfectant concentration" (C) in milligrams per liter determined before or at the first customer tap where water is provided for human consumption and the corresponding "disinfectant contact time" (T) in minutes.
(33) "Department" means the Department of Natural Resources of the State of Georgia.
(34) "Diatomaceous earth filtration" means a process resulting in substantial particulate removal in which (1) a pre-coat cake of diatomaceous earth filter media is deposited on a support membrane (septum), and (2) while the water is filtered by passing through the cake on the septum, additional filter media known as the body feed is continuously added to feed water to maintain the permeability of the filter cake.
(35) "Direct filtration" means a series of processes including coagulation and filtration but excluding sedimentation resulting in substantial particulate removal.
(36) "Director" means the Director of the Environmental Protection Division, Department of Natural Resources of the State of Georgia, or his designee.
(37) "Disinfectant" means any oxidant, including but not limited to chlorine, chlorine dioxide, chloramines, and ozone added to water in any part of the treatment or distribution process, that is intended to kill or inactivate pathogenic microorganisms.
(38) "Disinfectant contact time" ("T" in CT calculations) means the time in minutes that it takes for water to move from the point of disinfectant application or the previous point where residual disinfectant concentration ("C") is measured.
(39) "Disinfection" means a process, which inactivates pathogenic organisms in water by chemical oxidants or equivalent agents.
(40) "Disinfection profile" means a summary of Giardia lamblia inactivation through the treatment plant. The procedure for developing a disinfection profile is contained in 40 CFR § 141.172. (Disinfection profiling and benchmarking) in subpart P and §§141.530-141 .536 (Disinfection profile) in subpart T of 40 CFR Part 141.
(41) "Division" means the Environmental Protection Division, Department of Natural Resources of the State of Georgia.
(42) "Domestic or other non-distribution system plumbing problem" means a coliform contamination problem in a public water system with more than one service connection that is limited to the specific service connection from which the coliform-positive sample was taken.
(43) "Dose equivalent" means the product of the absorbed dose from ionizing radiation and such factors as account for differences in biological effectiveness due to the type of radiation and its distribution in the body as specified by the International Commission on Radiological Units and Measurements (ICRU).
(44) "Drinking Water" means water supplied to the public for human consumption from a public water system.
(45) "Dual sample set" is a set of two samples collected at the same time and same location, with one sample analyzed for TTHM and the other sample analyzed for HAA5. Dual sample sets are collected for the purposes of conducting an IDSE under subpart U of 40 CFR, Part 141 and determining compliance with the TTHM and HAA5 MCLs under subpart V of 40 CFR, Part 141.
(46) "Effective corrosion inhibitor residual" for the purpose of compliance with Rule 395-3-5-.25, means a concentration sufficient to form a protective film on the interior walls of a pipe.
(47) "Enhanced coagulation" means the addition of sufficient coagulant for improved removal of disinfection byproduct precursors by conventional filtration treatment.
(48) "Enhanced softening" means the improved removal of disinfection byproduct precursors by precipitative softening.
(49) "Entry Point" means the sample point where after treatment drinking water enters the distribution system. For purposes of the Act and the Rules, "entry point" shall be defined as a sample location anywhere on the finished water line after treatment, up to and including the first service or customer tap.
(50) "EPA" means the United States Environmental Protection Agency.
(51) "Exemption" means approval from the Division affording a public water system, existing as of the effective date of these rules, an extended time for compliance with a maximum contaminant level or treatment technique contained in a drinking water standard. An exemption pertains to non-compliance with a maximum contaminant level for reasons other than that instance when application of a generally available treatment method fails to adequately treat the raw water source.
(52) "Federal Act" means the Federal Safe Drinking Water Act, 1974 P.L. 93-523, as amended.
(53) "Filter profile" means a graphical representation of individual filter performance, based on continuous turbidity measurements or total particle counts versus time for an entire filter run, from startup to backwash inclusively, that includes an assessment of filter performance while another filter is being backwashed.
(54) "Filtration" means a process for removing particulate matter from water by passage through porous media.
(55) "Finished water" is water that is introduced into the distribution system of a public water system and is intended for distribution and consumption without further treatment, except as treatment necessary to maintain water quality in the distribution system (e.g., booster disinfection, addition of corrosion control chemicals).
(56) "First draw sample" means a one-liter sample of tap water collected in accordance with Rule 391-3-5-.25, that has been standing in the plumbing pipes at least 6 hours and is collected without flushing the tap.
(57) "Flocculation" means a process to enhance agglomeration or collection of smaller floc particles into larger, more easily settleable particles by gentle stirring by hydraulic or mechanical means.
(58) "Flowing stream" is a course of running water flowing in a definite channel.
(59) "GAC10" means granular activated carbon filter beds with an empty-bed contact time of 10 minutes based on average daily flow and a carbon reactivation frequency of every 180 days, except that the reactivation frequency for GAC10 used as a best available technology for compliance with subpart V MCLs under 40 CFR § 141.64(b)(2) shall be 120 days.
(60) "GAC20" means granular activated carbon filter beds with an empty-bed contact time of 20 minutes based on average daily flow and a carbon reactivation frequency of every 240 days.
(61) "Gross alpha particle activity" means the total radioactivity due to alpha particle emission as inferred from measurements on a dry sample.
(62) "Gross beta particle activity" means the total radioactivity due to beta particle emission as inferred from measurement on a dry sample.
(63) "Ground water" means water obtained from wells and/or springs used as a source of water supply for a public water system.
(64) "Ground water under the direct influence of surface water" (GWUDI) means any water beneath the surface of the ground with:
(a) significant occurrence of insects or other microorganisms, algae, or large-diameter pathogens such as Giardia lamblia, or Cryptosporidium, or
(b) significant and relatively rapid shifts in water characteristics such as turbidity, temperature, conductivity, or pH which closely correlate to climatological or surface water conditions.
(65) "Haloacetic acids (five)" (HAA5) mean the sum of the concentrations in milligrams per liter of the haloacetic acid compounds (monochloroacetic acid, dichloroacetic acid, trichloroacetic acid, monobromoacetic acid, and dibromoacetic acid), rounded to two significant figures after addition.
(66) "Halogen" means one of the chemical elements chlorine, bromine or iodine.
(67) "Hazardous Material" means any chemical, substance or material that is classified as Hazardous by the U.S. Environmental Protection Agency (CFR 40, Part 261).
(68) "Health hazards" mean any conditions, devices, or practices in a water supply system or its operation, which create or may create an imminent and substantial danger to the health and well-being to the water consumer.
(69) "Heterotrophic plate count" formerly known as the standard plate count, is a procedure for estimating the number of live heterotrophic bacteria in water. Unless stated otherwise, heterotrophic plate count refers to Method 9215, the pour plate method, as set forth in Standard Methods for the Examination of Water and Wastewater, American Public Health Association, 18th Edition, 1992, pp. 9-32 to 9-34, or subsequent edition.
(70) "Initial compliance period" means the first full three-year compliance period that begins January 1, 1993.
(71) "Inventory" for the purpose of Rule 391-3-5-.40 means a written or computer database listing of all potential sources of ground-water pollution located within a wellhead protection area.
(72) "Lake/reservoir" refers to a natural or man-made basin or hollow on the Earth's surface in which water collects or is stored that may or may not have a current or single direction of flow.
(73) "Large water system" for the purpose of Rule 391-3-5-.25 (Lead & Copper) means a water system that serves more than 50,000 persons.
(74) "Lead service line" means a line made of lead, which connects the discharge side of the water meter to the building inlet and any lead pigtail, gooseneck or other fitting, which is connected to such lead line.
(75) "Legionella" means a genus of bacteria, some species of which have caused a type of pneumonia called Legionnaires Disease.
(76) "Level 1 assessment" is an evaluation to identify the possible presence of sanitary defects, defects in distribution system coliform monitoring practices, and (when possible) the likely reason that the system triggered the assessment. It is conducted by the system operator or owner. Minimum elements include review and identification of atypical events that could affect distributed water quality or indicate that distributed water quality was impaired; changes in distribution system maintenance and operation that could affect distributed water quality (including water storage); source and treatment considerations that bear on distributed water quality, where appropriate (e.g., whether a ground water system is disinfected); existing water quality monitoring data; and inadequacies in sample sites, sampling protocol, and sample processing. The system must conduct the assessment consistent with any Division directives that tailor specific assessment elements with respect to the size and type of the system and the size, type, and characteristics of the distribution system.
(77) "Level 2 assessment" is an evaluation to identify the possible presence of sanitary defects, defects in distribution system coliform monitoring practices, and (when possible) the likely reason that the system triggered the assessment. A Level 2 assessment provides a more detailed examination of the system (including the system's monitoring and operational practices) than does a Level 1 assessment through the use of more comprehensive investigation and review of available information, additional internal and external resources, and other relevant practices. It is conducted by an individual approved by the Division, which may include the system operator. Minimum elements include review and identification of atypical events that could affect distributed water quality or indicate that distributed water quality was impaired; changes in distribution system maintenance and operation that could affect distributed water quality (including water storage); source and treatment considerations that bear on distributed water quality, where appropriate (e.g., whether a ground water system is disinfected); existing water quality monitoring data; and inadequacies in sample sites, sampling protocol, and sample processing. The system must conduct the assessment consistent with any Division directives that tailor specific assessment elements with respect to the size and type of the system and the size, type, and characteristics of the distribution system. The system must comply with any expedited actions or additional actions required by the Division in the case of an E. coli MCL violation.
(78) "Locational running annual average" (LRAA) is the average of sample analytical results for samples taken at a particular monitoring location during the previous four calendar quarters.
(79) "Man-made beta particle and photon emitters" means all radionuclides emitting beta particles and/or photons listed in Maximum Permissible Body Burdens and Maximum Permissible Concentration of Radionuclides in Air or Water for Occupational Exposure, NBS Handbook 69, except the daughter products of thorium-232, uranium-235 and uranium-238.
(80) "Maximum contaminant level" (MCL) means the highest level of a contaminant that is allowed in drinking water. MCLs are set as close to the MCLGs as feasible using the best available treatment technology.
(81) "Maximum contaminant level goal" (MCLG) means the level of a contaminant in drinking water below which there is no known or expected risk to health. MCLGs allow for a margin of safety.
(82) "Maximum residual disinfectant level" (MRDL) means a level of a disinfectant added for water treatment that may not be exceeded at the consumer's tap without an unacceptable possibility of adverse health effects.
(83) "Maximum residual disinfectant level goal" (MRDLG) means the maximum level of a disinfectant added for water treatment at which no known or anticipated adverse effect on the health of persons would occur, and which allows an adequate margin of safety. MRDLGs are non-enforceable health goals and do not reflect the benefit of the addition of the chemical for control of waterborne microbial contamination.
(84) "Medium-size water system" for the purpose of Rule 391-3-5-.25 (Lead & Copper), means a water system that serves greater than 3,300 and less than or equal to 50,000 persons.
(85) "Membrane filtration" is a pressure or vacuum driven separation process in which particulate matter larger than 1 micrometer is rejected by an engineered barrier, primarily through a size-exclusion mechanism, and which has a measurable removal efficiency of a target organism that can be verified through the application of a direct integrity test. This definition includes the common membrane technologies of microfiltration, ultrafiltration, nanofiltration, and reverse osmosis.
(86) "Minimum Community Population Determination" for the purpose of the Act and the Rules means the minimum residential population shall be determined by a mathematical calculation of the total number of active residential service connections, multiplied by Georgia's average population per household, as published in the most recent Federal Census Bureau Statistics. Multiple residential units served by a single connection (master meter) shall be included in the determination of population for a water system.
(87) "Near the first service connection" means at one of the 20 percent of all service connections in the entire system that are nearest the water supply treatment facility, as measured by water transport time within the distribution system.
(88) "Non-community water system" or "NCWS" means a public water system, which provides piped water for human consumption to at least 15 service connections or which serves at least 25 individuals at least 60 days out of the year but which is not a community water system. A non-community water system may be further classified as a "non-transient, non-community water system" or a "transient, non-community water system".
(89) "Non-transient, non-community water system" or "NTNCWS" means a public water system that is not a community water system and that regularly serves at least 25 of the same persons over 6 months per year.
(90) "Operator" means the person responsible for the maintenance and operation of the public water system. A certified operator is an operator registered as a Water Treatment Plant Operator in the State of Georgia in accordance with the provisions of the Certification of Water and Wastewater Treatment Plant Operators and Laboratory Analysts Act (Georgia Laws 1969, pp. 272 et. seq., as amended). For purposes of this Act a certified operator also includes persons involved with only the storage and distribution of drinking water.
(91) "Optimal corrosion control treatment" as it applies to Rule 391-3-5.25 (Lead & Copper) of this Chapter, means the corrosion control treatment that minimizes the lead and copper concentrations at user's taps while insuring that the treatment does not cause the water to violate any national primary drinking water regulation.
(92) "Person" means any individual, corporation, company, association, partnership, county, municipality, State agency, State authority, Federal agency, agency, facility, or other entity.
(93) "Picocurie" (pCi) means that quantity of radioactive material producing 2.22 nuclear transformations per minute.
(94) "Plant intake" refers to the works or structures at the head of a conduit through which water is diverted from a source (e.g., river or lake) into the treatment plant.
(95) "Point of disinfection application" is the point where the disinfectant is applied and water downstream of that point is not subject to recontamination by surface water runoff.
(96) "Presedimentation" is a preliminary treatment process used to remove gravel, sand and other particulate material from the source water through settling before the water enters the primary clarification and filtration processes in a treatment plant.
(97) "Professional Engineer" means a person registered to practice professional engineering in the State of Georgia in accordance with the provisions of the Act governing the Practice of Professional Engineering in Georgia. (Ga. Laws 1945, p. 294 et. seq., as amended).
(98) "Professional Geologist" means a person registered to practice professional geology in the State of Georgia in accordance with the provisions of the Registration of Geologist Act of 1975, (Code 1933, § 84-2101a, enacted by the Georgia Legislature 1975, p.163, 1).
(99) "Public water system" or "PWS" means a system that provides water to the public for human consumption through pipes or other constructed conveyances, if such system has at least fifteen (15) service connections or regularly serves an average of twenty-five (25) individuals daily at least 60 days out of the year. Such terms include:
1) any collection, treatment, storage, and distribution facilities under control of the operator of such system and used primarily in connection with such system; and
2) any collection or pretreatment storage facilities not under such control which are used primarily in connection with such system. Such term does not include any "special irrigation district." A public water system is a "community water system", a "non-transient non-community water system" or a "transient non-community water system".
(100) "Raw water" means water from a source of water supply or a proposed source of water supply, which has not received any type of treatment to change the physical, chemical, biological, or radiological quality of the water.
(101) "Rem" means the unit of dose equivalent from ionizing radiation to the total body or any internal organ or organ system. A "millirem (mrem)" is 1/1000 of a rem.
(102) "Repeat compliance period" means any subsequent compliance period after the initial compliance period.
(103) "Repeat sample" means a sample that is collected and analyzed in response to a previous coliform-positive sample.
(104) "Residual disinfectant concentration" ("C" in CT calculations) means the concentration of disinfectant measured in milligrams per liter in a representative sample of water.
(105) "Sanitary defect" is a defect that could provide a pathway of entry for microbial contamination into the distribution system or that is indicative of a failure or imminent failure in a barrier that is already in place.
(106) "Sanitary survey" means an on-site review of the water source, facilities, equipment, treatment, operation and maintenance of a public water system for the purpose of evaluating the adequacy of each for producing and distributing safe drinking water.
(107) "Seasonal system" is a non-community water system that is not operated as a public water system on a year-round basis and starts up and shuts down at the beginning and end of each operating season.
(108) "Sedimentation" means a process for removal of solids before filtration by gravity or separation.
(109) "Service connection" means the point at which the water distribution main and the water service pipe, metered or unmetered, are connected to serve water to a residence or water customer. As used in the definition of PWS, "service connection" does not include a connection to a system that delivers water by a constructed conveyance other than a pipe if:
(a) The water is used exclusively for purposes other than residential uses (consisting of drinking, bathing, and cooking, or other similar uses);
(b) The Division determines that alternative water to achieve the equivalent level of public health protection provided by the applicable national primary drinking water regulation is provided for residential or similar uses for drinking and cooking; or
(c) The Division determines that the water provided for residential or similar uses for drinking, cooking, and bathing is centrally treated or treated at the point of entry by the provider, a pass-through entity, or the user to achieve the equivalent level of protection provided by the applicable national primary drinking water regulations.
(110) "Service line sample" means a one-liter sample of water collected in accordance with Rule 391-3-5-.25 that has been standing for at least 6 hours in the service line.
(111) "Single family structure" for the purpose of compliance with Rule 391-3-5-.25 (Lead & Copper), means a building constructed as a single-family residence that is currently used as either a residence or place of business.
(112) "Slow sand filtration" means a process involving passage of raw water through a bed of sand at low velocity (generally less than 0.4 meters per hour) resulting in substantial particulate removal by physical and biological mechanisms.
(113) "Small water system" for the purpose of Rule 391-3-5-.25 (Lead & Copper), means a water system that serves 3,300 persons or fewer.
(114) "Source of water supply" means the waters of the State from which raw water is taken into a public water system to be treated and/or distributed.
(115) "Source Water Assessment Plan" (SWAP) means a public report which documents a public drinking water system's and other stakeholders' reasonable efforts to ascertain the potential impact of natural or man-made pollutants, within a wellhead protection or watershed area, on the raw water source for the drinking water supply well or surface water intake.
(116) "Spring" means a source of water supply which naturally issues forth for the first time from rock or soil onto the land or into a body of water.
(117) "Standard sample" means the aliquot of finished drinking water that is examined for the presence of coliform bacteria.
(118) "Storage tank" or "Tank" means any covered structure, such as clearwell, standpipe, reservoir, elevated tank, hydropneumatic tank or other storage facility or combination thereof used to store drinking water.
(119) "Subpart H systems" means public water systems using surface water or ground water under the direct influence of surface water as a source.
(120) "Supplier of water" or "Supplier" means any person who owns or operates a public water system.
(121) "Surface water" means and includes any and all rivers, streams, branches, creeks, ponds, tributary streams, drainage basins, natural lakes, artificial reservoirs and impoundments and ground water under the direct influence of surface water.
(122) "SUVA" means Specific Ultraviolet Absorption at 254 nanometers (nm), an indicator of the humic content of water. It is a calculated parameter obtained by dividing a sample's ultraviolet absorption at a wavelength of 254 nm by its concentration of dissolved organic carbon (DOC) (in mg/L).
(123) "System with a single service connection" means a system, which supplies drinking water to consumers via a single service line.
(124) "Total Organic Carbon" (TOC) means total organic carbon in mg/L measured using heat, oxygen, ultraviolet irradiation, chemical oxidants, or combinations of these oxidants that convert organic carbon to carbon dioxide, rounded to two significant figures.
(125) "Total trihalomethanes" (TTHM) means the sum of the concentration in milligrams per liter of the trihalomethane compounds: trichloromethane (chloroform), dibromochloromethane, bromodichloromethane and tribromomethane (bromoform), rounded to two significant figures.
(126) "Too numerous to count" means that the total number of bacterial colonies exceed 200 on a 47-mm diameter membrane filter used for coliform detection.
(127) "Transient non-community water system" or "TNCWS" means a public water system that is not a community water system or a non-transient non-community water system. A transient non-community water system provides piped water for human consumption to at least 15 service connections or which regularly serves at least 25 persons at least 60 days a year.
(128) "Treatment Technique" means a required process intended to reduce the level of contaminants in drinking water.
(129) "Treatment technique requirement" means a requirement, which specifies for a contaminant, a specific treatment technique(s), which leads to a reduction in the level of such contaminant sufficient to comply with the requirements of these Rules.
(130) "Trihalomethane" (THM) means one of the family of organic compounds, named as derivatives of methane, wherein three of the four hydrogen atoms in methane are each substituted by a halogen atom in the molecular structure.
(131) "Two-stage lime softening" is a process in which chemical addition and hardness precipitation occur in each of two distinct unit clarification processes in series prior to filtration.
(132) "Unconfined aquifer" means an aquifer which is not separated from the land surface by a significant zone of low permeability and, therefore, is more susceptible to pollution from the activities of mankind. Wellhead Protection Areas for unconfined aquifers are larger than such areas for confined aquifers.
(133) "Uncovered finished water storage facility" means a tank, reservoir or other facility used to store water that will undergo no further treatment except residual disinfection and is open to the atmosphere.
(134) "Variance" means approval from the Division affording a public water system an extended time for compliance with a maximum contaminant level or treatment technique contained in a drinking water standard. A variance pertains to non-compliance with a maximum contaminant level due to the inability to meet the maximum contaminant level even when a treatment method has been applied to a raw water source. The non­compliance is due to the quality of the raw water.
(135) "Virus" means a microorganism of fecal origin, which is infectious to humans by waterborne transmission.
(136) "Waterborne disease outbreak" means the significant occurrence of acute infectious illness, epidemiologically associated with the ingestion of water from a public water system which is deficient in treatment, as determined by the Division.
(137) "Waters" or "Waters of the State" means and includes any and all rivers, streams, creeks, branches, lakes, reservoirs, ponds, drainage systems, springs, wells, and all other bodies of surface or underground water, natural or artificial, of this State.
(138) "Watershed Area" means the entire drainage basin upstream of a water intake located on a stream or lake.
(139) "Well" means any excavation that is cored, bored, drilled, jetted, dug, or otherwise constructed for the purpose of locating, testing, or withdrawing ground water.
(140) "Wellhead protection area" means an area of potential ground water recharge around a well which should be protected from surface and subsurface sources of manmade pollution in order to protect the quality of drinking water supplies.
(141) "Wholesale system" is a public water system that treats source water as necessary to produce finished water and then delivers some or all of that finished water to another public water system. Delivery may be through a direct connection or through the distribution system of one or more consecutive systems.

Rule 391-3-5-.03 Coverage

(1) Applicability. These rules shall apply to all public water systems in the state, except that such rules shall not apply to a public water system which meets all the following criteria:
(a) which consists only of distribution and storage facilities (and does not have any collection and treatment facilities);
(b) which obtains all of its water from, but is not owned or operated by the owner or operator of a public water system to which such rules apply;
(c) which does not sell water to any person; and
(d) which is not a carrier which conveys passengers in interstate commerce.

Rule 391-3-5-.04 Approval Required. Amended

(1) Approval. No person shall erect, construct, or operate a public water system, nor undertake substantial enlargements, extensions, additions, modifications, renovations or repairs to any public water system, including storage, distribution, purification, or treatment components, without having first secured the Division's approval of: the source of water supply; the means and methods of treating, purifying, storing and distributing said water; and obtaining a permit to operate a public water system, except as provided by paragraph (2) of this Rule. The approval of the Director must be obtained prior to the dividing of a public water system. For purposes of these rules "substantial" as used in this Rule shall not include routine maintenance.
(2) Limited Additions. Governmentally owned public water systems and water authorities and privately owned community water systems whose owners serves a combined population of greater than 10,000, with qualified staff and meeting operating criteria developed by the Division may, with prior approval from the Division, approve limited additions to the water system. These additions will be limited to water distribution lines to serve subdivisions, apartment complexes and shopping centers. The review of other additional types of water distribution system additions and/or extensions may be delegated to those water systems that have demonstrated the capability for such reviews. All delegations shall be by written agreement. Additions approved by the water system must be reported annually in a format prescribed by the Division. The report shall be due by July 1 of each year and describe additions approved in the previous calendar year.
(3) Local Governmental Approval. Before a person may initiate construction of a new public water system or increase the capacity of an existing public water system, the person shall notify the local government in which the system is located and obtain the local government's approval for development of the project within its jurisdiction, prior to the submittal of the plans and specifications to the Division for approval. To the extent practicable, the person should avoid locating part or all of the new or expanded facility at a site which:
(a) is subject to a significant risk from earthquakes, floods, fires or other disasters which could cause a breakdown of the public water system or a portion thereof; or
(b) except for intake structures, is within the floodplain of a 100- year flood or is lower than any recorded high tide where appropriate records exist; or
(c) is on or in close proximity to an abandoned landfill or any other site used for waste disposal.
(4) Connect to Local Governmental Public Water System. Any person who desires to own or operate or who desires to commence the operation of a public water system shall first evaluate connecting to an existing local governmentally owned and operated public water system.
(5) Approval for No Connection to Local Governmental Public Water System. No approval of the plans and specifications for the development of a separate source of water supply or the construction of the water system will be made and no permit to operate will be issued until the owner has provided acceptable certification to the Division outlining the reasons why the system cannot connect to an existing local governmentally owned water system.
(6) Pre-Operating Compliance Conditions. Beginning January 1, 1998, the Division shall require compliance with the following conditions prior to the issuance of the initial permit to operate to a new privately owned community public water system:
(a) The owner shall provide written certification from the local government in which the system is located, that the local government is in concurrence with the development of the privately owned public water system. The certification shall be provided to the Division with the submission of the permit application and prior to or concurrently with the submission to the Division of the plans and specifications for construction of the proposed public water system.
(b) The owner must retain a Professional Engineer, registered in the State of Georgia, to prepare plans and specifications for approval by the Division for the construction of the proposed public water system, and the owner shall submit to the Division a certification from the engineer that the water system was constructed according to the plans and specifications approved by the Division. The public water system must be designed and constructed in accordance with the Division's "Minimum Standards for Public Water Systems", latest edition.
(c) The owner must provide an approved back-up water source, such as an additional well, capable of providing adequate water service if the primary source becomes nonfunctional. The requirement for an approved back-up water source may be waived by the Director for systems with less than 25 service connections.
(7) Treatment Products and Materials. Products added directly to drinking water for its treatment or introduced indirectly into drinking water through its contact with surfaces of materials or products used for its treatment, storage, transmission, or distribution shall not adversely affect drinking water quality and public health.
(a) All treatment chemicals that come into contact with drinking water shall be certified for conformance with American National Standards Institute/National Sanitation Foundation Standard 60 (ANSI/NSF Standard 60) by an American National Standards Institute (ANSI) approved third-party certification program or laboratory.
(b) All products that come into contact with drinking water during its treatment, storage, transmission or distribution shall be certified for conformance with American National Standards Institute/ National Sanitation Foundation Standard 61 (ANSI/NSF Standard 61) by an American National Standards Institute (ANSI) approved third-party certification program or laboratory.
(8) Infrastructure Security. Public water systems must provide appropriate measures to protect and secure its critical drinking water supply infrastructure, including its water source, treatment, distribution, and any other component that is deemed pertinent to the safe operation and maintenance of the drinking water supply system.
(9) Performance Bond or Letter of Credit
(a) A performance bond or letter of credit may be required by the director to further assist in the assurance that a public water system serving year-round residents maintains compliance with the established contaminant levels and the provision of an adequate supply of water at or above the required minimum pressure. Such a performance bond or letter of credit shall be required of the owner or operator of any public water system serving year-round residents if:
1. After the first violation of contaminant or water supply standards or requirements, the owner or operator of the public water system fails to make the necessary corrections after receiving a notice from the director specifying:
(i) The corrections which must be made; and
(ii) A reasonable period of time for the completion of necessary corrective action; or
2. After a second violation of contaminant or water supply standards or requirements, the director makes a determination, based on factors such as past performance, frequency and severity of violations, and timeliness of corrective action, that a performance bond or letter of credit is required.
(b) Any owner or operator of a public water system serving year-round residents who is required to obtain a performance bond or letter of credit pursuant to subparagraph (9)(a) shall file with the director the following:
1. A performance bond, payable to the director and issued by an insurance company authorized to issue such bonds in this state; or
2. An irrevocable letter of credit, issued in favor of and payable to the director, from a commercial bank or other financial institution approved by the director.
(c) The bond or letter of credit required in subparagraph (9)(a) shall be:
1. Conditioned upon faithful compliance with the Georgia Safe Drinking Water Act of 1977, the Rules for Safe Drinking Water Chapter 391-3-5, and the conditions and terms of the permit issued for the operation of the public water system;
2. In such amount as determined by the director as necessary to ensure the continued lawful operation of the public water system for a period up to ten years in the event the owner or operator fails to do so; provided, however, the range shall be as follows:
(i) Systems with 25 service connections or less - an amount not to exceed $30,000.00;
(ii) Systems with 26 to 50 service connections - an amount not to exceed $40,000.00; or
(iii) Systems with more than 50 service connections - an amount not to exceed $50,000.00;
3. Subject to termination or expiration only upon 120 days' written notice to the director; and
4. Conditioned upon coverage for any violation occurring during the term of the bond or letter of credit of which written notice has been given to the owner or operator prior to 120 days after said term even though the initial or final determination of the violation occurs after the term of the bond or letter of credit.
(d) If an existing bond or letter of credit is to expire or terminate, the owner or operator of the public water system shall file a replacement bond or letter of credit meeting the requirements of this paragraph at least 60 days prior to the termination or expiration of the existing bond or letter of credit.
(e) Upon a determination by the director that an owner or operator has violated the Georgia Safe Drinking Water Act of 1977, the Rules for Safe Drinking Water Chapter 391-3-5, or the terms or conditions of a permit, the director may, after written notice of the violation to the owner or operator:
1. Forfeit or draw that amount of such bond or letter of credit that the director determines necessary to correct the violations determined and continue the lawful operation of the public water system; and
2. Expend such amount for such purposes.
(f) No action taken by the director pursuant to this paragraph, including the forfeiture of a bond or the drawing of funds from a letter of credit, shall relieve the owner or operator of a public water system from compliance with all provisions of this part, including the requirement to maintain in full force and effect a bond or letter of credit meeting the requirements of this paragraph.
(g) Every permit issued under the Rules for Safe Drinking Water, Chapter 391-3-5, shall be conditioned upon compliance with this paragraph.
(h) The provisions of this paragraph shall not apply to:
1. Any public water system of the state, an agency of the state, a county, a municipality, or of any other political subdivision or governmental entity;
2. Any water system owned by a church or other religious institution;
3. Any water system owned or provided by an employer and used primarily to serve employees; and
4. Any water system which is jointly owned by private individuals who are the users of the water supplied by the system.
(10) Business Plan. Beginning January 1, 1998, prior to the issuance of the initial permit to operate to a new community public water system, and beginning October 1, 1999, prior to the issuance of the initial permit to operate a new non transient, noncommunity water system, the Division shall require the owner to submit to the Division for approval a multiyear business plan. The multiyear business plan must adequately demonstrate the water system's managerial and financial capacity to comply with all drinking water regulations in effect, or likely to be in effect. The business plan shall be prepared in accordance with the latest edition of the Division's "Minimum Standards for Public Water Systems." The business plan shall be updated at intervals determined by the Director.

Rule 391-3-5-.05 Preparation and Submission of Engineering Reports, Plans and Specifications for Public Water Systems

(1) General Provisions. For any activity listed in paragraph (1) of Rule 391-3-5-.04 an engineering report prepared by a professional engineer shall be submitted to the Division prior to the preparation of the final construction plans and specifications. Plans and Specifications shall be prepared by a professional engineer and submitted to the Division, accompanied by a letter of submittal identifying the project, owner and owner's address. No construction shall be initiated without prior approval from the Division. The engineering report and/or plans and specifications may be waived by the Director when information submitted by the supplier of water allows an engineering appraisal of the proposed activity to be made by the Division as follows:
(a) For minor extensions, additions and/or modification to an existing governmentally owned public water systems which do not affect the normal operation of said water system.
(b) For new public water systems which are classified as transient non-community water systems and for additions to existing transient non-community water systems.
(2) Engineering Report. The Engineering report shall contain a comprehensive description of the proposed activity including, but not limited to the following:
(a) scope and description of proposed activity;
(b) description of the proposed source of water supply, and data concerning the quality of the water;
(c) pertinent information regarding present available sources of water supply, water treatment facilities, and existing public water systems;
(d) sufficient maps, diagrams, charts, tables, calculations, basis of design data and graphs to make the reports readily understandable; all sheets shall be descriptively labeled and bound together or folded in a folder attached to the report;
(e) operational and maintenance program description;
(f) the known character and depth of the natural earth formations through and from which groundwater sources are to developed;
(g) factors which may affect the quality of a source of water supply as determined by a survey of the water shed above the surface water intake or the surrounding area of a groundwater source.
(3) Minimum Standards. Beginning January 1, 1998, all new, additions, or extensions to public water systems shall be designed and constructed in accordance with the latest edition of the Division's "Minimum Standards for Public Water Systems".
(4) Plans and Specifications. Plans and specifications must be submitted with additional copies as may be requested, and shall include, but not be limited to the following:
(a) map plans of the area to be served by the public water system, including, but not limited to: geographical location of the project, location of all existing and proposed streets in the area to be served, location of the source of water supply and the treatment facilities, and elevations of the principal parts of the public water system;
(b) detailed plans of the location and the construction of the storage tank, water mains, valves, fire hydrants and appurtenances;
(c) detailed plans of: the location and construction of the water treatment facilities including layout and relationship of the various units of the treatment facility; general piping, pumps, reservoirs, flow measuring devices, controls, points of chemical application, water sampling points, plant control laboratory, chemical feed equipment and chemical storage area. Sufficient dimensions and elevations shall be provided to make all parts of the readily understandable.
(d) the dimensions of the plan sheets must be within the following limits: twenty (20) to thirty (30) inches in height and twenty-four (24) to forty-two (42) inches in length;
(e) each plan sheet shall have printed thereon the name and location of the public water system, name and registration stamp of the professional engineer, scale, true and magnetic north, and shall be bound together and numbered consecutively;
(f) if the plans are solely for extensions to an existing public water system, only such information as is necessary for comprehension of the plans and construction of the project will be required;
(g) specifications will be separate from the plans and shall have printed thereon the name and location of the public water system, name and stamp of the professional engineer, and shall be bound together and numbered consecutively;
(h) specifications for the construction of the public water system shall accompany all plans for new or existing public water systems and shall describe the plans for the whole and for each unit or component of construction of the proposed public water system, including where necessary, testing and disinfection, painting, laboratory equipment, metering and recording devices and related material;
(i) the specifications may be omitted for extensions or additions to existing systems provided the proposed construction is in accordance with specifications previously approved and on file with the Division;
(j) manufacturers' brochures of specifications of materials are not acceptable for purposes of this requirement.
(5) Deviations from Approved Plans. Any significant deviation from the approved plans or specification must receive prior approval by the Division.
(6) Installation According to Plans and Specifications. Upon completion of the installation of the public water system or any modification, the owner must send to the Division a statement from the engineer who prepared the plans and specifications that the system, as installed, is in accordance with the approved plans and specifications.
(7) Integrity of Treatment Units or Equipment. Approval of plans and specifications by the Division does not include approval of the structural, electrical, mechanical, or design integrity of the treatment units or equipment.
(8) Construction Without Division Approval. At the discretion of the Director, an existing public water system that is constructed without obtaining prior approval from the Division may be considered acceptable by the Director, provided all of the following are accomplished to the satisfaction of the Division:
(a) An engineering evaluation of the constructed facilities is made by a professional engineer, licensed in the state of Georgia, to evaluate and certify conformance of the constructed facilities with all of the applicable paragraphs of the rules in this Chapter. The engineer's certification, along with the "as-built" plans and specifications must be submitted to the Division for review and comment.
(b) All items, data, documentation and information required for source approvals and permit issuances for a public water system, as stated in the rules of this Chapter, must be submitted to the Division. Any additional and/or corrective action that is required by the Division for the owner or operator of the system to complete, prior to issuance of the permit, must be accomplished within ninety (90) days from the date of notification by the Division.

Rule 391-3-5-.06 Source of Water Supply

(1) Source of Water Supply. The source of water supply for all public water systems must have the approval of the Division and a valid ground water (Ground Water Use Act of 1972, as amended) or surface water (Georgia Water Quality Control Act of 1977, as amended) withdrawal permit where applicable. Beginning January 1, 1998, all owners and operators of new community public water systems with groundwater sources must provide an approved back-up water supply source, capable of providing adequate water service, if the primary source becomes nonfunctional. The Director may waive this requirement for systems with less than 25 service connections. Beginning December 1, 2009, any new ground water source must provide treatment that reliably achieves at least 4-log (99.99%) treatment of viruses before or at the first customer.
(a) All sources of water supply must be adequate as determined by the Division to meet anticipated growth. For human consumption in a community water system, one hundred (100) gallons per day for the projected population to be served at the end of the design period shall be considered adequate.
1. Beginning January 1, 1998, all new sources constructed for water supply systems, that are required to comply with the rules in this Chapter, shall be metered.
2. Beginning January 1, 1999, permitted water systems shall meter their existing water supply sources, when required by the Division or when the system's existing permit to operate a public water system is renewed or modified.
(b) The water must be of such quality that with reasonable treatment it will meet the Safe Drinking Water Rules of this Chapter.
(c) Before approval of a surface water source the following procedures and requirements must be met:
1. Raw water samples from the proposed source shall be collected by the supplier or designee and submitted to a certified laboratory for microbiological analysis for the period of time and frequency specified by the Division.
2. The supplier shall have the water from the proposed source analyzed for the physical, chemical and radiological parameters specified by the Division in a laboratory acceptable to the Division and shall furnish a copy of the results of the analysis to the Division.
3. For an impoundment source, allowance must be made for water losses including required releases, evaporation, seepage and siltation. Available stream flow and weather records must be used in estimating the yield of the source.
4. For water supply reservoirs, a reservoir management plan shall be developed in accordance with Rule 391-3-16-.01(8).
5. A Source Water Assessment Plan (SWAP) for the proposed surface water source intake must be developed in accordance with the Division's Source Water Assessment and Protection Implementation Plan for Public Drinking Water Sources, as outlined in Section 391-3-5-.42 of this Chapter.
(d) Before approval of a ground water source, whether from a well or a spring, the following procedures and requirements must be met:
1. Raw water samples of the proposed source shall be collected by the supplier and submitted to a laboratory certified by the Division for microbiological analysis for a period of time and frequency specified by the Division.
2. The supplier shall, when directed by the Division, have the water from the proposed source analyzed for the physical, chemical and radiological parameters specified by the Division in a laboratory acceptable to the Division and shall furnish a copy of the results of the analysis to the Division.
3. Any drilled well previously used as a source of public water supply but inactive for three or more years and proposed to be reactivated as a source of supply shall be test pumped and meet the requirements of subparagraphs 1. and 2. of this paragraph.
4. A Source Water Assessment Plan (SWAP) for the proposed ground water source must be developed, as applicable, in accordance with the Division's Source Water Assessment and Protection Implementation Plan for Public Drinking Water Sources, as outlined in Section 391-3-5-.42 of this Chapter.
(e) The Division may direct that a ground water source be evaluated for the influence of surface water. Within eighteen (18) months of Division notification that a ground water source is under the direct influence of surface water, the supplier shall install filtration treatment and may be required by the Division to install additional treatment in accordance with subparagraph (a) of Rule 391-3-5-.09.

Rule 391-3-5-.07 Wells

(1) Approval. No person shall construct a well as a source of water supply for a public water system without having first obtained approval from the Division. This requirement may be waived by the Director during emergency situations. Any well that is constructed and does not meet the rules of this Chapter shall not later be used as a drinking water source for a public water system.
(2) Prohibited Wells. Dug, bored, or jetted wells are prohibited for all new public water systems.
(3) Protection from Contamination. Each well must be protected from contamination by surface waters and other sources of contamination. The location of wells must be in compliance with the latest edition of the Division's "Minimum Standards for Public Water Systems."
(4) Fill, Plug and Seal. Whenever a bore hole of any depth is excavated for, but not used as a source of water supply it shall be the supplier's responsibility to fill, plug and seal the hole within thirty (30) days of the excavation in a manner approved by the Division to restore as nearly as possible the natural earth condition existing before the hole was excavated and to protect against contamination of the ground water. This paragraph shall not apply where some other use is made of the ground water from the well hole.
(5) Well Construction Standards. All wells must be constructed as hereinafter provided, however, deviations from these rules may be permitted or required by the Division due to the variable conditions of the subsurface and ground water quality in a specific area.
(a) Drilling fluids must be from an uncontaminated source or must be disinfected.
(b) All permanent casing, liners, screens and other manufactured material used in the well installation must be new and adequate to protect the well against entrance of contaminants during the expected life of the well. All casing and liner pipe joints shall be water tight the entire length in drilled wells.
1. Steel pipe well casing shall conform to American Society for Testing and Materials (ASTM) Specification A 53, American Petroleum Institute (API) Specification 5L, or equal standard, and meet the following minimum wall thickness unless otherwise approved by the Division.

Nominal Casing Diameter (inches)

Minimum Wall Thickness (inches)

4

0.237

5

0.258

6

0.280

8

0.322

10

0.365

12

0.375

14

0.375

16

0.375

18

0.375

20

0.375

24

0.500

26

0.500

2. The use of plastic well casing and screens must be approved by the Division prior to well installation. The well casing and couplings shall meet the requirements of the ASTM Standard F 480 or equal standard and the National Sanitation Foundation for use with potable water. When approved for use by the Division, plastic well casing shall conform to the following minimum wall thickness. However, plastic well casing diameters of 12 inches or greater or deep wells may require greater wall thickness to meet the collapse strength requirements.

Nominal Casing Diameter (inches)

Minimum Wall Thickness (inches)

4

0.265

4.5

0.291

6

0.390

8

0.508

10

0.632

12

0.750

Plastic well casing and screen shall not extend to a depth of greater than 300 feet below the ground surface.
(c) The outer, permanent, protective casing shall extend at least five (5) feet into the first solid, unweathered or impervious subsurface rock strata encountered, and shall have a minimum length of twenty-five (25) feet from the ground surface into a well excavated into water-bearing formations in crystalline rocks and fifty (50) feet in a well excavated into sedimentary water-bearing formations. The outer, permanent, protective casing shall be cement grouted its entire length with a cement slurry consisting of not more than six (6) gallons of water to one cubic foot cement, plus standard additives, when necessary, to facilitate placing or setting and shall be placed under pressure from the bottom of the annular space to be grouted upward until the grout is extruded at the earth's surface. The wall thickness of the cement grout surrounding the outer, permanent, protective casing shall be not less than one and one-half (1-1/2) inches at any point. Subsurface well construction shall cease for at least twenty-four (24) hours after grouting. Other grouting materials for sealing the annular space may be used upon the approval of the Division prior to well construction.
(d) Any ground water of unacceptable quality encountered during the well construction must be sealed off.
(e) The gravel for gravel-packed wells must be washed, free of organic matter, and composed of well rounded particles.
(6) Stoppage During Construction. During the periods of stoppage of the well construction and when the site is unattended, the drilling contractor must have the well opening securely covered to prevent tampering and possible contamination.
(7) Sanitary Conditions. During the well construction, the premises, construction material, tools and equipment must be maintained in a sanitary manner to prevent contamination of the well by the person excavating the well.
(8) Proper Well Development. Every well must be properly developed, disinfected, and pump tested by the drilling contractor. The well must be test pumped at not less than the desired yield for a period of at least twenty-four (24) hours and shall continue for at least four (4) hours after the pumping level has stabilized. The static water level, drawdown and pumping water level must be measured.
(9) Disinfection of the Well.
(a) The well must be disinfected prior to the pumping test by the introduction of a chlorine solution into the well under sufficient pressure to overcome the natural flow pressures of all developed water-bearing zones, and in sufficient quantity to produce a minimum chlorine residual of fifty (50) parts per million in six (6) hours after such application.
(b) After disinfection, the well must be pumped until no trace of chlorine remains in the water, and water samples taken for microbiological analysis. No water may be furnished for human consumption until samples of water are collected by the supplier, and submitted to the Division for microbiological examination, and the quality of the water approved by the Division. If the water samples submitted are found to be unsatisfactory, the disinfection procedure must be repeated as required by the Division.
(c) The permanent pump and pumping equipment shall be disinfected with a chlorine solution prior to being placed into service.
(d) Well disinfection shall be conducted in accordance with American Water Works Association (AWWA) Standard C654.
(10) Licensed Water Well Contractor. The person constructing the well shall be a licensed water well contractor in the State of Georgia in accordance with the provisions of the Water Well Standards Act of 1985 (O.C.G.A. § 12-5-120, et. seq.). The contractor must maintain accurate driller logs, material setting and grouting data, complete results of the pump test, including water level measurements, and must furnish a signed copy of the results to the owner and to the Division on forms provided by the Division.
(11) Installation Standards. A well used as a source of water supply must include the following:
(a) A concrete slab with a minimum thickness of six (6) inches shall be constructed around the well casing and shall extend at least two (2) feet in all directions, and slope away, from the casing.
(b) The well casing shall extend at least twelve (12) inches above the concrete slab of the floor.
(c) For submersible pump installations, the well casing shall be provided with a sealed cover plate and, when required by the Division, vented by a screened riser pipe so that the screened opening terminated downward at least twelve (12) inches above the top of the casing or ground level.
(d) For turbine pump installations, a concrete block to support the pump motor shall be constructed around the outer well casing and shall extend at least twelve (12) inches above the concrete slab, and:
1. the outer casing shall extend at least one (1) inch above the pump motor block;
2. the well head and pump base shall be sealed to prevent seepage and the casing shall be vented by a screened riser pipe so that the screen opening terminates downward and above any point of back flow of contaminants into the well; and
3. oil lubricated vertical turbine pumps shall be lubricated with an acceptable turbine oil as prescribed by the pump manufacturer.
(e) A raw water sampling tap shall be installed prior to the well discharge pipe check valve.
(f) An access port of not less than five-eights (5/8) inch in diameter, with screw cap, for water level measurements; a deep well air line and gage may also be used in conjunction with the access port.
(12) Deepening Existing Wells. Existing wells that are deepened shall be regarded by the Division as a development of a new ground water source and must meet the requirements for approval.
(13) Rehabilitating Existing Wells. When an existing well is rehabilitated or reworked, the well shall be disinfected according to procedures described in this Rule.
(14) Infrastructure Security. The pumping and water treatment equipment shall be protected from unauthorized entry and use by an enclosed shelter or enclosed by a fence. In addition, the water treatment equipment shall be enclosed in a weather proof shelter.

Rule 391-3-5-.08 Springs

(1) Enclosure Required. A spring to be used as a source of water supply for a public water system must be protected by an enclosed structure. The walls of the structure must extend down to bedrock, or into the soil sufficiently to provide for a proper foundation to prevent surface water infiltration.
(2) Runoff Diversion. All surface water runoff must be diverted from the spring.
(3) Surface Water Entry. The spring must be protected from any entry of surface water.
(4) Overflow. The overflow from the spring's enclosed structure must be designed to prevent entrance of contaminants or animals.
(5) Facility Enclosure. The pumping and water treatment facilities must be enclosed in shelters that are of weather and vandal-proof construction.
(6) Infrastructure Security. The spring area must be secured as specified by the Division to prevent unauthorized entry.

Rule 391-3-5-.09 Water Treatment Facilities

(1) Water Treatment Facility Requirements. All means and methods of treating, purifying and storing water for public water systems must be approved by the Division. The Division shall consider, but not be limited to, the following requirements when evaluating water treatment facilities for a public water system:
(a) Surface water treatment plants and ground water treatment plants must be of such design and capacity to provide for the required treatment of the raw water so that the drinking water will comply with the rules of this Chapter. In addition, surface water treatment plants and plants treating ground water under the influence of surface water must provide facilities for filtration of the raw water, and must provide, when required by the Division, flocculation and sedimentation of the raw water and continuous coagulation or application of other filter aids for optimization of filter performance.
1. Water treatment plants processing surface water sources shall include, but not be limited to, means for rapid mixing, flocculation, sedimentation, filtration and disinfection. The treatment plant shall be of such construction to allow units to be taken out of service without disrupting operation and required treatment processes.
2. Based upon the quality of raw water, the quality desired in the finished water and other factors, multiple-stage treatment facilities and/or presedimentation facilities, shall be provided when required by the Division.
(b) The Division may accept new and alternate treatment means, methods and technologies, provided the following are demonstrated to the satisfaction of the Division:
1. The treatment method has been thoroughly tested in full scale comparable installations by an acceptable third party, in accordance with protocol and standards acceptable to the Division.
2. The treatment method has been thoroughly tested in a pilot plant approved by the Division, by an acceptable third party, in accordance with protocol and standards acceptable to the Division, and operated for a period that will demonstrate the effectiveness and reliability of the proposed treatment system during changes in seasonal, and climatic conditions.
3. Compliance with the treatment technique requirements of paragraph (1)(p).
(c) Water from a spring shall be disinfected and retained in a detention tank for a minimum of thirty (30) minutes unless otherwise approved by the Division; and such additional water treatment as the Division may require for the drinking water to comply with the rules of this Chapter.
(d) Chemical feed equipment shall be of such design and capacity to accurately supply, at all times, the treatment chemicals required.
(e) Chlorination equipment may be solution-feed-gas-type but must have sufficient feed capacity for the treatment of the raw water and drinking water to maintain a chlorine residual in the drinking water as required by paragraph (2) of Rule 391-3-5-.14.
(f) Gas chlorination equipment and cylinders must be housed in a separate room or facility provided for that purpose, separated from the other treatment facilities and chemicals. The following shall be required:
1. Chlorine cylinders stored or used outdoors must be protected from the direct rays of the sun by shading and additionally protected to prevent unauthorized tampering.
2. Chlorine cylinders must be secured from accidental tipping or movement.
3. A chlorine gas mask or self-contained gas mask (air pack) must be provided outside the gas chlorine room or facility or otherwise made available and be readily accessible to the operator for repairs or emergencies.
4. Forced air ventilation, placed near floor level and near the cylinders, must be provided to exhaust any leaking chlorine gas from a confined room or facility. Exhaust fumes must be directed away from the entrance to the room or facility. The fan must be activated by an outside switch or start automatically when the door is opened.
5. A small bottle of fresh ammonia solution shall be provided for testing for chlorine gas leaks.
(g) Hypochlorite feeders are not required to be placed in a separate room or facility.
(h) Other means of disinfection such as iodine, ultra-violet light, or ozone treatment may be approved by the Division.
(i) There must be sufficient space for chemical storage.
(j) Fluoridation equipment and chemicals, where used, must be placed in a separate room or facility provided for that purpose, unless otherwise approved by the Division.
(k) Each water treatment facility must have, as may be required by the Division, a laboratory and laboratory equipment to perform daily tests pertinent to the proper control of the required water treatment operations.
(l) Water sampling taps shall be placed in the water treatment facility, as may be required by the Division, for obtaining water samples to perform laboratory tests to ensure the proper functioning of the water treatment facility.
(m) A metering device to measure the flow of raw water and/or treated water is required for all surface water treatment plants and all new wells serving public water systems.
(n) Water from a well used as a source of water supply shall be disinfected unless otherwise approved by the Division and such additional water treatment as the Division may require for the drinking water to comply with the rules of this Chapter.
(o) Chemical water treatment equipment must be installed in such a manner to prevent back-siphonage or overdosing of the chemicals to the water supply.
(p) Each public water system with a surface water source or a ground water source under the direct influence of surface water must provide treatment of that source water that complies with these treatment technique requirements. The treatment technique requirements consist of installing and properly operating water treatment processes which reliably achieve:
1. At least 99.9 percent (3-log) removal and/or inactivation of Giardia lamblia cysts between a point where the raw water is not subject to recontamination by surface water runoff and a point downstream before or at the first customer; and
2. At least 99.99 percent (4-log) removal and/or inactivation of viruses between a point where the raw water is not subject to recontamination by surface water runoff and a point downstream before or at the first customer.
3. At least 99 percent (2-log) removal of Cryptosporidium between a point where the raw water is not subject to recontamination by surface water runoff and a point downstream before or at the first customer for filtered systems. This treatment technique requirement is applicable to Subpart H systems serving at least 10,000 people, beginning January 1, 2002, and to systems serving fewer than 10,000 people, beginning January 14, 2005.
(q) Effective June 29, 1993, each public water system with a surface water source or a ground water source under the direct influence of surface water source shall conduct continuous monitoring of the residual disinfectant concentration of the water entering the distribution system. The continuous online chlorine analyzer shall be calibrated in accordance with EPA Method 334.0. Systems must record the results of the residual disinfectant monitoring every fifteen (15) minutes, and record and report the lowest value each day, except if there is a failure in the continuous monitoring equipment, grab sampling every 4 hours may be conducted in lieu of continuous monitoring, but for no more than 5 working days following the failure of the equipment, and systems serving 3,300 or fewer persons may take grab samples in lieu of providing continuous monitoring on an ongoing basis at the frequencies each day prescribed below:

Population Served

Samples per day1

500 or fewer

1

501 to 1,000

2

1,001 to 2,500

3

2,501 to 3,300

4

Note: 1 The day's samples cannot be taken at the same time. The sampling intervals are subject to Division review and approval. The residual disinfectant concentration in the water entering the distribution system cannot be less than 0.2 mg/L for more than four hours. If at any time the residual disinfectant concentration falls below 0.2 mg/L in a system using grab sampling in lieu of continuous monitoring, the system must take a grab sample every 4 hours until the residual disinfectant concentration is equal to or greater than 0.2 mg/L.

1. Maintenance of the disinfectant residual in the distribution system must conform to paragraph (2) of Rule 391-3-5-.14.
2. Until March 31, 2016, the residual disinfectant concentration must be measured at least at the same points in the distribution system and at the same time as total coliforms are sampled, as specified in 40 CFR § 141.21
3. Beginning April 1, 2016, the residual disinfectant concentration must be measured at least at the same points in the distribution system and at the same time as total coliforms are sampled, as specified in Rule 391-3-5-.55(4) through (8). The Division may allow a public water system which uses both a surface water source or a ground water source under the direct influence of surface water, and a ground water source, to take disinfectant residual samples at points other than the total coliform sampling points if the Division determines that such points are more representative of treated (disinfected) water quality within the distribution system. Heterotrophic bacteria, measured as heterotrophic plate count (HPC) as specified in 40 CFR § 141.74(a)(1), may be measured in lieu of residual disinfectant concentration.
(r) Filter backwash recycling requirement: 40 CFR § 141.76 is hereby incorporated by reference. All subpart H systems that employ conventional filtration or direct filtration treatment and that recycle spent filter backwash water, thickener supernatant, or liquids from dewatering processes must meet the requirements in paragraphs (b), (c) and (d) of 40 CFR § 141.76.
1. Treatment technique requirement. Any system that recycles spent filter backwash water, thickener supernatant, or liquids from dewatering processes must return these flows through the processes of a system's existing conventional or direct filtration system as defined in 40 CFR § 141.2 or at an alternate location approved by the Division by June 8, 2004. If capital improvements are required to modify the recycle location to meet this requirement, all capital improvements must be completed no later than June 8, 2006.
2. Record keeping. The system must collect and retain on file recycle flow information specified in paragraphs (d)(1) through (6) or 40 CFR § 141.76 for review and evaluation by the Division beginning June 8, 2004.

Rule 391-3-5-.10 Distribution System

(1) Design for Flow and Pressure. The water distribution system must be designed and the water lines sufficiently sized to furnish at all times the instantaneous demand flow of water required and to maintain at all times a pressure of twenty (20) pounds per square inch at each service connection in the distribution system under all conditions of flow.
(2) Looped Lines. Distribution lines must be looped whenever possible.
(3) Metering. Beginning January 1, 1998, all new services connected to community and non-transient non-community water systems shall be metered, unless specifically directed otherwise by the Director. For existing water systems, metering of existing services shall be performed when required by the Director.
(4) Prevent Contamination. It is the responsibility of the supplier of water to maintain the distribution system to prevent contamination of the drinking water and to provide the required pressure and flow at all times.
(5) Minimum Pipe Size. The minimum size water main shall be two (2) inches in nominal diameter. The Division may allow for a departure in sizing provided it is justified by hydraulic analysis and future water use of the area to be served and such departures will be considered only in special circumstances.
(6) Lines in Contaminated Areas. Water lines must not be installed in contaminated areas such as sanitary landfill or dump areas.
(7) Sewer Line Contact. No water main or pipe shall pass through or come into contact with any part of a sewer or sewer manhole.
(8) Minimum Cover. The minimum recommended cover for water distribution mains or lines shall be twenty-four (24) inches.
(9) Installation Requirements. All newly installed distribution mains and appurtenances shall be flushed, pressure tested and disinfected.
(10) Lead Free.
(a) For purposes of this rule, the term "lead free" means:
1. not containing more than 0.2 percent lead when used with respect to solder and flux; and
2. not more than a weighted average of 0.25 percent lead when used with respect to the wetted surfaces of pipes, pipe fittings, plumbing fittings, and fixtures.
(b) The weighted average lead content of a pipe, pipe fitting, plumbing fitting, or fixture shall be calculated by using the following formula: For each wetted component, the percentage of lead in the component shall be multiplied by the ratio of the wetted surface area of that component to the total wetted surface area of the entire product to arrive at the weighted percentage of lead of the component. The weighted percentage of lead of each wetted component shall be added together, and the sum of these weighted percentages shall constitute the weighted average lead content of the product. The lead content of the material used to produce wetted components shall be used to determine compliance with paragraph (a). For lead content of materials that are provided as a range, the maximum content of the range shall be used.
(c) When used with respect to plumbing fittings and fixtures intended by the manufacturer to dispense water for human ingestion refers to fittings and fixtures that are in compliance with standards established in accordance with 42 U.S.C. 300g-6(e).
(d) This term does not apply to leaded joints necessary for the repair of cast iron pipes.
(11) Notification of Lead-containing Service Lines. Suppliers of water shall identify and report to the Division any lead pipe and/or lead service connections known to be installed in the distribution system. Suppliers shall adopt a local plumbing code that requires use of lead free solder for plumbing.
(12) Infrastructure Security. Public water distribution network and its related components must be protected to prevent unauthorized tampering.

Rule 391-3-5-.11 Storage Tanks

(1) Tank Requirements. All storage tanks must be provided with a permanent cover, screened vents and openings, overflow piping and means of draining.
(2) Interior Paint. The paint used for the interior of a storage tank must be approved by the Division.
(3) Approval for Repairs. Repairs and renovations to existing storage tanks that may affect the quality of the drinking water must receive approval from the Division prior to starting such work. Upon completion of such work the storage tank must be disinfected according to Rule 391-3-5-.12.
(4) Contamination Prevention. It is the owner's responsibility to maintain the storage tank or tanks to prevent contamination of the drinking water by infiltration or other means.
(5) Buried Tanks. Buried or semi-buried storage tanks must have the ground surface sloping away from the facility.
(6) Pressure Tanks. Hydropneumatic pressure tanks must be provided with devices for maintaining the air-water volume at the designed water level and working pressures.
(7) Pre-Service Requirements. All new storage tanks must be cleaned, tested for leakage, and must be disinfected according to Rule 391-3-5-.12.

Rule 391-3-5-.12 Disinfection

(1) Disinfection Requirements. All newly constructed public water systems including extensions, additions, modifications, or repairs to existing public water systems including water mains, storage tanks, treatment plants, wells, or any other pipes or parts of the public water system which may affect the quality of the drinking water which is delivered, treated or stored, must be disinfected before being placed into service by the supplier or water by one of the following methods:
(a) Water mains. Any new or repaired water main must be disinfected in accordance with the latest edition of American Water Works Association (AWWA) Standard C651.
(b) Storage facilities. Any new or repaired water storage facility must be disinfected in accordance with the latest edition of American Water Works Association (AWWA) Standard C652.
(c) Water treatment plants. Any new or repaired portion of a water treatment plant must be disinfected in accordance with the latest edition of American Water Works Association (AWWA) Standard C653.
(d) Wells. Any new well or existing well that has been rehabilitated or reworked must be disinfected in accordance with the latest edition of American Water Works Association (AWWA) Standard C654.
(e) Any system required to develop a disinfection profile in accordance with the provisions specified in sections (8)(c)(i) and (ii) of Rule 391-3-5-.20 and that decides to make a significant change to its disinfection practice must consult with the Division prior to making such change. Significant changes to disinfection practice are: changes to the point of disinfection; changes to the disinfectant(s) used in the treatment plant; changes to the disinfection process; and, any other modification identified by the Division. Any system that is modifying its disinfection practice must calculate its disinfection benchmark as specified in section (8)(c)(iii) of Rule 391-3-5-.20.

Rule 391-3-5-.13 Cross Connections

(1) Prohibitions. No person shall construct, maintain or operate a physical arrangement whereby a public water system is or may be connected directly or indirectly with a non-potable water system or non-permitted water system, sewer, drain, conduit, pool, storage reservoir, plumbing fixture, or other device which contains or may contain contaminated water, liquid, gasses, sewage or other waste of unknown or unsafe quality, which may be capable of imparting contamination to the public water system as the results of backflow, bypass arrangements, jumper connections, removable sections, swivel or changeover devices, or other temporary, permanent or potential connections through which or because of which back-flow or back-siphonage could or would occur.
(2) Contamination Prevention. A supplier of water or any person having possession or control of facilities which may cause the contamination of a public water system has the responsibility to prevent water from unapproved sources or any contaminants from entering the public water system by such physical arrangements cited in paragraph (1) of this Section.
(3) Purchasers and Resellers. Any person connecting to and purchasing water from a public water system and reselling it to others is considered a supplier of the water so purchased as well as a consumer, and is also responsible for the quality of such water.
(4) Cross-Connection Control Program. A supplier shall, when requested by the Division, develop a control program for the elimination and prevention of all cross-connections. A written plan for the program shall be submitted to the Division for review and approval within two (2) years or less in accordance with a written request by the Division. When the plan is approved, the owner shall implement the program immediately.
(5) Conformance with National Standards. The procedures for back-flow and back-siphonage prevention and cross-connection control shall conform to those recommended by the American Water Works Association, Manual 14, and the U.S. Environmental Protection Agency Cross-Connection Manual.
(6) Backflow Prevention Assemblies Field Testing. The supplier shall require that all backflow prevention assemblies installed pursuant to this section be field tested following installation, repair, or relocation and at least annually thereafter.
(7) Certified Backflow Testing. After October 1, 2004, all required field testing shall be performed by persons who are certified in the testing of backflow prevention assemblies by the Georgia Statewide Backflow Prevention Assembly Certification Program, as approved by the Division, the American Backflow Prevention Association (ABPA), the American Society of Sanitary Engineers (ASSE) or the University of Florida TREEO Center.
(8) Gauge Accuracy. Gauges used in the testing of backflow prevention assemblies shall be tested for accuracy annually in accordance with the University of Southern California Manual of Cross-Connection Control or American Water Works Association Manual 14. Public water systems shall require testers to include test gauge serial numbers on "Test and Maintenance" report forms and ensure testers have gauges tested for accuracy.
(9) Record Maintenance. Each water supplier shall maintain records of the following for a minimum of three (3) years:
(a) Most current hazard assessment, conducted pursuant to Section 608 of the Georgia State Minimum Standard Plumbing Code (International Plumbing Code);
(b) Locations and types of backflow protection and associated hazards;
(c) Results of all backflow prevention assembly field testing and air gap inspections; and
(d) Repairs made to, or replacement or relocation of, backflow protection.
(e) Summaries of the information in sections (9)(a) - (d) shall be available to the Division on request for a minimum of three years.
(f) The supplier shall ensure that backflow prevention assemblies that fail the field test are repaired or replaced within thirty (30) days.
(g) The supplier shall ensure that bypass piping installed around any approved backflow preventer is equipped with a backflow preventer providing an equivalent level of protection.
(h) Reduced pressure principal backflow prevention assemblies shall not be installed in any location subject to possible flooding. This includes pits and/or vaults which are not provided with a gravity drain to the ground's surface that is capable of exceeding the discharge rate of the relief valve.
(i) Each supplier shall notify the Division of any known incident of backflow into the public water system as soon as possible but no later than the end of the next business day upon discovery of the incident. If requested to do so by the Division, the supplier shall submit a written report of the incident describing the nature and severity of the backflow, the actions taken by the water supplier in response to the incident, and the action plan intended to prevent such incidents in the future.
(j) The supplier of water shall deny or discontinue water service to a commercial consumer if a required backflow prevention device is not installed or properly maintained. Water service shall not be restored to such premises until the deficiencies have been corrected or eliminated to the satisfaction of the supplier and the Division. Residential connections shall be maintained in accordance with the Georgia State Minimum Standard Plumbing Code (International Plumbing Code).

Rule 391-3-5-.14 Operation

(1) Compliance with Safe Drinking Water Rules. A supplier of water shall treat the water supplied so the water complies with the Safe Drinking Water rules of this Chapter. Public water systems shall not use bottled water to achieve compliance with a maximum contaminant level (MCL). Bottled water may be used on a temporary basis to avoid unreasonable risk to health. Community and non-transient non-community water systems shall not use point-of-use or point-of-entry treatment units to achieve compliance with an MCL or a treatment technique requirement.
(2) Continuous Chlorination. The supplier of water must continuously chlorinate the water to maintain a detectable residual of free chlorine in all parts of the distribution system in the recommended amount of at least 0.2 parts per million, and such additional amounts as may be determined necessary by the Division, unless other means of disinfection have been approved by the Director. If the residual disinfectant concentration is measured by approved analytical methods and not detected, the supplier may, upon approval by the Division, determine and report detectability by the use of heterotrophic plate count measurements as required by 40 CFR § 141.72 (1989) and other applicable paragraphs of 40 CFR Part 141.
(3) Disinfection Waiver. After consideration of the microbiological quality of the source of water supply, the local geology, the population served and the extent of the water distribution system, the disinfection treatment may be waived by the Director.
(4) Fluoridation Requirements. The supplier of water of a fluoridated public water system shall daily sample and analyze the fluoride concentration of the drinking water. Daily records of the analytical results shall be kept on forms provided by the Division or on forms acceptable to the Division and a copy of the result submitted to the Division in accordance with Rule 391-3-5-.30.
(5) Surface Water Source Certified Operator. A supplier having a surface water source must have a certified operator on duty and onsite at all times when the water plant is in operation. A supplier having a groundwater source under the direct influence of surface water must have a certified operator on duty and onsite at all times when the water plant is in operation, unless otherwise approved by the Division, depending upon the complexity of the water treatment processes, quality of the water sources, and the size of the system.
(6) Groundwater Source Certified Operator. A supplier having only ground water sources must have a certified operator to comply with the classification prescribed in Section 391-3-5-.39 of this Chapter. The Director may find that the availability of a certified operator to a system with only groundwater sources is sufficient to comply with Section 391-3-5-.39 of this Chapter and may so allow, but only if the Director determines that the complexity of the water treatment processes, quality of the water sources, and the size of the system so warrant.
(7) Record Maintenance. The supplier of water shall maintain daily records of the operation of the water treatment facility and water distribution system as may be required by the Division including the amount of water treated daily, results of the performance of daily tests pertinent to the control of the water treatment processes, disinfectant residuals, and tests performed in the water distribution system. Daily records shall be kept by the supplier on forms furnished by the Division and a copy of the record submitted to the Division in accordance with Rule 391-3-5-.30. Based on the complexity of the water treatment process, the quality of the water sources, and the size of the system, the Director may establish less frequent maintenance of record requirements for small groundwater systems.
(8) Microbiological Laboratory. All community water systems which have a surface water source with water treatment facilities and those public water systems having only a ground water source or only a water distribution system and serving a population of more than 12,900 must have, or have available, the services of a microbiological laboratory certified by the Division to perform the microbiological tests necessary for compliance with the maximum microbiological contaminant levels. The laboratory and equipment must be kept in good working order at all times.
(9) Summary Microbiological Analytical Results. A supplier of water required to have, or have available, a microbiological laboratory under paragraph (8) of Section 391-3-5-.14 shall collect and analyze drinking water samples in accordance with the minimum number specified in paragraph (1) of Section 391-3-5-.23 and such additional samples as may be required by the Director. The supplier shall furnish the Division, on forms provided by the Division, a monthly microbiological summary of the number of samples analyzed and the results in accordance with Section 391-3-5-.30.
(10) Routine Microbiological Samples. The supplier of water shall collect routine drinking water samples for microbiological analysis as follows:
(a) the minimum number of routine samples per month shall be in accordance with paragraph (1) of Section 391-3-5-.23;
(b) at the treatment plant and at various points in the distribution system which are representative of the drinking water when three or more samples per month are required; or
(c) at various points in the distribution system which are representative of the drinking water when only one or two samples per month are required.
(11) Certified Laboratories. For the purposes of determining compliance with Rules 391-3-5-.18, .19, .20, .21, .22, .23, .24, .25, .26, .27 samples may be considered only if they have been analyzed by a laboratory certified by the Division, except that measurements used solely for operational control, including but not limited to turbidity, free chlorine residual, fluoride residual, temperature, pH, conductivity, calcium, alkalinity, orthophosphate, chloramines, chlorine dioxide, chlorite and silica may be performed by any person acceptable to the Division.
(12) Operations and Maintenance Plan. All public surface water and ground water under the direct influence of surface water systems shall develop an Operations and Maintenance Plan (O & M Plan). The plan shall be prepared in accordance with the Division's "Operation and Maintenance Plan - Guidance Manual for Preparing Public Water Supply System O & M Plans", latest edition. The plan shall be updated at intervals determined by the Director. For public groundwater systems and systems that are using alternate treatment technologies, development of such a plan may be required by the Director when the complexity of the water treatment processes, quality of the water sources, and the size of the system so warrant.

Rule 391-3-5-.15 Record Maintenance

(1) Requirements for Records and Retention. Any supplier of water shall retain on its premises or at a convenient location near its premises, the following records:
(a) Records of microbiological analyses and turbidity analyses made pursuant to these rules shall be kept for not less than five (5) years. Records of chemical analyses made pursuant to these rules shall be kept for not less than ten (10) years. Actual laboratory reports may be kept, or data may be transferred to tabular summaries, provided that the following information is included:
1. the date, place and time of sampling and the name of the person who collected the sample;
2. identification of the sample as to whether it was routine distribution system sample, check sample, raw or drinking water sample or other special purpose sample;
3. date of analysis;
4. laboratory and person responsible for performing analysis;
5. the analytical technique/method used; and
6. the results of the analysis.
(b) Records of public notices, certifications of public notices and any actions taken by the system to correct violations of these rules shall be kept for a period not less than three (3) years after either the public notice was issued, certification was submitted or the last corrective action was taken with respect to the particular violation involved.
(c) Copies of any written reports, summaries or communications relating to sanitary surveys of the system conducted by the system itself, by a private consultant, or by any local, state or federal agency, shall be kept for a period not less than ten (10) years after completion of the sanitary survey involved.
(d) Records concerning a variance or exemption granted to the system shall be kept for a period ending not less than five (5) years following the expiration of such variance or exemption.
(e) Any system subject to the lead and copper requirements shall retain on its premises original records of all sampling data, analyses, reports, surveys, letters, evaluations, schedules, Division determinations, and any other information required by Rules 391-3-5-.25 or .30. Each water system shall retain the records required by this rule for no fewer than twelve (12) years.
(f) Systems must maintain the results of individual filter monitoring taken under Rule 391-3-5-.20(7)(c) and (8)(h) for at least three (3) years.
(g) Any system subject to disinfection profiling and benchmarking shall keep the results of the profile and the benchmark (including raw data and analysis) indefinitely.
(h) Copies of monitoring plans developed pursuant to this part shall be kept for the same period of time as the records of analyses taken under the plan are required to be kept under paragraph (1)(a), except as specified elsewhere in this part.

Rule 391-3-5-.16 Fluoridation

All potable water supplies in incorporated communities and counties lying wholly within this State must be fluoridated in compliance with the Act.

Rule 391-3-5-.17 Permit to Operate a Public Water System

(1) Permit Required from the Director. Any person who owns or operates a public water system or who desires to commence operation of a public water system shall obtain a permit from the Director.
(2) Permit Application. Applicants for permits under the Act shall be on forms as may be prescribed and furnished by the Division. The permit application form shall be signed by the owner or their duly authorized agent.
(3) Additional Information. Any applicant for a permit whose application is pending final consideration shall upon the request of the Director provide such additional information as may be necessary to enable the Director to properly pass upon the application. Such additional information may include, but not be limited to, complete engineering report, quantitative and qualitative determinations of the source of water supply and drinking water, plans, specifications, maps, measurements, records, documentation to demonstrate system's financial, technical and managerial capacity with respect to drinking water regulations in effect or likely to be in effect, source water assessments and protection plan, water conservation plan, cross-connection plan, operations and maintenance plan, infrastructure protection plan, and all related material.
(4) Complete Applications. Applications for permits will be reviewed together with the submitted information and when the Director is satisfied that the application is complete a determination to issue or deny the permit will be made.
(5) Public Participation. Whenever in the judgment of the Director public participation may be required prior to the final determination to issue or deny a permit the Director may give public notice of the proposed action. Public notice will be prepared and circulated in a manner designed to inform interested and potentially interested persons of the permit application. Procedures for circulation of the public notice shall include the following:
(a) A copy of the public notice will be provided to the permit applicant, will be available at the Division office in Atlanta, and will be posted to the Division's website.
(b) Electronic mailing (e-mail) notification of the public notice to any persons or groups included on the electronic mailing list to receive such notices. The EPD shall maintain an electronic mailing list for distribution of public notices. Any person or group may request that their e-mail address be added to the electronic mailing list or they may sign-up through the EPD website.
(c) The Director shall provide a period of not less than thirty (30) days following the public notice in which interested persons may submit their written views with respect to the permit application. All written comments submitted during the thirty (30) day comment period will be retained by the Division and considered in the final determination of the permit application.
(d) The contents of the public notice will be in accordance with applicable Federal regulations and State laws.
(6) Public Hearing. The Director shall hold a public hearing if he determines that there is sufficient public interest or need for a public hearing prior to the final determination to issue or deny a permit.
(a) Any public hearing held pursuant to this paragraph shall be held in the geographical area of the proposed or existing public water system or other appropriate location at the discretion of the Director.
(b) The Director may hold one public hearing on related groups of permit applications.
(c) Public notice of any public hearing held pursuant to this paragraph shall be provided at least thirty (30) days in advance of the hearing date and shall be circulated in accordance with paragraph (5) of this rule.
(7) Permit Conditions. A permit issued by the Director shall stipulate such terms, and conditions and schedules of compliance as the Director deems necessary to meet the requirements of these rules and which are consistent and in conformity with the Act and the Federal Act. Any permit issued pursuant to the Act may be subject to such monitoring, recording and reporting requirements as may be reasonably required by the Director including the installation, use and maintenance of monitoring equipment or methods; specific requirements for recording of monitoring activities and results; and periodic reporting of monitoring results. The monitoring, recording and reporting requirements shall be specified in a permit issued, provided, however, the Director may modify or require additional monitoring, recording and reporting by written notification to the permittee.
(8) Permit Transfers. A permit issued by the Director may be transferred due to a change in ownership of the public water system. The permittee shall notify the succeeding owner by letter of the existing permit and shall surrender the permit to the Director along with a copy of the letter to the succeeding owner. It shall be the succeeding owner's responsibility to request a transfer of the permit. A completed permit application shall be submitted to the Director on the forms prescribed and furnished by the Division within 30 days of transfer. The succeeding owner shall upon the request of the Director provide such additional information as may be necessary (including but not limited to proof of ownership and business plan) to enable the Director to transfer the permit.
(9) Permit Application Denials. Based on the information submitted or available to the Director, a permit application may be denied by the Director for any one of the following reasons where the proposed activity or system would:
(a) present an immediate or potential health hazard to the public, or
(b) not adequately supply water under sufficient pressure and flow at all times, or
(c) not meet the requirements of these rules or the Act.
(10) Notice In Case of Application Denial. In the event an applicant's permit is denied, the Director shall serve written notice of such action to the applicant setting forth in such notice the reason for the action.
(11) Permit Expiration Term. Each permit issued under this Rule shall have a fixed term not to exceed ten (10) years. The permittee shall apply for a renewal at least 90 days prior to the expiration of the permit. A new permit may be issued by the Director if, after a review, the Director determines that the continued operation of such public water system meets or will meet all applicable drinking water standards, maximum contaminant levels and all requirements of the Act and these rules. Any permit issued under this paragraph may include any of the terms, conditions and schedules of compliance under paragraph (7) of this Rule.
(12) Revocation, Suspension, or Modification. The Director may revoke, suspend, or modify a permit issued under this Rule for cause, including, but not limited to, the following:
(a) violation of any condition of said permit;
(b) obtaining a permit by misrepresentation, or failure to disclose fully all relevant facts;
(c) change in any condition that requires either:
1. a temporary or permanent decrease in the maximum contaminant levels; or
2. elimination of the permitted operation.
(13) Notice In Case of Permit Revocation, Suspension, or Modification. In the event of modification, suspension, or revocation of a permit, the Director shall serve written notice of such action on the permit holder and shall set forth in such notice the reason for the action.
(14) Access by Division. The Director or any agents or employees of the Division shall be permitted access in or upon any private or public property at all reasonable times for the purpose of investigating conditions, processes, methods of treatment, records relating to the operation of any public water system, compliance with any operating permit issued, to make sanitary surveys, to determine compliance with the Act and any rules promulgated thereunder, or to make such investigations and studies as the Director deems advisable and necessary for the protection of the public health.
(15) Previous Permits. In the event of reissue, modification, suspension, revocation or transfer of a permit all previously issued permits for the system shall be surrendered to the Division upon written notice by the Director.
(16) Compliance with Wellhead Protection. All community public water systems utilizing ground water sources and serving a municipality, county, or an authority are required to comply with the Wellhead Protection rule, Rule 391-3-5-.40.
(17) Conformance with Minimum Standards. Design and construction of all public water systems shall conform to the latest edition of the Division's "Minimum Standards for Public Water Systems".

Rule 391-3-5-.18 Primary Maximum Contaminant Levels for Drinking Water

(1) Primary MCLs for Inorganics. INORGANICS - The maximum contaminant levels (MCLs) for antimony, arsenic, asbestos, barium, beryllium, cadmium, chromium, mercury, nickel, selenium and thallium of this Rule apply to community water systems and non-transient, non-community water systems. The MCLs for fluoride in this Rule apply to community water systems. The MCLs for nitrate, nitrite, and total nitrate-nitrite of this Rule apply to all (CWS, NTNCWS, TNCWS) public water systems.
(a) The following are the maximum contaminant levels for inorganic chemicals:

Contaminant

Maximum Contaminant Level (mg/L)

Applicable Systems

Antimony

0.006

CWS, NTNCWS

Arsenic

0.010

CWS, NTNCWS

Asbestos

7 Million Fibers/Liter Longer than 10 µm

CWS, NTNCWS

Barium

2

CWS, NTNCWS

Beryllium

0.004

CWS, NTNCWS

Cadmium

0.005

CWS, NTNCWS

Chromium

0.1

CWS, NTNCWS

Cyanide

0.2

CWS, NTNCWS

Fluoride1,2

4.0

CWS

Lead

see 391-3-5-.25 Treatment Technique

CWS, NTNCWS

Mercury

0.002

CWS, NTNCWS

Nickel

0.1

CWS, NTNCWS

Nitrate

10 (as N)

CWS, NTNCWS, TNCWS

Nitrite

1 (as N)

CWS, NTNCWS, TNCWS

Total Nitrate

+ Nitrite

10 (as N)

CWS, NTNCWS, TNCWS

Selenium

0.05

CWS, NTNCWS

Thallium

0.002

CWS, NTNCWS

NOTES:

1. Effective date for fluoride was October 2, 1987.
2. Fluoride also has a secondary MCL (Rule 391-3-5-.19(2) ).
(b) At the discretion of the Director, nitrate levels not to exceed 20 mg/L may be allowed in a non-community water system if the supplier of water demonstrates to the satisfaction of the Director that:
1. such water will not be available to children under 6 months of age;
2. the water system is meeting the public notification requirements under Rule 391-3-5-.32, including continuous posting of the fact that nitrate levels exceed 10 mg/L and the potential health effects of exposure;
3. local and State public health authorities will be notified annually of nitrate levels that exceed 10 mg/L; and
4. no adverse health effects shall result.
(2) Primary MCLs for Organics. ORGANIC CHEMICALS - The following maximum contaminant levels for organic contaminants apply to community water systems and non-transient, non-community water systems. Compliance with maximum contaminant levels for the following organics is to be calculated pursuant to Rule 391-3-5-.22.
(a) Synthetic Organic Chemicals, Pesticides and Polychlorinated biphenyls

Contaminant

Maximum Contaminant Level (mg/L)

Alachlor

0.002

Aldicarb

Deferred

Aldicarb sulfone

Deferred

Aldicarb sulfoxide

Deferred

Atrazine

0.003

Benzo(a)Pyrene

0.0002

Carbofuran

0.04

Chlordane

0.002

Dalapon

0.2

Di(2-ethylhexyl) adipate

0.4

Di(2-ethylhexyl) phthalate

0.006

Dibromochloropropane (DBCP)

0.0002

Dinoseb

0.007

Diquat

0.02

2,4-D

0.07

Endothall

0.1

Endrin

0.002

Ethylene dibromide (EDB)

0.00005

Glyphosate

0.7

Heptachlor

0.0004

Heptachlor Epoxide

0.0002

Hexachlorobenzene

0.001

Hexachlorocyclopentadiene

0.05

Lindane

0.0002

Methoxychlor

0.04

Oxamyl (Vydate)

0.2

Pentachlorophenol

0.001

Picloram

0.5

Polychlorinated biphenyls (PCBs)

0.0005

Simazine

0.004

Toxaphene

0.003

2,4,5-TP (Silvex)

0.05

2,3,7,8-TCDD (Dioxin)

3 x 10 -8

(b) Volatile Organic Contaminants (VOCs)

Contaminant

Maximum Contaminant Level (mg/L)

Vinyl chloride

0.002

Benzene

0.005

Carbon tetrachloride

0.005

1,2-Dichloroethane

0.005

Trichloroethylene

0.005

para-Dichlorobenzene

0.075

1,1-Dichloroethylene

0.007

1,1,1-Trichloroethane

0.2

cis-1,2-Dichloroethylene

0.07

1,2-Dichloropropane

0.005

Ethylbenzene

0.7

Monochlorobenzene

0.1

o-Dichlorobenzene

0.6

Styrene

0.1

Tetrachloroethylene

0.005

Toluene

1

trans-1,2-Dichloroethylene

0.1

Xylenes (total)

10

Dichloromethane

0.005

1,2,4-Trichlorobenzene

0.07

1,1,2-Trichloroethane

0.005

(3) Primary MCLs for Turbidity. Turbidity - Treatment Technique Requirements:
(a) The maximum contaminant level for turbidity is determined by a treatment technique requirement as set forth in this Rule.
(b) The treatment technique requirement for turbidity is applicable to both community water systems and non-community water systems using surface water sources or ground water sources under the direct influence of surface water in whole or in part. The treatment technique requirement for turbidity in drinking water, measured at a representative point(s) in the filtered water is:
1. Less than or equal to 0.3 turbidity unit in at least 95 percent of the monthly measurements. One turbidity unit is the maximum allowable level and must not be exceeded at any time.
2. Five turbidity units is the maximum allowable level and must not be exceeded at any time.
3. In accordance with 40 CFR § 141.73, the Division may allow higher turbidity levels for slow sand filtration, diatomaceous earth filtration, or other filtration technologies.
4. Beginning January 1, 2002, public water systems that use surface water or ground water under the direct influence of surface water and serve at least 10,000 people must meet the filtration requirements specified in 40 CFR § 141.173 (see Rule 391-3-5-.20(5) ).
5. The Enhanced Filtration and Disinfection requirements specified in 40 CFR Part 141 , Subpart P are applicable to Subpart H systems serving at least 10,000 people (see Rule 391-3-5-.20(8) ).
6. Beginning January 14, 2005, public water systems that use surface water or ground water under the direct influence of surface water as a source and serve fewer than 10,000 people must meet the filtration and disinfection requirements in 40 CFR Part 141, Subpart T. This requirement is in addition to complying with requirements in Subpart H of 40 CFR Part 141 [see Rule 391-3-5-.20(8) ].
(4) Primary MCLs for Microbiologicals. Microbiological - Maximum contaminant levels (MCLs) for microbiological contaminants.
(a) Until March 31, 2016, the total coliform MCL is based on the presence or absence of total coliforms in a sample, rather than coliform density.
1. For a system that collects at least 40 samples per month, if no more than 5.0 percent of the samples collected during a month are total coliform-positive, the system is in compliance with the MCL for total coliforms.
2. For a system that collects fewer than 40 samples per month, if no more than one sample collected during a month is total coliform-positive, the system is in compliance with the MCL for total coliforms.
(b) Until March 31, 2016, any fecal coliform-positive repeat sample or E. coli-positive repeat sample, or any total coliform-positive repeat sample following a fecal coliform-positive or E. coli­-positive routine sample, constitutes a violation of the MCL for total coliforms. For purposes of the public notification requirements in Rule 391-3-5-.32, this is a violation that may pose an acute risk to health.
(c) Beginning April 1, 2016, a system is in compliance with the MCL for E. coli for samples taken under the provisions of Rule 391-3-5-.55 unless any of the conditions identified in paragraphs (4)(c)1. through (4)(c)4. occur. For purposes of the public notification requirements in Rule 391-3-5-.32, violation of the MCL may pose an acute risk to health.
1. The system has an E. coli-positive repeat sample following a total coliform-positive routine sample.
2. The system has a total coliform-positive repeat sample following an E. coli-positive routine sample.
3. The system fails to take all required repeat samples following an E. coli-positive routine sample.
4. The system fails to test for E. coli when any repeat sample tests positive for total coliform.
(d) Until March 31, 2016, a public water system must determine compliance with the MCL for total coliforms in paragraphs (4)(a) and (4)(b) for each month in which it is required to monitor for total coliforms. Beginning April 1, 2016, a public water system must determine compliance with the MCL for E. coli in paragraph (4)(c) for each month in which it is required to monitor for total coliforms.
(e) The EPA Administrator, pursuant to section 1412 of the federal Safe Drinking Water Act, identifies the following as the best technology, treatment techniques, or other means available for achieving compliance with the maximum contaminant level for total coliforms in paragraphs (4)(a) and (4)(b) and for achieving compliance with the maximum contaminant level for E. coli in paragraph (4)(c):
1. Protection of wells from fecal contamination by appropriate placement and construction;
2. Maintenance of a disinfectant residual throughout the distribution system;
3. Proper maintenance of the distribution system including appropriate pipe replacement and repair procedures, main flushing programs, proper operation and maintenance of storage tanks and reservoirs, cross connection control, and continual maintenance of positive water pressure in all parts of the distribution system;
4. Filtration and/or disinfection of surface water, as described in 40 CFR Part 141 Subparts H, P, T, and W, or disinfection of ground water, as described in 40 CFR Part 141 Subpart S, using strong oxidants such as chlorine, chlorine dioxide, or ozone; and
5. For systems using ground water, compliance with the requirements of an EPA-approved Division Wellhead Protection Program developed and implemented under section 1428 of the federal Safe Drinking Water Act.
(f) The EPA Administrator, pursuant to section 1412 of the federal Safe Drinking Water Act, identifies the technology, treatment techniques, or other means available identified in paragraph (4)(e) as affordable technology, treatment techniques, or other means available to systems serving 10,000 or fewer people for achieving compliance with the maximum contaminant level for total coliforms in paragraphs (4)(a) and (4)(b) and for achieving compliance with the maximum contaminant level for E. coli in paragraph (4)(c).
(5) Primary MCLs for Radioactivity and Radionuclides. Radioactivity - Maximum contaminant levels for Radium-226, Radium-228, gross alpha particle radioactivity, beta particle and photon radioactivity from man-made radionuclides in community water systems.
(a) The following are the maximum contaminant levels for Radium-226, Radium-228, gross alpha radioactivity, and Uranium:

Radionuclides / Radioactivity

Maximum Contaminant Level

Combined Radium-226 and

Radium-228 (226 Ra, 228 Ra)

5 pCi/L

Gross alpha particle activity (including Radium-226 but excluding Radon and Uranium)

15 pCi/L

Uranium

30 µg/L

(b) The average annual concentration of beta particle and photon radioactivity from man­made radionuclides in drinking water shall not produce an annual dose equivalent to the total body or any internal organ greater than 4 millirem per year.
(c) Except for the radionuclides listed in Table A, the concentration of man-made radionuclides causing 4 mrem total body or organ dose equivalents shall be calculated on the basis of a 2 liter per day drinking water intake using the 168 hour data listed in "Maximum Permissible Body Burdens and Maximum Permissible Concentrations of Radionuclides in Air or Water for Occupational Exposure", NBS Handbook 69 as amended August, 1963, U.S. Department of Commerce. If two or more radionuclides are present, the sum of their annual dose equivalent to the total body or to any organ shall not exceed 4 millirem per year.

TABLE A. - Average annual concentrations assumed for the purpose of this rule to produce a total body or organ dose of 4 millirem per year.

Radionuclide

Critical Organ

Average Annal Concentration

Tritium (3H)

Total Body

20,000 pCi/L

Strontium-90 (90 Sr)

Bone Marrow

8 pCi/L

(6) Primary MCLs for Trihalomethanes. TRIHALOMETHANES - Maximum contaminant level for trihalomethanes: see paragraph (7), DISINFECTANTS and DISINFECTION BYPRODUCTS, below.
(7) Primary MCLs for Disinfectants and Disinfection Byproducts. DISINFECTANTS and DISINFECTION BYPRODUCTS (D/DBPs). Beginning January 1, 2002, this paragraph shall be applicable as specified below:
(a) The maximum contaminant levels (MCLs) for disinfection byproducts (DBPs) are as specified in 40 CFR § 141.64 and the maximum residual disinfectant levels (MRDLs) are as specified in 40 CFR § 141.65.

Disinfection Byproduct

Maximum Contaminant Level (mg/L)

Total trihalomethanes

0.080

Haloacetic acids (five)

0.060

Bromate

0.010

Chlorite

1.0

Disinfectant Residuals

Maximum Residual Disinfectant Level (mg/L)

Chlorine

4.0 (as Cl2)

Chloramines

4.0 (as Cl2)

Chlorine Dioxide

0.8 (as ClO2)

(b) Beginning January 1, 2002, community and non-transient, non-community Subpart H water systems which serve a population of 10,000 people or more must comply with paragraph (7). All systems must comply with these MCLs until the date specified for Subpart V compliance in 40 CFR § 141.620(c).
(c) Beginning January 1, 2004, community and non-transient, non-community Subpart H water systems serving fewer than 10,000 people and systems using only ground water not under the direct influence of surface water must comply with paragraph (7). All systems must comply with these MCLs until the date specified for Subpart V compliance in 40 CFR § 141.620(c).
(d) The Subpart V MCLs for TTHM and HAA5 must be complied with as a locational running annual average at each monitoring location beginning the date specified for Subpart V compliance in 40 CFR § 141.620(c).
(e) A system that is installing granular activated carbon (GAC) or membrane technology to comply with paragraph (7) may apply to the Division for an extension of up to 24 months past the dates in paragraphs (7)(b) and (7)(c), but not beyond December 31, 2003.
(f) Transient non-community Subpart H water systems serving 10,000 or more persons and using chlorine dioxide as a disinfectant or oxidant must comply with the chlorine dioxide MRDL beginning January 1, 2002.
(g) Transient non-community Subpart H water systems serving fewer than 10,000 persons and using chlorine dioxide as a disinfectant or oxidant and systems using only ground water not under the direct influence of surface water and using chlorine dioxide as a disinfectant or oxidant must comply with the chlorine dioxide MRDL beginning January 1, 2004.
(h) The best technology, treatment technique, or other means available for achieving compliance with the maximum contaminant levels for disinfection byproducts identified in paragraph (7)(a) shall be in accordance with 40 CFR §§ 141.64(a)(2) and (b)(2).
(8) Maximum Contamination Level Goals (MCLG). The maximum contaminant level goals for organic contaminants, inorganic contaminants, and microbiological contaminants shall be in accordance with 40 CFR §§ 141.50, 141.51, 141.52, 141.53, and 141.54.

Rule 391-3-5-.19 Secondary Maximum Contaminant Levels for Drinking Water

(1) Adverse Effects on Drinking Water. The drinking water should not contain any contaminant which will adversely affect the odor or appearance of the drinking water and consequently may cause a substantial number of the persons served by the public water system to discontinue its use or which may adversely affect the public welfare.
(2) Secondary MCLs. The Secondary maximum contaminant levels established below represent reasonable goals for drinking water quality:

Contaminant

Secondary Level

Aluminum (Al)

0.05 to 0.2 mg/L

Chloride

250 mg/L

Color

15 color units

Copper (Cu)

1.0 mg/L

Corrosivity

Non-corrosive

Fluoride (F)

2.0 mg/L

Foaming Agents

0.5 mg/L

Iron (Fe)

0.3 mg/L

Manganese (Mn)

0.05 mg/L

Odor

3 threshold odor number

pH

6.5 to 8.5

Silver (Ag)

0.1 mg/L

Sulfate

250 mg/L

Total dissolved solids (TDS)

500 mg/L

Zinc (Zn)

5.0 mg/L

(3) Standard Methods. Any analyses required under this rule shall be conducted in accordance with the analytical recommendations set forth in the latest edition of "Standard Methods of Examination of Water and Wastewater" as published by the American Public Health Association, or as such analyses may be modified by the Director.
(4) Collect and Submit Samples for Analyses. Upon written direction of the Director, the supplier shall collect drinking water samples and submit them to the Division's water laboratory or other laboratory for analyses in accordance with the schedule furnished to the supplier.

Rule 391-3-5-.20 Turbidity Sampling and Analytical Requirements

(1) Turbidity Testing Frequency. On and after June 29, 1993, representative samples of filtered water shall be taken and analyzed by said suppliers at least every four hours when the plant is in operation, for the purpose of making turbidity measurements to determine compliance with the treatment technique requirement of Rule 391-3-5-.18(3). If the Division determines that a reduced sampling frequency in a non-community system will not pose a risk to public health, it can reduce the required sampling frequency in accordance with 40 CFR 141.74 for systems using slow sand filtration or filtration treatment other than conventional treatment, direct filtration, or diatomaceous earth filtration. The option of reducing the turbidity frequency shall be permitted only in those public water systems that practice disinfection and which maintain an active residual disinfectant in the distribution system and in those cases where the Division has indicated in writing that no unreasonable risk to health existed under the circumstances of this option. The turbidity measurements shall be made in accordance with the recommendations set forth in 40 CFR Part 141.22.
(2) Exceedance Determination. If a turbidity treatment violation has occurred based on a single exceedance of the maximum allowable turbidity limit, the supplier of water shall consult with the Division as soon as practical but no later than 24 hours after learning of the violation ( 40 CFR 141.203(b)) . If the consultation does not occur within those 24 hours, the violation is elevated to Tier 1 under 40 CFR Subpart Q. If the monthly treatment technique requirement is exceeded, or if any measured turbidity level exceeds the maximum allowable level, the supplier of water shall report to the Division and notify the public as directed in Rules 391-3-5-.30 and .32.
(3) Applicability to Surface Water Sources. The requirements of this Rule shall apply only to public water systems, which use water obtained in whole or in part from surface water sources or ground water sources under the direct influence of surface water.
(4) Compliance and Enforcement. The Division has the authority to determine compliance or initiate enforcement action based upon analytical results or other information compiled by their sanctioned representatives or agencies.
(5) Filtration Requirements for Greater than 10,000 Population Water Systems. Beginning January 1, 2002, public water systems that use surface water or ground water under the direct influence of surface water and serve at least 10,000 people must meet the filtration requirements specified in 40 CFR § 141.173.
(6) Enhanced Filtration Requirements. The Enhanced Filtration and Disinfection requirements specified in 40 CFR, Subpart P are applicable to Subpart H systems serving at least 10,000 people.
(a) General requirements: 40 CFR, Subpart P § 141.170 is hereby incorporated by reference. Subpart H systems that did not conduct optional monitoring under § 141.172 because they served fewer than 10,000 persons when such monitoring was required, but serve more than 10,000 persons prior to January 14, 2005 must comply with §§ 141.170, 141.171, 141.173, 141.174, and 141.175. These systems must contact the Division and establish a disinfection benchmark. A system that decides to make a significant change to its disinfection practice, as described in § 141.172(c)(1)(i) through (iv) must obtain prior approval from the Division prior to making such change.
(b) Criteria for avoiding filtration: 40 CFR, Subpart P § 141.171 is hereby incorporated by reference.
(c) Disinfection profiling and benchmarking: 40 CFR, Subpart P § 141.172 is hereby incorporated by reference.
(d) Determination of systems required to profile: 40 CFR, Subpart P § 141.172(a) is hereby incorporated by reference.
(e) Disinfection profiling: 40 CFR, Subpart P § 141.172(b) is hereby incorporated by reference.
(f) Disinfection benchmarking: 40 CFR, Subpart P § 141.172(c) is hereby incorporated by reference.
(7) Filtration. 40 CFR, Subpart P § 141.173 is hereby incorporated by reference.
(a) Conventional filtration treatment or direct filtration: 40 CFR, Subpart P § 141.173(a) is hereby incorporated by reference. (For systems using conventional filtration or direct filtration, the turbidity level of representative samples of a system's filtered water must be less than or equal to 0.3 NTU (Nephelometric Turbidity Units) in at least 95 percent of the measurements taken each month, measured as specified in 40 CFR § 141.74(a) and (c), and the turbidity level of representative samples of a system's filtered water must at no time exceed 1 NTU, measured as specified in 40 CFR § 141.74(a) and (c) ).
(b) Systems using filtration technologies other than conventional filtration treatment, direct filtration, slow sand filtration, or diatomaceous earth filtration: 40 CFR, Subpart P § 141.173(b) is hereby incorporated by reference. Beginning January 1, 2002, systems serving at least 10,000 people must meet the requirements for other filtration technologies referenced in 141.173(b).
(c) Filtration sampling requirements: 40 CFR, Subpart P § 141.174 is hereby incorporated by reference. (A public water system subject to the requirements of this section that provides conventional filtration treatment or direct filtration must conduct continuous monitoring of turbidity for each individual filter using an approved method in 40 CFR § 141.74(a) and must calibrate turbidimeters using the procedure specified by the manufacturer. Systems must record the results of individual filter monitoring every fifteen (15) minutes. If there is a failure in the continuous turbidity monitoring equipment, the system must conduct grab sampling every four (4) hours in lieu of continuous monitoring, but for no more than five (5) working days following the failure of the equipment.)
(8) Filtration Requirements for Fewer than 10,000 Population Water Systems. Beginning January 14, 2005, public water systems that use surface water or ground water under the direct influence of surface water as a source and serve fewer than 10,000 people must meet the filtration and disinfection requirements in 40 CFR Part 141 , Subpart T. This requirement is in addition to complying with requirements in Subpart H of 40 CFR Part 141.
(a) Beginning January 14, 2005, public water systems that use surface water or ground water under the direct influence of surface water and serve fewer than 10,000 people must meet the filtration requirements specified in 40 CFR §§ 141.550 through 141.553.
(b) Other filtration technologies: 40 CFR § 141.73(d) is hereby incorporated by reference. Beginning January 14, 2005, systems serving fewer than 10,000 people must meet the requirements for other filtration technologies in 40 CFR §§ 141.550 through 141.553.
(c) General requirements: 40 CFR, Subpart T § 141.500 is hereby incorporated by reference.
(d) Additional watershed control requirements for unfiltered systems: 40 CFR, Subpart T §§ 141.520 through 141.522 is hereby incorporated by reference. This is in addition to the continued requirement to comply with the filtration avoidance criteria in 40 CFR § 141.71.
(e) Disinfection Profile: 40 CFR, Subpart T §§ 141.530 through 141.536 is hereby incorporated by reference. This requirement applies both to community and non-transient non-community water systems.
(f) Disinfection benchmark: 40 CFR, Subpart T §§ 141.540 through 141.544 is hereby incorporated by reference. If you are a subpart H system required to develop a disinfection profile under Rule 391-3-5-.20(10)(e), your system must develop a disinfection benchmark if you decide to make a significant change to your disinfection practice. Before implementing a significant disinfection practice change, a prior approval from the Division must be obtained. Significant changes to disinfection practice include:
1. Changes to the point of disinfection;
2. Changes to the disinfectant(s) used in the treatment plant;
3. Changes to the disinfection process; or
4. Any other modification identified by the Division.
(g) Combined filter effluent requirements: 40 CFR, Subpart T § 141.550 through 141.553 is hereby incorporated by reference. This requirement applies to all subpart H systems which serve populations fewer than 10,000, are required to filter, and utilize filtration other than slow sand filtration or diatomaceous earth filtration.
1. For systems using conventional filtration or direct filtration, the turbidity level of representative samples of a system's filtered water must be less than or equal to 0.3 NTU in at least 95 percent of the measurements taken each month, and the maximum turbidity level of representative samples of a system's filtered water must at no time exceed 1 NTU. All measurements must be taken as described in 40 CFR § 141.74(a) and (c).
2. For systems using "alternative" filtration (filtration other than slow sand filtration, diatomaceous earth filtration, conventional filtration, or direct filtration), the 95th percentile turbidity value, not to exceed 1 NTU, and the maximum turbidity value, not to exceed 5 NTU, shall be determined by the Division based on the demonstration as described in 40 CFR, Subpart T § 141.552. The systems, using pilot plant studies or other means, must demonstrate that the system's filtration, in combination with disinfection treatment, consistently achieves: two-log (99%) removal of Cryptosporidium oocysts; three-log (99.9%) removal and/or inactivation of Giardia lamblia cysts; and four-log (99.99%) removal and/or inactivation of viruses.
(h) Individual filter turbidity requirements for systems utilizing conventional filtration or direct filtration: 40 CFR, Subpart T §§ 141.560 through 141.564 is hereby incorporated by reference. A subpart H public water system subject to the requirements of this Rule must conduct continuous monitoring of turbidity for each individual filter using an approved method in 40 CFR § 141.74(a) and must calibrate turbidimeters using the procedure specified by the manufacturer. Systems must record the results of individual filter monitoring every fifteen (15) minutes. If there is a failure in the continuous turbidity monitoring equipment, the system must conduct grab sampling every four (4) hours in lieu of continuous monitoring until the turbidimeter is back on-line. The system has fourteen (14) days to resume continuous monitoring before a violation is incurred.
1. Systems with two or fewer filters may conduct continuous monitoring of combined filter effluent turbidity in lieu of individual filter effluent turbidity monitoring, in accordance with the same requirements set forth in 40 CFR § 141.560(a) through (d) and § 141.561.
2. Based on continuous turbidity monitoring of individual filters, the systems are required to take the follow-up actions described in 40 CFR § 141.563(a), (b) and (c).
(i) Reporting and recordkeeping requirements: 40 CFR, Subpart T §§ 141.570 through 141.571 is hereby incorporated by reference. The items which must be reported and the frequency of reporting must be as specified in 40 CFR § 141.570. Based on the requirements of subpart T of 40 CFR Part 141, applicable systems must keep several required records, in addition to the recordkeeping required under 40 CFR § 141.75. Specifically, the results of individual filter monitoring must be kept for at least three (3) years and the results of any disinfection profiling or benchmarking (including raw data and analysis) must be kept indefinitely.

Rule 391-3-5-.21 Inorganic Chemical Sampling and Analytical Requirements

(1) CWS and NTNCWS Monitoring. Community and non-transient, non-community water systems shall conduct monitoring to determine compliance with the maximum contaminant levels specified in Rule 391-3-5-.18 in accordance with this rule.
(2) TNCWS Monitoring. Transient, non-community water systems shall conduct monitoring to determine compliance with the nitrate and nitrite maximum contaminant levels in Rule 391-3-5-.18 in accordance with this rule.
(3) Nitrate Monitoring for NCWS with Alternate Limit. The frequency of monitoring conducted to determine compliance with the maximum contaminant level for Nitrate as specified in Rule 391-3-5-.18(1)(b) shall be conducted as follows:
(a) Analyses for all non community water systems (NTNCWS and TNCWS) utilizing surface water sources shall be repeated at yearly intervals. Analyses for all non community water systems (NTNCWS and TNCWS) utilizing only ground water sources shall be repeated at three-year intervals.
(b) For any non community water system (NTNCWS and TNCWS) that the Director has granted an alternate nitrate MCL of 20 mg/l pursuant to Rule 391-3-5-.18(1)(b) the monitoring frequency shall be conducted at intervals determined by the Director.
(c) If the result of an analysis made pursuant to paragraph (3) of this Rule indicates that the level of Nitrate listed in Rule 391-3-5-.18(1)(b) exceeds the maximum contaminant level, the supplier of water shall report to the Division in writing within seven (7) days and initiate three additional analyses at the same sampling point within fourteen (14) days.
(d) When the average of four analyses made pursuant to paragraph (3)(c), rounded to the same number of significant figures as the maximum contaminant level for the substance in question, exceeds the maximum contaminant level, the supplier of water shall notify the Division pursuant to Rule 391-3-5-.30 and give notice to the public pursuant to Rule 391-3-5-.32. Monitoring after public notification shall be at a frequency designated by the Division and shall continue until the maximum contaminant level has not been exceeded in two successive samples or until a monitoring schedule as a condition to a permit, variance, exception or enforcement action shall become effective.
(e) If the four analyses are not made pursuant to paragraph (3)(c), the Division will use the analyses available to prepare compliance calculations pursuant to paragraph (3)(d).
(f) The Division has the authority to determine compliance or initiate enforcement action based upon analytical results and other information compiled by their sanctioned representatives or agencies.
(g) The provisions of paragraphs (3)(c) and (3)(d) not withstanding, compliance with maximum contaminant for nitrate shall be determined based on the mean of the two analyses. When a level exceeding the maximum contaminant level for nitrate is found, a second analysis shall be initiated within 24 hours and if the mean of the two analyses exceeds the maximum contamination level, the supplier of water shall report the findings to the Director pursuant to Rule 391-3-5-.30 and shall notify the public pursuant to Rule 391-3-5-.32.
(4) Inorganic Monitoring. Monitoring for inorganic chemicals shall be conducted as follows:
(a) Groundwater systems shall take a minimum of one sample at every entry point to the distribution system which is representative of each well after treatment (hereafter called a sampling point) beginning in the compliance period starting January 1, 1993. The system shall take each sample at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant.
(b) Surface water systems shall take a minimum of one sample at every entry point to the distribution system after any application of treatment or in the distribution system at a point which is representative of each source after treatment (hereafter called a sampling point) beginning in the compliance period starting January 1, 1993. The system shall take each sample at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant. [NOTE: For purposes of this paragraph, surface water systems include systems with a combination of surface and ground sources.]
(c) If a system draws water from more than one source and the sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions (i.e., when water is representative of all sources being used).
(d) The Division may reduce the total number of samples, which must be analyzed by allowing the use of compositing. Composite samples shall be collected and analyzed in accordance with 40 CFR, Part 141.23(a)(4). In the case of arsenic, if a PWS supplies water to one or more other PWSs and the interconnection justifies treating them as a single system for monitoring purposes, then the PWSs receiving the supplied water may have their arsenic monitoring requirements modified.
(5) Asbestos Monitoring. The frequency of monitoring conducted to determine compliance with the maximum contaminant level for asbestos specified in Rule 391-3-5-.18 shall be conducted as follows:
(a) Community or non-transient, non-community water systems are required to monitor for asbestos during the first three-year compliance period of each nine-year compliance cycle beginning in the compliance period starting January 1, 1993.
(b) If the system believes it is not vulnerable to either asbestos contamination in its source water or due to corrosion of asbestos-cement pipe, or both, it may apply to the Division for a waiver of the monitoring requirements in paragraph (5)(a) above. If the waiver is granted by the Division, the system is not required to monitor.
(c) The Division may grant a waiver based on a consideration of the following factors:
1. Potential asbestos contamination of the water source.
2. The use of asbestos-cement pipe for finished water distribution and the corrosive nature of the water.
(d) A waiver remains in effect until the completion of the three-year compliance period. Systems not receiving a waiver must monitor in accordance with the provisions of paragraph (5)(a).
(e) A system vulnerable to asbestos contamination due solely to corrosion of asbestos-cement pipe shall take one sample at a tap served by asbestos-cement pipe and under conditions where asbestos contamination is most likely to occur.
(f) A system vulnerable to asbestos contamination due solely to source water shall monitor in accordance with the provision of paragraph (4).
(g) A system vulnerable to asbestos contamination due both to its source water supply and corrosion of asbestos-cement pipe shall take one sample at a tap served by asbestos-cement pipe and under conditions where asbestos contamination is most likely to occur.
(h) A system which exceeds the maximum contaminant levels as determined in Rule 391-3-5-.21(12) shall monitor quarterly beginning in the next quarter after the violation occurred.
(i) The Division may decrease the quarterly monitoring requirement to the frequency specified in paragraph (5)(a) provided the Division has determined that the system is reliably and consistently below the maximum contaminant level. In no case can the Division make this determination unless a groundwater system takes a minimum of two quarterly samples and a surface (or combined surface/ground) water system takes a minimum of four quarterly samples.
(j) If monitoring data collected after January 1, 1990 are generally consistent with the requirements of Rule 391-3-5-.21(5) then the Division may allow systems to use that data to satisfy the monitoring requirement for the initial compliance period beginning January 1, 1993.
(6) Other Inorganics Monitoring. The frequency of monitoring conducted to determine compliance with the maximum contaminant levels in Rule 391-3-5-.18 for antimony, arsenic, barium, beryllium, cadmium, chromium, cyanide, fluoride, mercury, nickel, selenium and thallium shall be as follows:
(a) Groundwater systems shall take one sample at each sampling point during each compliance period beginning in the compliance period starting January 1, 1993. Surface water systems (or combined surface/ground) shall take one sample annually at each sampling point beginning January 1, 1993.
(b) The system may apply to the Division for a waiver from the monitoring frequencies specified in paragraph (6)(a).
(c) A condition of the waiver shall require that a system shall take a minimum of one sample while the waiver is effective. The term during which the waiver is effective shall not exceed one compliance cycle (i.e., nine years).
(d) The Division may grant a waiver provided surface water systems have monitored annually for at least three years and groundwater systems have conducted a minimum of three rounds of monitoring. (At least one sample shall have been taken since January 1, 1990.) Both surface and groundwater systems shall demonstrate that all previous analytical results were less than the maximum contaminant level. Systems that use a new water source are not eligible for a waiver until three rounds of monitoring from the new source have been completed. In the case of arsenic, new water systems are not eligible for a waiver until three rounds of monitoring have been completed.
(e) In determining the appropriate reduced monitoring frequency, the Division shall consider:
1. Reported concentrations from all previous monitoring;
2. The degree of variation in reported concentrations; and
3. Other factors which may affect contaminant concentrations such as changes in groundwater pumping rates, changes in the system's configuration, changes in the system's operating procedures, or changes in stream flows or characteristics.
(f) A decision by the Division to grant a waiver shall be made in writing and shall set forth the basis for the determination. The determination may be initiated by the Division or upon an application by the public water system. The public water system shall specify the basis for its request. The Division shall review and, where appropriate, revise its determination of the appropriate monitoring frequency when the system submits new monitoring data or when other data relevant to the system's appropriate monitoring frequency become available.
(g) Systems which exceed the maximum contaminant levels as calculated in paragraphs (3)(d) and (12) shall monitor quarterly beginning in the next quarter after the violation occurred.
(h) The Division may decrease the quarterly monitoring requirement to the frequencies specified in paragraphs (3)(a), (3)(b), (6)(a) and (6)(b) provided it has determined that the system is reliably and consistently below the maximum contaminant level. In no case can the Division make this determination unless a groundwater system takes a minimum of two quarterly samples and a surface water system takes a minimum of four quarterly samples.
(i) All new systems or systems that use a new source of water that begin operation after January 22, 2004 must demonstrate compliance with the MCL within a period of time specified by the Division. The system must also comply with the initial sampling frequencies specified by the Division to ensure a system can demonstrate compliance with the MCL. Routine and increased monitoring frequencies shall be conducted in accordance with the requirements in this paragraph.
(7) Nitrate Monitoring. The frequency of monitoring for nitrate shall be as follows: All public water systems (community; non-transient, non-community; and transient, non-community systems) shall monitor to determine compliance with the maximum contaminant level for nitrate in Rule 391-3-5-.18.
(a) Community and non-transient, non-community water systems served by groundwater systems shall monitor annually beginning January 1, 1993; systems served by surface water shall monitor quarterly beginning January 1, 1993.
(b) For community and non-transient, non-community water systems, the repeat monitoring frequency for ground water systems shall be quarterly for at least one year following any one sample in which the concentration is greater than or equal to fifty percent (=50%) of the MCL. The Division may allow a groundwater system to reduce the sampling frequency to annually after four consecutive quarterly samples are reliably and consistently less than the MCL.
(c) For community and non-transient, non-community water systems, the Division may allow a surface water system to reduce the sampling frequency to annually if all analytical results from four consecutive quarters are less than fifty percent (50%) of the MCL. A surface water system shall return to quarterly monitoring if any one sample is greater than or equal to fifty percent (=50%) of the MCL.
(d) Each transient non-community water system shall monitor annually beginning January 1, 1993.
(e) After the initial round of quarterly sampling is completed, each community and non-transient non-community system which is monitoring annually shall take subsequent samples during the quarter(s) which previously resulted in the highest analytical result.
(8) Nitrite Monitoring. The frequency of monitoring for nitrite shall be as follows: All public water systems (community; non-transient, non-community; and transient, non-community systems) shall monitor to determine compliance with the maximum contaminant level for nitrite in Rule 391-3-5-.18.
(a) All public water systems shall take one sample at each sampling point in the compliance period beginning January 1, 1993 and ending December 31, 1995.
(b) After the initial sample, systems where an analytical result for nitrite is less than fifty percent (<50%) of the MCL shall monitor at the frequency specified by the Division.
(c) For community, non-transient, non-community, and transient non-community water systems, the repeat monitoring frequency for any water system shall be quarterly for at least one year following any one sample in which the concentration is greater than or equal to fifty percent (>=50%) of the MCL. The Division may allow a system to reduce the sampling frequency to annually after determining the system is reliably and consistently less than the MCL.
(d) Systems which are monitoring annually shall take each subsequent sample during the quarter(s) which previously resulted in the highest analytical result.
(9) Confirmation samples.
(a) Where the results of sampling for antimony, arsenic, asbestos, barium, beryllium, cadmium, chromium, cyanide, fluoride, mercury, nickel, selenium, or thallium indicate an exceedance of the maximum contaminant level, the Division may require that one additional sample be collected as soon as possible after the initial sample was taken (but not to exceed two weeks) at the same sampling point.
(b) Where nitrate or nitrite sample results indicate an exceedance of the maximum contaminant level, the system shall take a confirmation sample within 24 hours of the system's receipt of notification of the analytical results of the first sample. Systems unable to comply with the 24-hour sampling requirement must immediately notify the customers served by the area served by the public water system in accordance with Rule 391-3-5-.32. Systems exercising this option must take and analyze a confirmation sample within two weeks of notification of the analytical results of the first sample.
(c) If a Division-required confirmation sample is taken for any contaminant, then the results of the initial and confirmation sample shall be averaged. The resulting average shall be used to determine the system's compliance in accordance with paragraph (12).
(10) Increased Frequency of Monitoring. The Division may require more frequent monitoring than specified in paragraphs (5), (6), (7), and (8) or may require confirmation samples for positive and negative results at its discretion.
(11) Request for Increased Monitoring Frequency. Systems may apply to the Division to conduct more frequent monitoring than the minimum monitoring frequencies specified in this rule.
(12) Compliance Based on Analytical Results. Compliance with Rule 391-3-5-.18 (as appropriate) shall be determined based on the analytical result(s) obtained at each sampling point.
(a) For systems which are conducting monitoring at a frequency greater than annual, compliance with the maximum contaminant levels for antimony, arsenic, asbestos, barium, beryllium, cadmium, chromium, cyanide, fluoride, mercury, nickel, selenium and thallium is determined by a running annual average at each sampling point. If the average at any sampling point is greater than the MCL, then the system is out of compliance. If any single sample would cause the annual average to be exceeded, then the system is out of compliance immediately. Any sample below the detection limit shall be calculated at zero for the purpose of determining the annual average.
(b) For systems which are monitoring annually, or less frequently, the system is out of compliance with the maximum contaminant levels for antimony, arsenic, asbestos, barium, beryllium, cadmium, chromium, cyanide, fluoride, mercury, nickel, selenium and thallium if the level of a contaminant at any sampling point is greater than the MCL. The Division may require one or more additional confirmation samples per paragraph (10). If a confirmation sample is required, the determination of compliance will be based on the annual average of the initial MCL exceedance and any state required confirmation sample(s).
(c) Compliance with the maximum contaminant levels for nitrate and nitrite is determined based on one sample if the levels of these contaminants are below the MCLs. If the levels of nitrate and/or nitrite exceed the MCLs in the initial sample, a confirmation sample is required in accordance with paragraph (9), and compliance shall be determined based on the average of the initial and confirmation samples.
(d) If a public water system has a distribution system separable from other parts of the distribution system with no interconnections, the Division may allow the system to give public notice to only the area served by that portion of the system which is out of compliance.
(13) Monitor at Time Designed by Division. Each public water system shall monitor at the time designated by the Division during each compliance period.
(14) Analyses to Determine Compliance. All analyses conducted to determine compliance with paragraph (1)(a) of Rule 391-3-5-.18 and this Rule shall be in accordance with 40 CFR, Part 141.23(k). Detection limits must be no less stringent than the detection limits presented in 40 CFR Part 141.23(a)(4). Arsenic sampling results shall be reported to the nearest 0.001 mg/L.
(15) Certified Laboratories. Analysis under this rule shall only be conducted by laboratories that have received approval by EPA fulfilling the requirements listed in 40 CFR, Part 141.23(k)(3) or have received certification from the Division. Laboratories may conduct sample analysis under provisional certification until January 1, 1996.
(16) Treatment to Achieve Compliance. The best technology, treatment technique, or other means available for achieving compliance with the maximum contaminant level for inorganic contaminants identified in Rule 391-3-5-.18(1)(a) shall be in accordance with 40 CFR, Part 141.62(c).

Rule 391-3-5-.22 Organic Chemical Sampling and Analytical Requirements

(1) Organic Monitoring. Beginning on January 1, 1993, analysis of the contaminants listed in Rule 391-3-5-.18(2)(b)1 -21 for the purpose of determining compliance with the maximum contaminant level shall be conducted as follows:
(a) Groundwater systems shall take a minimum of one sample at every entry point to the distribution system which is representative of each well after treatment (hereafter called a sampling point). Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source, treatment plant, or within the distribution system.
(b) Surface water systems (or combined surface/ground) shall take a minimum of one sample at points in the distribution system that are representative of each source or at each entry point to the distribution system after treatment (hereafter called a sampling point). Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source, treatment plant, or within the distribution system.
(c) If the system draws water from more than one source and the sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions (i.e., when water representative of all sources is being used).
(d) Each community and non-transient non-community water system shall take four consecutive quarterly samples for each contaminant listed in Rule 391-3-5-.18(2)(b)2 -21 during each compliance period.
(e) If the initial monitoring for contaminants listed in Rule 391-3-5-.18(2)(b)1 -8 and the monitoring for the contaminants listed in Rule 391-3-5-.18(2)(b)9 -21 as allowed in paragraph (1)(q) has been completed by December 31, 1992 and the system did not detect any contaminant listed in Rule 391-3-5-.18(2)(b)1 -21, then each ground and surface water system shall take one sample annually.
(f) After a minimum of three years of annual sampling, the Division may allow groundwater systems with no previous detection of any contaminant listed in Rule 391-3-5-.18(2)(b) to take one sample during each compliance period.
(g) Each community and non-transient groundwater system which does not detect a contaminant listed in Rule 391-3-5-.18(2)(b)1 -21 may apply to the Division for a waiver from the requirement of paragraph (1)(e) and (1)(f) after completing the initial monitoring. (For the purposes of paragraph (1), detection is defined as 0.0005 mg/L.) A waiver shall be effective for no more than six years (two compliance periods). The Division may also issue waivers to small systems for the initial round of monitoring for 1,2,4-trichlorobenzene.
(h) The Division may grant a waiver after evaluating the factors in accordance with 40 CFR, Part 141.24(f)(8-9).
(i) Each community and non-transient surface water system which does not detect a contaminant listed in Rule 391-3-5-.18(2)(b)1 -21 may apply to the Division for a waiver from the requirements of paragraph (1)(e) after completing the initial monitoring. Composite samples from a maximum of five sampling points are allowed, provided that the detection limit of the method used for analysis is less than one-fifth of the MCL. Systems meeting this criteria must be determined by the Division to be non-vulnerable based on a vulnerability assessment during each compliance period. Each system receiving a waiver shall sample at the frequency specified by the Division (if any).
(j) If a contaminant listed in Rule 391-3-5-.18(2)(b)2 -21 is detected at a level exceeding 0.0005 mg/L in any sample, then:
1. The system must monitor quarterly at each sampling point which resulted in a detection.
2. The Division may decrease the quarterly monitoring requirements specified in paragraph (1)(j)(1); provided it has determined that the system is reliably and consistently below the maximum contaminant level. In no case shall the Division make this determination unless a groundwater system takes a minimum of two quarterly samples and a surface water system takes a minimum of four quarterly samples.
3. If the Division determines that the system is reliably and consistently below the MCL, the Division may allow the system to monitor annually. Systems which monitor annually must monitor during the quarter(s) which previously yielded the highest analytical result.
4. Systems which have three consecutive annual samples with no detection of a contaminant may apply to the Division for a waiver as specified in paragraph (1)(g).
5. Groundwater systems which have detected one or more of the following two-carbon organic compounds: trichloroethylene, tetrachloroethylene, 1,2-dichloroethane, 1,1,1-trichloroethane, cis-1,2-dichloroethylene, trans-1,2-dichloroethylene, or 1,1-dichloroethylene shall monitor quarterly for vinyl chloride. A vinyl chloride sample shall be taken at each sampling point at which one or more of the two-carbon organic compounds was detected. If the results of the first analysis do not detect vinyl chloride, the Division may reduce the quarterly monitoring frequency of vinyl chloride monitoring to one sample during each compliance period. Surface water systems are required to monitor for vinyl chloride as specified by the Division.
(k) Systems which violate the requirements of Rule 391-3-5-.18(2)(b)1 -21 as determined by paragraph (l)(n) must monitor quarterly. After a minimum of four quarterly samples which show the system is in compliance as specified in paragraph (l)(n), and the Division determines that the system is reliably and consistently below the maximum contaminant level, the system may monitor at the frequency and time specified in paragraph (l)(j)3.
(l) The Division may require a confirmation sample for positive or negative results. If a confirmation sample is required by the Division, the result must be averaged with the first sampling result and the average is used for the compliance determination as specified by paragraph (l)(n). The Division has the discretion to delete results of obvious sampling errors from this calculation.
(m) The Division may reduce the total number of samples a system must analyze by allowing the use of compositing. Composite sampling and their analysis shall be in accordance with 40 CFR, Part 141.24(f)(14).
(n) Compliance with Rule 391-3-5-.18(2)(b)1 -21 shall be determined based on the analytical results obtained at each sampling point.
1. For systems which are conducting monitoring at a frequency greater than annual, compliance is determined by a running annual average of all samples taken at each sampling point. If the annual average of any sampling point is greater than the MCL, then the system is out of compliance. If the initial sample or a subsequent sample would cause the annual average to be exceeded, then the system is out of compliance immediately.
2. If monitoring is conducted annually, or less frequently, the system is out of compliance if the level of a contaminant at any sampling point is greater than the MCL. If a confirmation sample is required by the Division, the determination of compliance will be based on the average of two samples.
3. If a public water system has a distribution system separable from other parts of the distribution system with no interconnections, the Division may allow the system to give public notice to only that area served by that portion of the system which is out of compliance.
4. If a system fails to collect the required number of samples, compliance will be based on the total number of samples collected.
(o) Analysis for the contaminants listed in Rule 391-3-5-.18(2)(b)1 -21 shall be conducted in accordance with 40 CFR, Part 141.24(f)(17). These methods are contained in Methods for the Determination of Organic Compounds in Drinking Water, EPA/600/4-88/039, December 1988 and are available from the National Technical Information Service (NTIS) NTIS PB91-231480 and PB91-146027, U.S. Department of Commerce, 5285 Port Royal Road, Springfield, Virginia 22161.
(p) Analysis under paragraph (1) shall only be conducted by laboratories certified by the Division or laboratories certified by EPA in accordance with conditions listed in 40 CFR, Part 141.24(f)(17).
(q) The Division may allow the use of monitoring data collected after January 1, 1998 required under section 1445 of the Public Health Service Act, as amended by the Federal Safe Drinking Water Act, Public Law 93-523, for purposes of initial monitoring compliance. If the data are generally consistent with the other requirements in this rule, the Division may use these data (i.e., a single sample rather than four quarterly samples) to satisfy the initial monitoring requirement of paragraph (l)(d). Systems which use grandfathered samples and did not detect any contaminant listed in Rule 391-3-5-.18(2)(b)2 -21 shall begin monitoring annually in accordance with paragraph 1(e).
(r) The Division may increase required monitoring where necessary to detect variations within the system.
(s) Each certified laboratory must determine the method detection limit (MDL), as defined in 40 CFR, Part 136 appendix B, at which it is capable of detecting VOCs. The acceptable MDL is 0.0005 mg/L. This concentration is the detection concentration for purposes of paragraph (1).
(t) Each public water system shall monitor at the time designated by the Division within each compliance period.
(2) Initial Organic Monitoring. For systems in operation before January 1, 1993, for purposes of initial monitoring, analysis of the contaminants listed in Rule 391-3-5-.18(2)(b)1 -8 for purposes of determining compliance with the maximum contaminant levels shall be conducted as follows:
(a) Ground-water systems shall sample at points of entry to the distribution system representative of each well after any application of treatment. Sampling must be conducted at the same location(s) or more representative location(s) every three months for one year except as provided in paragraph (2)(h).
(b) Surface water systems shall sample at points in the distribution system representative of each source or at entry points to the system after any application of treatment. Surface water systems must sample each source every three months except as provided in paragraph (2)(h). Sampling must be conducted at the same location or a more representative location each quarter.
(c) If the system draws water from more than one source and sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions.
(d) All community water systems and non-transient, non-community water systems serving more than 10,000 people shall analyze all distribution or entry-point samples, as appropriate, representing all source waters beginning no later than January 1, 1988. All community water systems and non-transient, non-community water systems serving from 3,300 to 10,000 people shall analyze all distribution or entry point samples, as required in this paragraph (2), representing source waters no later than January 1, 1989. All other community and non-transient, non-community water systems shall analyze distribution or entry-point samples as required in this paragraph (2), representing all source waters beginning no later than January 1, 1991.
(e) The Division may require confirmation samples for positive or negative results. If a confirmation sample)s) is required by the Division, then the sample results(s) should be averaged with the first sampling result and used for compliance determination in accordance with paragraph (2)(i). The Division has the discretion to delete results of obvious sampling errors from this calculation.
(f) Analysis for vinyl chloride is required only for ground water systems that have detected one or more of the following two-carbon organic compounds: Trichloroethylene, tetrachloroethylene, 1,2-dichloroethane, 1,1,1-trichloroethane, cis-1,2-dichloroethylene, trans-1,2-dichloroethylene, or 1,1-dichloroethylene. The analysis for vinyl chloride is required at each distribution or entry point at which one or more of the two-carbon organic compounds were found. If the first analysis does not detect vinyl chloride, the Division may reduce the frequency of vinyl chloride monitoring to once every three years for that sample location or other sample locations that are more representative of the same source. Surface water systems may be required to analyze for vinyl chloride at the discretion of the Division.
(g) The Division may allow compositing of up to five samples from one or more public water systems.
(h) The Division may reduce the monitoring frequency specified in paragraphs (2)(a) and (b) as explained in this paragraph.
(i) Compliance with Rule 391-3-5-.18(2)(b) shall be determined based on the results of running annual average of quarterly sampling for each sampling location. If one location's average is greater than the MCL, then the system shall be deemed to be out of compliance. If a public water system has a distribution system separable from other parts of the distribution system with no interconnections, only that part of the system that exceeds any MCL as specified in Rule 391-3-5-.18(2)(b) will be deemed out of compliance. The Division may reduce the public notice requirement to that portion of the system which is out of compliance. If any single sample result would cause the annual average to be exceeded, then the system shall be deemed to be out of compliance immediately. For systems that only take one sample per location because no VOCs were detected, compliance shall be based on that one sample.
(j) Analysis under paragraph (2) shall only be conducted by laboratories certified by the Division or have been certified by the EPA.
(k) The Division may allow the use of monitoring data collected after January 1, 1983, for purposes of monitoring compliance. If the data is consistent with other requirements of this rule, the Division may use that data to represent the initial monitoring if the system is determined by the Division not to be vulnerable under the requirements of paragraph (2). In addition, the result of EPA's Ground Water Supply Survey may be used in a similar manner for systems supplied by a single well.
(l) The Division may increase required monitoring where necessary to detect variations within the system.
(m) The Division may determine compliance or initiate enforcement action based on analytical results or other information compiled by their sanctioned representatives and agencies.
(n) Each certified laboratory must determine the method detection limit (MDL), as defined in 40 CFR, Part 136 appendix B, at which it is capable of detecting VOCs. The acceptable MDL is 0.0005 mg/L. This concentration is the detection level for purposes of paragraphs (2)(e), (f), and (g).
(3) Ongoing Organic Monitoring. Analysis of the contaminants listed in Rule 391-3-5-.18(2)(a) for the purposes of determining compliance with the maximum contaminant level shall be conducted as follows:
(a) Groundwater systems shall take a minimum of one sample at every entry point to the distribution system which is representative of each well after treatment (hereafter called a sampling point). Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant.
(b) Surface water systems shall take a minimum of one sample at points in the distribution system that are representative of each source or at each entry point to the distribution system after treatment (hereafter called a sampling point). Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant. [Note: For purposes of this paragraph, surface water systems include systems with a combination of surface and ground sources.]
(c) If the system draws water from more than one source and the sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions (i.e., when water representative of all sources is being used).
(d) Monitoring frequency:
1. Each community and non-transient non-community water system shall take four consecutive quarterly samples for each contaminant listed in Rule 391-3-5-.18(2)(a) during each compliance period beginning with the compliance period starting January 1, 1993.
2. Systems serving more than 3,300 persons which do not detect a contaminant in the initial compliance period, may reduce the sampling frequency to a minimum of two quarterly samples in one year during each repeat compliance period.
3. Systems serving less than or equal to 3,300 persons which do not detect a contaminant in the initial compliance period may reduce the sampling frequency to a minimum of one sample during each repeat compliance period.
(e) Each community and non-transient water system may apply to the Division for a waiver from the requirement of paragraph (3)(d). A system must reapply for a waiver for each compliance period.
(f) The Division may grant a waiver after evaluating the factors in accordance with 40 CFR, Part 141.24(h)(6).
(g) If an organic contaminant listed in Rule 391-3-5-.18(2)(a) is detected (as defined by paragraph (3)(q)) in any sample, then:
1. Each system must monitor quarterly at each sampling point which resulted in a detection.
2. The Division may decrease the quarterly monitoring requirement specified in paragraph (3)(g)1 provided it has determined that the system is reliably and consistently below the maximum contaminant level. In no case shall the Division make this determination unless a groundwater system takes a minimum of two quarterly samples and a surface water system takes a minimum of four quarterly samples.
3. After the Division determines the system is reliably and consistently below the maximum contaminant level the Division may allow the system to monitor annually. Systems which monitor annually must monitor during the quarter that previously yielded the highest analytical result.
4. Systems which have three (3) consecutive annual samples with no detection of a contaminant may apply to the Division for a waiver as specified in paragraph (3)(f).
5. If monitoring results in detection of one or more of certain related contaminants (aldicarb, aldicarb sulfone, aldicarb sulfoxide and heptachlor, heptachlor epoxide), then subsequent monitoring shall analyze for all related contaminants.
(h) Systems which violate the requirements of Rule 391-3-5-.18(2)(a) as determined by paragraph (3)(k) must monitor quarterly. After a minimum of four quarterly samples show the system is in compliance and the Division determines the system is reliably and consistently below the MCL, as specified in paragraph (3)(k), the system shall monitor at the frequency specified in paragraph (3)(g)3.
(i) The Division may require a confirmation sample for positive or negative results. If a confirmation sample is required by the Division, the result must be averaged with the first sampling result and the average used for the compliance determination as specified by paragraph (3)(k). The Division has the discretion to delete results of obvious sampling errors from this calculation.
(j) The Division may reduce the total number of samples a system must analyze by allowing the use of compositing. Composite sampling and their analysis shall be in accordance with 40 CFR, Part 141.24(h)(10).
(k) Compliance with Rule 391-3-5-.18(2)(a) shall be determined based on the analytical results obtained at each sampling point.
1. For systems which are conducting monitoring at a frequency greater than annual, compliance is determined by a running annual average of all samples taken at each sampling point. If the annual average of any sampling point is greater than the MCL, then the system is out of compliance. If the initial sample or a subsequent sample would cause the annual average to be exceeded, then the system is out of compliance immediately. Any samples below the detection limit shall be calculated as zero for purposes of determining the annual average.
2. If monitoring is conducted annually, or less frequently, the system is out of compliance if the level of a contaminant at any sampling point is greater than the MCL. If a confirmation sample is required by the Division, the determination of compliance will be based on the average of two samples.
3. If a public water system has a distribution system separable from other parts of the distribution system with no interconnections, the Division may allow the system to give public notice to only that portion of the system which is out of compliance.
4. If a system fails to collect the required number of samples, compliance will be based on the total number of samples collected.
(l) Analysis for the contaminants listed in Rule 391-3-5-.18(2)(a) shall be conducted in accordance with 40 CFR, Part 141.24(h) (12-13). These methods are contained in "Methods for the Determination of Organic Compounds in Drinking Water", ORD Publications, CERI, EPA/600/4-88/039, December 1988.
(m) If monitoring data collected after January 1, 1990, are generally consistent with the requirements of Rule 391-3-5-.22(3), then the Division may allow systems to use that data to satisfy the monitoring requirement for the initial compliance period beginning January 1, 1993.
(n) The Division may increase the required monitoring frequency, where necessary, to detect variations within the system (e.g., fluctuations in concentration due to seasonal use, changes in water source).
(o) The Division has the authority to determine compliance or initiate enforcement action based upon analytical results and other information compiled by their sanctioned representatives and agencies.
(p) Each public water system shall monitor at the time designated by the Division within each compliance period.
(q) Detection limits for contaminants used in paragraph (3) shall be in accordance with 40 CFR, Part 141.24(h)(18).
(r) Analysis under paragraph (3) shall conform to paragraph (1) of Rule 391-3-5-.29.
(s) The best technology, treatment technique, or other means available for achieving compliance with the maximum contaminant level for organic contaminants in Rule 391-3-5-.18(2)(a) and (2)(b) shall be in accordance with 40 CFR, Part 141.61(b).

Rule 391-3-5-.23 Coliform Sampling

(1) Routine Coliform Monitoring.
(a) Public water systems must collect total coliform samples at sites which are representative of water throughout the distribution system according to a written sample siting plan. These plans are subject to Division review and revision.
(b) The minimum residential population of a community water system shall be determined by a mathematical calculation of the total number of active residential service connections multiplied by Georgia's average population per household, as published in the most recent Federal Census Bureau Statistics. Multiple residential units served by a single connection (master meter) shall be included in the determination of population for a water system. The minimum monitoring frequency for total coliforms for community water systems is based on the population served by the system, as follows:

Population Served

Minimum Number of Samples per Month

25 to 1,0001

1

1,001 to 2,500

2

2,501 to 3,300

3

3,301 to 4,100

4

4,101 to 4,900

5

4,901 to 5,800

6

5,801 to 6,700

7

6,701 to 7,600

8

7,601 to 8,500

9

8,501 to 12,900

10

12,901 to 17,200

15

17,201 to 21,500

20

21,501 to 25,000

25

25,001 to 33,000

30

33,001 to 41,000

40

41,001 to 50,000

50

50,001 to 59,000

60

59,001 to 70,000

70

70,001 to 83,000

80

83,001 to 96,000

90

96,001 to 130,000

100

130,001 to 220,000

120

220,001 to 320,000

150

320,001 to 450,000

180

450,001 to 600,000

210

600,001 to 780,000

240

780,001 to 970,000

270

970,001 to 1,230,000

300

1,230,001 to 1,520,000

330

1,520,001 to 1,850,000

360

1,850,001 to 2,270,000

390

2,270,001 to 3,020,000

420

3,020,001 to 3,960,000

450

3,960,001 or more

480

1Includes public water systems which have at least 15 service connections, but serve fewer than 25 persons.

If a community water system serving 25 to 1,000 persons has no history of total coliform contamination in its current configuration and a sanitary survey conducted in the past five years shows that the system is supplied solely by a protected ground water source and is free of sanitary defects, the Division may reduce the monitoring frequency specified above, except that in no case shall it be reduced to less than one sample per quarter.
(c) The monitoring frequency for total coliform for non-community water systems is as follows:
1. A non-community water system using only ground water (except ground water under the direct influence of surface water) and serving 1,000 persons or fewer must monitor each calendar quarter that the system provides water to the public, except that the Division may adjust this monitoring frequency in writing, if a sanitary survey shows that the system is free of sanitary defects.
2. A non-community water system using only ground water (except ground water under the direct influence of surface water) and serving more than 1,000 persons during any month must monitor at the same frequency as a like-sized community water system, except that the Division may adjust this monitoring frequency, in writing for any month the system serves 1,000 persons or fewer.
3. A non-community water system using surface water, in total or in part, must monitor at the same frequency as a like-sized community water system, regardless of the number of persons it serves.
4. A non-community water system using ground water under the direct influence of surface water must monitor at the same frequency as a like-sized community water system. The system must begin monitoring at this frequency beginning six months after the Division determines that the ground water is under the direct influence of surface water.
(d) The public water system must collect samples at regular time intervals throughout the month, except that a system which uses only ground water (except ground water under the direct influence of surface water), and serves 4,900 persons or fewer, may collect all required samples on a single day if they are taken from different sites.
(e) Special purpose samples, such as those taken to determine whether disinfection practices are sufficient following pipe placement, replacement, or repair, shall not be used to determine compliance with the MCL for total coliforms. Repeat samples are not considered special purpose samples, and must be used to determine compliance with the MCL for total coliforms.
(2) Repeat Coliform Monitoring.
(a) If a routine sample is total coliform-positive, the public water system must collect a set of repeat samples within 24 hours of being notified of the positive result. A system which collects more than one routine sample per month must collect no fewer than three repeat samples for each total coliform-positive sample found. A system which normally collects one routine sample per month or fewer must collect no fewer than four repeat samples for each total coliform-positive sample found. The Division may extend the 24- hour limit on a case-by-case basis if the system has a logistical problem in collecting the repeat samples within 24 hours that is beyond its control.
(b) The system must collect at least one repeat sample from the sampling tap where the original total coliform-positive sample was taken, and at least one repeat sample at a tap within five service connections upstream and at least one repeat sample at a tap within five service connections downstream of the original sampling site. If a total coliform-­positive sample is at the end of the distribution system, or one away from the end of the distribution system, the Division may waive the requirement to collect at least one repeat sample upstream or downstream of the original sampling site.
(c) The system must collect all repeat samples on the same day, except that the Division may allow a system with a single service connection to collect the required set of repeat samples over a four-day period.
(d) If one or more repeat samples in the set is total coliform-positive, the public water system must collect an additional set of repeat samples in the manner specified in paragraph (2). The additional samples must be collected within 24 hours of being notified of the positive result, unless the Division extends the limit as provided in paragraph (2). The system must repeat this process until either total coliforms are not detected in one complete set of repeat samples or the system determines that the MCL for total coliforms has been exceeded and notifies the Division.
(e) If a system collecting fewer than five routine samples per month has one or more total coliform-positive samples and the Division does not invalidate the sample(s), it must collect at least five routine samples during the next month the system provides water to the public, except that the Division may waive this requirement if the conditions specified below are met. The Division cannot waive the requirement for a system to collect repeat samples.
1. The Division may waive the requirement to collect five routine samples the next month the system provides water to the public if the Division, or an agent approved by the Division, performs a site visit before the end of the next month the system provides water to the public. Although a sanitary survey need not be performed, the site visit must be sufficiently detailed to allow the Division to determine whether additional monitoring and/or any corrective action is needed. The Division cannot approve an employee of the system to perform this site visit, even if the employee is an agent approved by the Division to perform sanitary surveys.
2. The Division may waive the requirement to collect five routine samples the next month the system provides water to the public if the Division has determined why the sample was total coliform-positive and establishes that the system has corrected the problem or will correct the problem before the end of the next month the system serves water to the public. The Division cannot waive the requirement to collect five routine samples the next month the system provides water to the public solely on the grounds that all repeat samples are total coliform-negative. Under this paragraph, a system must still take at least one routine sample before the end of the next month it serves water to the public and use it to determine compliance with the MCL for total coliforms, unless the Division has determined that the system has corrected the contamination problem before the system took the set of repeat samples required above, and all repeat samples were total coliform­-negative.
(f) After a system collects a routine sample and before it learns the results of the analysis of that sample, if it collects another routine sample(s) from within five adjacent service connections of the initial sample, and the initial sample, after analysis, is found to contain total coliforms, then the system may count the subsequent sample(s) as a repeat sample instead of as a routine sample.
(g) Results of all routine and repeat samples not invalidated by the Division must be included in determining compliance with the MCL for total coliforms.
(3) Invalidation of Total Coliform Samples. A total coliform-positive sample invalidated under this paragraph does not count towards meeting the minimum monitoring requirements of this Rule.
(a) The Division may invalidate a total coliform-positive sample only if the conditions that follow below are met:
1. The laboratory establishes that improper sample analysis caused the total coliform-­positive result.
2. The Division, on the basis of the results of repeat samples collected as required by this Rule, determines that the total coliform-positive sample resulted from a domestic or other non-distribution system plumbing problem. The Division cannot invalidate a sample on the basis of repeat sample results unless all repeat sample(s) collected at the same tap as the original total coliform-positive sample are also total coliform-positive, and all repeat samples collected within five service connections of the original tap are total coliform-negative (e.g., the Division cannot invalidate a total coliform-positive sample on the basis of repeat samples if all the repeat samples are total coliform-negative, or if the public water system has only one service connection).
3. The Division has substantial grounds to believe that a total coliform-positive result is due to a circumstance or condition which does not reflect water quality in the distribution system. In this case, the system must still collect all repeat samples required under this Rule, and use them to determine compliance with the MCL for total coliforms. The Division may not invalidate a total coliform-positive sample solely on the grounds that all repeat samples are total coliform-negative.
(b) A laboratory must invalidate a total coliform sample (unless total coliforms are detected) if the sample produces a turbid culture in the absence of gas production using an analytical method where gas formation is examined (e.g., the Multiple-Tube Fermentation Technique), produces a turbid culture in the absence of an acid reaction in the Presence-Absence (P-A) Coliform Test, or exhibits confluent growth or produces colonies too numerous to count with an analytical method using a membrane filter (e.g., Membrane Filter Technique). If a laboratory invalidates a sample because of such interference, the system must collect another sample from the same location as the original sample within 24 hours of being notified of the interference problem, and have it analyzed for the presence of total coliforms. The system must continue to re-sample within 24 hours and have the samples analyzed until it obtains a valid result. The Division may waive the 24-hour time limit on a case-by-case basis.
(4) Sanitary Surveys.
(a) All ground water systems must undergo sanitary surveys no less frequently than every three years for community systems, except as provided in paragraph (4)(b), and no less frequently than every five years for non-community systems. The initial sanitary survey for each community ground water system must be conducted by December 31, 2012, unless the system meets requirements of paragraph (4)(b).
(b) For community ground water systems determined by the Division to have outstanding performance based on prior sanitary surveys, or that provide at least 4-log (99.99%) treatment of viruses (using inactivation, removal, or a combination of the two) subsequent sanitary surveys may be conducted no less than every five years. The initial sanitary survey for community systems that meet these requirements and for each non-community system must be conducted by December 31, 2014.
(c) All surface water systems (including ground water under the influence) must undergo sanitary surveys no less frequently than every three years for community systems and no less frequently than every five years for non-community systems. For community systems determined by the Division to have outstanding performance based on prior sanitary surveys, subsequent sanitary surveys may be conducted no less than every five years.
(d) Sanitary surveys must be performed by the Division or an agent approved by the Division. The system is responsible for ensuring the survey takes place.
(5) Fecal Coliforms - Escherichia coli (E. coli) Testing.
(a) If any routine or repeat sample is total coliform-positive, the system must analyze that total coliform-positive culture medium to determine if fecal coliforms are present, except that the system may test for E. coli in lieu of fecal coliforms. If fecal coliforms or E. coli are present, the system must notify the Division by the end of the day when the system is notified of the test result, unless the system is notified of the result after the Division office is closed, in which case the system must notify the Division before the end of the next business day.
(b) The Division has the discretion to allow a public water system, on a case-by-case basis, to forego fecal coliform or E. coli testing on a total coliform-positive sample if that system assumes that the total coliform-positive sample is fecal coliform-positive or E. coli-positive. Accordingly, the system must notify the Division as specified in this Rule and the MCL applies.
(6) Analytical Methodology.
(a) The standard sample volume required for total coliform analysis, regardless of analytical method used, is 100 mL.
(b) Public water systems need only determine the presence or absence of total coliforms; a determination of total coliform density is not required.
(c) Public water systems must conduct total coliform analyses in accordance with 40 CFR § 141.21.
(d) Public water systems must conduct fecal coliform analyses in accordance with 40 CFR § 141.21.
(7) Response to Violation.
(a) A public water system which has exceeded the MCL for total coliforms must report the violation to the Division no later than the end of the next business day after it learns of the violation, and notify the public in accordance with this chapter.
(b) A public water system which has failed to comply with a coliform monitoring requirement, including the sanitary survey requirement, must report the monitoring violation to the Division within ten days after the system discovers the violation, and notify the public in accordance with this chapter.
(8) The provisions of paragraphs (1) and (4) are applicable until March 31, 2016. The provisions of paragraphs (2), (3), (5), (6), and (7) are applicable until all required repeat monitoring under paragraph (2) and fecal coliform or E. coli testing under paragraph (5) that was initiated by a total coliform-positive sample taken before April 1, 2016 is completed, as well as analytical method, reporting, recordkeeping, public notification, and consumer confidence report requirements associated with that monitoring and testing. Beginning April 1, 2016, the provisions of Rule 391-3-5-.55 are applicable, with systems required to begin regular monitoring at the same frequency as the system-specific frequency required on March 31, 2016, except for seasonal systems which must monitor monthly beginning April 1, 2016.

Rule 391-3-5-.24 Disinfectant Residuals, Disinfection Byproducts, and Disinfection Byproduct Precursors Sampling, Analytical and Other Requirements

(1) Purpose. The purpose of this Rule is to provide for the procedures for establishing maximum contaminant levels, monitoring and other requirements for trihalomethanes, disinfectant residuals, disinfection byproducts, and disinfection byproduct precursors.
(2) Variances. Variances from the maximum contaminant level for total trihalomethanes shall be conducted in accordance with 40 CFR § 142.60.
(3) Disinfectant Residuals, Disinfection Byproducts, and Disinfection Byproduct Precursors.
(a) Community water systems and non-transient, non-community water systems which add a chemical disinfectant to the water in any part of the drinking water treatment process must modify their practices to meet MCLs and MRDLs specified in subparagraph (7)(a) of Rule 391-3-5-.18, and must meet the treatment technique requirements for disinfection byproduct precursors specified in paragraph (10).
(b) Transient non-community water systems that use chlorine dioxide as a disinfectant or oxidant must modify their practices to meet the MRDL for chlorine dioxide specified in subparagraph (7)(a) of Rule 391-3-5-.18.
(c) Community Subpart H water systems and non-transient, non-community Subpart H water systems must comply with the requirements of this Rule, as specified in paragraphs (7)(b) and (7)(c) of Rule 391-3-5-.18, respectively.
(d) Beginning January 1, 2002, transient non-community Subpart H water systems serving 10,000 or more persons and using chlorine dioxide as a disinfectant or oxidant must comply with the requirements for chlorine dioxide and chlorite in this Rule.
(e) Beginning January 1, 2004, transient non-community Subpart H water systems serving fewer than 10,000 people and using chlorine dioxide as a disinfectant or oxidant and systems using only ground water not under the direct influence of surface water and using chlorine dioxide as a disinfectant or oxidant must comply with the requirements for chlorine dioxide and chlorite in this Rule.
(f) Systems may increase residual disinfectant levels in the distribution system of chlorine or chloramines (but not chlorine dioxide) to a level and for a time necessary to protect public health, to address specific microbiological contamination problems caused by circumstances such as, but not limited to, distribution line breaks, storm run-off events, source water contamination events, or cross-connection events.
(g) Systems must use the analytical method(s) specified in 40 CFR § 141.131 to demonstrate compliance with the requirements of this Rule. The analytical requirements specified in 40 CFR § 141.131, which is hereby incorporated by reference, are required to demonstrate compliance with the requirements of Subpart L (Disinfectant Residuals, Disinfection ByProducts, and Disinfection ByProduct Precursors), Subpart U (Initial Distribution System Evaluations), and Subpart V (Stage 2 Disinfection ByProducts Requirements) of 40 CFR Part 141.
(h) Monitoring Requirements. 40 CFR § 141.132, in its entirety, is hereby incorporated by reference. For compliance with the requirements of this Rule, the water systems must monitor the applicable parameters included in this Rule at the frequency specified in 40 CFR § 141.132. Failure to monitor will be treated as a violation for the entire period covered by the annual average where compliance is based on a running annual average of monthly or quarterly samples or averages and the system's failure to monitor makes it impossible to determine compliance with MCLs or MRDLs.
1. Systems must take all samples during normal operating conditions.
2. Systems may consider multiple wells drawing water from a single aquifer as one treatment plant for determining the minimum number of TTHM and HAA5 samples required, with the Division approval.
3. Systems may use only data collected under the provisions of this Rule to qualify for reduced monitoring.
4. Each system required to monitor under this Rule must develop and implement a monitoring plan. The plan must include at least the following elements: specific locations and schedules for collecting samples for any parameters included in this Rule; how the system will calculate compliance with MCLs, MRDLs, and treatment techniques; and if approved for monitoring as a consecutive system, or if providing water to a consecutive system, the sampling plan must reflect the entire distribution system.
(i) The system must maintain the plan and make it available for inspection by the Division and the general public no later than thirty (30) days following applicable compliance dates stated in paragraph (3)(c).
(ii) All Subpart H systems serving more than 3,300 people must submit a copy of the monitoring plan to the Division no later than the date of the first report required under 40 CFR § 141.134.
(iii) The Division may require a monitoring plan to be submitted by any other system. The Division may also require changes in any plan elements.
(4) Monitoring and Compliance for Disinfection Byproducts. Monitoring for disinfection byproducts shall be conducted as specified in 40 CFR § 141.132(b). Compliance with the disinfection byproducts requirements shall be determined in accordance with 40 CFR § 141.133(b).
(5) Monitoring and Compliance for Disinfectant Residuals.
(a) Monitoring for disinfectant residuals shall be conducted as specified in 40 CFR § 141.132(c). Compliance with the disinfectant residuals requirements shall be determined in accordance with 40 CFR § 141.133(c).
(b) Routine monitoring. Until March 31, 2016, community and non-transient non-community water systems that use chlorine or chloramines must measure the residual disinfectant level in the distribution system at the same point in the distribution system and at the same time as total coliforms are sampled, as specified in 40 CFR § 141.21. Beginning April 1, 2016, community and non-transient non-community water systems that use chlorine or chloramines must measure the residual disinfectant level in the distribution system at the same point in the distribution system and at the same time as total coliforms are sampled, as specified in Rule 391-3-5-.55(4) through (8). 40 CFR Part 141 Subpart H systems may use the results of residual disinfectant concentration sampling conducted under 40 CFR § 141.74(c)(3)(i) for systems which filter, in lieu of taking separate samples.
(6) Monitoring and Compliance for Disinfection Byproduct Precursors. Monitoring for disinfection byproduct precursors shall be conducted as specified in 40 CFR § 141.132(d). Compliance with the disinfection byproduct precursors requirements shall be determined in accordance with 40 CFR § 141.133(c) and as specified by 40 CFR § 141.135(b).
(7) Non-Compliance in First Monitoring Year. If, during the first year of monitoring under 40 CFR § 141.132, any individual quarter's average will cause the running annual average of that system to exceed the MCL, the system shall be considered out of compliance at the end of that quarter.
(8) Samples for Compliance Determination. All samples taken and analyzed under the provisions of this Rule must be included in determining compliance, even if that number is greater than the minimum required. Compliance requirements specified in 40 CFR Part 141, Subpart L § 141.133 is hereby incorporated by reference.
(9) Treatment Techniques. Treatment techniques for control of disinfection byproduct precursors requirements specified in 40 CFRPart 141, Subpart L § 141.135 is hereby incorporated by reference.
(a) Subpart H systems using conventional filtration treatment (as defined in § 141.2) must operate with enhanced coagulation or enhanced softening to achieve the TOC percent removal levels specified in 40 CFR § 141.135(b) unless the system meets at least one of the alternative compliance criteria specified in 40 CFR §§ 141.135(a)(2) or (a)(3).
(b) Alternative compliance criteria for enhanced coagulation and enhanced softening systems: 40 CFR Part 141, Subpart L § 141.135(a)(2) is hereby incorporated by reference.
(c) Additional alternative compliance criteria for softening systems: 40 CFR Part 141, Subpart L, § 141.135(a)(3) is hereby incorporated by reference.
(d) Enhanced coagulation and enhanced softening performance requirements: 40 CFR Part 141, Subpart L § 141.135(b) is hereby incorporated by reference.
(e) Compliance calculations: 40 CFR Part 141, Subpart L § 141.135(c) is hereby incorporated by reference.
(f) Treatment technique requirements for disinfection byproduct precursors: 40 CFR Part 141, Subpart L § 141.135(d) is hereby incorporated by reference.
(g) Required additional health information: 40 CFR § 141.154 is hereby incorporated by reference.

Rule 391-3-5-.25 Treatment Techniques, Lead and Copper Requirements

(1) General Requirements.
(a) These requirements constitute the primary drinking water rules for lead and copper. Unless otherwise indicated, each of these provisions applies to community water systems and non-transient, non-community water systems (hereinafter referred to as "water systems" or "systems").
(b) These rules establish a treatment technique that includes requirements for corrosion control treatment, source water treatment, lead service line replacement, and public education. These requirements are triggered, in some cases, by lead and copper action levels measured in samples collected at consumers' taps.
(c) Lead and copper action levels:
1. The lead action level is exceeded if the concentration of lead in more than 10 percent of tap water samples collected during any monitoring period conducted in accordance with paragraph (7) is greater than 0.015 mg/L.
2. The copper action level is exceeded if the concentration of copper in more than 10 percent of tap water samples collected during any monitoring period conducted in accordance with paragraph (7) is greater than 1.3 mg/L.
3. Calculation of the lead and copper action levels shall be based on the "90th percentile" rule in accordance with 40 CFR, Part 141.80(c)(3).
(d) Corrosion control treatment requirements:
1. All water systems shall install and operate optimal corrosion control treatment as defined in Rule 391-3-5-.02(73).
2. Any water system that complies with the applicable corrosion control treatment requirements specified by the Division under paragraphs (2) and (3) shall be deemed in compliance with the treatment requirement contained in paragraph (d)(1).
(e) Source water treatment requirements; Any system exceeding the lead or copper action level shall implement all applicable source water treatment requirements specified by the "Division" under paragraph (4).
(f) Lead service line replacement requirements; Any system exceeding the lead action level after implementation of applicable corrosion control and source water treatment requirements shall complete the lead service replacement requirements contained in paragraph (5).
(g) Public education requirements; Pursuant to 40 CFR, Part 141.85, all water systems must provide a consumer notice of lead tap water monitoring results to persons served at the sites/taps that are tested. Any system exceeding the lead action level shall implement the public education requirements contained in paragraph (6).
(h) Monitoring and analytical requirements; Tap water monitoring for lead and copper, monitoring for water quality parameters, source water monitoring for lead and copper, and analyses of the monitoring results under this subpart shall be completed in compliance with paragraphs (7) - (10).
(i) Reporting requirements; Systems shall report to the Division any information required by the treatment provisions of this subpart and Rule 391-3-5-.30(7).
(j) Record keeping requirements; Systems shall maintain records in accordance with Rule 391-3-5-.15.
(k) Violation of national primary drinking water regulations; Failure to comply with the applicable requirements of paragraphs (1) - (10), including requirements established by the Division pursuant to the provisions, shall constitute a violation of the national primary drinking water regulations for lead and/or copper.
(l) The maximum contaminant level goals (MCLGs) for lead and copper are as follows:

Contaminant

MCLG (mg/L)

Copper

1.3

Lead

0 (zero)

(2) Applicability of Corrosion Control Treatment Steps to Small, Medium and Large Water Systems.
(a) Systems shall complete the applicable corrosion control treatment requirements described in paragraph (3) by the deadlines established in this paragraph.
1. A large system (serving more than 50,000 persons) shall complete the corrosion control treatment steps specified in paragraph (2)(d), unless it is deemed to have optimized corrosion control under paragraphs (2)(b)2. or (2)(b)3..
2. A small system (serving less than 3,301 persons) and a medium-size system (serving more than 3,300 and less than 50,001 persons) shall complete the corrosion control treatment steps specified in paragraph (2)(d), unless it is deemed to have optimized corrosion control under paragraphs (2)(b)1., (2)(b)2., or (2)(b)3..
(b) A system is deemed to have optimized corrosion control and is not required to complete the applicable control treatment steps identified in this section if the system satisfies one of the criteria specified in paragraphs (2)(b)1. through (2)(b)3.. Any such system deemed to have optimized corrosion control under this paragraph, and which has treatment in place, shall continue to operate and maintain optimal corrosion control treatment and meet any requirements that the State determines appropriate to ensure optimal corrosion control treatment is maintained.
1. A small or medium-size water system is deemed to have optimized corrosion control if the system meets the lead and copper action levels during each of two consecutive six-month monitoring periods conducted in accordance with paragraph (7).
2. Any water system may be deemed by the Division to have optimized corrosion control treatment if the system demonstrates to the satisfaction of the Division that it has conducted activities equivalent to the corrosion control steps applicable to such system under this rule. If the Division makes this determination, it shall provide the system with written notice explaining the basis for its decision and shall specify the water quality control parameters representing optimal corrosion control in accordance with paragraph (3). Water systems deemed to have optimized corrosion control under this paragraph shall operate in compliance with the Division designated optimal water quality control parameters in accordance with paragraph (3) and continue to conduct lead and copper tap water quality parameter sampling in accordance with paragraphs (7)(d) 3. and (8)(d). A system shall provide the Division with the following information in order to support a determination under this paragraph.
(i) the results of all test samples collected for each of the water quality parameters in paragraph (3).
(ii) a report explaining the test methods used by the water system to evaluate the corrosion control treatments listed in paragraph (3), the results of all tests conducted, and the basis for the system's selection of optimal corrosion control treatment.
(iii) a report explaining how corrosion control has been installed and how it is being maintained to insure minimal lead and copper concentrations at consumers' taps.
(iv) the results of tap water samples collected in accordance with paragraph (7) at least once every six months for one year after corrosion control has been installed.
3. Any water system is deemed to have optimized corrosion control if it submits results of tap water monitoring conducted in accordance with paragraph (7) and source water monitoring conducted in accordance with paragraph (9) that demonstrates for two consecutive six-month monitoring periods that the difference between the 90th percentile tap water lead level computed under paragraph (1)(c) 3., and the highest source water lead concentration, is less than the Practical Quantitation Level for lead specified in paragraph (10).
(i) Those systems whose highest source water lead level is below the Method Detection Limit may also be deemed to have optimized corrosion control under this paragraph if the 90th percentile tap water lead levels is less than or equal to the Practical Quantitation Level for the lead for two consecutive 6-month monitoring periods.
(ii) Any water system deemed to have optimized corrosion control in accordance with this paragraph shall continue monitoring for lead and copper at the tap no less frequently than once every three calendar years using the reduced number of sites specified in Rule 391-3-5-.25(7)(c) and collecting samples at times and locations specified in Rule 391-3-5-.25(7)(d) 4.
(iii) Any water system deemed to have optimized corrosion control pursuant to this paragraph shall notify the Division in writing pursuant to Rule 391-3-5-.25(11) of any upcoming long-term change in treatment or addition of a new source. The Division must review and approve the addition of a new source or long-term change in water treatment before it is implemented by the water system. The Division may require any system to conduct additional monitoring or to take other action the Division deems appropriate to ensure that such systems maintain minimal levels of corrosion in the distribution system.
(iv) As of July 12, 2001, a system is not deemed to have optimized corrosion control under this paragraph, and shall implement corrosion control treatment pursuant to paragraph (2)(b)3.(v) unless it meets the copper action level.
(v) Any system triggered into corrosion control because it is no longer deemed to have optimized corrosion control under this paragraph shall implement corrosion control treatment in accordance with the deadlines in paragraph (2)(d). Any such large system shall adhere to schedule specified in that paragraph for medium-size systems, with the time periods for completing each step being triggered by the date the system is no longer deemed to have optimized corrosion control under this paragraph.
(c) Any small or medium-size water system that is required to complete the corrosion control steps due to its exceedance of the lead or copper action level may request approval from the Division to cease completing the treatment steps if the system meets both lead and copper action levels during each of two consecutive monitoring periods conducted pursuant to paragraph (7) and submits the results to the Division. If approval is granted, any such water system thereafter exceeds the lead or copper action level during any monitoring period, the system (or the Division, as the case may be) shall recommence completion of the applicable treatment steps, beginning with the first treatment step which was not previously completed in its entirety. The Division may require a system to repeat treatment steps previously completed by the system where the Division determines that this is necessary to implement properly the treatment requirements of this rule. The Division shall notify the water system in writing of such a determination and explain the basis for its decision. The requirement for any small- or medium-size water system to implement corrosion control treatment steps in accordance with paragraph (2)(d) (including, water systems deemed to have optimized corrosion control under paragraph (2)(b)1.) is triggered whenever any small- or medium-size water system exceeds the lead or copper action level.
(d) Treatment steps and deadlines for all systems affected by this rule shall be in accordance with 40 CFR, Part 141.81(d) and (e).
(3) Description of Corrosion Control Treatment Requirements. Each system shall complete the corrosion control treatment requirements as described and in accordance with 40 CFR Part 141.82 and as approved by the Division.
(4) Source Water Treatment Requirements. Systems shall complete the applicable source water monitoring and treatment requirements, described in the referenced portions of paragraph (4)(b), and in paragraphs (7) and (9) by the following deadlines.
(a) Deadlines for Completing Source Water Treatment Steps.
1. Step 1: A system exceeding the lead or copper action level shall complete lead and copper source water monitoring (paragraph (9)(b)) and make a treatment recommendation to the Division (paragraph (4)(b) 1.) no later than 180 days after the end of the monitoring period in which the lead or copper action level was exceeded.
2. Step 2: The Division shall make a determination regarding source water treatment (paragraph (4)(b) 2.) within 6 months after submission of monitoring results under Step 1.
3. Step 3: If the Division requires installation of source water treatment, the system shall install the treatment (paragraph (4)(b) 3.) within 24 months after completion of Step 2.
4. Step 4: The system shall complete follow-up tap water monitoring for lead and copper (paragraph (7)(d) 2.) and source water monitoring for lead and copper (paragraph (9)(c)) within 36 months after completion of Step 2.
5. Step 5: The Division shall review the system's installation and operation of source water treatment and specify maximum permissible source water levels (paragraph (4)(b) 4.) within 6 months after completion of Step 4.
6. Step 6: The system shall operate in compliance with the Division specified maximum permissible lead and copper source water levels (paragraph (4)(b) 4.) and continue source water monitoring for lead and copper (paragraph (9)(d)).
(b) Description of Source Water Treatment Requirements:
1. System treatment recommendation. Any system which exceeds the lead or copper action level shall recommend in writing to the Division the installation and operation of one of the source water treatments listed in paragraph (4)(b)2.. A system may recommend that no treatment be installed based upon a demonstration that source water treatment is not necessary to minimize lead and copper levels at users' taps.
2. Division determination regarding source water treatment. The Division shall complete an evaluation of the results of all source water samples submitted by the water system to determine whether source water treatment is necessary to minimize lead or copper levels in water delivered to users' taps. If the Division determines that treatment is needed, the Division shall either require installation and operation of the source water treatment recommended by the system (if any) or require the installation and operation of another source water treatment such as: ion exchange, reverse osmosis, lime softening or coagulation/filtration. If the Division requests additional information to aid in its review, the water system shall provide the information by the date specified by the Division in its request. The Division shall notify the system in writing of its determination and set forth the basis for its decision.
3. Installation of source water treatment. Each system shall properly install and operate the source water treatment designated by the Division under paragraph (4)(b)2..
4. Division review of source water treatment and specification of maximum permissible source water levels. The Division shall review the source water samples taken by the water system both before and after the system installs source water treatment, and determine whether the system has properly installed and operated the source water treatment designated by the Division. Based upon its review, the Division shall designate the maximum permissible lead and copper concentrations for finished water entering the distribution system. Such levels shall reflect the contaminant removal capability of the treatment properly operated and maintained. The Division shall notify the system in writing and explain the basis for its decision.
5. Continued operation and maintenance. Each water system shall maintain lead and copper levels below the maximum permissible concentrations designated by the Division at each sampling point monitored in accordance with paragraph (9). The system is out of compliance with this paragraph if the level of lead and/or copper at any sampling point is greater than the maximum permissible concentration designated by the Division.
6. Modification of Division treatment decisions. Upon its own initiative or in response to a request by a water system or other interested party, the Division may modify its determination of the source water treatment under paragraph (2), or maximum permissible lead and copper concentrations for finished water entering the distribution system under paragraph (4. A request for modification by a system or other interested party shall be in writing, explain why the modification is appropriate, and provide supporting documentation. The Division may modify its determination where it concludes that such change is necessary to ensure that the system continues to minimize lead and copper concentrations in source water. A revised determination shall be made in writing, set forth the new treatment requirements, explain the basis for the Division's decision, and provide an implementation schedule for completing the treatment modifications.
7. EPA may review treatment determinations made by the Division and issue federal treatment determinations as outlined in 40 CFR, Part 141.83(b)(7).
(5) Lead Service Line Replacement Requirements. Systems may be required to replace lead service lines in accordance with 40 CFR Parts 141.84 and 141.90(e) when they fail to meet the lead action level in tap samples. 40 CFR Part 141.84 describes the conditions that will require lead service line replacement.
(6) Public Educational and Supplemental Monitoring Requirements. All water systems must deliver a consumer notice of lead tap water monitoring results to persons served by the water system at the sites/taps that are tested. A water system that exceeds the lead action level based on tap water samples collected in accordance with paragraph (7) shall carry out a public education program as described in 40 CFR, Part 141.85.
(7) Monitoring Requirements for Lead and Copper in Tap Water.
(a) Sample site location.
1. By the applicable date for commencement of monitoring under paragraph (7)(d)1., each water system shall complete a materials evaluation of its distribution system. In order to identify a pool of targeted sampling sites that meets the requirements of this rule, and which is sufficiently large to ensure that the water system can collect the number of lead and copper tap samples required in paragraph (7)(c). All sites from which first draw samples are collected shall be selected from this pool of targeted sampling sites. Sampling sites may not include faucets that have point-of-use or point-of-entry treatment devices.
2. A water system shall use the information on lead, copper, and galvanized steel that it is required to collect under Rule 391-3-5-.26(4) of this part [special monitoring for corrosivity characteristics] when conducting a materials evaluation. When an evaluation of the information collected pursuant to Rule 391-3-5-.26(4) is insufficient to locate the requisite number of lead and copper sampling sites that meet the targeting criteria in paragraph (7)(a)1., the water system shall review the sources of information listed below in order to identify a sufficient number of sampling sites. In addition, the system shall seek to collect such information where possible in the course of its normal operations (e.g., checking service line materials when reading water meters or performing maintenance activities):
(i) all plumbing codes, permits, and records in the files of the building department(s) which indicate the plumbing materials that are installed within publicly and privately owned structures connected to the distribution system;
(ii) all inspections and records of the distribution system that indicate the material composition of the service connections that connect a structure to the distribution system; and
(iii) all existing water quality information, which includes the results of all prior analyses of the system or individual structures connected to the system, indicating locations that may be particularly susceptible to high lead or copper concentrations.
3. The sampling sites selected for a community water system's sampling pool ("tier 1 sampling sites") shall consist of single family structures that:
(i) contain copper pipes with lead solder installed after 1982 or contain lead pipes; and/or
(ii) are served by a lead service line. When multiple-family residences comprise at least 20 percent of the structures served by a water system, the system may include these types of structures in its sampling pool.
4. Any community water system with insufficient tier 1 sampling sites shall complete its sampling pool with "tier 2 sampling sites", consisting of buildings, including multiple-family residences that:
(i) contain copper pipes with lead solder installed after 1982 or contain lead pipes; and/or
(ii) are served by a lead service line.
5. Any community water system with insufficient tier 1 and tier 2 sampling sites shall complete its sampling pool with "tier 3 sampling sites", consisting of single family structures that contain copper pipes with lead solder installed before 1983. A community water system with insufficient tier 1, tier 2, and tier 3 sampling sites shall complete its sampling pool with representative sites throughout the distribution system. For the purpose of this paragraph, a representative site is a site in which the plumbing materials used at that site would be commonly found at other sites served by the water system.
6. The sampling sites selected for a non-transient non-community water system ("tier 1 sampling sites") shall consist of buildings that:
(i) contain copper pipes with lead solder installed after 1982 or contain lead pipes; and/or
(ii) are served by a lead service line.
7. A non-transient non-community water system with insufficient tier 1 sites that meet the targeting criteria in paragraph (7)(a)6 shall complete its sampling pool with sampling sites that contain copper pipes with lead solder installed before 1983. If additional sites are needed to complete the sampling pool, the nontransient non-community water system shall use representative sites throughout the distribution system. For the purpose of this paragraph, a representative site is a site in which the plumbing materials used at that site would be commonly found at other sites served by the water system.
8. Any water system whose sampling pool does not consist exclusively of tier 1 sites shall demonstrate to the Division under paragraph (11) why a review of the information listed in paragraph (7)(a)2. was inadequate to locate a sufficient number of tier 1 sites. Any community water system which includes tier 3 or other representative sampling sites in its sampling pool shall demonstrate why it was unable to locate a sufficient number of tier 1 and tier 2 sampling sites.
9. Any water system whose distribution system contains lead service lines shall draw 50 percent of the samples it collects during each monitoring period from sites that contain lead pipes, or copper pipes with lead solder, and 50 percent of those samples from sites served by a lead service line. A water system that cannot identify a sufficient number of sampling sites served by lead service line shall collect first draw samples from all of the sites identified as being served by such lines.
(b) Sample collection methods.
1. All tap samples for lead and copper collected in accordance with this subpart, with the exception of lead service line samples collected under paragraph (5), shall be first draw samples.
2. Each first-draw tap sample for lead and copper shall be one liter in volume and must have stood motionless in the plumbing system of each sampling site for at least six hours. First draw samples from residential housing shall be collected from the cold-water kitchen or bathroom sink tap. First-draw samples from a non-residential building shall be one liter in volume and shall be collected at an interior tap from which is typically drawn for consumption. First draw samples may be collected by the system or the system may allow residents to collect first draw samples after instructing the residents of the sampling procedures specified in this paragraph. To avoid problems of residents handling nitric acid, acidification of first-draw samples may be done up to fourteen (14) days after the sample is collected. After acidification to resolubilize the metals, the sample must stand in the original container for the time specified in the approved EPA method before the sample can be analyzed. If a system allows residents to perform sampling, the system may not challenge, based on alleged errors in sample collection, the accuracy of sampling results.
3. Each service line sample shall be one liter in volume and have stood motionless in the lead service line for at least six hours. Lead service line samples shall be collected in one of the following three ways:
(i) at the tap after flushing the volume of water between the tap and the lead service line. The volume of water shall be calculated based on the interior diameter and length of the pipe between the tap and the lead service line;
(ii) tapping directly into the lead service line; or
(iii) if the sampling site is a building constructed as a single-family residence, allowing the water to run until there is a significant change in temperature which would be indicative of water that has been standing in the lead service line.
4. A water system shall collect each first draw tap sample from the same sampling site from which it collected a previous sample. If, for any reason, the water system cannot gain entry to a sampling site in order to collect a follow-up tap sample or a particular site is no longer available, the system may collect the follow-up tap sample from another sampling site in its sampling pool as long as the new site meets the same targeting criteria, and is within reasonable proximity of the original site.
5. A non-transient non-community water system, or a community water system that meets the criteria of Rule 391-3-5-.25(7)(a) 3. -7. that does not have enough taps that can supply first-draw samples, as defined in Rule 391-3-5-.25(7)(b) 2., must collect multiple samples from available sites/taps, provided the samples are collected at different times and/or on different days in order to meet the "first-draw"/6-hour minimum non-use time criteria.
(c) Number of samples.

Water systems shall collect at least one sample during each monitoring period specified in paragraph (7)(d) from the number of sites listed in the first column below ("# of Sites Standard Monitoring") of the table in this paragraph. A system conducting reduced monitoring under paragraph (7)(d)4. shall collect at least one sample from the number of sites specified in the second column ("# of Sites Reduced Monitoring") of the table in this paragraph during each monitoring period specified in paragraph (7)(d)4.. Such reduced monitoring sites shall be representative of the sites required for standard monitoring. States may specify sampling locations when a system is conducting reduced monitoring. The table is as follows:

System Size Population Served

Number of Sites Standard Monitoring

Number of Sites Reduced Monitoring

100,001 or more

100

50

10,001 to 100,000

60

30

3,301 to 10,000

40

20

501 to 3,300

20

10

101 to 500

10

5

100 or fewer

5

5

(d) Timing of monitoring.
1. Initial tap sampling: Two consecutive six-month periods, between January-June and between July-December.
(i) All large systems shall monitor at the required number of standard monitoring sites during two consecutive six-month periods.
(ii) All small and medium-size systems shall monitor at the required number of standard monitoring sites during each six-month monitoring period until:
(I) the system exceeds the lead or copper action level and is therefore required to implement the corrosion control treatment requirements under paragraph (2), in which case the system shall continue monitoring in accordance with paragraph (7)(d)2., or
(II) the system meets the lead or copper action levels during two consecutive six-month monitoring periods, in which case the system may reduce monitoring in accordance with paragraph (7)(d)4..
2. Monitoring after installation of corrosion control and source water treatment.
(i) Any large system which installs optimal corrosion control treatment pursuant to paragraph (2)(d) shall monitor during two consecutive six-month monitoring periods by the date specified in paragraph (2)(d).
(ii) Any small or medium-size system which installs optimal corrosion control treatment pursuant to paragraph (2) shall monitor during two consecutive six-month monitoring periods by the date specified in paragraph (2)(d).
(iii) Any system which installs source water treatment pursuant to paragraph (4)(a) 3. shall monitor during two consecutive six-month monitoring periods by the date specified in paragraph (4)(a) 4.
3. Monitoring after Division specifies water quality parameter values for optimal corrosion control. After the Division specifies the value for water quality control parameters under paragraph (3), the system shall monitor during each subsequent six-month monitoring period, with the first monitoring period to begin on the date the Division specifies the optimal values under paragraph (3).
4. Reduced monitoring.
(i) A small or medium-size water system that meets the lead and copper action levels during each of two consecutive six-month monitoring periods may reduce the number of samples in accordance with paragraph (7)(c), and reduce the frequency of sampling to once per year between the months of June and September of the calendar year immediately following the end of the second consecutive six-month monitoring period.
(ii) Any water system that meets the lead and copper action levels and maintains the range of values for the water quality control parameters reflecting optimal corrosion control treatment specified by the Division under paragraph (3) during each of two consecutive six-month monitoring periods may reduce the frequency of monitoring to once per year between the months of June and September and reduce the number of lead and copper samples in accordance with paragraph (7)(c) if it receives written approval from the division. This sampling shall begin during the calendar year immediately following the end of the second consecutive six-month monitoring period. The Division shall review monitoring, treatment, and other relevant information submitted by the water system in accordance with paragraph (11) and shall notify the water system in writing when the Division determines the water system is eligible to commence reduced monitoring to once every three (3) years pursuant to this paragraph. The Division shall review, and where appropriate, revise its determination when the system submits new monitoring or treatment data, or when other data relevant to the number and frequency of tap sampling becomes available.
(iii) A small or medium-size water system that meets the lead and copper action levels during three consecutive years of monitoring may reduce the frequency of monitoring for lead and copper from annually to once every three years. Sampling must still occur between the months of June and September of the year in which monitoring is required. Any water system that meets the lead and copper action levels and maintains the range of values for the water quality control parameters reflecting optimal corrosion control treatment specified by the Division under paragraph (3) during three consecutive years of monitoring may reduce the frequency from annually to once every three years if it receives written approval from the Division. Samples collected once every three years must be collected no later than every third calendar year. The Division shall review monitoring, treatment, and other relevant information submitted by the water system in accordance with paragraph (11) and shall notify the system in writing when it determines the system is eligible to reduce the frequency of monitoring to once every three years. The Division shall review, and where appropriate, revise its determination when the system submits new monitoring or treatment data, or when other data relevant to the number and frequency of tap sampling becomes available.
(iv) A water system that reduces the number and frequency of sampling shall collect these samples from representative sites included in the original pool of targeted sampling sites identified in paragraph (7)(a)1. Systems sampling annually or less frequently shall conduct the lead and copper tap sampling during the months of June, July, August or September unless the Division has approved a different sampling period in accordance with paragraph (7)(d)4.(iv)(1).
(I) The Division, at its discretion, may approve a different period for conducting the lead and copper tap sampling for systems collecting a reduced number of samples. Such a period shall be no longer than four consecutive months and must represent a time of normal operation where the highest levels of lead are most likely to occur. For non-transient non-community water system that does not operate during the months of June, through September, and for which the period of normal operation where the highest levels of lead are most likely to occur is not known, the Division shall designate a period that represents a time of normal operation for the system. Any alternate reduced monitoring must meet criteria set forth in 40 CFR, part 141.86(d)(4)(iv)(A).
(II) Systems monitoring annually, that have been collecting samples during the months of June through September and that receive Division approval to alter their sample collection period under paragraph (7)(d)4.(iv)(I), must collect their next round of samples during a time period that ends no later than 21 months after the previous round of sampling. Systems monitoring triennially that have been collecting samples during the months of June through September, and receive Division approval to alter the sampling collection period per paragraph (7)(d)4.(iv)(I), must collect their next round of samples during a time period that ends no later than 45 months after the previous round of sampling. Subsequent rounds of sampling must be collected annually or triennially, as requested by this rule. Small systems with waivers, granted pursuant to paragraph (7)(g), that have been collecting samples during the months of June through September and receive Division approval to alter their sample collection period under paragraph (7)(d)4.(iv)(I) must collect their next round of samples before the end of the 9-year period.
(v) Any water system that demonstrates for two consecutive 6- month monitoring periods that the tap water lead level computed under paragraph (1)(c) 3. is less than or equal to 0.005 mg/L and the tap water copper level computed under paragraph (1)(c) 3. is less than or equal to 0.65 mg/L may reduce the number in accordance with paragraph (3) and reduce the frequency of sampling to once every three calendar years.
(vi)
(I) A small or medium-size water system subject to reduced monitoring that exceeds the lead or copper action level shall resume sampling in accordance with paragraph (7)(d)3. and collect the number of samples for standard monitoring under paragraph (7)(c). Such a system shall also conduct water quality parameter monitoring in accordance with 40 CFR, Part 141.87(b), (c) or (d) (as appropriate) during the monitoring period in which it exceeded the action level. Any such system may resume annual monitoring for lead and copper at the tap at the reduced number of sites specified in paragraph (7)(c) after it has completed two consecutive six-month rounds of monitoring with no action level exceeded.
(II) Any water system subject to the reduced monitoring frequency that fails to meet the lead or copper action level during any four-month monitoring period or that fails to operate at or above the minimum value or within the range of values for the water quality parameters specified by the Division for more than nine days in any six-month monitoring period shall conduct tap water sampling for lead and copper at the frequency specified in paragraph (7)(d)3., collect the number of samples specified for standard monitoring under paragraph (c), and shall resume monitoring for water quality parameters within the distribution system in accordance with 40 CFR, Part 141.87(d). This standard tap water sampling shall begin no later than the six-month period beginning January 1 of the calendar year following the lead or copper action level exceedance or water quality parameter excursion. Such a system may resume reduced monitoring for lead and copper at the tap and for water quality parameters within the distribution system under the following conditions:
I. The system may resume annual monitoring for lead and copper at the tap at the reduced number of sites specified in paragraph (7)(c) after it has completed two consecutive six-month rounds of monitoring that meet both lead and copper action levels and the system has received written approval from the Division that it is appropriate to resume reduced monitoring on an annual frequency. This sampling shall begin during the calendar year immediately following the end of the second consecutive six-month monitoring period.
II. The system may resume triennial monitoring for lead and copper at the tap at the reduced number of sites after it demonstrates through subsequent rounds of monitoring that it meets the action level criteria for lead and copper and has received approval from the Division that it is appropriate to resume triennial monitoring.
III. The system may reduce the number of water quality parameter tap water samples required and the frequency with which it collects such samples in accordance with 40 CFR, Part 141.87(e)(1) and (2). Such a system may not resume triennial monitoring for water quality parameters at the tap until it demonstrates that it has re-qualified for triennial monitoring, in accordance with 40 CFR, Part 141.87(e)(2).
(vii) Any water system subject to a reduced monitoring frequency under paragraph (7)(d)(4) shall notify the Division in writing of any upcoming long-term change in treatment or addition of a new source as described in 40 CFR, Part 141.90(a)(3). The Division must review and approve the addition of a new source or long-term change in water treatment before it is implemented by the water system. The Division may require the system to resume sampling in accordance with paragraph (7)(d)3. and collect the number of samples specified for standard monitoring under paragraph (7)(c) or take other appropriate steps such as increased water quality parameter monitoring or re-evaluation of its corrosion control treatment given the potentially different water quality considerations.
(e) Additional monitoring by systems. The results of any monitoring conducted in addition to the minimum requirements of this section shall be considered by the system and the Division in making any determinations (i.e., calculating the 90th percentile lead or copper level) under this subpart or 40 CFR Part 141.82.
(f) Invalidation of lead or copper tap water samples. A sample invalidated under this paragraph does not count toward determining lead or copper 90th percentile levels under paragraph (1)(c) or toward meeting the minimum monitoring requirements of paragraph (7)(c).
1. The Division may invalidate a lead or copper tap water sample if at least one of the following conditions is met.
(i) The laboratory establishes that improper sample analysis caused erroneous results.
(ii) The Division determines that the sample was taken from a site that did not meet the site selection criteria of this rule.
(iii) The sample container was damaged in transit.
(iv) There is substantial reason to believe that the sample was subject to tampering.
2. The system must report the results of all samples to the Division and all supporting documentation for samples the system believes should be invalidated.
3. To invalidate a sample under paragraph (7)(f)1., the decision and the rationale for the decision must be documented in writing. The Division may not invalidate a sample solely on the grounds that a follow-up sample result is higher or lower than that of the original sample.
4. The water system must collect replacement samples for any samples invalidated under this section if, after the invalidation of one or more samples, the system has too few samples to meet the minimum requirements of paragraph (7)(c). Any such replacement samples must be taken as soon as possible, but no later than 20 days after the date the Division invalidates the sample or by the end of the applicable monitoring period, whichever occurs later. Replacement samples taken after the end of the applicable monitoring period shall not be used to meet the monitoring requirements of a subsequent monitoring period. The replacement samples shall be taken at the same locations as the invalidated samples or, if that is not possible, at locations other than those already used for sampling during the monitoring period.
(g) Monitoring waivers for small systems. Any small system that meets the criteria of 40 CFR, Section 141.86(g) may apply to the Division to reduce the frequency of monitoring for lead and copper in accordance with the requirements of 40 CFR Section 141.86(g).
(8) Monitoring Requirements for Water Quality Parameters. All large water systems and all small and medium-size systems that exceed the lead or copper action level shall monitor water quality parameters in addition to lead and copper in accordance with this paragraph. The requirements of this paragraph are summarized in a table at the end of 40 CFR, Part 141.87.
(a) Systems will have to monitor water quality parameters at different locations.
1. Representative taps throughout the distribution system (system can use total coliform sample sites). The system should take into account the number of persons served, the different sources of water, the different treatment methods employed by the system, and seasonal variability.
2. Samples are to be collected of the treated water from each source before entry point to the distribution system. If the system draws water from more than one source and the sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions (i.e., when water is representative of all sources being used).
3. Number of samples.
(i) Systems shall collect two tap samples for applicable water quality parameters during each monitoring period as described in paragraphs (8)(b) thru (8)(e). The following number of sites is required:

Distribution System Tap Sampling Requirements for Water Quality Parameters. (Other Than Lead and Copper)

System Size Population Served

Number of Distribution Sampling Sites Base Monitoring

100,001 or more

25

10,001 to 100,000

10

3,301 to 10,000

3

501 to 3,300

2

101 to 500

1

100 or fewer

1

(ii) Except as provided in paragraph (8)(c), systems shall collect two samples for each water quality parameter at each entry point to the distribution system during each monitoring period as described in paragraph (8)(b). During each monitoring period specified in paragraphs (8)(c)-(8)(e), systems shall collect one sample for each applicable water quality parameter at each entry point to the distribution system.
(b) Initial Sampling - All large water systems shall measure the water quality parameters listed below at distribution system taps and at each entry point to the distribution system during each six-month monitoring period (specified in paragraph (7)(d) 1.).
1. pH;
2. alkalinity;
3. calcium;
4. conductivity;
5. orthophosphate, when an inhibitor containing phosphate is used;
6. silica, when an inhibitor containing silica is used;
7. Water temperature.
(c) Monitoring after installation of corrosion control. All large systems which install optimal corrosion control treatment according to paragraph (7)(d) 2.(i) shall measure water quality parameters at the locations and frequencies listed below during each six month monitoring period. All small or medium size systems which install optimal corrosion treatment shall conduct such monitoring during each six-month monitoring period specified in paragraph (7)(d) 2.(ii) only when the system exceeds the lead and copper action level.
1. At the required number of distribution system sites/taps, two samples every six months for:
(i) pH;
(ii) alkalinity;
(iii) orthophosphate, when an inhibitor containing phosphate is used;
(iv) silica, when an inhibitor containing silica is used;
(v) calcium;
2. At each entry point to the distribution system, one sample every two weeks for:
(i) pH;
(ii) when alkalinity is adjusted as part of optimal corrosion control, a reading of the dosage rate of the chemical used to adjust alkalinity, and the alkalinity concentration.
(iii) when a corrosion inhibitor is used as part of optimal corrosion control, a reading of the dosage rate of the inhibitor used, and the concentration of orthophosphate or silica.
(d) Monitoring after the Division specifies water quality parameter values for optimal corrosion control will be as follows. The Division will specify the values for applicable water quality control parameters reflecting optimal corrosion control treatment in accordance with 40 CFR Part, 141.82(f). All large systems shall measure the applicable water quality parameters in accordance with paragraph (8)(c) and determine compliance with the requirements of paragraph (7)(d) 3. every six months with the first six-month period to begin on January 1 or July 1, whichever comes first, after the Division specifies optimal values under 40 CFR, Part 141.82(f). Any small or medium-size system shall conduct such monitoring during each six-month period specified in this paragraph in which the system exceeds the lead and/or copper action level(s). For any such small and medium-size system that is subject to a reduced monitoring frequency pursuant to 391-3-5-.25(7)(d) 4. at the time of the action level exceedance, the start of the applicable six-month period under this paragraph shall coincide with the start of the applicable monitoring period under paragraph (7)(d) 4. Compliance with the division-designated optimal water quality parameter values shall be determined as specified under paragraph (7)(d) 3.
(e) Reduced monitoring for water quality parameters.
1. Any water system that maintains the range of values for the water quality parameters reflecting optimal corrosion control treatment during each of two consecutive six-month monitoring periods under paragraph (8)(d) shall continue monitoring at the entry point(s) to the distribution system as specified in paragraph (8)(c)2.. Such system may collect two tap samples for applicable water quality parameters from the following reduced number of sites during each six-month monitoring period.

System Size Population Served

Number of Distribution Sampling Sites Reduced Monitoring

100,001 or more

10

10,001 to 100,000

7

3,301 to 10,000

3

501 to 3,300

2

101 to 500

1

100 or fewer

1

2.
(i) Any water system that maintains the range of values for the water quality parameters reflecting optimal corrosion control treatment specified by the Division during three consecutive years of monitoring may reduce the frequency with which it collects the number of tap samples for applicable water quality parameters specified in paragraph (8)(e)1. from every six months to annually. This sampling begins during the calendar year immediately following the end of the monitoring period in which the third consecutive year of six-month monitoring occurs. Any water system that maintains the range of values for the water quality parameters reflecting optimal corrosion control treatment specified by the Division under 40 CFR Part 141.82(f) or Rule 391-3-5-.25(3) during three consecutive years of annual monitoring under this paragraph may reduce the frequency with which it collects the number of tap samples for applicable water quality parameters from annually to every three years. This sampling begins no later than the third calendar year following the end of the monitoring period in which the third consecutive year of monitoring occurs.
(ii) A water system may reduce the frequency with which it collects tap samples for applicable water quality parameters specified in paragraph (8)(e)1. to every three years if it demonstrates during two consecutive monitoring periods that its tap water lead level at the 90th percentile is less than or equal to the practical quantitation limit (PQL) for lead specified in paragraph (10), that its tap water copper level is less than or equal to 0.65 mg/L for copper in paragraph (2)(c), and that it also has maintained the range of values for the water quality parameters reflecting optimal corrosion control treatment specified by the division under paragraph (2)(d). Monitoring conducted every three years must be done no later than every third calendar year.
3. A water system that conducts sampling annually shall collect these samples evenly throughout the year so as to reflect seasonal variability.
4. Any water system subject to reduced monitoring frequency that fails to operate at or above the minimum value within the range of values for the water quality parameters specified by the Division under paragraph (3) shall resume distribution system tap water sampling in accordance with the number and frequency requirements in paragraph (8)(d). Such a water system may resume annual monitoring for water quality parameters at the tap at the reduced number of sites specified under paragraph (8)(e) 1. after it has completed two subsequent consecutive six-month rounds of monitoring that meet the criteria of that paragraph or may resume triennial monitoring for water quality parameters at the tap at the reduced number of sites after the water system demonstrates through subsequent rounds of monitoring that the water system meets the criteria of either paragraphs (8)(e)2.(i) or (e)2.(ii) or both.
(f) Additional monitoring by systems must be approved by the Division.
(9) Monitoring Requirements for Lead and Copper in Source Water.
(a) Sample location, collection methods, and number of samples.
1. A water system that fails to meet the lead or copper action level on the basis of routine tap samples collected in accordance with paragraph (7) shall collect lead and copper source water samples in accordance with the requirements regarding sample location, number of samples, and collection methods specified in 40 CFR, Part 141.88(a)(1)(i)-(iv) and (A)-(B).
2. Where the results of sampling indicate an exceedance of maximum permissible source water levels established under paragraph (4)(b) 4., the Division may require that one additional sample be collected as soon as possible after the initial sample was taken (but not to exceed two weeks) at the same sampling point. If a Division-required confirmation sample is taken for lead or copper, then the results of the initial and confirmation sample shall be averaged in determining compliance with the Division-specified maximum permissible levels. Any sample value below the detection limit shall be considered to be zero. Any value above the detection limit but below the PQL shall either be considered as the measured value or be considered one-half the PQL.
(b) Monitoring frequency after system exceeds tap water action level. Any system that exceeds the lead or copper action level during routine tap water monitoring shall collect one source water sample from each entry point to the distribution system no later than six months after the end of the monitoring period during which the action level was exceeded. For monitoring periods that are annual or less frequent, the end of the monitoring period is September 30 of the calendar year in which sampling occurs, or if the Division has established an alternate monitoring period, the last day of that period.
(c) Monitoring frequency after installation of source water treatment. Any system which installs source water treatment pursuant to paragraph (4)(a) 2. shall collect an additional source water sample from each entry point to the distribution system during two consecutive six-month monitoring periods by the deadline specified in paragraph (4)(a) 4.
(d) Monitoring frequency after Division specifies maximum permissible source water levels or determines that source water treatment is not needed.
1. A system shall monitor at the frequency specified below in cases where the Division specifies maximum permissible source water levels under paragraph (4)(b) 4. or determines that the system is not required to install source water treatment under paragraph (4)(b) 2.
(i) A water system using only groundwater shall collect samples once during the three-year compliance period (as that term is defined in Rule 391-3-5-.02) in effect when the applicable Division determination under paragraph (9)(d)1. is made. Such systems shall collect samples once during each subsequent compliance period. Triennial samples shall be collected every third year.
(ii) A water system using surface water (or a combination of surface and groundwater) shall collect samples once during each year, the first annual monitoring period to begin during the year in which the applicable Division determination is made under paragraph (9)(d)1. of this.
2. A system is not required to conduct source water sampling for lead and/or copper if the system meets the action level for the specific contaminant in tap water samples during the entire source water sampling period applicable to the system under paragraphs (9)(d)1.(i) or (ii).
(e) Reduced monitoring frequency.
1. A water system using only ground water may reduce the monitoring frequency for lead and copper in source water to once during each nine-year compliance cycle, as is defined in 40 CFR, Part 141.2, provided the samples are collected no later than every ninth calendar year and if the system meets one of the following:
(i) The system demonstrates that finished drinking water entering the distribution system has been maintained below the maximum permissible lead and copper concentrations specified by the Division under Rule 391-3-5-.25(1)(c) during at least three consecutive compliance periods under paragraph (9)(d)1.; or
(ii) The Division has determined that source water treatment is not needed and the system demonstrates that, at least three consecutive compliance periods in which sampling was conducted under paragraph (9)(d)1., the concentration of lead in source water was less than or equal to 0.005 mg/L and the concentration of copper in source water was less than or equal to 0.65 mg/L.
2. A water system using surface water or a combination of surface and groundwater may reduce the monitoring frequency in paragraph (9)(d)1. to once during each nine-year compliance cycle, as is defined in 40 CFR, Part 141.2, provided the samples are collected no later than every ninth calendar year and if the system meets one of the following:
(i) The system demonstrates that finished drinking water entering the distribution system has been maintained below the maximum permissible lead and copper concentrations specified by the Division under paragraph (1)(c) during at least three consecutive years; or
(ii) The Division has determined that source water treatment is not needed and the system demonstrates that, for at least three consecutive years, the concentration of lead in source water was less than or equal to 0.005 mg/L and the concentration of copper in source water was less than or equal to 0.65 mg/L.
3. A water system that uses a new source of water is not eligible for reduced monitoring for lead and/or copper until concentrations in samples collected from the new source during three consecutive monitoring periods are below the maximum permissible lead and copper concentrations specified in paragraph (4)(a) 5.
(10) Analytical Methods. Analyses for lead, copper, pH, conductivity, calcium, alkalinity, orthophosphate, silica, and temperature shall be conducted in accordance with 40 CFR, Part 141.89.
(11) Reporting Requirements. All water systems shall report all information to the Division in accordance with 40 CFR, Part 141.90.
(12) Record Keeping Requirements. All systems subject to the requirements of this rule shall retain on its premises original records of all sampling data and analyses, reports, surveys, letters, evaluations, schedules, Division determinations, and any other information required in accordance with 40 CFR, Part 141.91.
(13) Treatment Techniques.
(a) These regulations establish treatment techniques in lieu of maximum contaminant levels for acrylamide and epichlorohydrin.
(b) Each public water system must certify annually in writing to the Division (using third party or manufacturer's certification) that when acrylamide and epichlorohydrin are used in drinking water systems, the combination (or product) of dose and monomer level does not exceed the levels specified as follows:
1. Acrylamide = 0.05% dosed at 1 ppm (or equivalent);
2. Epichlorohydrin = 0.01% dosed at 20 ppm (or equivalent); certifications can rely on manufacturers or third parties, as approved by the Division.

Rule 391-3-5-.26 Unregulated Contaminants Sampling and Analytical Requirements

(1) Contaminant Monitoring.

Monitoring of the contaminants listed below in this section shall be conducted as follows:

(a) All community and non-transient, non-community water systems shall monitor for the contaminants listed in paragraphs (e) and (f) of this section by the date specified in Table 1. Systems serving 10,000 or fewer persons are not required to monitor for the contaminants in this section after December 31, 1998.

TABLE 1 - MONITORING SCHEDULE BY SYSTEM SIZE

Population Served

Monitoring to Begin No Later Than

Over 10,000

January 1, 1993

3,300 to 10,000

January 1, 1994

Less than 3,300

January 1, 1996

(b) Surface water systems shall sample at points in the distribution system representative of each water source or at entry points to the distribution system after application of treatment. The minimum number of samples is one year of quarterly samples per water source.
(c) Ground water systems shall sample at points of entry to the distribution system representative of each well after any application of treatment. The minimum number of samples is one sample per entry point to the distribution system.
(d) The Division may require confirmation samples for positive or negative results.
(e) Group III Unregulated Volatile Organic Contaminants.

Group III Unregulated Volatile Organic Contaminants

Chloroform

Bromodichloromethane

Chlorodibromomethane

Bromoform

Dibromomethane

m-Dichlorobenzene

1,1-Dichloropropene

1,1-Dichloroethane

1,1,2,2-Tetrachloroethane

1,3-Dichloropropane

Chloromethane

Bromomethane

1,2,3-Trichloropropane

1,1,1,2-Tetrachloroethane

Chloroethane

2,2-Dichloropropane

o-Chlorotoluene

p-Chlorotoluene

Bromobenzene

1,3-Dichloropropene

(f) Group IV Unregulated Volatile Organic Contaminants.

Group IV Unregulated Volatile Organic Contaminants

1,2,4-Trimethylbenzene

1,2,3-Trichlorobenzene

n-Propylbenzene

n-Butylbenzene

Naphthalene

Hexachlorobutadiene

1,3,5-Trimethylbenzene

p-Isopropyltoluene

Isopropylbenzene

Tert-butylbenzene

Sec-butylbenzene

Fluorotrichloromethane

Dichlorofluoromethane

Bromochloromethane

(g) Instead of performing the monitoring required by this section, a community water system or non-transient non-community water system serving fewer than 150 service connections may send a letter to the Division stating that the system is available for sampling. This letter must be sent to the Division by January 1, 1994. The system shall not send such samples to the Division, unless requested to do so by the Division.
(h) All community and non-transient, non-community water systems shall repeat the monitoring required in Section 391-3-5-.26(1) no less than every five (5) years from the dates specified in Section 391-3-5-.26(1)(a).
(i) The Division may allow the public water system to composite up to five samples when monitoring for substances listed in Section 391-3-5-.26(1)(e) and (f).
(j) Analysis under this section shall only be conducted by laboratories certified by the Division in accordance with Section 391-3-5-.29.
(2) Unregulated Contaminant Monitoring.

Monitoring of the contaminants listed in paragraphs (2)(k) and (2)(l) shall be conducted as follows:

(a) Each community and non-transient, non-community water system shall take four consecutive quarterly samples at each sampling point for each contaminant listed in paragraph (2)(k) of this section and report the results to the Division. Monitoring must be completed by December 31, 1995.
(b) Each community and non-transient non-community water system shall take one sample at each sampling point for each contaminant listed in paragraph (2)(l) of this section and report the results to the Division. Monitoring must be completed by December 31, 1995.
(c) Each community and non-transient non-community water system may apply to the Division for a waiver from the requirements of paragraph (2)(a) and (b) of this section.
(d) The Division may grant a waiver for the requirement of paragraph (2)(a) of this section based on the criteria specified in Section 391-3-5-.22(3)(f). The Division may grant a waiver from the requirement of paragraph (2)(b) of this section if previous analytical results indicate contamination would not occur, provided this data was collected after January 1, 1990.
(e) Groundwater systems shall take a minimum of one sample at every entry point to the distribution system which is representative of each well after treatment (hereafter called a sampling point). Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant.
(f) Surface water systems shall take a minimum of one sample at points in the distribution system that are representative of each source or at each entry point to the distribution system after treatment (hereafter called a sampling point.) Each sample must be taken at the same sampling point unless conditions make another sampling point more representative of each source or treatment plant. [Note: For purposes of this paragraph, surface water systems include systems with a combination of surface and ground sources.]
(g) If the system draws water from more than one source and the sources are combined before distribution, the system must sample at an entry point to the distribution system during periods of normal operating conditions (i.e., when water representative of all sources is being used).
(h) The Division may require a confirmation sample for positive or negative results.
(i) The Division may reduce the total number of samples a system must analyze by allowing the use of compositing. Composite samples from a maximum of five sampling points are allowed. Compositing of samples must be done in the laboratory and the composite sample must be analyzed within 14 days of collection. If the population served by the system is greater than 3,300 persons, then compositing may only be permitted by the Division at sampling points within a single system. In systems serving fewer than or equal to 3,300 persons, the Division may permit compositing among different systems provided the 5-sample limit is maintained.
(j) Instead of performing the monitoring required by this section, a community water system or non-transient non-community water system serving fewer than 150 service connections may send a letter to the Division stating that the system is available for sampling. This letter must be sent to the Division by January 1, 1994. The system shall not send such samples to the Division, unless requested to do so by the Division.
(k) Listed below are the unregulated organic contaminants. The analytical method shall be in accordance with 40 CFR, Part 141.40.

Unregulated Organic Contaminants

Aldrin

Butachlor

Carbaryl

Dicamba

Dieldrin

3-Hydroxycarbofuran

Methomyl

Metolachlor

Metribuzin

Propachlor

(l) Listed below are the unregulated inorganic contaminants. The analytical method shall be in accordance with 40 CFR, Part 141.40:
(m)

Unregulated Inorganic Contaminants

Sulfate

(n) Analysis under this section shall only be conducted by laboratories certified by the Division.
(3) Special Monitoring for Sodium.
(a) Suppliers of water for community public water systems shall collect and analyze one sample per plant at the entry point of the distribution system for the determination of sodium concentration levels; samples must be collected and analyzed annually for systems utilizing surface water sources in whole or in part, and at least every three years for systems utilizing solely ground water sources. The minimum number of samples required to be taken by the system shall be based on the number of treatment plants used by the system, except that multiple wells drawing raw water from a single aquifer may, with the Division approval, be considered one treatment plant for determining the minimum number of samples. The supplier of water may be required by the Division to collect and analyze water samples for sodium more frequently in locations where the sodium content is variable.
(b) The supplier of water shall report to the Division the results of the analyses for sodium within the first 10 days of the month following the month in which the sample results were received or within the first 10 days following the end of the required monitoring period as stipulated by the Division, whichever of these is first, unless such analysis is performed by the Division. If more than annual sampling is required the supplier shall report the average sodium concentration within 10 days of the month following the month in which the analytical results of the last sample used for the annual average was received.
(c) The supplier of water shall notify appropriate local and state public health officials of the sodium levels by written notice by direct mail within three months. A copy of each notice required to be provided by this paragraph shall be sent to the Division within 10 days of its issuance. The supplier of water is not required to notify appropriate local and state public health officials of the sodium levels where the Division provides such notices in lieu of the supplier.
(d) Analyses for sodium shall be performed in accordance with the Federal Regulations 40 CFR, Part 141.41(d) procedures.
(e) Initial analyses for sodium for new community public water systems shall be completed within one year from the effective date of the permit to operate.
(4) Special Monitoring for Corrosivity Characteristics.
(a) Suppliers of water for community public water systems when required by the Division shall collect samples from a representative entry point to the water distribution system for the purpose of analysis to determine the corrosivity characteristics of the water.
1. The supplier shall collect two samples per plant for analysis for each plant using surface water sources wholly or in part or more if required by the Division one during mid-winter and one during midsummer. The supplier of the water shall collect one sample per plant for analysis for each plant using ground water sources or more if required by the Division. The minimum number of samples required to be taken by the system shall be based on the number of treatment plants used by the system, except that multiple wells drawing raw water from a single aquifer may, with the Division approval, be considered one treatment plant for determining the minimum number of samples.
2. Determination of the corrosivity characteristics of the water shall include measurement of pH, calcium, hardness, alkalinity, temperature, total dissolved solids (total filterable residue), and calculation of the Langelier Index in accordance with subparagraph (c) below. The determination of corrosivity characteristics shall only include one round of sampling (two samples per plant for surface water and one sample per plant for ground water sources). However, the Division has the discretion to require monitoring for additional parameters which may indicate corrosivity characteristics, such as sulfates and chlorides. In certain cases, the Aggressive Index, as described in subparagraph (c), can be used instead of the Langelier Index; the supplier shall request in writing to the Division and the Division will make this determination.
(b) The supplier of water shall report to the Division the results of the analyses for the corrosivity characteristics within the first 10 days of the month following the month in which the sample results were received, unless the analysis is conducted by the Division. If more frequent sampling is required by the Division, the supplier can accumulate the data and shall report each value within 10 days of the month following the month in which the analytical results of the last sample was received.
(c) Analyses conducted to determine the corrosivity of the water shall be made in accordance with 40 CFR Part 141.42(c).
(d) When required by the Division, the supplier of water for community and non-transient, non-community public water systems shall implement a corrosion control program satisfactory to the Division to insure that the drinking water is not unduly corrosive.

Rule 391-3-5-.27 Monitoring Frequency and Analytical Methods for Radioactivity in Community Water Systems

(1) Monitoring Requirements for Gross Alpha Particle Activity, Radium-226, Radium-228, and Uranium.
(a) Compliance with Rule 391-3-5-.18(5) shall be based on the analysis of an annual composite of four consecutive quarterly samples or the average of the analyses of four samples obtained at quarterly intervals.
1. A gross alpha particle activity measurement may be substituted for the required Radium-226 and Radium-228 analysis provided that the measured gross alpha particle activity does not exceed 5 pCi/L, at a confidence level of 95 percent (1.65 [LOWER CASE SIGMA], where [LOWER CASE SIGMA] [sigma] is the standard deviation of the net counting rate of the sample). In localities where Radium-228 may be present in drinking water, Radium-226 and/or Radium-228 analyses are required when the gross alpha particle activity exceeds 2 pCi/L.
2. When the gross alpha particle activity exceeds 5 pCi/L, the same or an equivalent sample shall be analyzed for Radium-226. If the concentration of Radium-226 exceeds 3 pCi/L the same or an equivalent sample shall be analyzed for Radium-228.
(b) The initial analysis required by subparagraph (1)(a) for new water systems shall be completed within two years from the effective date of the permit to operate.
(c) Suppliers of water shall monitor at least once every four years following the procedure required by subparagraph (1)(a). At the discretion of the Director when an annual record taken in conformance with subparagraph (1)(a) has established that the average annual concentration is less than half the maximum contaminant levels established by Rule 391-3-5-.18(6), analysis of a single sample may be substituted for the quarterly sampling procedure required by subparagraph (1)(a).
1. More frequent monitoring shall be conducted when ordered by the Director in the vicinity of mining or other operations which may contribute alpha particle radioactivity to either surface or ground water sources of drinking water.
2. A supplier of water shall monitor in conformance with subparagraph (1)(a) within one year of the introduction of a new water source for a community water system. More frequent monitoring shall be conducted when ordered by the Director in the event of possible contamination or when changes in the distribution system or treatment process occur which may increase the concentration of radioactivity in drinking water.
3. A community water system using two or more sources having different concentrations of radioactivity shall monitor each source of water, in addition to water from a free flowing drinking water tap, when ordered by the Director.
4. Monitoring for compliance with Rule 391-3-5-.18(5) after the initial period need not include Radium-228 except when required by the Director provided, that the average annual concentration of Radium-228 has been assayed at least once using the quarterly sampling procedure required by subparagraph (l)(a).
5. Suppliers of water shall, as ordered by the Director, conduct annual monitoring of any community water system in which the Radium-228 concentration exceeds 3 pCi/L.
(d) If the MCL for gross alpha particle activity or total radium as set forth in Rule 391-3-5-.18(5) is exceeded, the supplier of a community water system shall give notice to the Division pursuant to Rule 391-3-5-.30 and notify the public pursuant to Rule 391-3-5-.32. Monitoring at quarterly intervals shall be continued until the annual average concentration no longer exceeds the maximum contaminant level or until a monitoring schedule as a condition to a permit, variance, exemption or enforcement action shall become effective.
(e) The Division may require more frequent monitoring than specified in this section, or may require confirmation samples at its discretion. The results of the initial and confirmation samples will be averaged for use in compliance determinations.
(f) Compliance with Rule 391-3-5-.18(5) will be determined based on the analytical result(s) obtained at each sampling point. If one sampling point is in violation of an MCL, the system is in violation of the MCL. Systems must include all samples taken and analyzed under the provisions of this section in determining compliance, even if that number is greater than the minimum required.
(2) Monitoring Requirements for Man-made Radioactivity in Community Water Systems.
(a) Within two years following June 24, 1977 systems using surface water sources and serving more than 100,000 persons and such other community water systems as are designated by the Division shall be monitored for compliance with Rule 391-3-5-.18(5) by analysis of a composite of four consecutive quarterly samples or analysis of four quarterly samples. Compliance with Rule 391-3-5-.18(5) may be assumed without further analysis if the average annual concentrations of tritium and strontium-90 are less than those listed in Table A, provided, that in no case shall the sum of their annual dose equivalents to bone marrow exceed 4 milligrams per year.
1. If the gross beta particle activity exceeds 50 pCi/L, an analysis of the sample must be performed to identify the major radioactive constituents present and the appropriate organ and total body doses shall be calculated to determine compliance with Rule 391-3-5-.18(5).
2. Suppliers of water shall conduct additional monitoring, as ordered by the Director, to determine the concentration of man-made radioactivity in principal watersheds designated by the Division.
3. At the discretion of the Director suppliers of water utilizing only ground waters may be required to monitor for man-made radioactivity.
(b) After the initial analysis required by subparagraph (2)(a) suppliers of water shall monitor at least every four years following the procedure given in subparagraph (2)(a).
(c) Within two years of June 24, 1977 the supplier of any community water system designated by the Division as utilizing waters contaminated by effluents from nuclear facilities shall initiate quarterly monitoring for gross beta particle and iodine-131 radioactivity and annual monitoring for strontium-90 and tritium.
1. Quarterly monitoring for gross beta particle activity shall be based on the analysis of monthly samples or the analysis of a composite of three monthly samples. The former is recommended. If the gross beta particle activity in a sample exceeds 15 pCi/L, the same or an equivalent sample shall be analyzed for strontium-89 and cesium-134. If the gross beta particle activity exceeds 50 pCi/L, an analysis of the sample must be performed to identify the major radioactive constituents present and the appropriate organ and total body doses shall be calculated to determine compliance with Rule 391-3-5-.18(5).
2. For iodine-131, a composite of five consecutive daily samples shall be analyzed once each quarter. As ordered by the Director, more frequent monitoring shall be conducted when iodine-131 is identified in the drinking water.
3. Annual monitoring for strontium-90 and tritium shall be conducted by means of the analysis of a composite of four consecutive quarterly samples or analysis of four quarterly samples. The latter procedure is recommended.
4. The Division may allow the substitution of environmental surveillance data taken in conjunction with a nuclear facility for direct monitoring of man-made radioactivity by the supplier of water where the Division determines such data is applicable to a particular community water system.
(d) If the average annual maximum contaminant level for manmade radioactivity set forth in Rule 391-3-5-.18(5) is exceeded, the operator of a community water system shall give notice to the Division pursuant to Rule 391-3-5-.30 and to the public as required by Rule 391-3-5-.32. Monitoring at monthly intervals shall be continued until the concentration no longer exceeds the maximum contaminant level or until a monitoring schedule as a condition to a permit, variance, exemption or enforcement action shall become effective.
(3) Sample Collection and Analysis. Upon written direction of the Director, the supplier shall collect and submit drinking water samples for analysis in accordance with the schedule furnished. The Division shall have the discretion to delete results of obvious sampling or analytic errors. CWSs must conduct more frequent monitoring when ordered by the State in the event of possible contamination or when changes in the distribution system or treatment processes occur which may increase the concentration of radioactivity in finished water.
(4) Analytical Methods. Analytical methods for measurements, detection limits and determining compliance with maximum contaminant levels listed in Rule 391-3-5-.18 for radioactivity shall be in accordance with 40 CFR, Part 141.25.
(5) Monitoring Requirements Effective December 7, 2003. All existing community water systems (CWSs) must conduct initial monitoring to determine compliance with this rule between December 7, 2003 and December 31, 2007. CWSs must sample each entry point to the distribution system for four consecutive quarters. All existing CWSs using ground water, surface water or systems using both ground and surface water systems must sample at every entry point to the distribution system that is representative of all sources being used under normal operating conditions. The system must take each sample at the same sampling point unless conditions make another sampling point more representative of each source or the Division has designated a distribution system location, in accordance with 40 CFR § 141.26(a)(2)(ii)(C).
(6) New Sources. All new CWSs or CWSs that use a new source of water shall begin to conduct initial monitoring within the first quarter after initiating use of the source.
(7) Initial Monitoring Waiver. For gross alpha particle activity, uranium, radium-226, and radium-228 monitoring, the Division may waive the final two quarters of initial monitoring for a sampling point if the results of the samples from the previous two quarters are below the detection limit.
(8) Initial Monitoring Above MCL. If the average of the initial monitoring results for a sampling point is above the MCL, the system must collect and analyze quarterly samples at the sampling point until the system has results from four consecutive quarters that are at or below the MCL, unless the system enters into another schedule as part of a formal compliance agreement with the Division.
(9) Reduced Monitoring. The Division may allow community water systems to reduce the future frequency of monitoring from once every three years to once every six or nine years at each sampling point, based on the following criteria:
(a) If the average of the initial monitoring results for each contaminant (i.e., gross alpha particle activity, uranium, radium-226, or radium-228) is below the detection limit specified in Table B, in Sec. 141.25(c)(1), the system must collect and analyze for that contaminant using at least one sample at the sampling point every nine years.
(b) For gross alpha particle activity and uranium, if the average of the initial monitoring results for each contaminant is at or above the detection limit but at or below half (1/2) the MCL, the system must collect and analyze for that contaminant using at least one sample at that sampling point every six years. For combined radium-226 and radium-228, the analytical results must be combined. If the average of the combined initial monitoring results for radium-226 and radium-228 is at or above the detection limit but at or below half (1/2) the MCL, the system must collect and analyze for that contaminant using at least one sample at that sampling point every six years.
(c) For gross alpha particle activity and uranium, if the average of the initial monitoring results for each contaminant is above half (1/2) the MCL but at or below the MCL, the system must collect and analyze at least one sample at that sampling point every three years. For combined radium-226 and radium-228, the analytical results must be combined. If the average of the combined initial monitoring results for radium-226 and radium-228 is above half (1/2) the MCL but at or below the MCL, the system must collect and analyze at least one sample at that sampling point every three years.
(d) Systems must use the samples collected during the reduced monitoring period to determine the monitoring frequency for subsequent monitoring periods, (e.g., if a system's sampling point is on a nine year monitoring period, and the sample result is above half (1/2) MCL, then the next monitoring period for that sampling point is three years).
(e) If a system has a monitoring result that exceeds the MCL while on reduced monitoring, the system must collect and analyze quarterly samples at that sampling point until the system has results from four consecutive quarters that are below the MCL, unless the system enters into another schedule as part of a formal compliance agreement with the Division.
(10) Compositing. To fulfill quarterly monitoring requirements for gross alpha particle activity, radium-226, radium-228, or uranium, a system may composite up to four consecutive quarterly samples from a single entry point if analysis is done within a year of the first sample. The Division will treat analytical results from the composited as the average analytical result to determine compliance with the MCLs and the future monitoring frequency. If the analytical result from the composited sample is greater than half (1/2) MCL, the Division may direct the system to take additional quarterly samples before allowing the system to sample under a reduced monitoring schedule.
(11) Gross Alpha Particle Activity. A gross alpha particle activity measurement may be substituted for the required radium-226 measurement provided that the measured gross alpha particle activity does not exceed 5 pCi/L. A gross alpha particle activity measurement may be substituted for the required uranium measurement provided that the measured gross alpha particle activity does not exceed 15 pCi/L. The gross alpha measurement shall have a confidence interval of 95% (1.65 [LOWER CASE SIGMA], where [LOWER CASE SIGMA] is the standard deviation of the net counting rate of the sample) for radium-226 and uranium. When a system uses a gross alpha particle activity measurement in lieu of a radium-226 and/or uranium measurement, the gross alpha particle activity analytical result will be used to determine the future monitoring frequency for radium-226 and/or uranium. If the gross alpha particle activity result is less than detection, the detection limit will be used to determine compliance and the future monitoring frequency.
(12) Monitoring and Compliance Requirements for Beta Particle and Photon Radioactivity. To determine compliance with the maximum contaminant levels in 40 CFR Sec. 141.66(d) for beta particle and photon radioactivity, a system must monitor at a frequency as follows:
(a) Community water systems (both surface and ground water) designated by the Division as vulnerable must sample for beta particle and photon radioactivity. Systems must collect quarterly samples for both beta emitters and annual samples for tritium and strontium-90 at each entry point to the distribution system (hereafter called a sampling point), beginning within one quarter after being notified by the Division. Systems already designated by the Division must continue to sample until the Division reviews and either reaffirms or removes the designation.
1. If the gross beta particle activity minus the naturally occurring potassium-40 beta particle activity at a sampling point has a running annual average (computed quarterly) less than or equal to 50 pCi/L (screening level), the Division may reduce the frequency of monitoring at that sampling point to once every 3 years. Systems must collect all samples required in paragraph 12(a) during the reduced monitoring period.
2. For systems in the vicinity of a nuclear facility, the Division may allow the CWS to utilize environmental surveillance data collected by the nuclear facility in lieu of monitoring at the system's entry point(s), where the Division determines if such data is applicable to a particular water system. In the event that there is a release from a nuclear facility, systems which are using surveillance data must begin monitoring at the community water system's entry point(s) in accordance with paragraph 12(a) of this rule.
(b) Community water systems (both surface and ground water) designated by the Division as utilizing waters contaminated by effluents from nuclear facilities must sample for beta particle and photon radioactivity. Systems must collect quarterly samples for beta emitters and iodine-131 and annual samples for tritium and strontium-90 at each entry point to the distribution system (hereafter called a sampling point), beginning within one quarter after being notified by the Division. Systems already designated by the Division as systems using waters contaminated by effluents from nuclear facilities must continue to sample until the Division reviews and either reaffirms or removes the designation.
1. Quarterly monitoring for gross beta particle activity shall be based on the analysis of monthly samples or the analysis of a composite of three monthly samples. The former is recommended.
2. For iodine-131, a composite of five consecutive daily samples shall be analyzed once each quarter. As ordered by the Division, more frequent monitoring shall be conducted when iodine-131 is identified in the finished water.
3. Annual monitoring for strontium-90 and tritium shall be conducted by means of the analysis of a composite of four consecutive quarterly samples or analysis of four quarterly samples. The latter procedure is recommended.
4. If the gross beta particle activity beta minus the naturally occurring potassium-40 beta particle activity at a sampling point has a running annual average (computed quarterly) less than or equal to 15 pCi/L, the Division may reduce the frequency of monitoring at that sampling point to every 3 years. Systems must collect the same type of samples required in paragraph 12(b) during the reduced monitoring period.
5. For systems in the vicinity of a nuclear facility, the Division may allow the CWS to utilize environmental surveillance data collected by the nuclear facility in lieu of monitoring at the system's entry point(s), where the Division determines if such data is applicable to a particular water system. In the event that there is a release from a nuclear facility, systems which are using surveillance data must begin monitoring at the community water system's entry point(s) in accordance with paragraph 12(b).
(c) Community water systems designated by the Division to monitor for beta particle activity and photon radioactivity cannot apply to the Division for a waiver from the monitoring frequencies specified in paragraphs 12(a) or 12(b).
(d) Community water systems may analyze for naturally occurring potassium-40 beta particle activity from the same or equivalent sample used for the gross beta particle activity analysis. Systems are allowed to subtract the potassium-40 beta particle activity value from the total gross beta particle activity value to determine if the screening level is exceeded. The potassium-40 beta particle activity must be calculated by multiplying elemental potassium concentrations (in mg/L) by a factor of 0.82.
(e) If the gross beta particle activity minus the naturally occurring potassium-40 beta particle activity exceeds the screening level, an analysis of the sample must be performed to identify the major radioactive constituents present in the sample and the appropriate doses must be calculated and summed to determine compliance with 40 CFR Sec. 141.66(d)(1), using the formula in 40 CFR Sec. 141.66(d)(2). Doses must also be calculated and combined for measured levels of tritium and strontium to determine compliance.
(13) Monthly Sampling. Systems must monitor monthly at the sampling point(s) which exceed the maximum contaminant level in 40 CFR Sec. 141.66(d) beginning the month after the exceedance occurs. Systems must continue monthly monitoring until the system has established, by a rolling average of 3 monthly samples, that the MCL is being met. Systems who establish that the MCL is being met must return to quarterly monitoring until they meet the requirements set forth in paragraphs (12)(a)(1) or 12(b)(4).
(14) Running Annual Average. For systems monitoring more than once per year, compliance with the MCL is determined by a running annual average at each sampling point. If the average of any sampling point is greater than the MCL, then the system is out of compliance with the MCL.
(15) Exceeding MCL. For systems monitoring more than once per year, if any sample result will cause the running average to exceed the MCL at any sample point, the system is out of compliance with the MCL immediately.
(16) Running Annual Average Calculation. If a system does not collect all required samples when compliance is based on a running annual average of quarterly samples, compliance will be based on the running average of the samples collected.
(17) Detection Limit and Running Annual Average Calculation. If a sample result is less than the detection limit, zero will be used to calculate the annual average, unless a gross alpha particle activity is being used in lieu of radium-226 and/or uranium. If the gross alpha particle activity result is less than detection, half (1/2) the detection limit will be used to calculate the annual average.
(18) MCLGs. The Maximum Contaminant Level Goal (MCLG) for Combined radium-226 and radium-228, Gross alpha particle activity, Beta particle and photon radioactivity, and uranium is zero.
(19) MCLs. The Maximum Contaminant Level (MCL) for radioactive particles is as follows:
(a) MCL for combined radium-226 and radium-228. The maximum contaminant level for combined radium-226 and radium-228 is 5 pCi/L. The combined radium-226 and radium-228 value is determined by the addition of the results of the analysis for radium-226 and the analysis for radium-228.
(b) MCL for gross alpha particle activity (excluding radon and uranium). The maximum contaminant level for gross alpha particle activity (including radium-226 but excluding radon and uranium) is 15 pCi/L.
(c) MCL for beta particle and photon radioactivity. The average annual concentration of beta particle and photon radioactivity from man-made radionuclides in drinking water must not produce an annual dose equivalent to the total body or any internal organ greater than four millirem per year (4 mrem/yr).
(d) MCL for uranium. The maximum contaminant level for uranium is 30 µg/L.
(20) Best available technology. 40 CFR Parts 141.66(g) and 141.66(h) are incorporated by reference.

Rule 391-3-5-.28 Alternative Analytical Techniques

With the written permission of the Director, concurred in by the administrator of the U.S. Environmental Protection Agency, an alternative analytical technique may be employed. An alternative technique shall be acceptable only if it is accuracy as it relates to the determination of compliance with any maximum contaminant level. The use of the alternative analytical techniques shall not decrease the frequency of monitoring required by these rules, in accordance with 40 CFR, Part 141.27.

Rule 391-3-5-.29 Certified Laboratories

(1) Laboratories Approved by the Division. For the purpose of determining compliance with Rules 391-3-5-.18, .19, .20, .21, .22, .23, .24, .25, .26, .27, .28, .52, .53, .54 and .55, samples may be considered only if they have been analyzed by a laboratory approved by the Division or by EPA, in accordance with 40 CFR Part 141.28, except that measurements for turbidity, disinfectant residual, fluoride residual, temperature, pH, conductivity, calcium, alkalinity, orthophosphate, and silica may be performed by any person acceptable to the Division. Fluoride analysis for determining compliance with MCL must be conducted by a laboratory approved by the Division or by EPA.
(2) Laboratory Personnel Changes. All drinking water analysis laboratories certified by the Division must notify the Division of personnel changes within thirty (30) days from the time of the change.
(3) Division-Collected Samples. Nothing in this Chapter shall be construed to preclude the Division or any duly designated representative of the Division from taking samples or from using the results from such samples to determine compliance by a supplier of water with the applicable requirements of this Chapter.

Rule 391-3-5-.30 Reporting Requirements

(1) Reporting Period. Except where a shorter period is specified by the Director, the supplier of water shall report to the Division the results of any test measurement or analysis required by this Chapter within:
(a) the first ten days following the month in which the results are received; or
(b) the first ten days following the end of the required monitoring period as stipulated by the Division, whichever of these is shortest. Note: Test measurements and results should be reported on the Division's reporting forms. Copies of these forms can be found on the Division web page.
(2) Violation. Failure to comply with paragraphs (1)(a) and (b) of Rule 391-3-5-.30 will result in a monitoring/reporting violation.
(3) Analysis by Division Laboratory. The supplier of water is not required to report analytical results to the Division in cases where the Division's laboratory performs the analysis and reports the results to the Division's office which would normally receive such notification from the supplier.
(4) Analysis by Non-Division Laboratory. The supplier of water is not required to report analytical results to the Division in cases where the Division's laboratory performs the analysis and reports the results to the Division's office, which would normally receive such notification from the supplier. When the Division's laboratory does not perform the analysis, and the supplier chooses to use a laboratory certified by the Division, analytical results shall be reported to the Division's office in a manner that is specified by the Division.
(5) Records Maintained by Public Water System. The water supply system shall submit to the Division within the time stated in the request copies of any records required to be maintained under Rule 391-3-5-.15 hereof or copies of any documents then in existence which the Division is entitled to inspect pursuant to the authority of the Act.
(6) Failure to Comply with National Primary Drinking Water Regulation. Each system, upon discovering that an exceedance of any National Primary Drinking Water Regulation has occurred, must report that occurrence to the Division by telephone within forty-eight (48) hours or before the end of the next business day, whichever is earlier, followed by a written report, except where a different reporting period is specified in federal regulations.
(7) Lead and Copper Information. All water systems shall report all lead and copper information in accordance with 40 CFR Part 141.90 when applicable. Separate reports are required for each of the following:
1. tap water monitoring for lead and copper, and other water quality monitoring;
2. source water monitoring;
3. corrosion control treatment;
4. source water treatment;
5. lead service line replacement;
6. public education programs.
(8) Reserved.
(9) Disinfection Byproducts Information. Systems monitoring for disinfection by products (TTHM, HAA5, chlorite, bromate) under the requirements of 40 CFR § 141.132(b) must report the information specified in section 40 CFR § 141.134(b).
(10) Disinfectants Information. Systems monitoring for disinfectants (chlorine, chloramines, chlorine dioxide) under the requirements of 40 CFR § 141.132(c) must report the information specified in Section 40 CFR § 141.134(c).
(11) Disinfection Byproduct Precursors Information. Systems monitoring for disinfection byproduct precursors (TOC) under the requirements of 40 CFR § 141.132(d) and required to meet the enhanced coagulation or enhanced softening requirements in 141.135(b)(2) or (3) or meeting one or more of the alternative compliance criteria in 141.135(a)(2) or (3) must report the information specified in section 40 CFR § 141.134(d).
(12) Conventional or Direct Filtration Information for Systems Serving At Least 10,000 Persons. Beginning January 1, 2002, in addition to the requirement in this Chapter, the Subpart H water systems serving at least 10,000 people and providing conventional filtration treatment or direct filtration must report monthly to the Division the information specified in 40 CFR § 141.175(a) and (b). Those systems using filtration technologies other than conventional filtration treatment, direct filtration, slow sand filtration, or diatomaceous earth filtration must report monthly to the Division the information in 40 CFR § 141.175(a) in lieu of reporting in (b)(1).
(13) Content of Consumer Confidence Reports. 40 CFR § 141.153 is hereby incorporated by reference.
(14) Filtration Information for Systems Serving Less Than 10,000 Persons. In addition to the requirements in this Chapter, the Subpart H water systems serving fewer than 10,000 people must report the required items at the frequency described in 40 CFR Subpart T § 141.570.
(15) Filter Backwash Information. All subpart H systems that employ conventional filtration or direct filtration treatment and that recycle spent filter backwash water, thickener supernatant, or liquids from dewatering processes must report the information specified in 40 CFR § 141.76(b)(1) and (2) to the Division no later than December 8, 2003.
(16) Waterborne Disease Outbreak. Each system, upon discovering that a waterborne disease outbreak potentially attributable to that water system has occurred, must report that occurrence to the Division by telephone within forty-eight (48) hours or before the end of the next business day, whichever is earlier, followed by a written report.

Rule 391-3-5-.31 Monitoring of Consecutive Public Water Systems

Purchased water systems may be monitored as consecutive systems with the consent of the system involved and the approval of the Director. Monitoring schedules and reporting procedures for consecutive water systems must be in the form and manner as specified by the Division.

Rule 391-3-5-.32 Public Notification

(1) Public Notification Requirements. 40 CFR, Part 141 , Subpart Q §§ 141.201 through 141.210, including Appendices A, B and C to subpart Q of Part 141, is hereby incorporated by reference. Any amendments to any part of the appendices in 40 CFR, Subpart Q are hereby incorporated by reference. If a community or non-community water system fails to comply with an applicable primary maximum contaminant level or maximum residual disinfectant level established in Rule 391-3-5-.18; fails to comply when applicable with the secondary maximum contaminant level for fluoride established in Rule 391-3-5-.19; fails to comply with an applicable testing procedure established in Rules 391-3-5-.20, .21, .22, .23, .24, .25, .27, .52, .53, .54, or .55; is granted a variance or an exemption from an applicable maximum contaminant level; fails to comply with the requirements of any schedule prescribed pursuant to a variance or exemption; or fails to comply with any treatment technique requirement specified by the Director; or fails to perform any monitoring or reporting required pursuant to Rules 391-3-5-.20, .21, .22, .23, .24, .25, .26, .27, .30, .52, .53, .54, and .55; the supplier of water shall notify persons (including the mandatory health effects language) served by the system as required in 40 CFR, Part 141, Subpart Q. Other situations that require public notification include: occurrence of waterborne disease outbreak or other waterborne emergency; availability of unregulated contaminant monitoring data; detection of E. Coli in source water samples collected under Rule 391-3-5-.54(3); exceedance of the nitrate MCL by non-community water systems, where granted permission by the Division in accordance with Rule 391-3-5-.18(1)(b); and other situations not already listed and determined by EPD to require a public notice. The public water system, within ten (10) days of completing the public notification requirements under 40 CFR, Parts 141, Subpart Q for the initial public notice and any repeat notices, must submit to the Division a certification that it has fully complied with the public notification regulations. The public water system must include with this certification a representative copy of each type of notice distributed, published, posted, and made available to the persons served by the system and to the media.
(2) Public Notification of Lead Contamination. The owner or operator of each community water system and each non-transient, non-community water system shall issue notice, in accordance with 40 CFR, Part 141.34, to persons served by the system that may be affected by lead contamination of their drinking water. The owner or operator shall provide notice under this rule even if there is no violation of the national primary drinking water regulation for lead.
(3) Provide Notice Prior to New Service. The owner or operator of a community or non-community water system must deliver a copy of the most recent public notice for any outstanding violation of any maximum contaminant level, any maximum residual disinfectant level, any treatment technique requirement, any monitoring or reporting requirement, any variance or exemption schedule and other situations requiring public notice to all new consumers at the time service begins. The owner or operator of a non-community water system shall continuously post such public notice in conspicuous locations to inform new consumers for as long as the situation persists.
(4) Cryptosporidium Public Notice. Special public notice for repeated failure to conduct monitoring of the source water for Cryptosporidium and for failure to determine bin classification or mean Cryptosporidium level: 40 CFR, Subpart Q § 141.211, in its entirety, including Appendix A, is hereby incorporated by reference. The specified mandatory language must be included in the special notice.
(5) Non-Applicability. Any reference to public notification requirements in 40 CFR 141.32 is not applicable.

Rule 391-3-5-.33 Variances and Exemptions

(1) Variances and exemptions from certain provisions of these regulations may be granted by the Director pursuant to O.C.G.A. Sec. 12-5-178 and 40 CFR § 141.4 and in the case of arsenic, 40 CFR § 142.20(b).
(2) Variances or exemptions from the MCLs for total coliforms and E. coli and variances from any of the treatment technique requirements of Subpart H systems may not be granted. As provided in 40 CFR § 142.304(a), small systems variances are not available for rules addressing microbial contaminants, which would include 40 CFR Part 141 Subparts H, P, S, T, W, and Y.
(3) The Division has stayed the effective date relating to the total coliform MCL of Rule 391-3-5-.18(4)(a) for systems that demonstrate to the Division that the violation of the total coliform MCL is due to a persistent growth of total coliforms in the distribution system rather than fecal or pathogenic contamination, a treatment lapse or deficiency, or a problem in the operation or maintenance of the distribution system. This is stayed until March 31, 2016, at which time the total coliform MCL is no longer effective.

Rule 391-3-5-.34 Emergencies

Whenever the Director finds that an emergency exist, presenting an imminent hazard to the public health, safety or welfare, requiring immediate action to protect the public health and to insure that the need for safe drinking water is met, he may, without notice or hearing, issue such order or orders as he deems necessary and appropriate to meet to emergency. Any such order shall cite the existence of an emergency and shall contain a brief statement of the reasons for his finding that an emergency exists. Such orders shall be immediately effective and any person affected thereby shall comply therewith immediately. Such orders shall, however, contain a notice of the time and place of a hearing scheduled within twenty (20) days from the issuance of such order before a Hearing Officer, appointed by the Department. Based upon the findings, of the Hearing Officer, the order shall be modified, revoked, or continued as the Hearing Officer deems appropriate.

Rule 391-3-5-.35 Inspections and Investigations

(1) Access for Inspection or Investigation. The Director, or his appointed agent, shall be permitted access in or upon any private or public property at all reasonable times for the purpose of inspecting or investigating conditions, processes, equipment, methods, treatment, facilities, or records relating to or associated with the operation of any water system, to determine applicability of and compliance with the Act and these rules, to investigate any apparent violation of the Act, and to make such other investigations as he deems advisable and necessary for the protection of the public health or welfare pursuant to the Act.
(2) Issue Orders for Compliance. Based on the Director's findings in any such inspection or investigation, or upon denial of entry pursuant to the above paragraph, the Director may issue such orders as are necessary to insure compliance with the Act and these rules.

Rule 391-3-5-.36 Enforcement

The administration and enforcement of these rules and regulations shall be in accordance with the Georgia Administrative Procedure Act. Such enforcement measures include, but are not limited to, administrative orders, court orders, injunctive relief, and civil and criminal penalties pursuant to the Act.

Rule 391-3-5-.37 State Primacy Maintenance

(1) Notwithstanding any other section, the requirements of these Safe Drinking Water Rules shall in any event be the same as the requirements of the National Primary Drinking Water Regulations in 40 CFR, Part 141 promulgated pursuant to Section 1412 of the Federal Act ( 42 U.S.C. 300g-1) .
(2) The Director may prescribed more stringent requirements than those specified by any other section of these Safe Drinking Water Rules when necessary to:
(a) meet any requirements of the Federal Act and Regulations; or
(b) safeguard the public health, safety and welfare.

Rule 391-3-5-.38 [Repealed]

Rule 391-3-5-.39 Public Water System Classification

(1) Purpose. In accordance with Section 10 of the Certification of Water and Wastewater Treatment Plant Operators and Laboratory Analysts Act (O.C.G.A. Section 43-51-1) the following classifications shall be considered as minimum levels, and the Division may classify any system or plant at a higher level if the complexity of the system or plant warrants such higher classification in the judgment of the Division. Any system or plant not fitting any of the following standard descriptions shall be classified individually according to the judgment of the Division. Where water is supplied to a distribution system from two or more sources, the classification may be set by the Division.
(2) Minimum Classifications. The following classifications shall be considered as minimum levels:

Public Water System Classification for Community and Non-transient Non-community Systems1

System Type

Class I

Class II

Class III

Class IV

Surface water with conven-tional treatment plant

5.0 MGD or greater

4.99 MGD or less

n/a

n/a

Surface water with package or non-conven-tional treatment plant

1.0 MGD or greater

0.99 MGD or less

n/a

n/a

Surface water with approved high-rate filtration

3.0 gpm/sq.ft. or greater

Less than 3.0 gpm/sq.ft.

n/a

n/a

Groundwater under the direct influence of surface water

1.0 MGD or greater

Greater than 0.1 MGD to 0.99 MGD

0.1 MGD or less

n/a

Ground-water

50,000 or greater population

10,000 to 49,999 population

1,000 to 9,999 population

25 to 999 population

Distribution systems

Certification is required for the operator of public water distribution systems.

Note: 1 MGD is million gallons per day; gpm/sq.ft. is gallons per minute per square-foot filter surface area; n/a is not applicable.
(3) Groundwater Transient Non-community Water Systems. All Transient Non-community water systems with groundwater sources must have at least a Class IV operator certification.
(4) Surface Water Transient Non-community Water Systems. Certification of Transient Non-community water systems with surface water will be specified in their permit to operate a public water system.
(5) Higher Classification. When the complexity of water treatment warrants it, a higher classification may be required and specified in the permit to operate a public water system.

Rule 391-3-5-.40 Wellhead Protection

(1) Purpose. The following rule for wellhead protection serve to help protect wells and springs used as sources of water supply for community public water systems owned by and/or serving municipalities, counties, and authorities from nearby pollution sources.
(2) Development of Wellhead Protection Plan. The Division shall develop a Wellhead Protection Plan for every well, well field or spring which is used as a source for a community public water supply owned by and/or serving a municipality, county, or an authority.
(3) Components of Wellhead Protection Plans. Wellhead Protection Plans shall consist of five parts; namely:
(a) an identification and location of a Control Zone for each well or spring;
(b) an identification and location of each required Management Zone for each well or spring;
(c) an inventory of potential pollution sources in the designated wellhead protection areas;
(d) a management plan for potential pollution sources identified in the inventory; and
(e) if available, a contingency plan submitted by the supplier to the Division describing how alternate water supplies will be provided in case the well(s) in question become polluted. The Division shall develop all individual Wellhead Protection Plans consistent with the rules.
(4) Wellhead Protection Zones. Every Wellhead Protection Area shall consist of two zones, as follows:
(a) The Control Zone: Within this zone, the owner shall control all activities so that there are minimal sources of potential pollution in the immediate vicinity of the well bore.
(b) The Management Zone: Within this zone, certain potential pollution sources are prohibited or certain activities must be performed in accordance with the rules listed below. The size and shape of the management zone will vary according to aquifer type, aquifer hydraulic conductivity, pumpage rate, hydrologic province, and proximity to recharge.
(5) Control Zone. All wells used as a source of public water supply for community public water systems owned by and/or serving municipalities, counties, or authorities shall have a control zone.
(6) Delineation of Management Zone. The Division shall delineate the size and shape of the management zone of a wellhead protection area as defined below:
(a) wells determined by the Division as drawing water only from confined aquifers shall have an inner management zone extending outward from the center of the borehole for a radius of 100 feet. No outer management zone is required for such wells.
(b) wells drawing water from unconfined aquifers as determined by the Division and springs, except those determined by the Division to lie in areas of karst, shall have an inner management zone extending outward from the center of the borehole or spring head for a radius of 250 feet.
(c) wells drawing water from unconfined aquifers as determined by the Division and springs, which the Division has identified as being in areas of karst, shall have an inner management zone extending outward from the center of the borehole or spring head for a radius of 500 feet.
(d) unconfined wells which the Division has determined utilize fractured crystalline rock aquifers shall have an outer management zone determined according to the "Health Method Curve" contained in the EPA approved Georgia Wellhead Protection Plan.
(e) unconfined aquifer wells determined by the Division as lying in karst regions and all springs shall have an outer management zone determined by hydrogeologic mapping or other method acceptable to the Division.
(f) Other wells not meeting the above criteria shall have their outer management zones determined by time of travel calculations (a minimum of a 5-year time of travel) or by volumetric calculations as appropriate.
(7) Inventory of Potential Pollution Sources. The Division shall carry out an inventory of potential pollution sources within the control zone and management zones. Inventories shall be permanently maintained by the Division in computer data base format. Minimum information shall be the name and address of the owner of the well or spring, location of the well or spring, applicable permit data, the size and shape of the control and management zones, and the types of potential pollution sources. Inventories shall be carried out by the Division every ten (10) years.
(8) Inner and Outer Management Zones. Within the inner and outer management zones of existing wells and springs, the following shall apply:
(a) The Division shall not issue any new permits for municipal solid waste landfills, industrial waste landfills or construction/demolition waste landfills.
(b) The Division shall not issue any new permits for the land disposal of hazardous wastes.
(c) The Division shall require all new facilities permitted to handle, treat, store or dispose of hazardous waste or hazardous materials to perform such operations on an impermeable pad having a spill and leak collection system.
(d) The Division shall require all new agricultural waste impoundments to have an impermeable synthetic liner.
(e) The Division shall not issue any new permits for land application of wastewater or sludge.
(f) Deleted.
(g) The Division shall not issue permits for any new quarries or underground mines unless a hydrogeological investigation carried out by the applicant clearly demonstrates that operation of the quarry or mine will not pollute the well or spring or cause a reduction of ground water flow to the well or spring. Such investigation shall be performed by a professional engineer or professional geologist.
(h) The Division shall require that all new underground storage tanks installed shall meet the highest standards applicable under the Underground Storage Tank Act. All preexisting underground storage tanks shall be required to have ground water or vapor monitoring. All abandoned underground storage tanks shall meet the requirements of Section 391-3-15-.11 of the Rules for Underground Storage Tanks.
(i) The Division shall require all new wastewater treatment basins to have an impermeable synthetic liner.
(9) New Sources that are Wells or Springs. For new wells or springs that are to be used as a source of water supply for a community public water system owned by and/or serving a municipality, county, or authority the following shall apply:
(a) The Division shall not issue any permit for the addition of a new well or spring until the Division has delineated an appropriate wellhead protection area and carried out an inventory of potential pollution sources in the wellhead protection area of the proposed well or spring. The Division shall make provision for emergency situations.
(b) Once the owner and/or supplier requests the Divisions approval for the construction and/or development of a new well, well field, or spring, the Division shall require the Owner and/or supplier to provide the Division with the exact location, intended aquifer, projected depth and expected production of the planned well(s) or springs.
(c) The Division shall not issue approval for the construction and/ or development of well or spring where the following potential pollution sources are known to be present within the inner management zone:
1. underground storage tanks;
2. non-domestic septic tanks with drain fields;
3. animal feedlots, poultry enclosures, or animal enclosures (this rule shall not be construed to apply to family pets);
4. Environmental facilities permitted by the Division or other potential pollution sources identified in the inventory unless the Division has determined that there will be no releases to the ground or that such releases, if they occur, will not be a threat to public health and safety. Domestic septic systems that are identified within the inner management zone shall be excluded from the requirements of this section, provided they are located in accordance with the criteria specified in Rule 391-3-5-.07 of this Chapter.
(10) Notification. The Division shall notify the owner of any regulated or unregulated chemicals which the Division believes, based on the potential pollution source inventory, may be present in the control zone or management zones of new or existing individual wells, well fields, or springs.
(11) Underground Injection Wells. Within the inner management zone of existing wells and springs, the Division shall not issue any new permits for underground injection wells, with the exception of remediation wells.

Rule 391-3-5-.41 Consumer Confidence Reports

(1) Purpose and Applicability.40 CFR Part 141, Subpart O§141.151 is hereby incorporated by reference.
(2) Effective Dates.
(a) Each existing community water system must deliver to all its customers its first report by October 19, 1999, its second report by July 1, 2000, and subsequent reports by July 1 annually thereafter. The first report must contain data collected during, or prior to, calendar year 1998 as prescribed in 40 CFR Part 141, Subpart O§141.153(d)(3). Each report thereafter must contain data collected during, or prior to, the previous calendar year.
(b) A new community water system must deliver to all its customers its first report by July 1 of the year after its first full calendar year in operation and annually thereafter.
(c) A community water system that sells water to another community water system must deliver the applicable information required in 40 CFR Part 141, Subpart O§141.153 to the buyer system:
1. No later than April 19, 1999, by April 1, 2000, and by April 1 annually thereafter or
2. On a date mutually agreed upon by the seller and the purchaser, and specifically included in a contract between the parties.
(3) Content of the reports:40 CFR Part 141, Subpart O§141.153 is hereby incorporated by reference.
(4) Required additional health information:40 CFR Part 141, Subpart O§141.154 is hereby incorporated by reference.
(5) Report delivery and recordkeeping:40 CFR Part 141, Subpart O§141.155 is hereby incorporated by reference.
(6) Appendix A to Subpart O of 40 CFR Part 141 - Regulated Contaminants is hereby incorporated by reference.
(7) Electronic Delivery.
(a) Community water systems may provide Consumer Confidence Reports electronically provided that:
1. The manner of the electronic delivery is a direct communication link, without use of an intermediary service;
2. There is an explanatory notice that accompanies the direct communication link;
3. The entire content of the Consumer Confidence Report is accessible;
4. The community water system shall provide the Consumer Confidence Report through another method should the community water system become aware of a customer's inability to receive the Consumer Confidence Report by the chosen electronic delivery method.

Rule 391-3-5-.42 Source Water Assessment

(1) Purpose. The following Rule for Source Water Assessment serves to help protect the source waters of public water systems of the State.
(2) Requirement to Develop a Source Water Assessment Plan. By May 2003, each public water system of the State shall develop a Source Water Assessment Plan (SWAP) for every well and surface water intake used by the water system. SWAPs will be developed in accordance with the Division's Source Water Assessment and Protection Implementation Plan for Public Drinking Water Sources. Large surface water systems, which supply water (directly or through wholesale) to a population of 50,000 or more, will be delegated the responsibility of developing and implementing a Source Water Assessment Plan. Surface water systems which supply water (directly or through wholesale) to a population less than 50,000 will have the assessment done by the Division. The Division encourages both large and small surface water systems to create partnerships with each other and the Division in order to conduct assessment of common regional watersheds.
(3) Components of a Source Water Assessment Plan. A SWAP shall consist of four parts:
(a) The delineation of the area in proximity to the water well(s) or surface water intake(s) shall consist of:
1. At a minimum, a zone equivalent to the outer management zone of a wellhead protection area for water wells.
2. At a minimum, the upstream surface drinking water intake catchment area portions of the watershed as defined in the SWAP Implementation Plan.
(b) The water system shall inventory the potential pollution sources of natural and manmade origin within the area delineated in (a) above. The inventory will include the potential pollution sources as defined in the SWAP Implementation Plan.
(c) The water system shall carry out an assessment of the potential pollution sources' impact within the areas described by (a) above, on the raw water that may reach the water well(s) or surface water intake(s). Assessments for surface water intakes are to follow the guidance published in the SWAP Implementation Plan.
(d) The water system shall prepare a comprehensive SWAP report describing items (a), (b) and (c) above and submit the report to the Division for review and approval. The water system will make this report available to the public.
(1) Use of Wellhead Protection Plans. Public groundwater systems may use their prepared Wellhead Protection Plans and Vulnerability Assessments to satisfy the Source Water Assessment requirements.

Rule 391-3-5-.43 Repealed

Rule 391-3-5-.44 Repealed

Rule 391-3-5-.45 Repealed

Rule 391-3-5-.46 Repealed

Rule 391-3-5-.47 Repealed

Rule 391-3-5-.48 Repealed

Rule 391-3-5-.49 Repealed

Rule 391-3-5-.50 Repealed

Rule 391-3-5-.51 Repealed

Rule 391-3-5-.52 Long Term 2 Enhanced Surface Water Treatment Rule (LT2ESWTR)

(1) Purpose. The purpose of the Long Term 2 Enhanced Surface Water Treatment Rule (LT2ESWTR) is to reduce illness linked with the contaminant Cryptosporidium and other disease-causing microorganisms in drinking water. The rule supplements existing regulations by targeting additional Cryptosporidium treatment requirements to higher risk systems. This rule also contains provisions to reduce risks from uncovered finished water reservoirs and to ensure that systems maintain microbial protection when they take steps to decrease the formation of disinfection byproducts that result from chemical water treatment.
(2) Applicability. This regulation applies to all public water systems that use surface water or ground water under the direct influence (GWUDI) of surface water.
(3) Enhanced Treatment for Cryptosporidium.
(a) General requirements. The requirements of 40 CFR Part 141 Subpart W are national primary drinking water regulations. The regulations in this subpart establish or extend treatment technique requirements in lieu of maximum contaminant levels for Cryptosporidium. These requirements are in addition to requirements for filtration and disinfection in Subparts H, P, and T of 40 CFR Part 141.
(b) Applicability. The requirements of 40 CFR Part 141 SubpartW apply to all public water systems supplied by a surface water source and public water systems supplied by a ground water source under the direct influence of surface water.
1. Wholesale systems, as defined in 40 CFR § 141.2, must comply with the requirements of 40 CFR Part 141 Subpart W based on the population of the largest system in the combined distribution system.
2. The requirements of 40 CFR Part 141 Subpart W for filtered systems apply to systems required by National Primary Drinking Water Regulations to provide filtration treatment, whether or not the system is currently operating a filtration system.
3. The requirements of 40 CFR Part 141 Subpart W for unfiltered systems apply only to unfiltered systems that timely met and continue to meet the filtration avoidance criteria in Subparts H, P, and T of 40 CFR Part 141, as applicable.
(c) Requirements. Systems subject to 40 CFR Part 141 Subpart W must comply with the following requirements:
1. Systems must conduct an initial and a second round of source water monitoring for each plant that treats a surface water or GWUDI source. This monitoring may include sampling for Cryptosporidium, E. coli, and turbidity as described in 40 CFR § 141.701 through 141.706, to determine what level, if any, of additional Cryptosporidium treatment they must provide.
2. Systems that plan to make a significant change to their disinfection practice must develop disinfection profiles and calculate disinfection benchmarks, as described in 40 CFR §§ 141.708 through 141.709.
3. Filtered systems must determine their Cryptosporidium treatment bin classification as described in 40 CFR § 141.710 and provide additional treatment for Cryptosporidium, if required, as described in 40 CFR § 141.711. All unfiltered systems must provide treatment for Cryptosporidium as described in 40 CFR § 141.712. Filtered and unfiltered systems must implement Cryptosporidium treatment according to the schedule in 40 CFR § 141.713.
4. Systems with uncovered finished water storage facilities must comply with the requirements to cover the facility or treat the discharge from the facility as described in 40 CFR § 141.714.
5. Systems required to provide additional treatment for Cryptosporidium must implement microbial toolbox options that are designed and operated as described in 40 CFR § 141.715 through 141.720.
6. Systems must comply with the applicable recordkeeping and reporting requirements described in 40 CFR § 141.721 through 141.722.
7. Systems must address significant deficiencies identified in sanitary surveys performed by EPA or Division as described in 40 CFR § 141.723.
(4) Source Water Monitoring. 40 CFR, Subpart W § 141.701(a) through (h), in its entirety, is hereby incorporated by reference. Systems are required to conduct source water monitoring for Cryptosporidium, E. coli, and turbidity in accordance with the monitoring schedule specified in this section.
(5) Sampling Schedules. 40 CFR, Subpart W § 141.702(a) through (c), in its entirety, is hereby incorporated by reference. Systems required to conduct source water monitoring under 40 CFR § 141.701 must submit a sampling schedule that specifies the calendar dates when the system will collect each required sample.
(6) Sampling Locations. 40 CFR, Subpart W § 141.703(a) through (f), in its entirety, is hereby incorporated by reference. Systems required to conduct source water monitoring under 40 CFR § 141.701 must collect samples for each plant that treats a surface water or GWUDI source. Where multiple plants draw water from the same influent, such as the same pipe or intake, the Division may approve one set of monitoring results to be used to satisfy the requirements of 40 CFR § 141.701 for all plants. Systems must collect source water samples prior to chemical treatment, such as coagulants, oxidants and disinfectants, unless the Division determines that collecting a sample prior to chemical treatment is not feasible for the system and that the chemical treatment is unlikely to have a significant adverse effect on the analysis of the sample.
(7) Analytical Methods. 40 CFR, Subpart W § 141.704(a) through (c), in its entirety, is hereby incorporated by reference.
(8) Approved Laboratories. 40 CFR, Subpart W § 141.705(a) through (c), in its entirety, is hereby incorporated by reference.
(9) Reporting Source Water Monitoring Results. 40 CFR, Subpart W § 141.706(a) through (e), in its entirety, is hereby incorporated by reference.
(10) Grandfathering Previously Collected Data. 40 CFR, Subpart W § 141.707(a) through (h), in its entirety, is hereby incorporated by reference. Systems may comply with the initial source water monitoring requirements of 40 CFR § 141.701(a) by grandfathering sample results collected before the system is required to begin monitoring (i.e., previously collected data). To be grandfathered, the sample results and analysis must meet the criteria in this section and the Division must approve.
(11) Requirements when Making a Significant Change in Disinfection Practice. 40 CFR, Subpart W § 141.708(a) through (b), in its entirety, is hereby incorporated by reference. Following the completion of initial source water monitoring under 40 CFR § 141.701(a), a system that plans to make a significant change to its disinfection practice, as defined in this section, must calculate disinfection benchmarks for Giardia lamblia and viruses as described in 40 CFR § 141.709. Prior to changing the disinfection practice, the system must notify the Division and must include in this notice the information outlined in this section. Significant changes to disinfection practice are defined as follows:
(a) Changes to the point of disinfection;
(b) Changes to the disinfectant(s) used in the treatment plant;
(c) Changes to the disinfection process; or
(d) Any other modification identified by the State as a significant change to disinfection practice.
(12) Developing the Disinfection Profile and Benchmark. 40 CFR, Subpart W § 141.709(a) through (e), in its entirety, is hereby incorporated by reference. Systems required to develop disinfection profiles under 40 CFR § 141.708 must follow the requirements of this section. Systems must monitor at least weekly for a period of 12 consecutive months to determine the total log inactivation for Giardia lamblia and viruses. The disinfection benchmark is the lowest monthly mean value (for systems with one year of profiling data) or the mean of the lowest monthly mean values (for systems with more than one year of profiling data) of Giardia lamblia and virus log inactivation in each year of profiling data.
(13) Bin Classification for Filtered Systems. 40 CFR, Subpart W § 141.710(a) through (f), in its entirety, is hereby incorporated by reference. Following completion of the initial round of source water monitoring required under 40 CFR § 141.701(a), filtered systems must calculate an initial Cryptosporidium bin concentration for each plant for which monitoring was required. Calculation of the bin concentration must use the Cryptosporidium results reported under 40 CFR § 141.701(a) and must follow the procedures outlined in this section.
(a) Filtered systems must determine their initial bin classification from the table in 40 CFR 141.710(c) and using the Cryptosporidium bin concentration calculated under paragraphs (a)-(b) of this section ( 40 CFR, Subpart W § 141.710) .
(b) Following completion of the second round of source water monitoring required under 40 CFR § 141.701(b), filtered systems must recalculate their Cryptosporidium bin concentration using the Cryptosporidium results reported under 40 CFR § 141.701(b) and following the procedures in paragraphs (b)(1) through (4) of 40 CFR § 141.710. Systems must then redetermine their bin classification using this bin concentration and the table in paragraph (c) of 40 CFR § 141.710.
(14) Filtered System Additional Cryptosporidium Treatment Requirements. 40 CFR, Subpart W § 141.711(a) through (d), in its entirety, is hereby incorporated by reference. Filtered systems must provide the level of additional treatment for Cryptosporidium specified in paragraph (a) of 40 CFR § 141.711 based on their bin classification as determined under 40 CFR § 141.710 and according to the schedule in 40 CFR § 141.713.
(a) Filtered systems must use one or more of the treatment and management options listed in 40 CFR § 141.715, termed the microbial toolbox, to comply with the additional Cryptosporidium treatment required in paragraph (a) of 40 CFR § 141.711.
(b) Systems classified in Bin 3 and Bin 4 must achieve at least 1-log of the additional Cryptosporidium treatment required under paragraph (a) of 40 CFR § 141.711 using either one or a combination of the following: bag filters, bank filtration, cartridge filters, chlorine dioxide, membranes, ozone, or UV, as described in 40 CFR §§ 141.716 through 141.720.
(c) Failure by a system in any month to achieve treatment credit by meeting criteria in §§ 141.716 through 141.720 for microbial toolbox options that is at least equal to the level of treatment required in paragraph (a) of 40 CFR § 141.711 is a violation of the treatment technique requirement.
(15) Unfiltered System Cryptosporidium Treatment Requirements. All systems that are using surface water sources or groundwater sources that are determined to be under the direct influence of surface water supplies are required to provide filtration and disinfection treatments, in addition to that other treatments that are required by the Division, in order to comply with the drinking water standards, regulations and operating permit conditions, required by the Rules for Safe Drinking Water, Chapter 391-3-5. In order to provide regulatory information on the Cryptosporidium treatment requirements for unfiltered water systems, 40 CFR, Subpart W § 141.712(a) through (d) is hereby incorporated by reference.
(16) Schedule for Compliance with Cryptosporidium Treatment Requirements.
(a) Following initial bin classification under 40 CFR § 141.710(c), filtered systems must provide the level of treatment for Cryptosporidium required under 40 CFR § 141.711 according to the schedule in paragraph (16)(c).
(b) Following initial determination of the mean Cryptosporidium level under 40 CFR § 141.712(a)(1), unfiltered systems must provide the level of treatment for Cryptosporidium required under 40 CFR § 141.712 according to the schedule in paragraph (16)(c).
(c) Cryptosporidium treatment compliance dates.

CRYPTOSPORIDIUM TREATMENT COMPLIANCE DATES TABLE

Systems that serve ...

Must comply with Cryptosporidium treatment requirements no later than ...(1)

At least 100,000 people.

April 1, 2012

From 50,000 to 99,999 people.

October 1, 2012

From 10,000 to 49,999 people.

October 1, 2013

Fewer than 10,000 people.

October 1, 2014

Note: (1) States may allow up to an additional two years for complying with the treatment requirement for systems making capital improvements.

(d) If the bin classification for a filtered system changes following the second round of source water monitoring, as determined under 40 CFR § 141.710(d), the system must provide the level of treatment for Cryptosporidium required under 40 CFR § 141.711 on a schedule the Division approves.
(e) If the mean Cryptosporidium level for an unfiltered system changes following the second round of monitoring, as determined under 40 CFR § 141.712(a)(2), and if the system must provide a different level of Cryptosporidium treatment under 40 CFR § 141.712 due to this change, the system must meet this treatment requirement on a schedule the Division approves.
(17) Requirements for Uncovered Finished Water Storage Facilities. All finished water storage facilities must be provided with a permanent cover, in accordance with Rule 391-3-5-.11. In order to provide regulatory information on the requirements for uncovered finished water storage facilities, 40 CFR, Subpart W § 141.714(a) through (d) is hereby incorporated by reference.
(18) Microbial Toolbox Options for Meeting Cryptosporidium Treatment Requirements. 40 CFR, Subpart W § 141.715(a) through (b) is hereby incorporated by reference.
(a) Source toolbox components. 40 CFR, Subpart W § 141.716(a) through (b) is hereby incorporated by reference.
(b) Pre-filtration treatment toolbox components. 40 CFR, Subpart W § 141.717(a) through (c) is hereby incorporated by reference.
(c) Treatment performance toolbox components. 40 CFR, Subpart W § 141.718(a) through (c) is hereby incorporated by reference.
(d) Additional filtration toolbox components. 40 CFR, Subpart W § 141.719(a) through (d) is hereby incorporated by reference.
(e) Inactivation toolbox components. 40 CFR, Subpart W § 141.720(a) through (d) is hereby incorporated by reference.
(19) Reporting Requirements. 40 CFR, Subpart W § 141.721(a) through (f) is hereby incorporated by reference.
(20) Recordkeeping Requirements. 40 CFR, Subpart W § 141.722(a) through (c) is hereby incorporated by reference.
(21) Requirements to Respond to Significant Deficiencies Identified in Sanitary Surveys Performed by EPA or Division. 40 CFR, Subpart W § 141.723(a) through (d) is hereby incorporated by reference. Systems must respond in writing to significant deficiencies identified in sanitary survey reports no later than forty-five (45) days after receipt of the report, indicating how and on what schedule the system will address significant deficiencies noted in the survey. Systems must correct significant deficiencies identified in sanitary survey reports according to the approved schedule, or if there is no approved schedule, according to the schedule submitted by the system if such deficiencies are within the control of the system.
(22) Division Recordkeeping. The records kept by the Division shall be in accordance with 40 CFR § 142.14.
(23) Division Reporting. The reporting by the Division shall be performed as required by 40 CFR § 142.15.

Rule 391-3-5-.53 Stage 2 Disinfection Byproducts Rule (Stage 2 DBPR)

Purpose. The Stage 2 Disinfection Byproducts Rule (DBPR) (40 CFR, Subpart V § 141) builds on existing regulations by requiring water systems to meet disinfection byproduct (DBP) maximum contaminant levels (MCLs) at each monitoring site in the distribution system to better protect public health. The Stage 2 DBPR includes a provision requiring all community water systems (CWS) and only non-transient non-community water systems (NTNCWS) serving more than 10,000 people to conduct an initial distribution system evaluation (IDSE) (40 CFR, Subpart U § 141) . NTNCWS serving less than 10,000 are exempted from IDSE requirements, but will need to comply with the Stage 2 DBPR compliance monitoring requirements. The goal of the IDSE is to characterize the distribution system and identify monitoring sites where customers may be exposed to high levels of total trihalomethanes (TTHM) and haloacetic acids (HAA5).

(1) Initial Distribution System Evaluations.
(a) General requirements: The requirements of 40 CFR Part 141Su bpart U constitute national primary drinking water regulations. The regulations in 40 CFR Part 141 Subpart U establish monitoring and other requirements for identifying 40 CFR Part 141 Subpart V compliance monitoring locations for determining compliance with maximum contaminant levels for total trihalomethanes (TTHM) and haloacetic acids (five) (HAA5). A system must use an Initial Distribution System Evaluation (IDSE) to determine locations with representative high TTHM and HAA5 concentrations throughout its distribution system. IDSEs are used in conjunction with, but separate from, compliance monitoring per 40 CFR Part 141 Subpart L, to identify and select compliance monitoring locations per 40 CFR Part 141 Subpart V.
(b) Applicability: Public water systems are subject to these requirements if the water system is a community water system that uses a primary or residual disinfectant other than ultraviolet light or delivers water that has been treated with a primary or residual disinfectant other than ultraviolet light; or if the water system is a non-transient non-community water system that serves at least 10,000 people and uses a primary or residual disinfectant other than ultraviolet light or delivers water that has been treated with a primary or residual disinfectant other than ultraviolet light.
(c) Schedule: 40 CFR Subpart U § 141.600(c), in its entirety, is hereby incorporated by reference. Systems required to comply with Initial Distribution System Evaluations - Subpart U, must comply with the schedule specified in the table 40 CFR § 141.600(c)(1). A wholesale system or a consecutive system must comply with the specified schedule at the same time as the system with the earliest compliance date in the combined distribution system.
(d) 40 CFR Subpart U § 141.600(d) through (f), in its entirety, is hereby incorporated by reference.
(e) Standard Monitoring: 40 CFR Subpart U § 141.601is hereby incorporated by reference.
1. Standard monitoring plan: 40 CFR Subpart U § 141.601(a) through (c), in its entirety, is hereby incorporated by reference.
2. System specific studies: 40 CFR Subpart U § 141.602(a) through (b), in its entirety, is hereby incorporated by reference.
3. 40/30 Certification: 40 CFR Subpart U § 141.603(a) through (b), in its entirety, is hereby incorporated by reference.
4. Very small system waivers: 40 CFR Subpart U § 141.604(a) through (b), in its entirety, is hereby incorporated by reference.
(f) 40 CFR Part 141 Subpart V Compliance Monitoring Location Recommendations: 40 CFR Subpart U § 141.605(a) through (e), in its entirety, is hereby incorporated by reference. Water system's IDSE report must include the recommendations and justification for where and during what month(s) TTHM and HAA5 monitoring for Subpart V of part 141 should be conducted. Water system must base its recommendations on the criteria in paragraphs (b) through (e) of this section.
(2) Stage 2 Disinfection Byproducts Requirements.
(a) General Requirements: The requirements of 40 CFR Part 141Su bpart V constitute national primary drinking water regulations. The regulations establish monitoring and other requirements for achieving compliance with maximum contaminant levels based on locational running annual averages (LRAA) for total trihalomethanes (TTHM) and haloacetic acids (five) (HAA5), and for achieving compliance with maximum residual disinfectant residuals for chlorine and chloramine for certain consecutive systems.
(b) Applicability: Public water systems are subject to these requirements if the system is a community water system or a non-transient non-community water system that uses a primary or residual disinfectant other than ultraviolet light or delivers water that has been treated with a primary or residual disinfectant other than ultraviolet light.
(c) Schedule: 40 CFR Subpart V § 141.620(c), in its entirety, is hereby incorporated by reference. Systems required to comply with Stage 2 Disinfection Byproducts Requirements - Subpart V, must comply with the schedule specified in the table 40 CFR § 141.620(c). A wholesale system or a consecutive system must comply with the specified schedule at the same time as the system with the earliest compliance date in the combined distribution system.
1. Systems serving 100,000 or more people: April 1, 2012
2. Systems serving 50,000-99,999 people: October 1, 2012
3. Systems serving 10,000-49,999 people: October 1, 2013
4. Systems serving fewer than 10,000 people: October 1, 2013 if no Cryptosporidium monitoring is required under 40 CFR § 141.701(a)(4) OR October 1, 2014 if Cryptosporidium monitoring is required under 40 CFR § 141.701(a)(4) or (a)(6).
(d) Monitoring frequency must be in accordance with 40 CFR Subpart V § 141.621(a)(2).
1. If a water system is required to conduct quarterly monitoring, it must begin monitoring in the first full calendar quarter that includes the compliance date in the table in paragraph 40 CFR § 141.620(c).
2. If a water system is required to conduct monitoring at a frequency that is less than quarterly, it must begin monitoring in the calendar month recommended in the IDSE report prepared under 40 CFR § 141.601 or 40 CFR § 141.602 or the calendar month identified in the Subpart V monitoring plan developed under 40 CFR § 141.622 no later than twelve (12) months after the compliance date in paragraph 40 CFR § 141.620(c).
3. If a water system is required to conduct quarterly monitoring, it must make compliance calculations at the end of the fourth calendar quarter that follows the compliance date and at the end of each subsequent quarter (or earlier if the LRAA calculated based on fewer than four quarters of data would cause the MCL to be exceeded regardless of the monitoring results of subsequent quarters). If a water system is required to conduct monitoring at a frequency that is less than quarterly, it must make compliance calculations beginning with the first compliance sample taken after the compliance date.
4. For the purpose of the schedule in paragraph 40 CFR § 141.620(c), the Division may determine that the combined distribution system does not include certain consecutive systems based on factors such as receiving water from a wholesale system only on an emergency basis or receiving only a small percentage and small volume of water from a wholesale system. The Division may also determine that the combined distribution system does not include certain wholesale systems based on factors such as delivering water to a consecutive system only on an emergency basis or delivering only a small percentage and small volume of water to a consecutive system.
(e) Monitoring and Compliance.
1. Systems required to monitor quarterly. To comply with Subpart V MCLs in 40 CFR § 141.64(b)(2), water systems must calculate LRAAs for TTHM and HAA5 using monitoring results collected under this Subpart and determine that each LRAA does not exceed the MCL. If a water system fails to complete four consecutive quarters of monitoring, it must calculate compliance with the MCL based on the average of the available data from the most recent four quarters. If a water system takes more than one sample per quarter at a monitoring location, it must average all samples taken in the quarter at that location to determine the quarterly average to be used in the LRAA calculation.
2. Systems required to monitor yearly or less frequently. To determine compliance with Subpart V MCLs in 40 CFR § 141.64(b)(2), water systems must determine that each sample taken is less than the MCL. If any sample exceeds the MCL, the water system must comply with the requirements of 40 CFR § 141.625. If no sample exceeds the MCL, the sample result for each monitoring location is considered the LRAA for that monitoring location.
(f) Violations: A water system is in violation of the monitoring requirements for each quarter that a monitoring result would be used in calculating an LRAA if it fails to monitor.
(g) Routine Monitoring: If a water system submitted an IDSE report, it must begin monitoring at the locations and months it has recommended in its IDSE report submitted under 40 CFR § 141.605 following the schedule in 40 CFR § 141.620(c), unless the Division requires other locations or additional locations after its review. If a water system submitted a 40/30 certification under 40 CFR § 141.603 or it qualified for a very small system waiver under 40 CFR § 141.604 or it is a non-transient non-community water system serving less than 10,000, it must monitor at the location(s) and dates identified in its monitoring plan in 40 CFR § 141.132(f), updated as required by 40 CFR § 141.622.
(h) Water systems must monitor at no fewer than the number of locations identified in this paragraph:

Source Water Type

Population Served

Monitoring Frequency(1)

Distribution System Monitoring Locations Total per Monitoring Period(2)

Subpart H

Fewer than 500

per year

2

500-3,300

per quarter

2

3,301-9,999

per quarter

2

10,000-49,999

per quarter

4

50,000-249,999

per quarter

8

250,000-999,999

per quarter

12

1,00,000-4,999,999

5,000, 000 or more

per quarter per quarter

16

20

Ground

Water

Fewer than 500

per year

2

500-9,999

per year

2

10,000-99,999

per quarter

4

100,000-499,999

per quarter

6

500,000 or more

per quarter

8

NOTES:

(1) All systems must monitor during the highest month of DBP concentrations.
(2) Systems on quarterly monitoring must take dual sample sets every 90 days at each monitoring location, except for Subpart H systems serving 500-3,300 persons. Systems on annual monitoring and Subpart H systems serving 500-3,300 persons are required to take individual TTHM and HAA5 samples (instead of a dual sample set) at the locations with the highest TTHM and HAA5 concentrations, respectively. Only one location with a dual sample set per monitoring period is needed if highest TTHM and HAA5 concentrations occur at the same location (and month, if monitored annually).
(i) If a water system is an undisinfected system that begins using a disinfectant other than UV light after the dates in 40 CFR Part 141 Subpart U for complying with the Initial Distribution System Evaluation requirements, it must consult with the Division to identify compliance monitoring locations for 40 CFR Part 141 Subpart V. The water system must then develop a monitoring plan under 40 CFR § 141.622 that includes those monitoring locations.
(j) Analytical Methods: The water system must use an approved method listed in 40 CFR § 141.131, as stated in Rule 391-3-5-.24(4)(g) for TTHM and HAA5 analyses. Analyses must be conducted by laboratories that have received certification by EPA or the Division.
(3) Monitoring Plans for Stage 2 Disinfection Byproducts Requirements.
(a) Water systems must develop and implement a monitoring plan to be kept on file for Division and public review. The monitoring plan must contain the following elements and be complete no later than the date it conducts its initial monitoring under 40 CFR Part 141 Subpart V.
1. Monitoring locations;
2. Monitoring dates;
3. Compliance calculation procedures; and
4. Monitoring plans for any other systems in the combined distribution system.
(b) If a water system was not required to submit an IDSE report under either 40 CFR § 141.601 or § 141.602, and it does not have sufficient 40 CFR Part 141 Subpart L (Stage 1 DBPR) monitoring locations to identify the required number of 40 CFR Part 141 Subpart V (Stage 2 DBPR) compliance monitoring locations indicated in 40 CFR § 141.605(b), it must identify additional locations by alternating selection of locations representing high TTHM levels and high HAA5 levels until the required number of compliance monitoring locations have been identified. It must also provide the rationale for identifying the locations as having high levels of TTHM or HAA5. If it has more Subpart L monitoring locations than required for Subpart V compliance monitoring in 40 CFR § 141.605(b), it must identify which locations it will use for Subpart V compliance monitoring by alternating selection of locations representing high TTHM levels and high HAA5 levels until the required number of Subpart V compliance monitoring locations have been identified.
(c) A Subpart H water system serving over 3,300 people must submit a copy of its monitoring plan to the Division prior to the date it conducts its initial monitoring under this Subpart, unless its IDSE report submitted under Subpart U of this part contains all the information required by this section.
(d) A water system may revise its monitoring plan to reflect changes in treatment, distribution system operations and layout (including new service areas), or other factors that may affect TTHM or HAA5 formation, or for Division-approved reasons, after consultation with the Division regarding the need for changes and the appropriateness of changes. If a water system changes monitoring locations, it must replace existing compliance monitoring locations with the lowest LRAA with new locations that reflect the current distribution system locations with expected high TTHM or HAA5 levels. The Division may also require modifications in water system's monitoring plan. A Subpart H system serving over 3,300 people must submit a copy of its modified monitoring plan to the Division prior to the date it is required to comply with the revised monitoring plan.
(4) Reduced Monitoring.
(a) The water system may reduce monitoring to the level specified in table 40 CFR § 141.623(a) any time the LRAA is less than or equal to (<=) 0.040 mg/L for TTHM and less than or equal to (<=) 0.030 mg/L for HAA5 at all monitoring locations. It may only use data collected under the provisions of this Subpart or Subpart L of this part to qualify for reduced monitoring. In addition, the source water annual average TOC level, before any treatment, must be less than or equal to (<=)4.0 mg/L at each treatment plant treating surface water or ground water under the direct influence of surface water, based on monitoring conducted under either 40 CFR § 141.132(b)(1)(iii) or § 141.132(d).
(b) The water system may remain on reduced monitoring as long as the TTHM LRAA less than or equal to (<=) 0.040 mg/L and the HAA5 LRAA less than or equal to (<=) 0.030 mg/L at each monitoring location (for systems with quarterly reduced monitoring) or each TTHM sample less than or equal to (<=) 0.060 mg/L and each HAA5 sample less than or equal to (<=) 0.045 mg/L (for systems with annual or less frequent monitoring). In addition, the source water annual average TOC level, before any treatment, must be less than or equal to (<=) 4.0 mg/L at each treatment plant treating surface water or ground water under the direct influence of surface water, based on monitoring conducted under either 40 CFR § 141.132(b)(1)(iii) or § 141.132(d).
(c) If the LRAA based on quarterly monitoring at any monitoring location exceeds either 0.040 mg/L for TTHM or 0.030 mg/L for HAA5 or if the annual (or less frequent) sample at any location exceeds either 0.060 mg/L for TTHM or 0.045 mg/L for HAA5, or if the source water annual average TOC level, before any treatment, is greater than () 4.0 mg/L at any treatment plant treating surface water or ground water under the direct influence of surface water, the water system must resume routine monitoring under 40 CFR § 141.621 or begin increased monitoring if 40 CFR § 141.625 applies.
(d) The Division may return the water system to routine monitoring at its discretion.
(5) Additional Requirements for Consecutive Systems. A consecutive system that does not add a disinfectant but delivers water that has been treated with a primary or residual disinfectant other than ultraviolet light must comply with analytical and monitoring requirements for chlorine and chloramines in 40 CFR § 141.131(c) and § 141.132(c)(1) and the compliance requirements in 40 CFR § 141.133(c)(1) beginning April 1, 2009, unless required earlier by the Division, and report monitoring results under 40 CFR § 141.134(c).
(6) Conditions Requiring Increased Monitoring.
(a) A water system that is required to monitor at a particular location annually or less frequently than annually under 40 CFR § 141.621 or § 141.623 must increase monitoring to dual sample sets once per quarter (taken every 90 days) at all locations if a TTHM sample is >0.080 mg/L or a HAA5 sample is >0.060 mg/L at any location.
(b) A water system is in violation of the MCL when the LRAA exceeds the Subpart V MCLs in 40 CFR § 141.64(b)(2), calculated based on four consecutive quarters of monitoring (or the LRAA calculated based on fewer than four quarters of data if the MCL would be exceeded regardless of the monitoring results of subsequent quarters). The water system is in violation of the monitoring requirements for each quarter that a monitoring result would be used in calculating an LRAA if it fails to monitor.
(c) A water system may return to routine monitoring once it has conducted increased monitoring for at least four consecutive quarters and the LRAA for every monitoring location is <=0.060 mg/L for TTHM and <=0.045 mg/L for HAA5.
(7) Operational Evaluation Levels.
(a) The water system has exceeded the operational evaluation level at any monitoring location where the sum of the two previous quarters' TTHM results plus twice the current quarter's TTHM result, divided by 4 to determine an average, exceeds 0.080 mg/L, or where the sum of the two previous quarters' HAA5 results plus twice the current quarter's HAA5 result, divided by 4 to determine an average, exceeds 0.060 mg/L.
1. If a water system exceeds the operational evaluation level, it must conduct an operational evaluation and submit a written report of the evaluation to the Division no later than 90 days after being notified of the analytical result that causes it to exceed the operational evaluation level. The written report must be made available to the public upon request.
2. The operational evaluation must include an examination of system treatment and distribution operational practices, including storage tank operations, excess storage capacity, distribution system flushing, changes in sources or source water quality, and treatment changes or problems that may contribute to TTHM and HAA5 formation and what steps could be considered to minimize future exceedences.
(i) The water system may request and the Division may allow limiting the scope of the water system's evaluation if it is able to identify the cause of the operational evaluation level exceedance.
(ii) The water system's request to limit the scope of the evaluation does not extend the schedule in paragraph (7)(a)1. for submitting the written report. The Division must approve this limited scope of evaluation in writing and the water system must keep that approval with the completed report.
(8) Requirements for Remaining on Reduced TTHM and HAA5 Monitoring Based on Subpart L Results. 40 CFR Subpart V § 141.627 is hereby incorporated by reference.
(9) Requirements for Remaining on Increased TTHM and HAA5 Monitoring Based on Subpart L Results. 40 CFR Subpart V § 141.628 is hereby incorporated by reference.
(10) Reporting and Recordkeeping Requirements. 40 CFR Subpart V § 141.629 is hereby incorporated by reference.
(11) Division Recordkeeping. The records kept by the Division shall be in accordance with 40 CFR § 142.14.

Rule 391-3-5-.54 Ground Water Rule

Purpose. The United States Environmental Protection Agency established the Ground Water Rule, which the Division has adopted, to provide increased protection against microbial pathogens in public water systems that use ground water as the source of drinking water.

(1) General Requirements and Applicability. 40 CFR Part 141 , Subpart S § 141.400 is hereby incorporated by reference.
(a) This Rule applies to the following:
1. Systems relying totally on ground water; purchased water systems or consecutive systems receiving ground water;
2. Mixed surface and ground water systems where ground water is added directly to the distribution system or to the treated surface water prior to entry into the distribution system.
(b) Hydrogeologic Sensitivity Assessments.
1. Hydrogeologically sensitive settings include Karst (carbonate rock, i.e. limestone and dolostone), fractured bedrock and gravel.
2. Drinking water produced by water systems from aquifers consisting of the above geologic materials require hydrogeologic sensitivity assessments prepared by the Division.
3. The information that the Division requires to prepare a hydrogeologic sensitivity assessment may be requested by the Division from the water source's owner and/or found in one or all of three regulatory reports approved by the EPA:
(i) A water source's Well Head Protection Plan,
(ii) The Source Water Assessment, and/or
(iii) The Individual Source Vulnerability Assessment.
4. A water source Well Head Protection Plan consists of the information outlined in Rule 391-3-5-.40(3) through (7).
5. A water source, Source Water Assessment consists of the information outlined in Rules 391-3-5-.06(4) and 391-3-5-.42(3) and (4).
6. A water source Individual Source Vulnerability Assessment consists of the information outlined in Rule 391-3-5-.22(g) through (i).
7. The water source rating developed for Individual Source Vulnerability Assessments is to be used to determine if a source is at high, medium, or low risk to microbiological contamination.
(c) Ground water systems must comply with the requirements of this Rule beginning December 1, 2009.
(2) Sanitary Surveys for Ground Water Systems.40 CFR Part 141, Subpart S § 141.401 is hereby incorporated by reference.
(a) Ground water systems must provide the Division, at the Division's request, any existing information that will enable the Division to conduct a sanitary survey.
(b) A sanitary survey conducted by the Division includes an onsite review of the water source(s), facilities, equipment, operation, maintenance, and monitoring compliance of a public water system to evaluate the adequacy of the system, its sources and operations and the distribution of safe drinking water.
(c) The sanitary survey includes an evaluation of the applicable components listed below:
1. Source,
2. Treatment,
3. Distribution system,
4. Finished water storage,
5. Pumps, pump facilities, and controls,
6. Monitoring, reporting, and data verification,
7. System management and operation, and
8. Operator compliance with Division requirements.
(3) Ground Water Source Microbial Monitoring and Analytical Methods. 40 CFR Part 141, Subpart S § 141.402 is hereby incorporated by reference with the exceptions that the Division only allows E. Coli as a fecal indicator for compliance under this rule and the Division does not allow triggered source water samples collected under paragraph (3)(a) to also serve as repeat samples collected under Rule 391-3-5-.55(8)(a).
(a) Triggered source water monitoring.
1. General requirements. A ground water system must conduct triggered source water monitoring in accordance with 40 CFR § 141.402(a) if the conditions identified in paragraphs (3)(a)1.(i) and either (3)(a)1.(ii) or (3)(a)1.(iii) exist.
(i) The system does not provide at least 4-log treatment of viruses (using inactivation, removal, or a Division-approved combination of 4-log virus inactivation and removal) before or at the first customer for each ground water source; and either
(ii) The system is notified that a sample collected under Rule 391-3-5-.23(1) is total coliform-positive and the sample is not invalidated under Rule 391-3-5-.23(3) until March 31, 2016, or
(iii) The system is notified that a sample collected under Rule 391-3-5-.55(4) through (7) is total coliform-positive and the sample is not invalidated under Rule 391-3-5-.55(3)(c) beginning April 1, 2016.
2. Sampling requirements. A ground water system must collect, within 24 hours of notification of the total coliform-positive sample, at least one ground water source sample from each ground water source in use at the time the total coliform-positive sample was collected under Rule 391-3-5-.23(1) until March 31, 2016, or collected under Rule 391-3-5-.55(4) through (7) beginning April 1, 2016, except as provided in paragraph (3)(a)2.(ii).
(i) The Division may extend the 24-hour time limit on a case-by-case basis if the system cannot collect the ground water source water sample within 24 hours due to circumstances beyond its control. In the case of an extension, the Division must specify how much time the system has to collect the sample.
(ii) If approved by the Division, systems with more than one ground water source may meet the requirements of paragraph (3)(a)2. by sampling a representative ground water source or sources. If directed by the Division, systems must submit for Division approval a triggered source water monitoring plan that identifies one or more ground water sources that are representative of each monitoring site in the system's sample siting plan under Rule 391-3-5-.23(1) until March 31, 2016, or under Rule 391-3-5-.55(3) beginning April 1, 2016, and that the system intends to use for representative sampling under this paragraph.
3. Additional requirements. If the Division does not require corrective action under paragraph (4)(a)2 for an E. coli positive source water sample collected under paragraph (3)(a)2. that is not invalidated under paragraph (3)(d), the system must collect five additional source water samples from the same source within 24 hours of being notified of the E. coli-positive sample.
4. Consecutive and wholesale systems.
(i) In addition to the other requirements of paragraph (3)(a), a consecutive ground water system that has a total coliform-positive sample collected under Rule 391-3-5-.23(1) until March 31, 2016, or under Rule 391-3-5-.55(4) through (7) beginning April 1, 2016, must notify the wholesale system(s) within 24 hours of being notified of the total coliform-positive sample.
(ii) In addition to the other requirements of paragraph (3)(a), a wholesale ground water system must comply with paragraphs (3)(a)4.(ii)(I) and (3)(a)4.(ii)(II).
(I) A wholesale ground water system that receives notice from a consecutive system it serves that a sample collected under Rule 391-3-5-.23(1) until March 31, 2016, or collected under Rule 391-3-5-.55(4) through (7) beginning April 1, 2016, is total coliform-positive must, within 24 hours of being notified, collect a sample from its ground water source(s) under paragraph (3)(a)(2) and analyze it for E. Coli under paragraph (3)(c).
(II) If the sample collected under paragraph (3)(a)4.(ii)(I) is E. Coli-positive, the wholesale ground water system must notify all consecutive systems served by that ground water source of the E. Coli source water positive within 24 hours of being notified of the ground water source sample monitoring result and must meet the requirements of paragraph (3)(a)3.
5. Exceptions to the triggered source water monitoring requirements. A ground water system is not required to comply with the source water monitoring requirements of paragraph (3)(a) if either of the following conditions exists:
(i) The Division determines, and documents in writing, that the total coliform-positive sample collected under Rule 391-3-5-.23(1) until March 31, 2016, or under Rule 391-3-5-.55(4) through (7) beginning April 1, 2016, is caused by a distribution system deficiency; or
(ii) The total coliform-positive sample collected under Rule 391-3-5-.23(1) until March 31, 2016, or under Rule 391-3-5-.55(4) through (7) beginning April 1, 2016, is collected at a location that meets Division criteria for distribution system conditions that will cause total coliform-positive samples.
(b) Assessment Source Water Monitoring. If directed by the Division, ground water systems must conduct assessment source water monitoring that meets Division-determined requirements for such monitoring. A ground water system conducting assessment source water monitoring may use a triggered source water sample collected under 40 CFR § 141.402(a)(2) to meet the requirements of this paragraph. Division-determined assessment source water monitoring requirements may include:
1. Collection of a total of 12 ground water source samples thatrepresent each month the system provides ground water to the public,
2. Collection of samples from each well unless the system obtains written Division approval to conduct monitoring at one or more wells within the ground water system that are representative of multiple wells used by that system and that draw water from the same hydrogeological setting,
3. Collection of a standard sample volume of at least 100 mL for E. coli analysis,
4. Analysis of all ground water source samples using one of the analytical methods listed in 40 CFR § 141.402(c)(2) for the presence of E. coli,
5. Collection of ground water source samples at a location prior to any treatment of the ground water source unless the Division approves a sampling location after treatment, and
6. Collection of ground water source samples at the well itself unless the system's configuration does not allow for sampling at the well itself and the Division approves an alternate sampling location that is representative of the water quality of that well.
(c) Analytical Methods.
1. A ground water system subject to the source water monitoring requirements of paragraph (3)(a) must collect a standard sample volume of at least 100 mL for E. coli analysis.
2. A ground water system must analyze all ground water source samples collected under paragraph (3)(a) using one of the analytical methods listed in the following table in 40 CFR § 141.402(c)(2) or one of the alternative methods listed in Appendix A to Subpart C of 40 CFR Part 141 (Alternative Testing Methods Approved for Analyses Under the Safe Drinking Water Act) for the presence of E. coli.
(d) Invalidation of a Fecal Indicator-Positive Ground Water Source Sample.
1. A ground water system may obtain Division invalidation of an E. coli -positive ground water source sample collected under paragraph (3)(a) only under the conditions specified in paragraphs (3)(d)1.(i) and (ii).
(i) The system provides the Division with written notice from the laboratory that improper sample analysis occurred; or
(ii) The Division determines and documents in writing that there is substantial evidence that an E. coli-positive ground water source sample is not related to source water quality.
2. If the Division invalidates an E. coli-positive ground water source sample, the ground water system must collect another source water sample under paragraph (3)(a) within 24 hours of being notified by the Division of its invalidation decision and have it analyzed using the analytical methods in paragraph (3)(c). The Division may extend the 24-hour time limit on a case-by-case basis if the system cannot collect the source water sample within 24 hours due to circumstances beyond its control. In the case of an extension, the Division must specify how much time the system has to collect the sample.
(e) Sampling Location.
1. Any ground water source sample required under 40 CFR § 141.402(a) must be collected at a location prior to any treatment of the ground water source unless the Division approves a sampling location after treatment.
2. If the system's configuration does not allow for sampling at the well itself, the system may collect a sample at a Division-approved location to meet the requirements of paragraph (3)(a) if the sample is representative of the water quality of that well.
(f) New Sources. If directed by the Division, a ground water system that places a new ground water source into service after November 30, 2009, must conduct assessment source water monitoring under paragraph (3)(b). If directed by the Division, the system must begin monitoring before the ground water source is used to provide water to the public.
(g) Public Notification. A ground water system with a ground water source sample collected under 40 CFR § 141.402(a) or (b) that is E. Coli-positive and that is not invalidated under 40 CFR § 141.402(d), including consecutive systems served by the ground water source, must conduct public notification under 40 CFR § 141.202.
(h) Monitoring Violations. Failure to meet the requirements of paragraphs (3)(a) through (3)(f) is a monitoring violation and requires the ground water system to provide public notification under 40 CFR § 141.204.
(4) Treatment Technique Requirements for Ground Water Systems. 40 CFR Part 141, Subpart S § 141.403 is hereby incorporated by reference.
(a) The treatment technique requirements of this paragraph must be met by ground water systems with significant deficiencies or source water fecal contamination:
1. When a significant deficiency is identified or when a groundwater source sample collected under 40 CFR § 141.402(a)(3) is fecal positive.
2. When directed by the Division, if a ground water system with a ground water source sample collected under 40 CFR § 141.402(a)(2), § 141.402(a)(4), or § 141.402(b) is fecal positive.
3. When a significant deficiency is identified at a 40 CFR Part 141 Subpart H public water system that uses both ground water and surface water or ground water under the direct influence of surface water, the system must comply with paragraph (4) except in cases where the Division determines that the significant deficiency is in a portion of the distribution system that is served solely by surface water or ground water under the direct influence of surface water.
4. Unless directed by the Division to implement a specific corrective action, the ground water system must consult with the Division regarding the appropriate corrective action within thirty (30) days of receiving written notice from the Division of a significant deficiency, written notice from a laboratory that a ground water source sample collected under 40 CFR § 141.402(a)(3) was found to be fecal positive, or direction from the Division that a fecal positive collected under 40 CFR § 141.402(a)(2), § 141.402(a)(4), or § 141.402(b) requires corrective action. For purposes of this section, significant deficiencies include, but are not limited to, defects in design, operation, or maintenance, or a failure or malfunction of the sources, treatment, storage, or distribution system that the Division determines to be causing, or have the potential for causing, the introduction of contamination into the water delivered to consumers.
5. Within 120 days (or earlier if directed by the Division) of receiving written notification from the Division of a significant deficiency, written notice from a laboratory that a ground water source sample collected under 40 CFR § 141.402(a)(3) was found to be fecal positive, or direction from the Division that a fecal positive collected under 40 CFR § 141.402(a)(2), § 141.402(a)(4), or § 141.402(b) requires corrective action, the ground water system must either:
(i) Have completed corrective action in accordance with a Division approved corrective action plan.
(ii) Be in compliance with a Division approved corrective action plan and schedule subject to the following conditions.
(I) The Division must approve any modifications to the corrective action plan and schedule.
(II) The system must comply with any interim measures specified by the Division for the protection of the public health pending Division approval of the corrective action plan and schedule or pending completion of the corrective action.
6. Ground water systems that meet the conditions of paragraphs (4)(a)1. or (4)(a)2. must implement one or more of the following corrective action alternatives:
(i) Correct all significant deficiencies;
(ii) Provide an alternate source of water;
(iii) Eliminate the source of contamination; or
(iv) Provide treatment that reliably achieves at least 4-log treatment of viruses (using inactivation, removal, or a Division-approved combination of both) before or at the first customer for the ground water source.
7. Special Notice to the public of significant deficiencies or source water fecal contamination.
(i) In addition to the applicable public notification requirements of 40 CFR § 141.4202, a community ground water system that receives notice from the Division of a significant deficiency or notification of a fecal positive ground water source sample that is not invalidated by the Division under 40 CFR § 141.402(d) must inform the public served by the water system under 40 CFR § 141.153(h)(6) of the fecal positive source sample or of any significant deficiency that has not been corrected. The system must continue to inform the public annually until the significant deficiency is corrected or the fecal contamination in the groundwater source is determined by the Division to be corrected under paragraph (4)(a)5.
(ii) In addition to the applicable public notification requirements of 40 CFR § 141.4202, a non-community ground water system that receives notice from the Division of a significant deficiency must inform the public served by the water system in a manner approved by the Division of any significant deficiency that has not been corrected within twelve (12) months of being notified, or earlier if directed by the Division. The system must continue to inform the public annually until the significant deficiency is corrected. The information must include:
(I) The nature of the significant deficiency and the date the significant deficiency was identified by the Division;
(II) The Division approved plan and schedule for correction of the significant deficiency, including interim measures, progress to date, and any interim measures completed; and
(III) For systems with a large portion of non-English speaking consumers, as determined by the Division, information in the appropriate language regarding the importance of the notice or a telephone number or address where consumers may contact the system to obtain a translated copy of the notice or assistance in the appropriate language.
(iii) If directed by the Division, a non-community water system with significant deficiencies that have been corrected must inform its customers of the significant deficiencies, how the deficiencies were corrected, and the dates of correction.
(b) Compliance Monitoring.
1. A ground water system that is not required to meet the source water monitoring requirements in this Rule because it provides at least 4-log treatment of viruses for any ground water source must notify the Division in writing that it is providing at least 4-log treatment of viruses and begin compliance monitoring in accordance with paragraph (4)(b) by December 1, 2009.
2. A ground water system that places a ground water source in service after November 30, 2009, and provides at least 4-log treatment of viruses before or at the first customer is not required to meet the source water monitoring requirements in this Rule. Such system must notify the Division in accordance with 40 CFR § 141.403(b)(2)(i), (b)(2)(ii) and (b)(2)(iii) and conduct compliance monitoring as required under 40 CFR § 141.403(b)(3) within thirty days of placing the source in service.
3. If the system subsequently discontinues 4-log treatment of viruses before or at the first customer for a ground water source, the system must conduct ground water source monitoring as required under 40 CFR § 141.402.
4. A ground water system serving greater than 3,300 people that is required to conduct compliance monitoring must continuously monitor the residual disinfectant concentration using analytical methods specified in 40 CFR § 141.74(a)(2) at a location approved by the Division and must record the lowest residual disinfectant concentration each day that water from the ground water source is served to the public. The ground water system must maintain the Division-determined residual disinfectant concentration every day the ground water system serves water from the ground water source to the public. If there is a failure in the continuous monitoring equipment, the ground water system must conduct grab sampling every four hours until the continuous monitoring equipment is returned to service. The system must resume continuous residual disinfectant monitoring within 14 days.
5. A ground water system serving 3,300 or fewer people that is required to conduct compliance monitoring must monitor the residual disinfectant concentration using analytical methods specified in 40 CFR § 141.74(a)(2) at a location approved by the Division and record the residual disinfectant concentration each day that water from the ground water source is served to the public. The ground water system must maintain the Division-determined residual disinfectant concentration every day the ground water system serves water from the ground water source to the public. The ground water system must take a daily grab sample during the hour of peak flow or at another time specified by the Division. If any daily grab sample measurement falls below the Division-determined residual disinfectant concentration, the ground water system must take follow-up samples every four hours until the residual disinfectant concentration is restored to the Division-determined level. Alternatively, a ground water system that serves 3,300 or fewer people may monitor continuously and meet the requirements of 40 CFR § 141.403(b)(3)(i)(A).
6. Membrane Filtration. A ground water system that uses membrane filtration to meet the requirements of this section must monitor the membrane filtration process in accordance with all Division-specified monitoring requirements and must operate the membrane filtration in accordance with all Division-specified compliance requirements. A ground water system that uses membrane filtration is in compliance with the requirement to achieve at least 4-log removal of viruses when:
(i) The membrane has an absolute molecular weight cut-off (MWCO), or an alternate parameter that describes the exclusion characteristics of the membrane, that can reliably achieve at least 4-log removal of viruses;
(ii) The membrane process is operated in accordance with Division-specified compliance requirements; and
(iii) The integrity of the membrane is intact.
7. Alternative treatment. A ground water system that uses a Division-approved alternative treatment to meet the requirements of this subpart by providing at least 4-log treatment of viruses (using inactivation, removal, or a Division-approved combination of 4-log virus inactivation and removal) before or at the first customer must:
(i) Monitor the alternative treatment in accordance with all Division-specified monitoring requirements; and
(ii) Operate the alternative treatment in accordance with all compliance requirements that the Division determines to be necessary to achieve at least 4-log treatment of viruses.
8. A ground water system may discontinue 4-log treatment of viruses if the Division determines and documents in writing that 4-log treatment of viruses is no longer necessary for that groundwater source. A system that discontinues 4-log treatment of viruses is subject to the source water monitoring and analytical methods requirements of 40 CFR Part 141 Subpart S, § 141.402.
9. Failure to meet the monitoring requirements of paragraph (4)(b) is a monitoring violation and requires the ground water system to provide public notification under 40 CFR Part 141 Subpart Q, § 141.204.
10. A ground water system conducting compliance monitoring under 40 CFR § 141.403(b) must notify the Division any time the system fails to meet any Division-specified requirements including, but not limited to, minimum residual disinfectant concentration, membrane operating criteria or membrane integrity, and alternative treatment operating criteria, if operation in accordance with the criteria or requirements is not restored within four hours. The ground water system must notify the Division as soon as possible, but in no case later than the end of the next business day.
(5) Treatment Technique Violations for Ground Water Systems. 40 CFR, Subpart S, § 141.404 is hereby incorporated by reference.
(a) A ground water system with a significant deficiency is in violation of the treatment technique requirement if, within 120 days (or earlier if directed by the Division) of receiving written notice from the Division of the significant deficiency, the system:
1. Does not complete corrective action in accordance with any applicable Division plan review processes including interim actions and measures specified by the Division, or
2. Is not in compliance with a Division approved corrective action plan and schedule.
(b) Unless the Division invalidates a fecal positive ground water source sample under 40 CFR § 141.402(d), a ground water system is in violation of the treatment technique requirement if, within 120 days (or earlier if directed by the Division) of meeting the conditions of 40 CFR § 141.403(a)(1) or § 141.403(a)(2), the system:
1. Does not complete corrective action in accordance with any applicable Division plan review processes including interim actions and measures specified by the Division, or
2. Is not in compliance with a Division approved corrective action plan and schedule.
(c) A ground water system subject to the requirements of 40 CFR § 141.403(b)(3) that fails to maintain at least 4-log treatment of viruses (using inactivation, removal, or a Division-approved combination of both) is in violation of the treatment technique requirement if the failure is not corrected within four hours of determining the system is not maintaining at least 4-log treatment of viruses before or at the first customer.
(d) Ground water systems must give public notification under 40 CFR § 141.203 for the treatment technique violations specified in paragraphs (5)(a), (5)(b) and (5)(c).
(6) Reporting and Recordkeeping for Ground Water Systems.40 CFR Part 141, Subpart S, § 141.405 is hereby incorporated by reference.
(a) In addition to the requirements of 40 CFR § 141.31, a groundwater system regulated under 40 CFR Part 141 Subpart S must provide the following information to the Division:
1. A ground water system conducting compliance monitoring under 40 CFR § 141.403(b) must notify the Division any time the systems fails to meet any Division-specified requirements including, but not limited to, minimum residual disinfectant concentration, membrane operating criteria or integrity, and alternative treatment operating criteria, if operation in accordance with the criteria or requirements is not restored within four (4) hours. The ground water system must notify the Division as soon as possible, but in no case later than the end of the next business day.
2. After completing any corrective action under 40 CFR § 141.403(a), a ground water system must notify the Division within thirty (30) days of completion of the corrective action.
3. If a ground water system that is subject to the requirements of 40 CFR § 141.402(a) does not conduct source water monitoring under 40 CFR § 141.402(a)(5)(ii), the system must provide documentation to the Division within thirty (30) days of the total coliform positive sample that it met the Division criteria.
(b) In addition to the requirements of 40 CFR § 141.33, a groundwater system regulated under 40 CFR Part 141 Subpart S must maintain the following information in its records:
1. Documentation of corrective actions. Documentation shall be kept for a period of not less than ten years.
2. Documentation of notice to the public as required under 40 CFR § 141.403(a)(7). Documentation shall be kept for a period not less than three years.
3. Records of decisions under 40 CFR § 141.402(a)(5)(ii) and records of invalidation of fecal indicator-positive ground water samples under 40 CFR § 141.402(d). Documentation shall be kept for a period of not less than five years.
4. For consecutive systems, documentation of notification to the wholesale system(s) of total coliform-positive samples that are not invalidated under Rule 391-3-5-.23(3) until March 31, 2016, or under Rule 391-3-5-.55(3) beginning April 1, 2016. Documentation shall be kept for a period of not less than five years.
5. For systems, including wholesale systems, that are required to perform compliance monitoring under 40 CFR § 141.403(b):
(i) Records of the Division-specified minimum disinfectant residual. Documentation shall be kept for a period of not less than ten years.
(ii) Records of lowest daily residual disinfectant concentration and records of the date and duration of any failure to maintain the Division-prescribed minimum residual disinfectant concentration for a period of more than four hours. Documentation shall be kept for a period of not less than five years.
(iii) Records of Division-specified compliance requirements for membrane filtration and of parameters specified by the Division for Division-approved alternative treatment and records of the date and duration of any failure to meet the membrane operating, membrane integrity, or alternative treatment operating requirements for more than four hours. Documentation shall be kept for a period of not less than five years.
(7) Division Recordkeeping. The records kept by the Division shall be in accordance with 40 CFR § 142.14.
(8) Division Reporting. The reporting by the Division shall be performed as required by 40 CFR § 142.15.

Rule 391-3-5-.55 Revised Total Coliform Rule

(1) General.
(a) General. The provisions of this Rule include both maximum contaminant level and treatment technique requirements.
(b) Applicability. The provisions of this Rule apply to all public water systems.
(c) Compliance date. Systems must comply with the provisions of this Rule beginning April 1, 2016, unless otherwise specified in this Rule.
(d) Violations of national primary drinking water regulations. Failure to comply with the applicable requirements of this Rule, including requirements established by the Division pursuant to these provisions, is a violation of the national primary drinking water regulations.
(2) Analytical Methods and Laboratory Certification
(a) Analytical Methodology.
1. The standard sample volume required for analysis, regardless of analytical method used, is 100 ml.
2. Systems need only determine the presence or absence of total coliforms and E. coli; a determination of density is not required.
3. The time from sample collection to initiation of test medium incubation may not exceed 30 hours. Systems are encouraged but not required to hold samples below 10 deg. C during transit.
4. If water having residual chlorine (measured as free, combined, or total chlorine) is to be analyzed, sufficient sodium thiosulfate (Na2S2O3) must be added to the sample bottle before sterilization to neutralize any residual chlorine in the water sample. Dechlorination procedures are addressed in Section 9060A.2 of Standard Methods for the Examination of Water and Wastewater (20th and 21st editions).
5. Systems must conduct total coliform and E. coli analyses in accordance with one of the analytical methods in 40 CFR § 141.852(a)(5) or one of the alternative methods listed in Appendix A to Subpart C of 40 CFR Part 141.
(b) Laboratory certification. Systems must have all compliance samples required under this Rule analyzed by a laboratory certified by the Division or by EPA to analyze drinking water samples. The laboratory used by the system must be certified for each method (and associated contaminant(s)) used for compliance monitoring analyses under this Rule.
(c) Incorporation by reference. The standards required in paragraph (2) of this Rule are incorporated by reference under 40 CFR § 141.852(c).
(3) General Monitoring Requirements for all Public Water Systems
(a) Sample Site Plans.
1. Systems must develop a written sample siting plan that identifies sampling sites and a sample collection schedule that are representative of water throughout the distribution system not later than March 31, 2016. These plans are subject to Division review and revision. Systems must collect total coliform samples according to the written sample siting plan. Monitoring required by paragraphs (4) through (8) of this Rule may take place at a customer's premise, dedicated sampling station, or other designated compliance sampling location. Routine and repeat sample sites and any sampling points necessary to meet the requirements of Rule 391-3-5-.54 must be reflected in the sampling plan.
2. Systems must collect samples at regular time intervals throughout the month, except that systems that use only groundwater and serve 4,900 or fewer people may collect all required samples on a single day if they are taken from different sites.
3. Systems must take at least the minimum number of required samples even if the system has had an E. coli MCL violation or has exceeded the coliform treatment technique triggers in paragraph (9)(a).
4. A system may conduct more compliance monitoring than is required by this Rule to investigate potential problems in the distribution system and use monitoring as a tool to assist in uncovering problems. A system may take more than the minimum number of required routine samples and must include the results in calculating whether the coliform treatment technique trigger in paragraphs (9)(a)1.(i) and (ii) has been exceeded only if the samples are taken in accordance with the existing sample siting plan and are representative of water throughout the distribution system.
5. Systems must identify repeat monitoring locations in the sample siting plan. Unless the provisions of paragraph (3)(a)5.(i) are met, the system must collect at least one repeat sample from the sampling tap where the original total coliform-positive sample was taken, and at least one repeat sample at a tap within five service connections upstream and at least one repeat sample at a tap within five service connections downstream of the original sampling site. If a total coliform-positive sample is at the end of the distribution system, or one service connection away from the end of the distribution system, the system must still take all required repeat samples. However, the Division may allow an alternative sampling location in lieu of the requirement to collect at least one repeat sample upstream or downstream of the original sampling site. Systems required to conduct triggered source water monitoring under 391-3-5-.54(3)(a) must take ground water source sample(s) in addition to repeat samples required under this Rule.
(i) Systems may propose repeat monitoring locations to the Division that the system believes to be representative of a pathway for contamination of the distribution system. A system may elect to specify either alternative fixed locations or criteria for selecting repeat sampling sites on a situational basis in a standard operating procedure (SOP) in its sample siting plan. The system must design its SOP to focus the repeat samples at locations that best verify and determine the extent of potential contamination of the distribution system area based on specific situations. The Division may modify the SOP or require alternative monitoring locations as needed.
6. The Division may review, revise, and approve, as appropriate, repeat sampling proposed by systems under paragraph (3)(a)5.(i). The system must demonstrate that the sample siting plan remains representative of the water quality in the distribution system. The Division may determine that monitoring at the entry point to the distribution system (especially for undisinfected ground water systems) is effective to differentiate between potential source water and distribution system problems.
(b) Special purpose samples. Special purpose samples, such as those taken to determine whether disinfection practices are sufficient following pipe placement, replacement, or repair, must not be used to determine whether the coliform treatment technique trigger has been exceeded. Repeat samples taken pursuant to paragraph (8) are not considered special purpose samples, and must be used to determine whether the coliform treatment technique trigger has been exceeded.
(c) Invalidation of total coliform samples. A total coliform-positive sample invalidated under this paragraph does not count toward meeting the minimum monitoring requirements of this Rule.
1. The Division may invalidate a total coliform-positive sample only if any of the following conditions are met:
(i) The laboratory establishes that improper sample analysis caused the total coliform-positive result.
(ii) The Division, on the basis of the results of repeat samples collected as required under paragraph (8)(a), determines that the total coliform-positive sample resulted from a domestic or other non-distribution system plumbing problem. The Division cannot invalidate a sample on the basis of repeat sample results unless all repeat sample(s) collected at the same tap as the original total coliform-positive sample are also total coliform-positive, and all repeat samples collected at a location other than the original tap are total coliform-negative (e.g., the Division cannot invalidate a total coliform-positive sample on the basis of repeat samples if all the repeat samples are total coliform-negative, or if the system has only one service connection).
(iii) The Division has substantial grounds to believe that a total coliform-positive result is due to a circumstance or condition that does not reflect water quality in the distribution system. In this case, the system must still collect all repeat samples required under paragraph (8)(a), and use them to determine whether a coliform treatment technique trigger in paragraph (9) has been exceeded. To invalidate a total coliform-positive sample under this paragraph, the decision and supporting rationale must be documented in writing, and approved and signed by the supervisor of the Division official who recommended the decision. The Division must make this document available to EPA and the public. The written documentation must state the specific cause of the total coliform-positive sample, and what action the system has taken, or will take, to correct this problem. The Division may not invalidate a total coliform-positive sample solely on the grounds that all repeat samples are total coliform-negative.
2. A laboratory must invalidate a total coliform sample (unless total coliforms are detected) if the sample produces a turbid culture in the absence of gas production using an analytical method where gas formation is examined (e.g., the Multiple-Tube Fermentation Technique), produces a turbid culture in the absence of an acid reaction in the Presence-Absence (P-A) Coliform Test, or exhibits confluent growth or produces colonies too numerous to count with an analytical method using a membrane filter (e.g., Membrane Filter Technique). If a laboratory invalidates a sample because of such interference, the system must collect another sample from the same location as the original sample within 24 hours of being notified of the interference problem, and have it analyzed for the presence of total coliforms. The system must continue to re-sample within 24 hours and have the samples analyzed until it obtains a valid result. The Division may waive the 24-hour time limit on a case-by-case basis. Alternatively, the Division may implement criteria for waiving the 24-hour sampling time limit to use in lieu of case-by-case extensions.
(4) Routine Monitoring Requirements for Non-Community Water Systems Serving 1,000 or Fewer People Using Only Ground Water
(a) General.
1. The provisions of this paragraph (4) apply to non-community water systems using only ground water (except ground water under the direct influence of surface water, as defined in Rule 391-3-5-.02(64)) and serving 1,000 or fewer people.
2. Following any total coliform-positive sample taken under the provisions of paragraph (4), systems must comply with the repeat monitoring requirements and E. coli analytical requirements in paragraph (8).
3. Once all monitoring required by paragraphs (4) and (8) for a calendar month has been completed, systems must determine whether any coliform treatment technique triggers specified in paragraph (9) have been exceeded. If any trigger has been exceeded, systems must complete assessments as required by paragraph (9).
4. For the purpose of determining eligibility for remaining on or qualifying for quarterly monitoring under the provisions of paragraphs (4)(d)4. and (4)(e)2., respectively, for transient non-community water systems, the Division may elect to not count monitoring violations under paragraph (10)(c)1. if the missed sample is collected no later than the end of the monitoring period following the monitoring period in which the sample was missed. The system must collect the make-up sample in a different week than the routine sample for that monitoring period and should collect the sample as soon as possible during the monitoring period. This authority does not affect the provisions of paragraphs (10)(c)1. and (11)(a)4.
(b) Monitoring frequency for total coliforms. Systems must monitor each calendar quarter that the system provides water to the public, except for seasonal systems or as provided under paragraphs (4)(c) through (4)(e) and (4)(g). Seasonal systems must meet the monitoring requirements of paragraph (4)(f).
(c) Transition to Rule 391-3-5-.55.
1. Systems, excluding seasonal systems, must continue to monitor according to the total coliform monitoring schedules under Rule 391-3-5-.23 that were in effect on March 31, 2016, unless any of the conditions for increased monitoring in paragraph (4)(d) are triggered on or after April 1, 2016, or unless otherwise directed by the Division. Seasonal Systems must comply with paragraph (4)(f) as of April 1, 2016.
2. Beginning April 1, 2016, the Division must perform a special monitoring evaluation during each sanitary survey to review the status of the system, including the distribution system, to determine whether the system is on an appropriate monitoring schedule. After the Division has performed the special monitoring evaluation during each sanitary survey, the Division may modify the system's monitoring schedule, as necessary, or it may allow the system to stay on its existing monitoring schedule, consistent with the provisions of paragraph (4). The Division may not allow systems to begin less frequent monitoring under the special monitoring evaluation unless the system has already met the applicable criteria for less frequent monitoring in paragraph (4).
(d) Increased monitoring requirements for systems on quarterly monitoring. A system on quarterly monitoring that experiences any of the events identified in paragraphs (4)(d)1. through (4)(d)4. must begin monthly monitoring the month following the event. The system must continue monthly monitoring until the requirements in paragraph (4)(e) for quarterly monitoring are met. A system on monthly monitoring for reasons other than those identified in paragraphs (4)(d)1. through (4)(d)4. is not considered to be on increased monitoring for the purposes of paragraph (4)(e).
1. The system triggers a Level 2 assessment or two Level 1 assessments under the provisions of paragraph (9) in a rolling 12-month period.
2. The system has an E. coli MCL violation.
3. The system has a coliform treatment technique violation.
4. The system has two monitoring violations under Rule 391-3-5-.55 or one monitoring violation under Rule 391-3-5-.55 and one Level 1 assessment under the provisions of paragraph (9) in a rolling 12-month period.
(e) Requirements for returning to quarterly monitoring. The Division may reduce the monitoring frequency for a system on monthly monitoring triggered under paragraph (4)(d) to quarterly monitoring if the system meets the following criteria:
1. Within the last 12 months, the system must have a completed sanitary survey or a site visit by the Division or a voluntary Level 2 assessment by a party approved by the Division, be free of sanitary defects, and have a protected water source; and
2. The system must have a clean compliance history for a minimum of 12 months.
(f) Seasonal systems.
1. Beginning April 1, 2016, all seasonal systems must demonstrate completion of a Division-approved start-up procedure, which includes a requirement for startup sampling prior to serving water to the public.
2. A seasonal system must monitor every month that it is in operation.
3. The Division may exempt any seasonal system from some or all of the requirements for seasonal systems if the entire distribution system remains pressurized during the entire period that the system is not operating.
(g) Additional routine monitoring the month following a total coliform-positive sample. Systems collecting samples on a quarterly frequency must conduct additional routine monitoring the month following one or more total coliform-positive samples (with or without a Level 1 treatment technique trigger). Systems must collect at least three routine samples during the next month, except that the Division may waive this requirement if the conditions of paragraph (4)(g)1., 2., or 3. are met. Systems may either collect samples at regular time intervals throughout the month or may collect all required routine samples on a single day if samples are taken from different sites. Systems must use the results of additional routine samples in coliform treatment technique trigger calculations under paragraph (9)(a).
1. The Division may waive the requirement to collect three routine samples the next month in which the system provides water to the public if the Division, or an agent approved by the Division, performs a site visit before the end of the next month in which the system provides water to the public. Although a sanitary survey need not be performed, the site visit must be sufficiently detailed to allow the Division to determine whether additional monitoring and/or any corrective action is needed. The Division cannot approve an employee of the system to perform this site visit, even if the employee is an agent approved by the Division to perform sanitary surveys.
2. The Division may waive the requirement to collect three routine samples the next month in which the system provides water to the public if the Division has determined why the sample was total coliform-positive and has established that the system has corrected the problem or will correct the problem before the end of the next month in which the system serves water to the public. In this case, the Division must document this decision to waive the following month's additional monitoring requirement in writing, have it approved and signed by the supervisor of the Division official who recommends such a decision, and make this document available to the EPA and public. The written documentation must describe the specific cause of the total coliform-positive sample and what action the system has taken and/or will take to correct this problem.
3. The Division may not waive the requirement to collect three additional routine samples the next month in which the system provides water to the public solely on the grounds that all repeat samples are total coliform-negative. If the Division determines that the system has corrected the contamination problem before the system takes the set of repeat samples required in paragraph (8), and all repeat samples were total coliform-negative, the Division may waive the requirement for additional routine monitoring the next month.
(5) Routine Monitoring Requirements for Community Water Systems Serving 1,000 or Fewer People Using Only Ground Water.
(a) General.
1. The provisions of paragraph (5) apply to community water systems using only ground water (except ground water under the direct influence of surface water, as defined in 391-3-5-.02(64)) and serving 1,000 or fewer people.
2. Following any total coliform-positive sample taken under the provisions of paragraph (5), systems must comply with the repeat monitoring requirements and E. coli analytical requirements in paragraph (8).
3. Once all monitoring required by paragraphs (5) and (8) for a calendar month has been completed, systems must determine whether any coliform treatment technique triggers specified in paragraph (9) have been exceeded. If any trigger has been exceeded, systems must complete assessments as required by paragraph (9).
(b) Monitoring frequency for total coliforms. The monitoring frequency for total coliforms is one sample/month, except as provided below:
1. All systems must continue to monitor according to the total coliform monitoring schedules under Rule 391-3-5-.23 that were in effect on March 31, 2016, unless otherwise directed by the Division.
2. Beginning April 1, 2016, the Division must perform a special monitoring evaluation during each sanitary survey to review the status of the system, including the distribution system, to determine whether the system is on an appropriate monitoring schedule. After the Division has performed the special monitoring evaluation during each sanitary survey, the Division may modify the system's monitoring schedule, as necessary, or it may allow the system to stay on its existing monitoring schedule, consistent with the provisions of paragraph (5).
(6) Routine Monitoring Requirements for 40 CFR Part 141 Subpart H Public Water Systems Serving 1,000 or Fewer People.
(a) General.
1. The provisions of paragraph (6) apply to 40 CFR Part 141 Subpart H public water systems serving 1,000 or fewer people.
2. Following any total coliform-positive sample taken under the provisions of paragraph (6), systems must comply with the repeat monitoring requirements and E. coli analytical requirements in paragraph (8).
3. Once all monitoring required by paragraphs (6) and (8) for a calendar month has been completed, systems must determine whether any coliform treatment technique triggers specified in paragraph (9) have been exceeded. If any trigger has been exceeded, systems must complete assessments as required by paragraph (9).
4. Seasonal systems.
(i) Beginning April 1, 2016, all seasonal systems must demonstrate completion of a Division-approved start-up procedure, which may include a requirement for start-up sampling prior to serving water to the public.
(ii) The Division may exempt any seasonal system from some or all of the requirements for seasonal systems if the entire distribution system remains pressurized during the entire period that the system is not operating.
(b) Routine monitoring frequency for total coliforms. 40 CFR Part 141 Subpart H systems (including consecutive systems) must monitor monthly. Systems may not reduce monitoring.
(7) Routine Monitoring Requirements for Public Water Systems Serving More than 1,000 People.
(a) General.
1. The provisions of paragraph (7) apply to public water systems serving more than 1,000 persons.
2. Following any total coliform-positive sample taken under the provisions of paragraph (7), systems must comply with the repeat monitoring requirements and E. coli analytical requirements in paragraph (8).
3. Once all monitoring required by paragraphs (7) and (8) for a calendar month has been completed, systems must determine whether any coliform treatment technique triggers specified in paragraph (9) have been exceeded. If any trigger has been exceeded, systems must complete assessments as required by paragraph (9).
4. Seasonal systems.
(i) Beginning April 1, 2016, all seasonal systems must demonstrate completion of a Division-approved start-up procedure, which may include a requirement for start-up sampling prior to serving water to the public.
(ii) The Division may exempt any seasonal system from some or all of the requirements for seasonal systems if the entire distribution system remains pressurized during the entire period that the system is not operating.
(b) Monitoring frequency for total coliforms. The monitoring frequency for total coliforms is based on the population served by the system, as follows:

Total Coliform Monitoring Frequency for Public Water Systems Serving More Than 1,000 People

Population Served

Minimum number of samples per month

1,001 to 2,500

2

2,501 to 3,300

3

3,301 to 4,100

4

4,101 to 4,900

5

4,901 to 5,800

6

5,801 to 6,700

7

6,701 to 7,600

8

7,601 to 8,500

9

8,501 to 12,900

10

12,901 to 17,200

15

17,201 to 21,500

20

21,501 to 25,000

25

25,001 to 33,000

30

33,001 to 41,000

40

41,001 to 50,000

50

50,001 to 59,000

60

59,001 to 70,000

70

70,001 to 83,000

80

83,001 to 96,000

90

96,001 to 130,000

100

130,001 to 220,000

120

220,001 to 320,000

150

320,001 to 450,000

180

450,001 to 600,000

210

600,001 to 780,000

240

780,001 to 970,000

270

970,001 to 1,230,000

300

1,230,001 to 1,520,000

330

1,520,001 to 1,850,000

360

1,850,001 to 2,270,000

390

2,270,001 to 3,020,000

420

3,020,001 to 3,960,000

450

3,960,001 or more

480

(8) Repeat Monitoring and E. Coli Requirements.
(a) Repeat Monitoring.
1. If a sample taken under paragraphs (4) through (7) of this Rule is total coliform-positive, the system must collect a set of repeat samples within 24 hours of being notified of the positive result. The system must collect no fewer than three repeat samples for each total coliform-positive sample found. The Division may extend the 24-hour limit on a case-by-case basis if the system has a logistical problem in collecting the repeat samples within 24 hours that is beyond its control. Alternatively, the Division may implement criteria for the system to use in lieu of case-by-case extensions. In the case of an extension, the Division must specify how much time the system has to collect the repeat samples. The Division cannot waive the requirement for a system to collect repeat samples in paragraphs (8)(a)1. through (8)(a)3.
2. The system must collect all repeat samples on the same day, except that the Division may allow a system with a single service connection to collect the required set of repeat samples over a three-day period or to collect a larger volume repeat sample(s) in one or more sample containers of any size, as long as the total volume collected is at least 300 ml.
3. The system must collect an additional set of repeat samples in the manner specified in paragraphs (8)(a)1. through (8)(a)3. if one or more repeat samples in the current set of repeat samples is total coliform-positive. The system must collect the additional set of repeat samples within 24 hours of being notified of the positive result, unless the Division extends the limit as provided in paragraph (8)(a)1. The system must continue to collect additional sets of repeat samples until either total coliforms are not detected in one complete set of repeat samples or the system determines that a coliform treatment technique trigger specified in paragraph (9)(a) has been exceeded as a result of a repeat sample being total coliform-positive and notifies the Division. If a trigger identified in paragraph (9) is exceeded as a result of a routine sample being total coliform-positive, systems are required to conduct only one round of repeat monitoring for each total coliform-positive routine sample.
4. After a system collects a routine sample and before it learns the results of the analysis of that sample, if it collects another routine sample(s) from within five adjacent service connections of the initial sample, and the initial sample, after analysis, is found to contain total coliforms, then the system may count the subsequent sample(s) as a repeat sample instead of as a routine sample.