OAR 340-041-0059
Variances


(1) Applicability. Subject to the requirements and limitations set out in sections (2) through (7) below, DEQ or the EQC may grant a water quality standards variance where the discharger or DEQ demonstrates that it is not feasible to attain the designated use and criterion during the term of the variance because of one of the factors listed in subsection (2)(a) of this rule. The director may grant an individual discharger variance and the commission may grant a multiple discharger variance or a water body variance. All water quality standards variances are subject to EPA approval. The variance may be used only for the purpose of establishing NPDES permit limits and requirements under CWA Section 301(b)(1)(C) or for issuing certifications under CWA Section 401. The underlying designated use and criterion otherwise remains in effect.
(2) Conditions to Grant a Variance. Before the EQC or DEQ may grant a variance, it must determine that:

(a)

Attaining the designated use and criterion during the term of the variance is not feasible for one or more of the following reasons:

(A)

Naturally occurring pollutant concentrations prevent attaining the use;

(B)

Natural, ephemeral, intermittent, or low flow conditions, or water levels prevent attaining the use, unless these conditions may be compensated for by discharging sufficient volume of effluent discharges to enable uses to be met without violating state water conservation requirements;

(C)

Human-caused conditions or sources of pollution prevent attaining the use and cannot be remedied or would cause more environmental damage to correct than to leave in place;

(D)

Dams, diversions, or other types of hydrologic modifications preclude attaining the use, and it is not feasible to restore the waterbody to its original condition or to operate such modification in a way which would result in the attainment of the use;

(E)

Physical conditions related to the natural features of the waterbody, such as the lack of a proper substrate, cover, flow, depth, pools, riffles, and the like, unrelated to water quality preclude attaining aquatic life protection uses;

(F)

Controls more stringent than those required by sections 301(b) and 306 of the federal Clean Water Act would result in substantial and widespread economic and social impact; or

(G)

Actions necessary to facilitate lake, wetland, or stream restoration through dam removal or other significant reconfiguration activities preclude attainment of the designated use and criterion while the actions are being implemented;

(b)

The effluent limit sufficient to meet the underlying designated use and criterion cannot be attained by implementing technology-based effluent limits required under sections 301(b) and 306 of the federal Clean Water Act.

(c)

The requirements that apply throughout the term of the water quality standards variance will not result in lowering the currently attained ambient water quality, unless the variance is needed for restoration activities as specified in paragraph(2)(a)(G) of this rule.

(3)

Variance Duration and Re-evaluation.

(a)

The duration of a variance must only be as long as necessary to achieve the highest attainable condition as described in section (5) of this rule.

(b)

The DEQ order or EQC rule will specify the duration of the variance.

(c)

If the duration of the variance is less than the term of the NPDES permit, the permittee must comply with the specified effluent limitation sufficient to meet the underlying water quality standard when the variance expires. The permit will include the date the variance and corresponding interim effluent limit will expire.

(d)

If the term of the variance exceeds five years, DEQ will re-evaluate the highest attainable condition using all existing and readily available information at least every five years. DEQ will specify the re-evaluation frequency in the variance. Following public input, DEQ will submit its re-evaluation to EPA within 30 days of completion. If DEQ does not submit the re-evaluation to EPA within the specified timeline, the variance will no longer be the applicable water quality standard until DEQ completes the re-evaluation and submits it to EPA.

(4)

Variance Submittal Requirements.

(a)

To request an individual variance, a permittee must submit the following information to DEQ:

(A)

The specific pollutant, discharger, and receiving waterbody to which the variance will apply;

(B)

A demonstration that attaining the designated use and criterion for the specific pollutant is not feasible for the requested duration of the variance based on one of the factors found in subsection (2)(a) of this rule;

(C)

A description of treatment or alternative options the permittee considered to meet permit limits based on the applicable underlying water quality criterion, and a description of why these options are not technologically, economically, or otherwise feasible;

(D)

Sufficient water quality data and analyses to characterize ambient and discharge water pollutant concentrations and determine the Highest Attainable Condition, as required in section (5) of this rule;

(E)

If the highest attainable condition for the variance is consistent with paragraph (5)(a)(C) of this rule, a proposed pollutant minimization plan covering the term of the variance that includes actions the permittee(s) will take that will result in progress toward meeting the underlying water quality standard; and

(F)

If the discharger is a publicly owned treatment works, a demonstration of the jurisdiction’s legal authority, such as a sewer use ordinance, to regulate the pollutant for which the variance is sought. The jurisdiction’s legal authority must be sufficient to control potential sources of that pollutant that discharge into the jurisdiction’s sewer collection system.

(b)

To be eligible for any multiple discharger variance or waterbody variance, a permittee must submit all the information required in the specific multiple discharger or waterbody variance rule.

(5)

Highest Attainable Condition. The highest attainable condition is a quantifiable expression of one of the following:

(a)

For individual or multiple discharger WQS variances:

(A)

The highest attainable interim criterion; or

(B)

The interim effluent condition that reflects the greatest pollutant reduction achievable; or

(C)

If no additional feasible pollutant control technology can be identified, the interim criterion or interim effluent condition that reflects the greatest pollutant reduction achievable with the pollutant control technologies installed at the time the State grants the WQS variance, and adoption and implementation of a pollutant minimization plan.

(b)

For WQS variances applicable to a waterbody or waterbody segment:

(A)

The highest attainable interim use and interim criterion; or

(B)

If no additional feasible pollutant control technology can be identified, the interim use and interim criterion that reflects the greatest pollutant reduction achievable with the pollutant control technologies installed at the time the State adopts the WQS variance, and the adoption and implementation of a pollutant minimization plan.

(c)

For any WQS variance that applies to a waterbody or waterbody segment, supporting documentation will identify and document any cost-effective and reasonable best management practices for nonpoint source controls related to the pollutant(s) or water quality parameter(s) and waterbody or waterbody segment(s) specified in the WQS variance that could be implemented to make progress towards attaining the underlying designated use and criterion. DEQ will provide public notice and comment for any such documentation.
(d) In any subsequent WQS variance for a waterbody or waterbody segment, DEQ will document whether and to what extent best management practices for nonpoint source controls were implemented to address the pollutant(s) or water quality parameter(s) subject to the WQS variance and the water quality progress achieved.

(6)

Variance Permit Conditions. DEQ must establish and incorporate into the discharger’s NPDES permit all conditions necessary to implement an approved variance in lieu of the underlying water quality standard, so long as the variance remains effective. The permit must include, at a minimum, the following requirements:

(a)

A permit limit or requirement deriving from the highest attainable effluent condition or highest attainable use and criterion specified in the variance, including any updated highest attainable effluent condition based on a five year re-evaluation;

(b)

For variances expressing the highest attainable condition per section 5(a)(C) or 5(b)(B) of this rule, a requirement to implement the Pollutant Minimization Program included in the applicable variance ;

(c)

Any studies, effluent monitoring, or other monitoring necessary to ensure compliance with the conditions of the variance; and

(d)

An annual progress report to DEQ describing the results of any required studies or monitoring during the reporting year, and identifying the pollutant reduction activities completed and any impediments to reaching any specific milestones stated in the variance.

(7)

Public Input and Notification Requirements.

(a)

If DEQ proposes to grant a variance, it must provide public notice of the proposed variance and accept public comment. The public notice may be coordinated with the public notification of a draft NPDES permit or draft 401 certification that would rely on the variance;

(b)

If DEQ is required to re-evaluate the highest attainable condition consistent with (3)(d) of this rule, DEQ will obtain public input on the re-evaluation prior to submitting the re-evaluation to EPA. The specific method of obtaining public input will be documented in the variance.

(c)

DEQ will publish a list of all variances approved under this rule on its website. DEQ will add newly approved variances to this list within 30 days of their effective date. The list will identify:

(A)

The effective date and duration of the variance;

(B)

The facility or facilities;

(C)

The pollutant(s) or water quality parameter(s);

(D)

The waters to which the variance applies;

(E)

The underlying designated use and criterion for the waterbody;

(F)

The highest attainable condition specified in the variance;

(G)

How to obtain additional information about the variance.
340‑041‑0001
Preface
340‑041‑0002
Definitions
340‑041‑0004
Antidegradation
340‑041‑0007
Statewide Narrative Criteria
340‑041‑0009
Bacteria
340‑041‑0011
Biocriteria
340‑041‑0016
Dissolved Oxygen
340‑041‑0019
Nuisance Phytoplankton Growth
340‑041‑0021
pH
340‑041‑0028
Temperature
340‑041‑0031
Total Dissolved Gas
340‑041‑0032
Total Dissolved Solids (TDS)
340‑041‑0033
Toxic Substances
340‑041‑0036
Turbidity
340‑041‑0046
Water Quality Limited Waters
340‑041‑0053
Mixing Zones
340‑041‑0057
Implementation at Domestic Wastewater Treatment Works
340‑041‑0059
Variances
340‑041‑0061
Other Implementation of Water Quality Criteria
340‑041‑0101
Basin-Specific Criteria (Main Stem Columbia River): Beneficial Uses to Be Protected in the Main Stem Columbia River
340‑041‑0103
Basin-Specific Criteria (Main Stem Columbia River): Approved TMDLs in the Basin
340‑041‑0104
Basin-Specific Criteria (Main Stem Columbia River): Water Quality Standards and Policies Specific to the Main Stem Columbia River
340‑041‑0121
Basin-Specific Criteria (Main Stem Snake River): Beneficial Uses to Be Protected in the Main Stem Snake River
340‑041‑0122
Basin-Specific Criteria (Main Stem Snake River): Approved TMDLs in the Basin
340‑041‑0124
Basin-Specific Criteria (Main Stem Snake River): Water Quality Standards and Policies Specific to the Main Stem Snake River
340‑041‑0130
Basin-Specific Criteria (Deschutes): Beneficial Uses to Be Protected in the Deschutes Basin
340‑041‑0133
Basin-Specific Criteria (Deschutes): Approved TMDLs in the Basin:
340‑041‑0135
Basin-Specific Criteria (Deschutes): Water Quality Standards and Policies for this Basin
340‑041‑0140
Basin-Specific Criteria (Goose and Summer Lakes): Beneficial Uses to be Protected in Goose and Summer Lake Basins
340‑041‑0143
Basin-Specific Criteria (Goose and Summer Lakes): Approved TMDLs in the Basin:
340‑041‑0145
Basin-Specific Criteria (Goose and Summer Lakes): Water Quality Standards and Policies for this Basin
340‑041‑0151
Basin-Specific Criteria (Grande Ronde): Beneficial Uses to Be Protected in the Grande Ronde Basin
340‑041‑0154
Basin-Specific Criteria (Grande Ronde): Approved TMDLs in the Basin:
340‑041‑0156
Basin-Specific Criteria (Grande Ronde): Water Quality Standards and Policies for this Basin
340‑041‑0160
Basin-Specific Criteria (Hood): Beneficial Uses to Be Protected in the Hood Basin
340‑041‑0164
Basin-Specific Criteria (Hood): Approved TMDLs in the Basin:
340‑041‑0165
Basin-Specific Criteria (Hood): Water Quality Standards and Policies for this Basin
340‑041‑0170
Basin-Specific Criteria (John Day): Beneficial Uses to Be Protected in the John Day Basin
340‑041‑0174
Basin-Specific Criteria (John Day): Approved TMDLs in the Basin:
340‑041‑0175
Basin-Specific Criteria (John Day): Water Quality Standards and Policies for this Basin
340‑041‑0180
Basin-Specific Criteria (Klamath): Beneficial Uses to Be Protected in the Klamath Basin
340‑041‑0184
Basin-Specific Criteria (Klamath): Approved TMDLs in the Basin:
340‑041‑0185
Basin-Specific Criteria (Klamath): Water Quality Standards and Policies for this Basin
340‑041‑0190
Basin-Specific Criteria (Malheur Lake): Beneficial Uses to Be Protected in the Malheur Lake Basin
340‑041‑0194
Basin-Specific Criteria (Malheur Lake): Approved TMDLs in the Basin:
340‑041‑0195
Basin-Specific Criteria (Malheur Lake): Water Quality Standards and Policies for this Basin
340‑041‑0201
Basin-Specific Criteria (Malheur River):Beneficial Uses to Be Protected in the Malheur River Basin
340‑041‑0204
Basin-Specific Criteria (Malheur River): Approved TMDLs in the Basin:
340‑041‑0207
Basin-Specific Criteria (Malheur River): Water Quality Standards and Policies for this Basin
340‑041‑0220
Basin-Specific Criteria (Mid Coast Basin): Beneficial Uses to Be Protected in the Mid Coast Basin
340‑041‑0224
Basin-Specific Criteria (Mid Coast Basin): Approved TMDLs in the Basin:
340‑041‑0225
Basin-Specific Criteria (Mid Coast Basin): Water Quality Standards and Policies for this Basin
340‑041‑0230
Basin-Specific Criteria (North Coast): Beneficial Uses to Be Protected in the North Coast Basin
340‑041‑0234
Basin-Specific Criteria (North Coast): Approved TMDLs in the Basin:
340‑041‑0235
Basin-Specific Criteria (North Coast): Water Quality Standards and Policies for this Basin
340‑041‑0250
Basin-Specific Criteria (Owyhee): Beneficial Uses to Be Protected in the Owyhee Basin
340‑041‑0254
Basin-Specific Criteria (Owyhee): Approved TMDLs in the Basin:
340‑041‑0256
Basin-Specific Criteria (Owyhee): Water Quality Standards and Policies for this Basin
340‑041‑0260
Basin-Specific Criteria (Powder/Burnt): Beneficial Uses to Be Protected in the Powder/Burnt Basins
340‑041‑0264
Basin-Specific Criteria (Powder/Burnt): Approved TMDLs in the Basin:
340‑041‑0265
Basin-Specific Criteria (Powder/Burnt): Water Quality Standards and Policies for this Basin
340‑041‑0271
Basin-Specific Criteria (Rogue): Beneficial Uses to Be Protected in the Rogue Basin
340‑041‑0274
Basin-Specific Criteria (Rogue): Approved TMDLs in the Basin:
340‑041‑0275
Basin-Specific Criteria (Rogue): Water Quality Standards and Policies for this Basin
340‑041‑0286
Basin-Specific Criteria (Sandy Basin): Beneficial Uses to Be Protected in the Sandy Basin
340‑041‑0289
Basin-Specific Criteria (Sandy Basin): Approved TMDLs in the Basin:
340‑041‑0290
Basin-Specific Criteria (Sandy Basin): Water Quality Standards and Policies for this Basin
340‑041‑0300
Basin-Specific Criteria (South Coast): Beneficial Uses to Be Protected in the South Coast Basin
340‑041‑0304
Basin-Specific Criteria (South Coast): Approved TMDLs in the Basin
340‑041‑0305
Water Quality Standards and Policies for South Coast Basin
340‑041‑0310
Basin-Specific Criteria (Umatilla): Beneficial Uses to Be Protected in the Umatilla Basin
340‑041‑0314
Basin-Specific Criteria (Umatilla): Approved TMDLs in the Basin:
340‑041‑0315
Basin-Specific Criteria (Umatilla): Water Quality Standards and Policies for this Basin
340‑041‑0320
Basin-Specific Criteria (Umpqua Basin): Beneficial Uses to Be Protected in the Umpqua Basin
340‑041‑0324
Basin-Specific Criteria (Umpqua Basin): Approved TMDLs in the Basin:
340‑041‑0326
Basin-Specific Criteria (Umpqua Basin): Water Quality Standards and Policies for this Basin
340‑041‑0330
Basin-Specific Criteria (Walla Walla): Beneficial Uses to Be Protected in the Walla Walla Basin
340‑041‑0334
Basin-Specific Criteria (Walla Walla): Approved TMDLs in the Basin:
340‑041‑0336
Basin-Specific Criteria (Walla Walla): Water Quality Standards and Policies for this Basin
340‑041‑0340
Basin-Specific Criteria (Willamette): Beneficial Uses to Be Protected in the Willamette Basin
340‑041‑0344
Basin-Specific Criteria (Willamette): Approved TMDLs in the Basin:
340‑041‑0345
Basin-Specific Criteria (Willamette): Water Quality Standards and Policies for this Basin
340‑041‑0350
The Three Basin Rule: Clackamas, McKenzie (above RM 15) & the North Santiam
340‑041‑8033
Division 41 Tables and Figures
Last Updated

Jun. 8, 2021

Rule 340-041-0059’s source at or​.us