OAR 333-061-0030
Maximum Contaminant Levels and Action Levels

(1) MCLs and action levels (ALs) for inorganic chemicals apply to all community and NTNC water systems and are listed in Table 1, except the MCL for fluoride which applies only to community water systems and the MCL for nitrate which applies to all water systems.
(a) Compliance with the MCLs for inorganic contaminants is calculated pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(2)(h).
(b) Exceeding the secondary contaminant level for fluoride as specified in section (6) of this rule requires a special public notice as specified in OAR 333-061-0042 (Public Notice)(7).
(c) 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 OAR 333-061-0036 (Sampling and Analytical Requirements)(10)(a) through (e) is greater than 0.015 mg/L (that is, if the “90th percentile” lead level is greater than 0.015 mg/L). 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 OAR 333-061-0036 (Sampling and Analytical Requirements)(10)(a) through (e) is greater than 1.3 mg/L (that is, if the “90th percentile” copper level is greater than 1.3 mg/L).
(A) The 90th percentile lead and copper levels shall be computed as follows: The results of all lead or copper samples taken during a monitoring period shall be placed in ascending order from the sample with the lowest concentration to the sample with the highest concentration. Each sampling result shall be assigned a number, ascending by single integers beginning with the number 1 for the sample with the lowest contaminant level. The number assigned to the sample with the highest contaminant level shall be equal to the total number of samples taken. The number of samples taken during the monitoring period shall be multiplied by 0.9. The contaminant concentration in the numbered sample yielded by this calculation is the 90th percentile contaminant level.
(B) For water systems serving fewer than 100 people that collect five samples per monitoring period, the 90th percentile is computed by taking the average of the highest and second highest concentrations. For a water system allowed by the Authority to collect fewer than five samples the sample result with the highest concentration is considered the 90th percentile value.
(2) MCLs for organic chemicals:
(a) The MCLs for synthetic organic chemicals are shown in Table 2 and apply to all community and NTNC water systems. Compliance with MCLs shall be calculated pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(3)(a)(H) and (I).
(b) The MCLs for disinfection byproducts are shown in Table 3 and apply to all community and NTNC water systems that add a disinfectant (oxidant) to the water supply at any point in the treatment process or deliver water in which a disinfectant has been added to the water supply.
(A) Compliance with the MCLs for TTHM and HAA5 shall be calculated as a LRAA according to OAR 333-061-0036 (Sampling and Analytical Requirements)(4)(c).
(B) Compliance with the MCL for bromate shall be calculated as a running annual average pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(4)(h).
(C) Compliance with the MCL for chlorite shall be calculated as a running annual average pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(4)(g).
(c) The MCLs for volatile organic chemicals are indicated in Table 4 and apply to all community and NTNC water systems. Compliance with MCLs shall be calculated pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(3)(b)(H) and (I).
(d) When the Authority has reason to believe that a water supply has been contaminated by a toxic organic chemical, it will determine whether a public health hazard exists and whether control measures must be carried out;
(e) The Authority may establish MCLs for additional organic chemicals as deemed necessary when there is reason to suspect that the use of those chemicals will impair water quality to an extent that poses an unreasonable risk to the health of the water users;
(f) Persons who apply pesticides within watersheds above surface water intakes of public water systems shall comply with federal and state pesticide application requirements. (Safe Drinking Water Act (EPA), Clean Water Act (EPA), Federal Insecticide, Fungicide and Rodenticide Act (EPA), ORS 536.220 (Policy on water resources generally) to 536.360 (State agencies and public corporations to conform to statement of state water resources policy) (Water Resources), 468B.005 (Definitions for water pollution control laws) (DEQ), 527.610 (Short title) to 527.990 (Criminal penalties) (DOF), 634.016 (Registration of pesticides and application devices) to 634.992 (Criminal penalties) (Department of Agriculture)). Any person who has reasonable cause to believe that his or her actions have led to organic chemical contamination of a public water system shall report that fact immediately to the water supplier.
(3) MCLs for turbidity are applicable to all public water systems using surface water sources or groundwater sources under the direct influence of surface water in whole or in part. Compliance with MCLs shall be calculated pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(5).
(a) Turbidity at water systems where filtration treatment is not provided cannot exceed 5 NTU in representative samples of the source water immediately prior to the first or only point of disinfectant application unless:
(A) The Authority determines that any such event was caused by circumstances that were unusual and unpredictable; and
(B) As a result of any such event, there have not been more than two such events in 12 months when water was served to the public, or more than five events in 120 months the system served water to the public, in which the turbidity level exceeded 5 NTU. An “event” is a series of consecutive days during which at least one turbidity measurement each day exceeds 5 NTU. Turbidity measurements must be collected as required by OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(a)(B).
(b) The MCLs for turbidity in drinking water, measured at a point representing filtered water prior to any storage, are as follows:
(A) Conventional filtration treatment or direct filtration treatment.
(i) At water systems where conventional filtration or direct filtration treatment is used, the turbidity level of representative samples of a system’s filtered water, measured as soon after filtration as possible and prior to any storage, must be less than or equal to 0.3 NTU in at least 95 percent of the measurements taken each month, measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5).
(ii) At water systems where conventional filtration or direct filtration treatment is used, the turbidity level of representative samples of a system’s filtered water, measured as soon after filtration as possible and prior to any storage, must at no time exceed 1 NTU measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5).
(B) Slow sand filtration.
(i) At water systems where slow sand filtration is used, the turbidity level of representative samples of filtered water, measured as soon after filtration as possible and prior to any storage, must be less than or equal to 1 NTU in at least 95 percent of the measurements taken each month, measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(b), except that if the Authority determines there is no significant interference with disinfection at a higher turbidity level, the Authority may substitute this higher turbidity limit for that system.
(ii) The turbidity level of representative samples of filtered water must at no time exceed 5 NTU, measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(b).
(C) Diatomaceous earth filtration.
(i) At water systems where diatomaceous earth filtration is used, the turbidity level of representative samples of filtered water, measured as soon after filtration as possible and prior to any storage, must be less than or equal to 1 NTU in at least 95 percent of the measurements taken each month, measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(b).
(ii) The turbidity level of representative samples of filtered water must at no time exceed 5 NTU, measured as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(b).
(D) Other filtration technologies. At water systems where filtration technologies other than those listed in paragraphs (3)(b)(A) through (C) of this rule are used, the turbidity level must be less than or equal to 1 NTU in at least 95 percent of the measurements taken each month and at no time exceed 5 NTU, as specified in OAR 333-061-0036 (Sampling and Analytical Requirements)(5)(b)(A). The Authority may substitute a lower turbidity value(s) if it is determined that the above limit(s) cannot achieve the required level of treatment. The water supplier must demonstrate to the Authority that the alternative filtration technology in combination with disinfection treatment as specified in OAR 333-061-0032 (Treatment Requirements and Performance Standards for Surface Water, Groundwater Under Direct Influence of Surface Water, and Groundwater) and monitored as specified by OAR 333-061-0036 (Sampling and Analytical Requirements) consistently achieves 99.9 percent removal or inactivation of Giardia lamblia cysts and 99.99 percent removal or inactivation of viruses, and 99 percent removal of Cryptosporidium oocysts.
(4) The MCL for E. coli applies to all public water systems as specified in this section.
(a) A water system exceeds or violates the MCL for E. coli if any of the conditions identified in paragraphs (4)(a)(A) through (4)(a)(D) of this rule occur.
(A) An E. coli-positive repeat sample follows a total coliform-positive routine sample.
(B) A total coliform-positive repeat sample follows an E. coli-positive routine sample.
(C) All required repeat samples are not collected following an E. coli-positive routine sample.
(D) Any repeat sample is not analyzed for E. coli when it tests positive for total coliform.
(b) Exceeding the MCL for E. coli may pose an acute risk to health and requires the distribution of public notification as specified in OAR 333-061-0042 (Public Notice).
(5) MCLs for radionuclides are applicable only to community water systems and are indicated in Table 5.

(a)

The average annual concentration of beta particle and photon radioactivity from man-made sources, including all radionuclides emitting beta particles or photons listed in Maximum Permissible Body Burdens and Maximum Permissible Concentration of Radionuclides in Air or Water for Occupational Exposure, National Bureau of Standards Handbook 69, except the daughter products of Thorium-232, Uranium-235 and Uranium-238, shall not produce an annual dose equivalent to the total body or any internal organ greater than 4 millirem per year. If two or more radionuclides are present, the sum total of their annual dose equivalent to the total body or to any organ shall not exceed 4 mrem/year.
(A) The average annual concentration of tritium assumed to produce a total body dose of 4 mrem/year is 20,000 pCi/L;
(B) The average annual concentration of strontium-90 assumed to produce a bone marrow dose of 4 mrem/year is 8 pCi/L.
(b) Compliance with the MCLs shall be calculated pursuant to OAR 333-061-0036 (Sampling and Analytical Requirements)(7)(c).
(6) Contaminant levels for secondary contaminants are applicable to all public water systems. These are indicated in Table 6. (Also note OAR 333-061-0036 (Sampling and Analytical Requirements)(8)).
(a) Exceeding the secondary contaminant level for fluoride requires a special public notice as specified in OAR 333-061-0042 (Public Notice)(7).
(b) Exceeding the MCL for fluoride as specified in section (1) of this rule requires public notification as specified in OAR 333-061-0042 (Public Notice)(2)(b)(A).
(7) Acrylamide and Epichlorohydrin. For every public water system, the water supplier must certify annually to the state in writing, using third party certification approved by the state 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:
(a) Acrylamide: 0.05 percent dosed at 1 ppm or equivalent.
(b) Epichlorohydrin: 0.01 percent dosed at 20 ppm or equivalent.
[ED. NOTE: To view attachments referenced in rule text, click here to view rule.]

Source: Rule 333-061-0030 — Maximum Contaminant Levels and Action Levels, https://secure.­sos.­state.­or.­us/oard/view.­action?ruleNumber=333-061-0030.

333–061–0005
Purpose 333–061–0010
Scope 333–061–0015
Adoption by Reference 333–061–0020
Definitions 333–061–0025
Responsibilities of Water Suppliers 333–061–0030
Maximum Contaminant Levels and Action Levels 333–061–0031
Maximum Residual Disinfectant Levels 333–061–0032
Treatment Requirements and Performance Standards for Surface Water, Groundwater Under Direct Influence of Surface Water, and Groundwater 333–061–0034
Treatment Requirements and Performance Standards for Corrosion Control 333–061–0036
Sampling and Analytical Requirements 333–061–0040
Reporting and Record Keeping 333–061–0042
Public Notice 333–061–0043
Consumer Confidence Reports 333–061–0045
Variances 333–061–0046
Permits 333–061–0050
Construction Standards 333–061–0055
Waivers from Construction Standards 333–061–0057
Voluntary Drinking Water Protection Program 333–061–0060
Plan Submission and Review Requirements 333–061–0061
Capacity Requirements for Public Water Systems 333–061–0062
Land Use Coordination 333–061–0063
Environmental Review Process for The Safe Drinking Water Revolving Loan Fund Program 333–061–0064
Emergency Response Plan Requirements 333–061–0065
Operation and Maintenance 333–061–0070
Cross Connection Control Requirements 333–061–0071
Backflow Prevention Assembly Installation and Operation Standards 333–061–0072
Backflow Assembly Tester Certification 333–061–0073
Cross Connection Specialist Certification 333–061–0074
Cross Connection Training Programs, Course, and Instructor Requirements 333–061–0075
Sanitary Surveys of Watersheds 333–061–0076
Sanitary Surveys 333–061–0077
Composite Correction Program & Comprehensive Performance Evaluations 333–061–0078
Coliform Investigations 333–061–0080
Role of Counties 333–061–0085
Supplemental Fluoridation 333–061–0087
Product Acceptability Criteria 333–061–0089
Annual Water System Fee 333–061–0090
Penalties 333–061–0095
Severability 333–061–0097
Adverse Health Effects Language 333–061–0098
References 333–061–0210
Operator Certification: Scope 333–061–0220
Classification of Water Treatment Plants and Water Distribution Systems 333–061–0225
General Requirements Applying to Water Suppliers and Water Systems 333–061–0228
Certification Requirements for Small Water System Operators 333–061–0230
Contracting For Services 333–061–0232
General Requirements Applying to Water System Operators 333–061–0235
Operator Certification Requirements, Levels 1–4 333–061–0245
Applications for Certification Levels 1–4 333–061–0250
Examinations for Certification, Levels 1–4 333–061–0260
Certificate Renewal Levels 1–4 333–061–0265
Fees 333–061–0270
Refusal, Suspension, or Revocation of Certification 333–061–0272
Suspension of Certification 333–061–0305
Domestic Well Program: Purpose 333–061–0310
Scope 333–061–0324
Area of Public Health Concern 333–061–0325
Domestic Well Tests 333–061–0330
Accredited Laboratories 333–061–0335
Sample Collection 333–061–0400
Reducing Lead in School Drinking Water 333–061–0510
Applicability of Cyanotoxin Rules 333–061–0520
Definitions 333–061–0530
Health Advisory Levels 333–061–0540
Cyanotoxin Monitoring 333–061–0550
Analytical Methods 333–061–0560
Reporting 333–061–0570
Public Notification 333–061–0580
Record Keeping
Last Updated

Jun. 8, 2021

Rule 333-061-0030’s source at or​.us