Minnesota Administrative Rules

7050.0222 SPECIFIC WATER QUALITY STANDARDS FOR CLASS 2 WATERS OF THE STATE; AQUATIC LIFE AND RECREATION.

Subpart 1.

General.

A.

The numeric and narrative water quality standards in this part prescribe the qualities or properties of the waters of the state that are necessary for the aquatic life and recreation designated public uses and benefits. If the standards in this part are exceeded in waters of the state that have the class 2 designation, it is considered indicative of a polluted condition which is actually or potentially deleterious, harmful, detrimental, or injurious with respect to the designated uses.

B.

Standards for metals are expressed as total metal in this part, but must be converted to dissolved metal standards for application to surface waters. Conversion factors for converting total to dissolved metal standards are listed in subpart 9. The conversion factor for metals not listed in subpart 9 is one. The dissolved metal standard equals the total metal standard times the conversion factor. Water-quality-based effluent limits for metals are expressed as total metal.

C.

The tables of standards in this part include the following abbreviations and acronyms:

*	an asterisk following the FAV and MS values or double dashes (--) means subpart 7, item E, applies
(c)	means the chemical is assumed to be a human carcinogen
°C	means degrees Celsius
CS	means chronic standard, defined in part 7050.0218, subpart 3
--	double dashes means there is no standard
°F	means degrees Fahrenheit
FAV	means final acute value, defined in part 7050.0218, subpart 3
HH	in the "basis" column means the standard is human health-based
MS	means maximum standard, defined in part 7050.0218, subpart 3
NA	means not applicable
su	means standard unit. It is the reporting unit for pH
TH	means total hardness in milligrams per liter, which is the sum of the calcium and magnesium concentrations expressed as CaCO3
Tox	in the "basis" column means the standard is toxicity-based

D.

Important synonyms or acronyms for some chemicals are listed in parentheses below the primary name.

Subp. 2.

Class 2A waters; aquatic life and recreation.

The quality of class 2A surface waters shall be such as to permit the propagation and maintenance of a healthy community of coldwater aquatic biota, and their habitats according to the definitions in subpart 2c. These waters shall be suitable for aquatic recreation of all kinds, including bathing, for which the waters may be usable. This class of surface waters is also protected as a source of drinking water. Abbreviations, acronyms, and symbols are explained in subpart 1.

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Acenaphthene	μg/L	20	HH	56	112	Tox
Acetochlor	μg/L	3.6	Tox	86	173	Tox
Acrylonitrile (c)	μg/L	0.38	HH	1,140*	2,281*	Tox
Alachlor (c)	μg/L	3.8	HH	800*	1,600*	Tox
Aluminum, total	μg/L	87	Tox	748	1,496	Tox
Ammonia un-ionized as N	μg/L	16	Tox	--	--	NA

The percent un-ionized ammonia can be calculated for any temperature and pH by using the following equation taken from Emerson, K., R.C. Russo, R.E. Lund, and R.V. Thurston, Aqueous ammonia equilibrium calculations; effect of pH and temperature. Journal of the Fisheries Research Board of Canada 32: 2379-2383 (1975):

	1
	f = _ x 100
	(pka - pH)

10

+ 1

where:	f = the percent of total ammonia in the un-ionized state
	pka= 0.09 + (2730/T) (dissociation constant for ammonia)
	T = temperature in degrees Kelvin (273.16° Kelvin = 0° Celsius)

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Anthracene	μg/L	0.035	Tox	0.32	0.63	Tox
Antimony, total	μg/L	5.5	HH	90	180	Tox
Arsenic, total	μg/L	2.0	HH	360	720	Tox
Atrazine (c)	μg/L	3.4	HH	323	645	Tox
Benzene (c)	μg/L	5.1	HH	4,487*	8,974*	Tox
Bromoform	μg/L	33	HH	2,900	5,800	Tox
Cadmium, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.7852[ln(total hardness mg/L)]-3.490)

The MS in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-3.828)

The FAV in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-3.1349)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total cadmium standards for five hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Cadmium, total
	CS μg/L	0.66	1.1	2.0	2.7	3.4
	MS μg/L	1.8	3.9	8.6	14	19
	FAV μg/L	3.6	7.8	17	27	37

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Carbon tetrachloride (c)	μg/L	1.9	HH	1750*	3500*	Tox
Chlordane (c)	ng/L	0.073	HH	1200*	2400*	Tox
Chloride	mg/L	230	Tox	860	1720	Tox

Chlorine, total residual

μg/L

11

Tox

19

38

Tox

Chlorine standard applies to conditions of continuous exposure, where continuous exposure refers to chlorinated effluents that are discharged for more than a total of two hours in any 24-hour period.

Chlorobenzene (Monochlorobenzene)	μg/L	20	HH	423	846	Tox
Chloroform (c)	μg/L	53	HH	1,392	2,784	Tox
Chlorpyrifos	μg/L	0.041	Tox	0.083	0.17	Tox
Chromium +3, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+1.561)

The MS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+3.688)

The FAV in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+4.380)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total chromium +3 standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Chromium +3, total
	CS μg/L	117	207	365	509	644
	MS μg/L	984	1,737	3,064	4,270	5,405
	FAV μg/L	1,966	3,469	6,120	8,530	10,797

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Chromium +6, total	μg/L	11	Tox	16	32	Tox
Cobalt, total	μg/L	2.8	HH	436	872	Tox
Color value	Pt/Co	30	NA	--	--	NA
Copper, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.620[ln(total hardness mg/L)]-0.570)

The MS in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-1.464)

The FAV in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-0.7703)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total copper standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Copper, total
	CS μg/L	6.4	9.8	15	19	23
	MS μg/L	9.2	18	34	50	65
	FAV μg/L	18	35	68	100	131

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Cyanide, free	μg/L	5.2	Tox	22	45	Tox
DDT (c)	ng/L	0.11	HH	550*	1100*	Tox
1,2-Dichloroethane (c)	μg/L	3.5	HH	45,050*	90,100*	Tox
Dieldrin (c)	ng/L	0.0065	HH	1,300*	2,500*	Tox
Di-2-ethylhexyl phthalate (c)	μg/L	1.9	HH	--*	--*	NA
Di-n-octyl phthalate	μg/L	30	Tox	825	1,650	Tox
Endosulfan	μg/L	0.0076	HH	0.084	0.17	Tox
Endrin	μg/L	0.0039	HH	0.090	0.18	Tox
Escherichia (E.) coli	See below	See below	HH	See below	See below	NA

Not to exceed 126 organisms per 100 milliliters as a geometric mean of not less than five samples representative of conditions within any calendar month, nor shall more than ten percent of all samples taken during any calendar month individually exceed 1,260 organisms per 100 milliliters. The standard applies only between April 1 and October 31.

Ethylbenzene

μg/L

68

Tox

1,859

3,717

Tox

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Eutrophication standards for class 2A lakes and reservoirs.

Designated lake trout lakes in all ecoregions (lake trout lakes support natural populations of lake trout, Salvelinus namaycush):

Phosphorus, total	μg/L	12	NA	--	--	NA
Chlorophyll-a	μg/L	3	NA	--	--	NA
Secchi disk transparency	meters	No less than 4.8	NA	--	--	NA

Designated trout lakes in all ecoregions, except lake trout lakes:

Phosphorus, total	μg/L	20	NA	--	--	NA
Chlorophyll-a	μg/L	6	NA	--	--	NA
Secchi disk transparency	meters	No less than 2.5	NA	--	--	NA

Additional narrative eutrophication standards for class 2A lakes and reservoirs are found under subpart 2a.

Eutrophication standards for class 2A rivers and streams.

North River Nutrient Region:
Phosphorus, total		μg/L	less than or equal to 50
Chlorophyll-a (seston)		μg/L	less than or equal to 7
Diel dissolved oxygen flux		mg/L	less than or equal to 3.0
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 1.5
Central River Nutrient Region:
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 18
Diel dissolved oxygen flux		mg/L	less than or equal to 3.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 2.0
South River Nutrient Region:
Phosphorus, total		μg/L	less than or equal to 150
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Diel dissolved oxygen flux		mg/L	less than or equal to 4.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 3.0

Additional narrative eutrophication standards for class 2A rivers and streams are found under subpart 2b.

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Fluoranthene	μg/L	1.9	Tox	3.5	6.9	Tox
Heptachlor (c)	ng/L	0.10	HH	260*	520*	Tox
Heptachlor epoxide (c)	ng/L	0.12	HH	270*	530*	Tox
Hexachlorobenzene (c)	ng/L	0.061	HH	--*	--*	Tox
Lead, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-4.705)

The MS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-1.460)

The FAV in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-0.7643)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total lead standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Lead, total
	CS μg/L	1.3	3.2	7.7	13	19
	MS μg/L	34	82	197	331	477
	FAV μg/L	68	164	396	663	956

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Lindane (c) (Hexachlorocyclohexane, gamma-)	μg/L	0.0087	HH	1.0*	2.0*	Tox
Mercury, total in water	ng/L	6.9	HH	2,400*	4,900*	Tox
Mercury, total in edible fish	mg/kg ppm	0.2	HH	NA	NA	NA
Methylene chloride (c) Dichloromethane)	μg/L	45	HH	13,875*	27,749*	Tox
Metolachlor	μg/L	23	Tox	271	543	Tox
Naphthalene	μg/L	65	HH	409	818	Tox
Nickel, total	μg/L	equation	Tox/HH	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS shall not exceed the human health-based standard of 297 μg/L. For waters with total hardness values less than 212 mg/L, the CS in μg/L is toxicity-based and shall not exceed: exp.(0.846[ln(total hardness mg/L)]+1.1645)

The MS in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+3.3612)

The FAV in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+4.0543)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total nickel standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Nickel, total
	CS μg/L	88	158	283	297	297
	MS μg/L	789	1,418	2,549	3,592	4,582
	FAV μg/L	1,578	2,836	5,098	7,185	9,164

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Oil	μg/L	500	NA	5,000	10,000	NA
Oxygen, dissolved	mg/L	See below	NA	--	--	NA

7.0 mg/L as a daily minimum. This dissolved oxygen standard requires compliance with the standard 50 percent of the days at which the flow of the receiving water is equal to the 7Q₁₀.

Parathion	μg/L	0.013	Tox	0.07	0.13	Tox
Pentachlorophenol	μg/L	0.93	HH	equation	equation	Tox

The MS and FAV vary with pH and are calculated using the following equations:

The MS in μg/L shall not exceed: exp.(1.005[pH]-4.830)

The FAV in μg/L shall not exceed: exp.(1.005[pH]-4.1373)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For pH values less than 6.0, 6.0 shall be used to calculate the standard and for pH values greater than 9.0, 9.0 shall be used to calculate the standard.

Example of pentachlorophenol standards for five pH values:

	pH su	6.5	7.0	7.5	8.0	8.5
	_
	Pentachlorophenol
	CS μg/L	0.93	0.93	0.93	0.93	0.93
	MS μg/L	5.5	9.1	15	25	41
	FAV μg/L	11	18	30	50	82

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

pH, minimum	su	6.5	NA	--	--	NA
pH, maximum	su	8.5	NA	--	--	NA
Phenanthrene	μg/L	3.6	Tox	32	64	Tox
Phenol	μg/L	123	Tox	2,214	4,428	Tox
Polychlorinated biphenyls, total (c)	ng/L	0.014	HH	1,000*	2,000*	Tox
Radioactive materials	NA	See below	NA	See below	See below	NA

Not to exceed the lowest concentrations permitted to be discharged to an uncontrolled environment as permitted by the appropriate authority having control over their use.

Selenium, total	μg/L	5.0	Tox	20	40	Tox
Silver, total	μg/L	0.12	Tox	equation	equation	Tox

The MS and FAV vary with total hardness and are calculated using the following equations:

The MS in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-7.2156)

The FAV in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-6.520)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of silver standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Silver, total
	CS μg/L	0.12	0.12	0.12	0.12	0.12
	MS μg/L	1.0	2.0	6.7	13	22
	FAV μg/L	1.2	4.1	13	27	44

Substance, Characteristic, or Pollutant (Class 2A)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Temperature	°C or °F	No material increase	NA	--	--	NA
1,1,2,2-Tetrachloroethane (c)	μg/L	1.1	HH	1,127*	2,253*	Tox
Tetrachloroethylene (c)	μg/L	3.8	HH	428*	857*	Tox
Thallium, total	μg/L	0.28	HH	64	128	Tox
Toluene	μg/L	253	Tox	1,352	2,703	Tox
Toxaphene (c)	ng/L	0.31	HH	730*	1,500*	Tox
1,1,1-Trichloroethane	μg/L	329	Tox	2,957	5,913	Tox
1,1,2-Trichloroethylene (c)	μg/L	25	HH	6,988*	13,976*	Tox
2,4,6-Trichlorophenol	μg/L	2.0	HH	102	203	Tox
Total suspended solids (TSS)	mg/L	10	NA	--	--	NA
TSS standards for class 2A may be exceeded for no more than ten percent of the time. This standard applies April 1 through September 30
Vinyl chloride (c)	μg/L	0.17	HH	--*	--*	NA
Xylene, total m,p,o	μg/L	166	Tox	1,407	2,814	Tox
Zinc, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.7615)

The MS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.8604)

The FAV in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+1.5536

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of zinc standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Zinc, total
	CS μg/L	59	106	191	269	343
	MS μg/L	65	117	211	297	379
	FAV μg/L	130	234	421	594	758

Subp. 2a.

Narrative eutrophication standards for lakes and reservoirs.

A.

Eutrophication standards for lakes and reservoirs are compared to summer-average data. Exceedance of the total phosphorus and either the chlorophyll-a or Secchi disk transparency standard is required to indicate a polluted condition.

B.

It is the policy of the agency to protect all lakes and reservoirs from the undesirable effects of cultural eutrophication. Lakes and reservoirs with a baseline quality better than the numeric eutrophication standards in subpart 2 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources, and the protection of lake or reservoir resources, including, but not limited to:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

C.

Lakes and reservoirs with a baseline quality that is poorer than the numeric eutrophication standards in subpart 2 must be considered to be in compliance with the standards if the baseline quality is the result of natural causes. The commissioner shall determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

D.

When applied to reservoirs, the eutrophication standards in this subpart and subpart 2 may be modified on a site-specific basis to account for characteristics unique to reservoirs that can affect trophic status, such as water temperature, variations in hydraulic residence time, watershed size, and the fact that reservoirs may receive drainage from more than one ecoregion. Information supporting a site-specific standard can be provided by the commissioner or by any person outside the agency. The commissioner shall evaluate all data in support of a modified standard and determine whether a change in the standard for a specific reservoir is justified. Any total phosphorus effluent limit determined to be necessary based on a modified standard shall only be required after the discharger has been given notice of the specific proposed effluent limits and an opportunity to request a hearing as provided in part 7000.1800.

E.

Eutrophication standards applicable to lakes and reservoirs that lie on the border between two ecoregions or that are in the Red River Valley (also referred to as Lake Agassiz Plains), Northern Minnesota Wetlands, or Driftless Area Ecoregion must be applied on a case-by-case basis. The commissioner shall use the standards applicable to adjacent ecoregions as a guide.

Subp. 2b.

Narrative eutrophication standards for rivers and streams.

A.

Eutrophication standards for rivers and streams are compared to summer-average data or as specified in subpart 2. Exceedance of the total phosphorus levels and chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels is required to indicate a polluted condition.

B.

Rivers and streams that exceed the phosphorus levels but do not exceed the chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels meet the eutrophication standard.

C.

For chlorophyll-a (periphyton), the standard is exceeded if concentrations exceed 150 mg/m² more than one year in ten.

D.

It is the policy of the agency to protect all rivers and streams from the undesirable effects of cultural eutrophication. Rivers and streams with a baseline quality better than the numeric eutrophication standards in subpart 3 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources, including:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable, in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

E.

Rivers and streams with a baseline quality that does not meet the numeric eutrophication standards in part 7050.0150, subpart 5b, are in compliance with the standards if the baseline quality is the result of natural causes. The commissioner must determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

Subp. 2c.

Beneficial use definitions for lotic coldwater aquatic life and habitats (class 2A).

A.

Subitems (1) to (5) apply to the beneficial uses in items B and C:

(1)

The designation and attainment of beneficial uses are based on the biological criteria in subpart 2d.

(2)

The attributes of species composition, diversity, and functional organization are measured using:

(a)

the fish IBI as defined in Fish Data Collection Protocols for Lotic Waters in Minnesota (2017); or

(b)

the macroinvertebrate IBI as defined in Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota (2017).

(3)

Water body types for streams and rivers are defined in the documents referenced in subitem (2).

(4)

The following documents are incorporated by reference and are not subject to frequent change:

(a)

Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(b)

Fish Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(c)

Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking; and

(d)

Development of Biological Criteria for Tiered Aquatic Life Uses, Minnesota Pollution Control Agency (2016). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking.

(5)

The beneficial use subclass designators "e" and "g" are added to the class 2A designator as specific additional designators. The additional subclass designators do not replace the class 2A designator. All requirements for class 2A coldwater stream and river habitats in parts 7050.0222 and 7052.0100 continue to apply in addition to requirements for class 2Ae or class 2Ag coldwater stream and river habitats in part 7050.0222. These subclass designators are applied to lotic waters only.

B.

"Exceptional coldwater aquatic life and habitat" or "class 2Ae" is a beneficial use that means waters capable of supporting and maintaining an exceptional and balanced, integrated, adaptive community of coldwater aquatic organisms having a species composition, diversity, and functional organization comparable to the 75th percentile of biological condition gradient level 3 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

C.

"General coldwater aquatic life and habitat" or "class 2Ag" is a beneficial use that means waters capable of supporting and maintaining a balanced, integrated, adaptive community of coldwater aquatic organisms having a species composition, diversity, and functional organization comparable to the median of biological condition gradient level 4 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

Subp. 2d.

Biological criteria for lotic coldwater aquatic life and habitats (class 2A).

Water Body Type	Tier	Class	Assemblage	Biocriterion
_
Southern coldwater streams	Exceptional	2Ae	Fish	82
	General	2Ag	Fish	50
Northern coldwater streams	Exceptional	2Ae	Fish	60
	General	2Ag	Fish	35
Northern coldwater streams	Exceptional	2Ae	Macroinvertebrates	52
	General	2Ag	Macroinvertebrates	32
Southern coldwater streams	Exceptional	2Ae	Macroinvertebrates	72
	General	2Ag	Macroinvertebrates	43

The biological criteria for lotic coldwater aquatic life and habitats (class 2A) are applicable to perennial and intermittent waters that allow for colonization of fish or macroinvertebrates.

Subp. 3.

Class 2Bd waters.

The quality of class 2Bd surface waters shall be such as to permit the propagation and maintenance of a healthy community of cool or warm water aquatic biota and their habitats according to the definitions in subpart 3c. These waters shall be suitable for aquatic recreation of all kinds, including bathing, for which the waters may be usable. This class of surface waters is also protected as a source of drinking water. The applicable standards are given below. Abbreviations, acronyms, and symbols are explained in subpart 1.

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Acenaphthene	μg/L	20	HH	56	112	Tox
Acetochlor	μg/L	3.6	Tox	86	173	Tox
Acrylonitrile (c)	μg/L	0.38	HH	1,140*	2,281*	Tox
Alachlor (c)	μg/L	4.2	HH	800*	1,600*	Tox
Aluminum, total	μg/L	125	Tox	1,072	2,145	Tox
Ammonia un-ionized as N	μg/L	40	Tox	--	--	NA

The percent un-ionized ammonia can be calculated for any temperature and pH by using the following equation taken from Emerson, K., R.C. Russo, R.E. Lund, and R.V. Thurston, Aqueous ammonia equilibrium calculations; effect of pH and temperature. Journal of the Fisheries Research Board of Canada 32: 2379-2383 (1975):

f = 1/(10^(pka-pH) + 1) x 100

where:	f = the percent of total ammonia in the un-ionized state
	pka = 0.09 + (2730/T) (dissociation constant for ammonia)
	T = temperature in degrees Kelvin (273.16° Kelvin = 0° Celsius)

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Anthracene	μg/L	0.035	Tox	0.32	0.63	Tox
Antimony, total	μg/L	5.5	HH	90	180	Tox
Arsenic, total	μg/L	2.0	HH	360	720	Tox
Atrazine (c)	μg/L	3.4	HH	323	645	Tox
Benzene (c)	μg/L	6.0	HH	4,487*	8,974*	Tox
Bromoform	μg/L	41	HH	2,900	5,800	Tox
Cadmium, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.7852[ln(total hardness mg/L)]-3.490)

The MS in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-1.685)

The FAV in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-0.9919)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total cadmium standards for five hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Cadmium, total
	CS μg/L	0.66	1.1	2.0	2.7	3.4
	MS μg/L	15	33	73	116	160
	FAV μg/L	31	67	146	231	319

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Carbon tetrachloride (c)	μg/L	1.9	HH	1,750*	3,500*	Tox
Chlordane (c)	ng/L	0.29	HH	1,200*	2,400*	Tox
Chloride	mg/L	230	Tox	860	1,720	Tox

Chlorine, total residual

μg/L

11

Tox

19

38

Tox

Chlorine standard applies to conditions of continuous exposure, where continuous exposure refers to chlorinated effluents that are discharged for more than a total of two hours in any 24-hour period.

Chlorobenzene (Monochlorobenzene)	μg/L	20	HH	423	846	Tox
Chloroform (c)	μg/L	53	HH	1,392	2,784	Tox
Chlorpyrifos	μg/L	0.041	Tox	0.083	0.17	Tox
Chromium +3, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+1.561)

The MS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+3.688)

The FAV in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+4.380)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total chromium +3 standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Chromium +3, total
	CS μg/L	117	207	365	509	644
	MS μg/L	984	1,737	3,064	4,270	5,405
	FAV μg/L	1,966	3,469	6,120	8,530	10,797

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Chromium +6, total	μg/L	11	Tox	16	32	Tox
Cobalt, total	μg/L	2.8	HH	436	872	Tox
Copper, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.620[ln(total hardness mg/L)]-0.570)

The MS in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-1.464)

The FAV in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-0.7703)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total copper standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Copper, total
	CS μg/L	6.4	9.8	15	19	23
	MS μg/L	9.2	18	34	50	65
	FAV μg/L	18	35	68	100	131

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Cyanide, free	μg/L	5.2	Tox	22	45	Tox
DDT (c)	ng/L	1.7	HH	550*	1,100*	Tox
1,2-Dichloroethane (c)	μg/L	3.8	HH	45,050*	90,100*	Tox
Dieldrin (c)	ng/L	0.026	HH	1,300*	2,500*	Tox
Di-2-ethylhexyl phthalate (c)	μg/L	1.9	HH	--*	--*	NA
Di-n-octyl phthalate	μg/L	30	Tox	825	1,650	Tox
Endosulfan	μg/L	0.029	HH	0.28	0.56	Tox
Endrin	μg/L	0.016	HH	0.090	0.18	Tox
Escherichia (E.) coli	See below	See below	HH	See below	See below	NA

Not to exceed 126 organisms per 100 milliliters as a geometric mean of not less than five samples representative of conditions within any calendar month, nor shall more than ten percent of all samples taken during any calendar month individually exceed 1,260 organisms per 100 milliliters. The standard applies only between April 1 and October 31.

Ethylbenzene

μg/L

68

Tox

1,859

3,717

Tox

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Eutrophication standards for class 2Bd lakes, shallow lakes, and reservoirs.

Lakes, Shallow Lakes, and Reservoirs in Northern Lakes and Forest Ecoregion

Phosphorus, total	μg/L	30	NA	--	--	NA
Chlorophyll-a	μg/L	9	NA	--	--	NA
Secchi disk transparency	meters	Not less than 2.0	NA	--	--	NA

Lakes and Reservoirs in North Central Hardwood Forest Ecoregion

Phosphorus, total	μg/L	40	NA	--	--	NA
Chlorophyll-a	μg/L	14	NA	--	--	NA
Secchi disk transparency	meters	Not less than 1.4	NA	--	--	NA

Lakes and Reservoirs in Western Corn Belt Plains and Northern Glaciated Plains Ecoregions

Phosphorus, total	μg/L	65	NA	--	--	NA
Chlorophyll-a	μg/L	22	NA	--	--	NA
Secchi disk transparency	meters	Not less than 0.9	NA	--	--	NA

Shallow Lakes in North Central Hardwood Forest Ecoregion

Phosphorus, total	μg/L	60	NA	--	--	NA
Chlorophyll-a	μg/L	20	NA	--	--	NA
Secchi disk transparency	meters	Not less than 1.0	NA	--	--	NA

Shallow Lakes in Western Corn Belt Plains and Northern Glaciated Plains Ecoregions

Phosphorus, total	μg/L	90	NA	--	--	NA
Chlorophyll-a	μg/L	30	NA	--	--	NA
Secchi disk transparency	meters	Not less than 0.7	NA	--	--	NA

Additional narrative eutrophication standards for class 2Bd lakes, shallow lakes, and reservoirs are found under subpart 3a.

Eutrophication standards for class 2Bd rivers and streams.

North River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 50
Chlorophyll-a (seston)		μg/L	less than or equal to 7
Diel dissolved oxygen flux		mg/L	less than or equal to 3.0
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 1.5
Central River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 18
Diel dissolved oxygen flux		mg/L	less than or equal to 3.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 2.0
South River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 150
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Diel dissolved oxygen flux		mg/L	less than or equal to 4.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 3.0

Additional narrative eutrophication standards for class 2Bd rivers and streams are found under subpart 3b.

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Fluoranthene	μg/L	1.9	Tox	3.5	6.9	Tox
Heptachlor (c)	ng/L	0.39	HH	260*	520*	Tox
Heptachlor epoxide (c)	ng/L	0.48	HH	270*	530*	Tox
Hexachlorobenzene (c)	ng/L	0.24	HH	--*	--*	Tox
Lead, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-4.705)

The MS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-1.460)

The FAV in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-0.7643)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total lead standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Lead, total
	CS μg/L	1.3	3.2	7.7	13	19
	MS μg/L	34	82	197	331	477
	FAV μg/L	68	164	396	663	956

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Lindane (c) (Hexachlorocyclohexane, gamma-)	μg/L	0.032	HH	4.4*	8.8*	Tox
Mercury, total in water	ng/L	6.9	HH	2,400*	4,900*	Tox
Mercury, total in edible fish tissue	mg/kg ppm	0.2	HH	NA	NA	NA
Methylene chloride (c) (Dichloromethane)	μg/L	46	HH	13,875*	27,749*	Tox
Metolachlor	μg/L	23	Tox	271	543	Tox
Naphthalene	μg/L	81	Tox	409	818	Tox
Nickel, total	μg/L	equation	Tox/HH	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS shall not exceed the human health-based standard of 297 μg/L. For waters with total hardness values less than 212 mg/L, the CS in μg/L is toxicity-based and shall not exceed: exp.(0.846[ln(total hardness mg/L)]+1.1645)

The MS in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+3.3612)

The FAV in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+4.0543)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total nickel standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Nickel, total
	CS μg/L	88	158	283	297	297
	MS μg/L	789	1,418	2,549	3,592	4,582
	FAV μg/L	1,578	2,836	5,098	7,185	9,164

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Oil	μg/L	500	NA	5,000	10,000	NA
Oxygen, dissolved	mg/L	See below	NA	--	--	NA

5.0 mg/L as a daily minimum. This dissolved oxygen standard may be modified on a site-specific basis according to part 7050.0220, subpart 7, except that no site-specific standard shall be less than 5 mg/L as a daily average and 4 mg/L as a daily minimum. Compliance with this standard is required 50 percent of the days at which the flow of the receiving water is equal to the 7Q₁₀.

Parathion	μg/L	0.013	Tox	0.07	0.13	Tox
Pentachlorophenol	μg/L	1.9	HH	equation	equation	Tox

The MS and FAV vary with pH and are calculated using the following equations:

The MS in μg/L shall not exceed: exp.(1.005[pH]-4.830)

The FAV in μg/L shall not exceed: exp.(1.005[pH]-4.1373)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For pH values less than 6.0, 6.0 shall be used to calculate the standard and for pH values greater than 9.0, 9.0 shall be used to calculate the standard.

Example of pentachlorophenol standards for five pH values:

	pH su	6.5	7.0	7.5	8.0	8.5
	_
	Pentachlorophenol
	CS μg/L	1.9	1.9	1.9	1.9	1.9
	MS μg/L	5.5	9.1	15	25	41
	FAV μg/L	11	18	30	50	82

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

pH, minimum	su	6.5	NA	--	--	NA
pH, maximum	su	9.0	NA	--	--	NA
Phenanthrene	μg/L	3.6	Tox	32	64	Tox
Phenol	μg/L	123	Tox	2,214	4,428	Tox
Polychlorinated biphenyls, total (c)	ng/L	0.029	HH	1,000*	2,000*	Tox
Radioactive materials	NA	See below	NA	See below	See below	NA

Not to exceed the lowest concentrations permitted to be discharged to an uncontrolled environment as permitted by the appropriate authority having control over their use.

Selenium, total	μg/L	5.0	Tox	20	40	Tox
Silver, total	μg/L	1.0	Tox	equation	equation	Tox

The MS and FAV vary with total hardness and are calculated using the following equations:

The MS in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-7.2156)

The FAV in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-6.520)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total silver standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Silver, total
	CS μg/L	1.0	1.0	1.0	1.0	1.0
	MS μg/L	1.0	2.0	6.7	13	22
	FAV μg/L	1.2	4.1	13	27	44

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Temperature

°F

See below

NA

--

--

NA

5°F above natural in streams and 3°F above natural in lakes, based on monthly average of the maximum daily temperatures, except in no case shall it exceed the daily average temperature of 86°F.

1,1,2,2-Tetrachloroethane (c)	μg/L	1.5	HH	1,127*	2,253*	Tox
Tetrachloroethylene (c)	μg/L	3.8	HH	428*	857*	Tox
Thallium, total	μg/L	0.28	HH	64	128	Tox
Toluene	μg/L	253	Tox	1,352	2,703	Tox
Toxaphene (c)	ng/L	1.3	HH	730*	1,500*	Tox
1,1,1-Trichloroethane	μg/L	329	Tox	2,957	5,913	Tox
1,1,2-Trichloroethylene (c)	μg/L	25	HH	6,988*	13,976*	Tox
2,4,6-Trichlorophenol	μg/L	2.0	HH	102	203	Tox
Total suspended solids (TSS)
North River Nutrient Region	mg/L	15	NA	-	-	NA
Central River Nutrient Region	mg/L	30	NA	-	-	NA
South River Nutrient Region	mg/L	65	NA	-	-	NA
Red River mainstem - headwaters to border	mg/L	100	NA	-	-	NA
TSS standards for the class 2Bd North, Central, and South River Nutrient Regions and the Red River mainstem may be exceeded for no more than ten percent of the time. This standard applies April 1 through September 30
Total suspended solids (TSS), summer average
Lower Mississippi River mainstem - Pools 2 through 4	mg/L	32	NA	-	-	NA
Lower Mississippi River mainstem below Lake Pepin	mg/L	30	NA	-	-	NA
TSS standards for the class 2Bd Lower Mississippi River may be exceeded for no more than 50 percent of the time. This standard applies June 1 through September 30

Substance, Characteristic, or Pollutant (Class 2Bd)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Vinyl chloride (c)	μg/L	0.18	HH	--*	--*	NA
Xylene, total m,p,o	μg/L	166	Tox	1,407	2,814	Tox
Zinc, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.7615)

The MS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.8604)

The FAV in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+1.5536)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total zinc standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Zinc, total
	CS μg/L	59	106	191	269	343
	MS μg/L	65	117	211	297	379
	FAV μg/L	130	234	421	594	758

Subp. 3a.

Narrative eutrophication standards for class 2Bd lakes, shallow lakes, and reservoirs.

A.

Eutrophication standards applicable to lakes, shallow lakes, and reservoirs that lie on the border between two ecoregions or that are in the Red River Valley (also referred to as Lake Agassiz Plains), Northern Minnesota Wetlands, or Driftless Area Ecoregion must be applied on a case-by-case basis. The commissioner shall use the standards applicable to adjacent ecoregions as a guide.

B.

Eutrophication standards are compared to summer-average data. Exceedance of the total phosphorus and either the chlorophyll-a or Secchi disk transparency standard is required to indicate a polluted condition.

C.

It is the policy of the agency to protect all lakes, shallow lakes, and reservoirs from the undesirable effects of cultural eutrophication. Lakes, shallow lakes, and reservoirs with a baseline quality better than the numeric eutrophication standards in subpart 3 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources, and the protection of lake, shallow lake, and reservoir resources, including, but not limited to:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

D.

Lakes, shallow lakes, and reservoirs with a baseline quality that is poorer than the numeric eutrophication standards in subpart 3 must be considered to be in compliance with the standards if the baseline quality is the result of natural causes. The commissioner shall determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

E.

When applied to reservoirs, the eutrophication standards in this subpart and subpart 3 may be modified on a site-specific basis to account for characteristics of reservoirs that can affect trophic status, such as water temperature, variations in hydraulic residence time, watershed size, and the fact that reservoirs may receive drainage from more than one ecoregion. Information supporting a site-specific standard can be provided by the commissioner or by any person outside the agency. The commissioner shall evaluate all data in support of a modified standard and determine whether a change in the standard for a specific reservoir is justified. Any total phosphorus effluent limit determined to be necessary based on a modified standard shall only be required after the discharger has been given notice of the specific proposed effluent limits and an opportunity to request a hearing as provided in part 7000.1800.

Subp. 3b.

Narrative eutrophication standards for rivers, streams, and navigational pools.

A.

Eutrophication standards for rivers, streams, and navigational pools are compared to summer-average data or as specified in subpart 3. Exceedance of the total phosphorus levels and chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels is required to indicate a polluted condition.

B.

Rivers, streams, and navigational pools that exceed the phosphorus levels but do not exceed the chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels meet the eutrophication standard.

C.

A polluted condition also exists when the chlorophyll-a (periphyton) concentration exceeds 150 mg/m² more than one year in ten.

D.

It is the policy of the agency to protect all rivers, streams, and navigational pools from the undesirable effects of cultural eutrophication. Rivers, streams, and navigational pools with a baseline quality better than the numeric eutrophication standards in subpart 3 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources including:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable, in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

E.

Rivers, streams, and navigational pools with a baseline quality that does not meet the numeric eutrophication standards in part 7050.0150, subpart 5b, are in compliance with the standards if the baseline quality is the result of natural causes. The commissioner must determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

Subp. 3c.

Beneficial use definitions for lotic warm or cool water aquatic life and habitats (class 2Bd).

A.

Subitems (1) to (5) apply to the beneficial uses in items B to D:

(1)

The designation and attainment of beneficial uses are based on the biological criteria in subpart 3d.

(2)

The attributes of species composition, diversity, and functional organization are measured using:

(a)

the fish IBI as defined in Fish Data Collection Protocols for Lotic Waters in Minnesota (2017); or

(b)

the macroinvertebrate IBI as defined in Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota (2017).

(3)

Water body types for streams and rivers are defined in the documents referenced in subitem (2).

(4)

The following documents are incorporated by reference and are not subject to frequent change:

(a)

Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(b)

Fish Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(c)

Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking; and

(d)

Development of Biological Criteria for Tiered Aquatic Life Uses, Minnesota Pollution Control Agency (2016). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking.

(5)

The beneficial use subclass designators "e," "g," and "m" are added to the class 2Bd designator as specific additional designators. The additional subclass designators do not replace the class 2Bd designator. All requirements for class 2Bd warm or cool water stream and river habitats in parts 7050.0222 and 7052.0100 continue to apply in addition to requirements for class 2Bde, class 2Bdg, or class 2Bdm warm or cool water stream and river habitats in part 7050.0222. These subclass designators are applied to lotic waters only.

B.

"Exceptional cool and warm water aquatic life and habitat, also protected as a source for drinking water" or "class 2Bde" is a beneficial use that means waters capable of supporting and maintaining an exceptional and balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the 75th percentile of biological condition gradient level 3 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

C.

"General cool and warm water aquatic life and habitat, also protected as a source for drinking water" or "class 2Bdg" is a beneficial use that means waters capable of supporting and maintaining a balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the median of biological condition gradient level 4 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

D.

"Modified cool and warm water aquatic life and habitat, also protected as a source for drinking water" or "class 2Bdm" is a beneficial use that means waters capable of supporting and maintaining a balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the median of biological condition gradient level 5 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

(1)

To meet the definition in this item, waters must have been the subject of a use attainability analysis where it is determined that attainment of the class 2Bdg beneficial use is not feasible because of human-induced modifications of the physical habitat. These modifications must be the result of direct alteration to the channel, such as drainageway maintenance, bank stabilization, and impoundments.

(2)

Examples of class 2Bdm waters are the stream channel modification activities regulated under:

(a)

sections 401 and 404 of the Clean Water Act; or

(b)

Minnesota Statutes, chapter 103E.

Subp. 3d.

Biological criteria for lotic warm or cool water aquatic life and habitats (class 2Bd).

Water Body Type	Tier	Class	Assemblage	Biocriterion
_
Southern rivers	Exceptional	2Bde	Fish	71
	General	2Bdg	Fish	49
Southern streams	Exceptional	2Bde	Fish	66
	General	2Bdg	Fish	50
	Modified	2Bdm	Fish	35
Southern headwaters	Exceptional	2Bde	Fish	74
	General	2Bdg	Fish	55
	Modified	2Bdm	Fish	33
Northern rivers	Exceptional	2Bde	Fish	67
	General	2Bdg	Fish	38
Northern streams	Exceptional	2Bde	Fish	61
	General	2Bdg	Fish	47
	Modified	2Bdm	Fish	35
Northern headwaters	Exceptional	2Bde	Fish	68
	General	2Bdg	Fish	42
	Modified	2Bdm	Fish	23
Low gradient	Exceptional	2Bde	Fish	70
	General	2Bdg	Fish	42
	Modified	2Bdm	Fish	15
Northern forest rivers	Exceptional	2Bde	Macroinvertebrates	77
	General	2Bdg	Macroinvertebrates	49
Prairie and southern forest rivers	Exceptional	2Bde	Macroinvertebrates	63
	General	2Bdg	Macroinvertebrates	31
High-gradient northern forest streams	Exceptional	2Bde	Macroinvertebrates	82
	General	2Bdg	Macroinvertebrates	53
Low-gradient northern forest streams	Exceptional	2Bde	Macroinvertebrates	76
	General	2Bdg	Macroinvertebrates	51
	Modified	2Bdm	Macroinvertebrates	37
High-gradient southern streams	Exceptional	2Bde	Macroinvertebrates	62
	General	2Bdg	Macroinvertebrates	37
	Modified	2Bdm	Macroinvertebrates	24
Low-gradient southern forest streams	Exceptional	2Bde	Macroinvertebrates	66
	General	2Bdg	Macroinvertebrates	43
	Modified	2Bdm	Macroinvertebrates	30
Low-gradient prairie streams	Exceptional	2Bde	Macroinvertebrates	69
	General	2Bdg	Macroinvertebrates	41
	Modified	2Bdm	Macroinvertebrates	22

The biological criteria for lotic warm or cool water aquatic life and habitats (class 2Bd) are applicable to perennial and intermittent waters that allow for colonization of fish or macroinvertebrates.

Subp. 4.

Class 2B waters.

The quality of class 2B surface waters shall be such as to permit the propagation and maintenance of a healthy community of cool or warm water aquatic biota, and their habitats according to the definitions in subpart 4c. These waters shall be suitable for aquatic recreation of all kinds, including bathing, for which the waters may be usable. This class of surface water is not protected as a source of drinking water. The applicable standards are given below. Abbreviations, acronyms, and symbols are explained in subpart 1.

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Acenaphthene	μg/l	20	HH	56	112	Tox
Acetochlor	μg/L	3.6	Tox	86	173	Tox
Acrylonitrile (c)	μg/l	0.89	HH	1,140*	2,281*	Tox
Alachlor (c)	μg/L	59	Tox	800	1,600	Tox
Aluminum, total	μg/L	125	Tox	1,072	2,145	Tox
Ammonia un-ionized as N	μg/L	40	Tox	--	--	NA

The percent un-ionized ammonia can be calculated for any temperature and pH by using the following equation taken from Emerson, K., R.C. Russo, R.E. Lund, and R.V. Thurston, Aqueous ammonia equilibrium calculations; effect of pH and temperature. Journal of the Fisheries Research Board of Canada 32: 2379-2383 (1975):

f = 1/(10^(pka-pH) + 1) x 100

where:	f = the percent of total ammonia in the un-ionized state
	pka = 0.09 + (2730/T) (dissociation constant for ammonia)
	T = temperature in degrees Kelvin (273.16° Kelvin = 0° Celsius)

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Anthracene	μg/L	0.035	Tox	0.32	0.63	Tox
Antimony, total	μg/L	31	Tox	90	180	Tox
Arsenic, total	μg/L	53	HH	360	720	Tox
Atrazine (c)	μg/L	10	Tox	323	645	Tox
Benzene (c)	μg/L	98	HH	4,487	8,974	Tox
Bromoform	μg/L	466	HH	2,900	5,800	Tox
Cadmium, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.7852[ln(total hardness mg/L)]-3.490)

The MS in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-1.685)

The FAV in μg/L shall not exceed: exp.(1.128[ln(total hardness mg/L)]-0.9919)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total cadmium standards for five hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Cadmium, total
	CS μg/L	0.66	1.1	2.0	2.7	3.4
	MS μg/L	15	33	73	116	160
	FAV μg/L	31	67	146	231	319

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Carbon tetrachloride (c)	μg/L	5.9	HH	1,750*	3,500*	Tox
Chlordane (c)	ng/L	0.29	HH	1,200*	2,400*	Tox
Chloride	mg/L	230	Tox	860	1,720	Tox

Chlorine, total residual

μg/L

11

Tox

19

38

Tox

Chlorine standard applies to conditions of continuous exposure, where continuous exposure refers to chlorinated effluents that are discharged for more than a total of two hours in any 24-hour period.

Chlorobenzene (Monochlorobenzene)	μg/L	20	HH	423	846	Tox
Chloroform (c)	μg/L	155	Tox	1,392	2,784	Tox
Chlorpyrifos	μg/L	0.041	Tox	0.083	0.17	Tox
Chromium +3, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations

The CS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+1.561)

The MS in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+3.688)

The FAV in μg/L shall not exceed: exp.(0.819[ln(total hardness mg/L)]+4.380)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total chromium +3 standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Chromium +3, total
	CS μg/L	117	207	365	509	644
	MS μg/L	984	1,737	3,064	4,270	5,405
	FAV μg/L	1,966	3,469	6,120	8,530	10,797

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Chromium +6, total	μg/L	11	Tox	16	32	Tox
Cobalt, total	μg/L	5.0	Tox	436	872	Tox
Copper, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.6200[ln(total hardness mg/L)]-0.570)

The MS in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-1.464)

The FAV in μg/L shall not exceed: exp.(0.9422[ln(total hardness mg/L)]-0.7703)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total copper standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Copper, total
	CS μg/L	6.4	9.8	15	19	23
	MS μg/L	9.2	18	34	50	65
	FAV μg/L	18	35	68	100	131

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Cyanide, free	μg/L	5.2	Tox	22	45	Tox
DDT (c)	ng/L	1.7	HH	550*	1,100*	Tox
1,2-Dichloroethane (c)	μg/L	190	HH	45,050*	90,100*	Tox
Dieldrin (c)	ng/L	0.026	HH	1,300*	2,500*	Tox
Di-2-ethylhexyl phthalate (c)	μg/L	2.1	HH	--*	--*	NA
Di-n-octyl phthalate	μg/L	30	Tox	825	1,650	Tox
Endosulfan	μg/L	0.031	HH	0.28	0.56	Tox
Endrin	μg/L	0.016	HH	0.090	0.18	Tox
Escherichia (E.) coli	See below	See below	HH	See below	See below	NA

Not to exceed 126 organisms per 100 milliliters as a geometric mean of not less than five samples representative of conditions within any calendar month, nor shall more than ten percent of all samples taken during any calendar month individually exceed 1,260 organisms per 100 milliliters. The standard applies only between April 1 and October 31.

Ethylbenzene

μg/L

68

Tox

1,859

3,717

Tox

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Eutrophication standards for class 2B lakes, shallow lakes, and reservoirs.

Lakes, Shallow Lakes, and Reservoirs in Northern Lakes and Forest Ecoregions

Phosphorus, total	μg/L	30	NA	--	--	NA
Chlorophyll-a	μg/L	9	NA	--	--	NA
Secchi disk transparency	meters	Not less than 2.0	NA	--	--	NA

Lakes and Reservoirs in North Central Hardwood Forest Ecoregion

Phosphorus, total	μg/L	40	NA	--	--	NA
Chlorophyll-a	μg/L	14	NA	--	--	NA
Secchi disk transparency	meters	Not less than 1.4	NA	--	--	NA

Lakes and Reservoirs in Western Corn Belt Plains and Northern Glaciated Plains Ecoregions

Phosphorus, total	μg/L	65	NA	--	--	NA
Chlorophyll-a	μg/L	22	NA	--	--	NA
Secchi disk transparency	meters	Not less than 0.9	NA	--	--	NA

Shallow Lakes in North Central Hardwood Forest Ecoregion

Phosphorus, total	μg/L	60	NA	--	--	NA
Chlorophyll-a	μg/L	20	NA	--	--	NA
Secchi disk transparency	meters	Not less than 1.0	NA	--	--	NA

Shallow Lakes in Western Corn Belt Plains and Northern Glaciated Plains Ecoregions

Phosphorus, total	μg/L	90	NA	--	--	NA
Chlorophyll-a	μg/L	30	NA	--	--	NA
Secchi disk transparency	meters	Not less than 0.7	NA	--	--	NA

Additional narrative eutrophication standards for class 2B lakes, shallow lakes, and reservoirs are found in subpart 4a.

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Eutrophication standards for class 2B rivers and streams.

North River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 50
Chlorophyll-a (seston)		μg/L	less than or equal to 7
Diel dissolved oxygen flux		mg/L	less than or equal to 3.0
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 1.5
Central River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 18
Diel dissolved oxygen flux		mg/L	less than or equal to 3.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 2.0
South River Nutrient Region
Phosphorus, total		μg/L	less than or equal to 150
Chlorophyll-a (seston)		μg/L	less than or equal to 40
Diel dissolved oxygen flux		mg/L	less than or equal to 5.0
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 3.5

Site-specific standards for specified river reaches or other waters are:

Mississippi River Navigational Pool 1 (river miles 854.1 to 847.7 reach from Fridley to Ford Dam in St. Paul)
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Mississippi River Navigational Pool 2 (river miles 847.7 to 815.2 reach from Ford Dam to Hastings Dam)
Phosphorus, total		μg/L	less than or equal to 125
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Mississippi River Navigational Pool 3 (river miles 815.2 to 796.9 reach from Hastings Dam to Red Wing Dam)
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Mississippi River Navigational Pool 4 (river miles 796.9 to 752.8 reach from Red Wing Dam to Alma Dam). Lake Pepin occupies majority of Pool 4 and Lake Pepin site-specific standards are used for this pool.
Mississippi River Navigational Pools 5 to 8 (river miles 752.8 to 679.1 Alma Dam to Genoa Dam)
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 35
Lake Pepin
Phosphorus, total		μg/L	less than or equal to 100
Chlorophyll-a (seston)		μg/L	less than or equal to 28
Crow Wing River from confluence of Long Prairie River to the mouth of the Crow Wing River at the Mississippi River
Phosphorus, total		μg/L	less than or equal to 75
Chlorophyll-a (seston)		μg/L	less than or equal to 13
Diel dissolved oxygen flux		mg/L	less than or equal to 3.5
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 1.7
Crow River from the confluence of the North Fork of the Crow River and South Fork of the Crow River to the mouth of the Crow River at the Mississippi River
Phosphorus, total		μg/L	less than or equal to 125
Chlorophyll-a (seston)		μg/L	less than or equal to 27
Diel dissolved oxygen flux		mg/L	less than or equal to 4.0
Biochemical oxygen demand (BOD5)		mg/L	less than or equal to 2.5

Additional narrative eutrophication standards for class 2B rivers and streams are found in subpart 4b.

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Fluoranthene	μg/L	1.9	Tox	3.5	6.9	Tox
Heptachlor (c)	ng/L	0.39	HH	260*	520*	Tox
Heptachlor epoxide (c)	ng/L	0.48	HH	270*	530*	Tox
Hexachlorobenzene (c)	ng/L	0.24	HH	--*	--*	Tox
Lead, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-4.705)

The MS in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-1.460)

The FAV in μg/L shall not exceed: exp.(1.273[ln(total hardness mg/L)]-0.7643)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total lead standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Lead, total
	CS μg/L	1.3	3.2	7.7	13	19
	MS μg/L	34	82	197	331	477
	FAV μg/L	68	164	396	663	956

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Lindane (c) (Hexachlorocyclobenzene, gamma-)	μg/L	0.036	HH	4.4*	8.8*	Tox
Mercury, total in water	ng/L	6.9	HH	2,400*	4,900*	Tox
Mercury, total in edible fish tissue	mg/kg ppm	0.2	HH	NA	NA	NA
Methylene chloride (c) (Dichloromethane)	μg/L	1,940	HH	13,875	27,749	Tox
Metolachlor	μg/L	23	Tox	271	543	Tox
Naphthalene	μg/L	81	Tox	409	818	Tox
Nickel, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+1.1645)

The MS in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/L)]+3.3612)

The FAV in μg/L shall not exceed: exp.(0.846[ln(total hardness mg/l)]+4.0543)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total nickel standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Nickel, total
	CS μg/L	88	158	283	399	509
	MS μg/L	789	1,418	2,549	3,592	4,582
	FAV μg/L	1,578	2,836	5,098	7,185	9,164

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Oil	μg/l	500	NA	5,000	10,000	NA
Oxygen, dissolved	mg/L	See below	NA	--	--	NA

5.0 mg/L as a daily minimum. This dissolved oxygen standard may be modified on a site-specific basis according to part 7050.0220, subpart 7, except that no site-specific standard shall be less than 5 mg/L as a daily average and 4 mg/L as a daily minimum. Compliance with this standard is required 50 percent of the days at which the flow of the receiving water is equal to the 7Q₁₀. This standard applies to all class 2B waters except for:

(1) those portions of the Mississippi River from the outlet of the Metro Wastewater Treatment Works in Saint Paul (River Mile 835) to Lock and Dam No. 2 at Hastings (River Mile 815). For this reach of the Mississippi River, the standard is not less than 5 mg/L as a daily average from April 1 through November 30, and not less than 4 mg/L at other times; and

(2) the portion of the Minnesota River from the outlet of the Blue Lake wastewater treatment works (River Mile 21) to the mouth at Fort Snelling. For the specified reach of the Minnesota River, the standard is not less than 5 mg/L as a daily average year round.

Parathion	μg/L	0.013	Tox	0.07	0.13	Tox
Pentachlorophenol	μg/L	equation	Tox/HH	equation	equation	Tox

The CS, MS, and FAV vary with pH and are calculated using the following equations:

For waters with pH values greater than 6.95, the CS shall not exceed the human health-based standard of 5.5 μg/L.

For waters with pH values less than 6.96, the CS in μg/L shall not exceed the toxicity-based standard of exp.(1.005[pH]-5.290)

The MS in μg/L shall not exceed: exp.(1.005[pH]-4.830)

The FAV in μg/L shall not exceed: exp.(1.005[pH]-4.1373)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For pH values less than 6.0, 6.0 shall be used to calculate the standard and for pH values greater than 9.0, 9.0 shall be used to calculate the standard.

Example of pentachlorophenol standards for five pH values:

	pH su	6.5	7.0	7.5	8.0	8.5
	_
	Pentachlorophenol
	CS μg/L	3.5	5.5	5.5	5.5	5.5
	MS μg/L	5.5	9.1	15	25	41
	FAV μg/L	11	18	30	50	82

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

pH, minimum	su	6.5	NA	--	--	NA
pH, maximum	su	9.0	NA	--	--	NA
Phenanthrene	μg/L	3.6	Tox	32	64	Tox
Phenol	μg/L	123	Tox	2,214	4,428	Tox
Polychlorinated biphenyls, total (c)	ng/L	0.029	HH	1,000*	2,000*	Tox
Radioactive materials	NA	See below	NA	See below	See below	NA

Not to exceed the lowest concentrations permitted to be discharged to an uncontrolled environment as permitted by the appropriate authority having control over their use.

Selenium, total	μg/L	5.0	Tox	20	40	Tox
Silver, total	μg/L	1.0	Tox	equation	equation	Tox

The MS and FAV vary with total hardness and are calculated using the following equations:

The MS in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-7.2156)

The FAV in μg/L shall not exceed: exp.(1.720[ln(total hardness mg/L)]-6.520

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total silver standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Silver, total
	CS μg/L	1.0	1.0	1.0	1.0	1.0
	MS μg/L	1.0	2.0	6.7	13	22
	FAV μg/L	1.2	4.1	13	27	44

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Temperature

°F

See below

NA

--

--

NA

5°F above natural in streams and 3°F above natural in lakes, based on monthly average of the maximum daily temperatures, except in no case shall it exceed the daily average temperature of 86°F.

1,1,2,2-Tetrachloroethane (c)	μg/L	13	HH	1,127	2,253	Tox
Tetrachloroethylene (c)	μg/L	8.9	HH	428	857	Tox
Thallium, total	μg/L	0.56	HH	64	128	Tox
Toluene	μg/L	253	Tox	1,352	2,703	Tox
Toxaphene (c)	ng/L	1.3	HH	730*	1,500*	Tox
1,1,1-Trichloroethane	μg/L	329	Tox	2,957	5,913	Tox
1,1,2-Trichloroethylene (c)	μg/L	120	HH	6,988	13,976	Tox
2,4,6-Trichlorophenol	μg/L	2.0	HH	102	203	Tox
Total suspended solids (TSS)
North River Nutrient Region	mg/L	15	NA	--	--	NA
Central River Nutrient Region	mg/L	30	NA	--	--	NA
South River Nutrient Region	mg/L	65	NA	--	--	NA
Red River mainstem - headwaters to border	mg/L	100	NA	--	--	NA
TSS standards for the class 2B North, Central, and South River Nutrient Regions and the Red River mainstem may be exceeded for no more than ten percent of the time. This standard applies April 1 through September 30
Total suspended solids (TSS), summer average
Lower Mississippi River mainstem - Pools 2 through 4	mg/L	32	NA	--	--	NA
Lower Mississippi River mainstem below Lake Pepin	mg/L	30	NA	--	--	NA
TSS standards for the class 2B Lower Mississippi River may be exceeded for no more than 50 percent of the time. This standard applies June 1 through September 30

Substance, Characteristic, or Pollutant (Class 2B)	Units	CS	Basis for CS	MS	FAV	Basis for MS, FAV
_

Vinyl chloride (c)	μg/L	9.2	HH	--*	--*	NA
Xylene, total m,p,o	μg/L	166	Tox	1,407	2,814	Tox
Zinc, total	μg/L	equation	Tox	equation	equation	Tox

The CS, MS, and FAV vary with total hardness and are calculated using the following equations:

The CS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.7615)

The MS in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+0.8604)

The FAV in μg/L shall not exceed: exp.(0.8473[ln(total hardness mg/L)]+1.5536)

Where: exp. is the natural antilogarithm (base e) of the expression in parenthesis.

For hardness values greater than 400 mg/L, 400 mg/L shall be used to calculate the standard.

Example of total zinc standards for five total hardness values:

	TH in mg/L	50	100	200	300	400
	_
	Zinc, total
	CS μg/L	59	106	191	269	343
	MS μg/L	65	117	211	297	379
	FAV μg/L	130	234	421	594	758

Subp. 4a.

Narrative eutrophication standards for class 2B lakes, shallow lakes, and reservoirs.

A.

Eutrophication standards applicable to lakes, shallow lakes, and reservoirs that lie on the border between two ecoregions or that are in the Red River Valley (also referred to as Lake Agassiz Plains), Northern Minnesota Wetlands, or Driftless Area Ecoregion must be applied on a case-by-case basis. The commissioner shall use the standards applicable to adjacent ecoregions as a guide.

B.

Eutrophication standards are compared to summer-average data. Exceedance of the total phosphorus and either the chlorophyll-a or Secchi disk transparency standard is required to indicate a polluted condition.

C.

It is the policy of the agency to protect all lakes, shallow lakes, and reservoirs from the undesirable effects of cultural eutrophication. Lakes, shallow lakes, and reservoirs with a baseline quality better than the numeric eutrophication standards in subpart 4 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources, and the protection of lake, shallow lake, and reservoir resources, including, but not limited to:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

D.

Lakes, shallow lakes, and reservoirs with a baseline quality that is poorer than the numeric eutrophication standards in subpart 4 must be considered to be in compliance with the standards if the baseline quality is the result of natural causes. The commissioner shall determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

E.

When applied to reservoirs, the eutrophication standards in this subpart and subpart 4 may be modified on a site-specific basis to account for characteristics of reservoirs that can affect trophic status, such as water temperature, variations in hydraulic residence time, watershed size, and the fact that reservoirs may receive drainage from more than one ecoregion. Information supporting a site-specific standard can be provided by the commissioner or by any person outside the agency. The commissioner shall evaluate all data in support of a modified standard and determine whether a change in the standard for a specific reservoir is justified. Any total phosphorus effluent limit determined to be necessary based on a modified standard shall only be required after the discharger has been given notice of the specific proposed effluent limits and an opportunity to request a hearing as provided in part 7000.1800.

Subp. 4b.

Narrative eutrophication standards for class 2B rivers and streams.

A.

Eutrophication standards for rivers and streams are compared to summer-average data or as specified in subpart 4. Exceedance of the total phosphorus levels and chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels is required to indicate a polluted condition.

B.

Rivers and streams that exceed the phosphorus levels but do not exceed the chlorophyll-a (seston), five-day biochemical oxygen demand (BOD₅), diel dissolved oxygen flux, or pH levels meet the eutrophication standard.

C.

A polluted condition also exists when the chlorophyll-a (periphyton) concentration exceeds 150 mg/m² more than one year in ten

D.

It is the policy of the agency to protect all rivers, streams, and navigational pools from the undesirable effects of cultural eutrophication. Rivers, streams, and navigational pools with a baseline quality better than the numeric eutrophication standards in subpart 4 must be maintained in that condition through the strict application of all relevant federal, state, and local requirements governing antidegradation, the discharge of nutrients from point and nonpoint sources, including:

(1)

the antidegradation requirements in parts 7050.0250 to 7050.0335;

(2)

the phosphorus effluent limits for point sources, where applicable in chapter 7053;

(3)

the requirements for feedlots in chapter 7020;

(4)

the requirements for individual sewage treatment systems in chapter 7080;

(5)

the requirements for control of stormwater in chapter 7090;

(6)

county shoreland ordinances; and

(7)

implementation of mandatory and voluntary best management practices to minimize point and nonpoint sources of nutrients.

E.

Rivers, streams, and navigational pools with a baseline quality that does not meet the numeric eutrophication standards in subpart 4 are in compliance with the standards if the baseline quality is the result of natural causes. The commissioner must determine baseline quality and compliance with these standards using data and the procedures in part 7050.0150, subpart 5.

Subp. 4c.

Beneficial use definitions for lotic warm or cool water aquatic life and habitats (class 2B).

A.

Subitems (1) to (5) apply to the beneficial uses in items B to D:

(1)

The designation and attainment of beneficial uses are based on the criteria in subpart 4d.

(2)

The attributes of species composition, diversity, and functional organization are measured using:

(a)

the fish IBI as defined in Fish Data Collection Protocols for Lotic Waters in Minnesota (2017); or

(b)

the macroinvertebrate IBI as defined in Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota (2017).

(3)

Water body types for streams and rivers are defined in the documents referenced in subitem (2).

(4)

The following documents are incorporated by reference and are not subject to frequent change:

(a)

Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(b)

Fish Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking;

(c)

Macroinvertebrate Data Collection Protocols for Lotic Waters in Minnesota, Minnesota Pollution Control Agency (2017). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking; and

(d)

Development of Biological Criteria for Tiered Aquatic Life Uses, Minnesota Pollution Control Agency (2016). The document is available on the agency's website at www.pca.state.mn.us/regulations/minnesota-rulemaking.

(5)

The beneficial use subclass designators "e," "g," and "m" are added to the class 2B designator as specific additional designators. The additional subclass designators do not replace the class 2B designator. All requirements for class 2B warm or cool water stream and river habitats in parts 7050.0222 and 7052.0100 continue to apply in addition to requirements for class 2Be, class 2Bg, or class 2Bm warm or cool water stream and river habitats in part 7050.0222. These subclass designators are applied to lotic waters only.

B.

"Exceptional cool and warm water aquatic life and habitat" or "class 2Be" is a beneficial use that means waters capable of supporting and maintaining an exceptional and balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the 75th percentile of biological condition gradient level 3 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

C.

"General cool and warm water aquatic life and habitat" or "class 2Bg" is a beneficial use that means waters capable of supporting and maintaining a balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the median of biological condition gradient level 4 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

D.

"Modified cool and warm water aquatic life and habitat" or "class 2Bm" is a beneficial use that means waters capable of supporting and maintaining a balanced, integrated, adaptive community of warm or cool water aquatic organisms having a species composition, diversity, and functional organization comparable to the median of biological condition gradient level 5 as established in Calibration of the Biological Condition Gradient for Streams of Minnesota, Gerritsen et al. (2012).

(1)

To meet the definition in this item, waters must have been the subject of a use attainability analysis where it is determined that attainment of the class 2Bg beneficial use is not feasible because of human-induced modifications of the physical habitat. These modifications must be the result of direct alteration to the channel, such as drainageway maintenance, bank stabilization, and impoundments.

(2)

Examples of class 2Bm waters are the stream channel modification activities regulated under:

(a)

sections 401 and 404 of the Clean Water Act; or

(b)

Minnesota Statutes, chapter 103E.

Subp. 4d.

Biological criteria for lotic warm or cool water aquatic life and habitats (class 2B).

Water Body Type	Tier	Class	Assemblage	Biocriterion
_
Southern rivers	Exceptional	2Be	Fish	71
	General	2Bg	Fish	49
Southern streams	Exceptional	2Be	Fish	66
	General	2Bg	Fish	50
	Modified	2Bm	Fish	35
Southern headwaters	Exceptional	2Be	Fish	74
	General	2Bg	Fish	55
	Modified	2Bm	Fish	33
Northern rivers	Exceptional	2Be	Fish	67
	General	2Bg	Fish	38
Northern streams	Exceptional	2Be	Fish	61
	General	2Bg	Fish	47
	Modified	2Bm	Fish	35
Northern headwaters	Exceptional	2Be	Fish	68
	General	2Bg	Fish	42
	Modified	2Bm	Fish	23
Low gradient	Exceptional	2Be	Fish	70
	General	2Bg	Fish	42
	Modified	2Bm	Fish	15
Northern forest rivers	Exceptional	2Be	Macroinvertebrates	77
	General	2Bg	Macroinvertebrates	49
Prairie and southern forest rivers	Exceptional	2Be	Macroinvertebrates	63
	General	2Bg	Macroinvertebrates	31
High-gradient northern forest streams	Exceptional	2Be	Macroinvertebrates	82
	General	2Bg	Macroinvertebrates	53
Low-gradient northern forest streams	Exceptional	2Be	Macroinvertebrates	76
	General	2Bg	Macroinvertebrates	51
	Modified	2Bm	Macroinvertebrates	37
High-gradient southern streams	Exceptional	2Be	Macroinvertebrates	62
	General	2Bg	Macroinvertebrates	37
	Modified	2Bm	Macroinvertebrates	24
Low-gradient southern forest streams	Exceptional	2Be	Macroinvertebrates	66
	General	2Bg	Macroinvertebrates	43
	Modified	2Bm	Macroinvertebrates	30
Low-gradient prairie streams	Exceptional	2Be	Macroinvertebrates	69
	General	2Bg	Macroinvertebrates	41
	Modified	2Bm	Macroinvertebrates	22

The biological criteria for lotic warm or cool water aquatic life and habitats (class 2B) are applicable to perennial and intermittent waters that allow for colonization of fish or macroinvertebrates.

Subp. 5.

[Repealed, 42 SR 441]

Subp. 6.

Class 2D waters; wetlands.

A.

The quality of class 2D wetlands shall be such as to permit propagation and maintenance of a healthy community of aquatic and terrestrial species indigenous to wetlands, and their habitats. Wetlands also add to the biological diversity of the landscape. These waters shall be suitable for boating and other forms of aquatic recreation for which the wetland may be usable. The standards for class 2B waters listed under subpart 4 shall apply to these waters except as listed below:

Substance, Characteristic, or Pollutant	Class 2D standard
Oxygen, dissolved	If background is less than 5.0 mg/L as a daily minimum, maintain background
pH	Maintain background
Temperature	Maintain background
Chloride (Cl)	If background is greater than the class 2B chloride standard, maintain background
Settleable solids	Must not be allowed in concentrations sufficient to create significant adverse impacts on aquatic life

B.

"Maintain background," as used in this subpart, means the concentration of the water quality substances, characteristics, or pollutants shall not deviate from the range of natural background concentrations or conditions such that there is a potential significant adverse impact to the designated uses.

C.

Activities in wetlands which involve the normal farm practices of planting with annually seeded crops or the utilization of a crop rotation seeding of pasture grasses or legumes, including the recommended applications of fertilizer and pesticides, are excluded from the standards in this subpart and the wetland standards in item A and parts 7050.0225, subpart 2, and 7050.0227. All other activities in these wetlands must meet water quality standards.

Subp. 7.

Additional standards; class 2 waters.

The following additional standards and requirements apply to all class 2 waters.

A.

No sewage, industrial waste, or other wastes from point or nonpoint sources shall be discharged into any of the waters of this category so as to cause any material change in any other substances, characteristics, or pollutants which may impair the quality of the waters of the state or the aquatic biota of any of the classes in subparts 2 to 6 or in any manner render them unsuitable or objectionable for fishing, fish culture, or recreational uses. Additional selective limits or changes in the discharge bases may be imposed on the basis of local needs.

B.

To prevent acutely toxic conditions, concentrations of toxic pollutants from point or nonpoint sources must not exceed the FAV as a one-day average at the point of discharge or in the surface water consistent with parts 7050.0210, subpart 5, item D; 7053.0215, subpart 1; 7053.0225, subpart 6; and 7053.0245, subpart 1.

If a discharge is composed of a mixture of more than one chemical, and the chemicals have the same mode of toxic action, the commissioner has the option to apply an additive model to determine the toxicity of the mixture using the following equation:

C 1 _	+	C 2 _	+	.	+	C n _	equals a value of one or more, an
FAV1		FAV2				FAVn	acutely toxic condition if indicated

where:	C1 .... Cn is the concentration of the first to the nth toxicant.
	FAV1 .... FAVn is the FAV for the first to the nth toxicant.

C.

To prevent chronically toxic conditions, concentrations of toxic pollutants must not exceed the applicable CS or CC and MS or MC in surface waters outside allowable mixing zones as described in part 7050.0210, subpart 5. The CS or CC and MS or MC will be averaged over the following durations: the MS or MC will be a one-day average; the CS or CC, based on toxicity to aquatic life, will be a four-day average; and the CS or CC, based on human health and applied in water or wildlife toxicity, will be a 30-day average.

D.

Concentrations of noncarcinogenic or nonlinear carcinogenic (NLC) chemicals in water or fish tissue from point or nonpoint sources, singly or in mixtures, must be below levels expected to produce known adverse effects. This is accomplished through the application of an additive noncancer health risk index using common health risk index endpoints or health endpoints. Mixtures of chemicals with listed CS or site-specific CC are evaluated using the following approach:

Chemicals must be grouped according to medium (water or fish) and each health endpoint. Chemicals for which no health endpoint is specified are not grouped. Chemicals that are also linear carcinogens must be grouped as described under item E. Using the following equation, a noncancer health risk index must be determined for each group of two or more chemicals that have a common health endpoint listed in this part. To meet the protection objectives in part 7050.0217, the noncancer health risk index must not exceed a value of one.

Noncancer health risk index by common health endpoint	=	C 1 _	+	C 2 _	+ ... +	C n _	≤ 1
		CS1 or CC1		CS2 or CC2		CSn or CCn

where:	Cn is the concentration of the first to the nth chemical by common health endpoint and medium
	CS1 ... CSn is the drinking water plus fish consumption and recreation chronic standard (CSdfr or CSdev), fish consumption and recreation chronic standard (CSfr), or fish tissue chronic standard (CSft) for the first to nth chemical by common health endpoint
	CC1 ... CCn is the drinking water plus fish consumption and recreation chronic criterion (CCdfr or CCdev), fish consumption and recreation chronic criterion (CCfr), or fish tissue chronic criterion (CCft) for the first to nth chemical by common health endpoint

E.

Concentrations of carcinogenic chemicals from point or nonpoint sources, singly or in mixtures, must not exceed an incremental or additional excess risk level of one in 100,000 (10^-5) in surface waters or fish tissue. Carcinogenic chemicals will be considered additive in their effect according to the following equation unless an alternative model is supported by available scientific evidence. The additive equation applies to chemicals that have a human health-based chronic standard (CS) or site-specific chronic criterion (CC) calculated with a cancer potency slope factor. To meet the protection objectives in part 7050.0217, the cancer health risk index must not exceed a value of one.

Cancer health risk index	=	C 1 _	+	C 2 _	+ ... +	C n _	≤ 1
		CS1 or CC1		CS2 or CC2		CSn or CCn

where:	C1 .... Cn is the concentration of the first to the nth carcinogen in water or fish tissue
	CS1 ... CSn is the drinking water plus fish consumption and recreation chronic standard (CSdfr), fish consumption and recreation chronic standard (CSfr), or fish tissue chronic standard (CSft) for the first to nth carcinogenic chemical
	CC1 .... CCn is the drinking water plus fish consumption and recreation chronic criterion (CCdfr) fish consumption and recreation chronic criterion (CCfr), or fish tissue chronic criterion (CCft) for the first to nth carcinogenic chemical

F.

When monitoring indicates that chemical breakdown products or environmental degradates are present in surface water or fish tissue, those products must be considered when meeting the objectives for toxic pollutants in part 7050.0217. When no human health-based CS or other MDH health-based guidance is available for the chemical breakdown product, the CS or CC for the parent chemical must be applied for that product. The parent CS or CC must also be applied to evaluate mixtures of chemicals.

G.

This item applies to maximum standards (MS), final acute values (FAV), and double dashes (--) in this part and part 7050.0220 marked with an asterisk (*). For carcinogenic or highly bioaccumulative chemicals with BCFs greater than 5,000 or log K_ow values greater than 5.19, the human health-based chronic standard (CS) may be two or more orders of magnitude smaller than the acute toxicity-based MS.

If the ratio of the MS to the CS is greater than 100, the CS times 100 must be substituted for the applicable MS, and the CS times 200 must be substituted for the applicable FAV. Any effluent limit derived using the procedures of this item must only be required after the discharger has been given notice of the specific proposed effluent limits and an opportunity to request a hearing as provided in part 7000.1800.

Subp. 8.

[Repealed, 32 SR 1699]

Subp. 9.

Conversion factors for dissolved metal standards.

Metal	Conversion Factor for CS	Conversion Factor for MS and FAV
Cadmium	0.909 1.1017-[(ln TH, mg/L) (0.0418)]	0.946 1.1367-[(ln TH, mg/L) (0.0418)]
Chromium +3	0.860	0.316
Chromium +6	0.962	0.982
Copper	0.960	0.960
Lead	0.791 1.4620-[(ln TH, mg/L) (0.1457)]	0.791 1.4620-[(ln TH, mg/L) (0.1457)]
Mercury	1.0	0.850
Nickel	0.997	0.998
Silver	0.850	0.850
Zinc	0.986	0.978

Conversion factors for cadmium and lead are hardness (TH) dependent. The factors shown in the table above are for a total hardness of 100 mg/L only. Conversion factors for cadmium and lead for other hardness values shall be calculated using the equations included in the table. The dissolved standard is the total standard times the conversion factor.

Statutory Authority:

MS s 14.06; 115.03; 115.44; 116.07

History:

18 SR 2195; 19 SR 1310; 24 SR 1105; 27 SR 1217; 32 SR 1699; 39 SR 154; 39 SR 1344; 18 SR 2195; 19 SR 1310; 24 SR 1105; 27 SR 1217; 32 SR 1699; 39 SR 154; 39 SR 1344; 41 SR 545; 18 SR 2195; 19 SR 1310; 24 SR 1105; 27 SR 1217; 32 SR 1699; 39 SR 154; 39 SR 1344; 41 SR 545; 42 SR 441; 46 SR 5

Published Electronically:

July 20, 2023