Ala. Admin. Code r. 335-6-10-.07
(1) The U.S. Environmental Protection Agency has listed the chemical constituents given in Table 1 of this rule as toxic pollutants pursuant to Section 307(a)(1) of the Federal Water Pollution Control Act (FWPCA). Concentrations of these toxic pollutants in State waters shall not exceed the criteria indicated in Table 1 of this rule to the extent commensurate with the designated usage of such waters.
(a) The freshwater and marine aquatic life criteria for certain pollutants are dependent on hardness or pH. For these pollutants, the criteria are given by the following equations. In the hardness-dependent equations for metals, a conversion factor converts the total recoverable value to a criterion expressed as the dissolved fraction in the water column. All numeric values listed for metals in Table 1 of this rule are expressed as dissolved metals unless otherwise noted.
1. Cadmium
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(0.9789 [ln(hardness in mg/l as CaCO3)]-3.866)(CF); (Eq. 1)
conversion factor (CF) = 1.136672 - [ln(hardness)(0.041838)]
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(0.7977 [ln(hardness in mg/l as CaCO3)]-3.909)(CF); (Eq. 2)
conversion factor (CF) = 1.101672 - [ln(hardness)(0.041838)]
2. Chromium (trivalent)
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(0.8190[ln(hardness in mg/l as CaCO3)]+3.7256)(CF); (Eq. 3)
conversion factor (CF) = 0.316
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(0.8190[ln(hardness in mg/l as CaCO3)]+0.6848)(CF); (Eq. 4)
conversion factor (CF) = 0.860
3. Copper
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(0.9422[ln(hardness in mg/l as CaCO3)]-1.700)(CF); (Eq. 5)
conversion factor (CF) = 0.960
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(0.8545[ln(hardness in mg/l as CaCO3)]-1.702)(CF); (Eq. 6)
conversion factor (CF) = 0.960
4. Lead
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(1.273[ln(hardness in mg/l as CaCO3)]-1.460)(CF); (Eq. 7)
conversion factor (CF) = 1.46203 - [ln(hardness)(0.145712)]
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(1.273[ln(hardness in mg/l as CaCO3)]-4.705)(CF); (Eq. 8)
conversion factor (CF) = 1.46203 - [ln(hardness)(0.145712)]
5. Nickel
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(0.8460[ln(hardness in mg/l as CaCO3)]+2.255)(CF); (Eq. 9)
conversion factor (CF) = 0.998
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(0.8460[ln(hardness in mg/l as CaCO3)]+0.0584)(CF); (Eq. 10)
conversion factor (CF) = 0.997
6. Pentachlorophenol
(i) freshwater acute aquatic life:
conc. μg/l = e[1.005(pH)-4.869] (Eq. 11)
(ii) freshwater chronic aquatic life:
conc. μg/l = e[1.005(pH)-5.134](Eq. 12)
7. Silver
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(1.72[ln(hardness in mg/l as CaCO3)]-6.59)(CF); (Eq. 13)
conversion factor (CF) = 0.85
8. Zinc
(i) freshwater acute aquatic life:
conc. (μg/l) = (e(0.8473[ln(hardness in mg/l as CaCO3)]+0.884)(CF); (Eq. 14)
conversion factor (CF) = 0.978
(ii) freshwater chronic aquatic life:
conc. (μg/l) = (e(0.8473[ln(hardness in mg/l as CaCO3)]+0.884)(CF); (Eq. 15)
conversion factor (CF) = 0.986
(d) Except as noted in Table 1 of this rule, two human health criteria are provided for each pollutant--a criterion for consumption of water and fish, and a criterion for consumption of fish only. For certain pollutants, the human health criterion for consumption of water and fish may represent a maximum contaminant level (MCL) developed under the Safe Drinking Water Act.
1. For pollutants classified by the U.S. Environmental Protection Agency as non-carcinogens, the criteria shall be given by the following equations, except where numeric values are given in Table 1 of this rule.
(i) Consumption of water and fish:
conc. (mg/l) = (HBW x RfD x RSC)/[(FCR x BCF) + WCR] (Eq. 16)
(ii) Consumption of fish only:
conc. (mg/l) = (HBW x RfD x RSC)/(FCR x BCF) (Eq. 17)
where (in Equations 16 and 17):
HBW = human body weight, set at 70 kg
RfD = reference dose, in mg/(kg-day)
RSC = relative source contribution
FCR = fish consumption rate, set at 0.030 kg/day
BCF = bioconcentration factor, in l/kg
WCR = water consumption rate, set at 2 l/day
2. For pollutants classified by the U.S. Environmental Protection Agency as carcinogens, the criteria shall be given by the following equations, except where numeric values are given in Table 1 of this rule.
(i) Consumption of water and fish:
conc. (mg/l) = (HBW x RL)/(CPF x [(FCR x BCF) + WCR]) (Eq. 18)
(ii) Consumption of fish only:
conc. (mg/l) = (HBW x RL)/(CPF x FCR x BCF) (Eq. 19)
where (in Equations 18 and 19):
HBW = human body weight, set at 70 kg
RL = risk level, set at 1 x 10-6 (except for arsenic which is set at 1 x 10-5)
CPF = cancer potency factor, in (kg-day)/mg
FCR = fish consumption rate, set at 0.030 kg/day
BCF = bioconcentration factor, in l/kg
WCR = water consumption rate, set at 2 l/day
(g) Numeric criteria may be computed by the Department from equations 16, 17, 18, and 19 using values for the reference dose (RfD), relative source contribution (RSC), cancer potency factor (CPF), and bioconcentration factor (BCF) determined by the Department in consultation with the Alabama Department of Public Health after review of information available from sources other than the U.S. Environmental Protection Agency's Integrated Risk Information System (IRIS) or ambient water quality criteria documents. Such criteria, or the RfD, RSC, CPF, and BCF values used to compute criteria, shall not be effective until adopted following established rulemaking procedures.
Table 1
Toxic Pollutant Criteria
| Aquatic Life Criteria (in µg/l unless otherwise noted) | Human Health Criteria (in µg/l unless otherwise noted) | ||||||
| Pollutant | Freshwater Acute | Freshwater Chronic | Marine Acute | Marine Chronic | Consumption of Water and Fish | Consumption of Fish Only | |
| Acenaphthene | Eq. 16 | Eq. 17 | |||||
| Acrolein | 3 | 3 | Eq. 16 | Eq. 17 | |||
| Acrylonitrile 1 | Eq. 18 | Eq. 19 | |||||
| Aldrin 1 | 3.0 | 1.3 | Eq. 18 | Eq. 19 | |||
| Anthracene | Eq. 16 | Eq. 17 | |||||
| Antimony | Eq. 16 | Eq. 17 | |||||
| Arsenic 1 (Risk level = 1 x 10‑5) | 340 (tri) | 150 (tri) | 69 (tri) | 36 (tri) | Eq. 18 | Eq. 19 | |
| Asbestos | 7,000,000 fibers/l (MCL) | ||||||
| Benzene 1 | Eq. 18 | Eq. 19 | |||||
| Benzidine 1 | Eq. 18 | Eq. 19 | |||||
| Benzo(a)anthracene 1 | Eq. 18 | Eq. 19 | |||||
| Benzo(a)pyrene 1 | Eq. 18 | Eq. 19 | |||||
| Benzo(b)fluoranthene 1 | Eq. 18 | Eq. 19 | |||||
| Benzo(k)fluoranthene 1 | Eq. 18 | Eq. 19 | |||||
| Bis(2‑chloroethyl)ether 1 | Eq. 18 | Eq. 19 | |||||
| Bis(2‑chloroisopropyl)ether | Eq. 16 | Eq. 17 | |||||
| Bis(2‑ethylhexyl)phthalate 1 | Eq. 18 | Eq. 19 | |||||
| Bromoform 1 | Eq. 18 | Eq. 19 | |||||
| Butylbenzyl phthalate | Eq. 16 | Eq. 17 | |||||
| Cadmium | Eq. 1 | Eq. 2 | 33 | 7.9 | |||
| Carbaryl | 2.1 | 2.1 | 1.6 | ||||
| Carbon tetrachloride 1 | Eq. 18 | Eq. 19 | |||||
| Chlordane 1 | 2.4 | 0.0043 | 0.09 | 0.004 | Eq. 18 | Eq. 19 | |
| Chlorine | 19 | 11 | 13 | 7.5 | |||
| Chlorobenzene | Eq. 16 | Eq. 17 | |||||
| Chlorodibromomethane 1 | Eq. 18 | Eq. 19 | |||||
| Chloroform 1 | Eq. 18 | Eq. 19 | |||||
| 2‑Chloronaphthalene | Eq. 16 | Eq. 17 | |||||
| 2‑Chlorophenol | Eq. 16 | Eq. 17 | |||||
| Chlorpyrifos | 0.083 | 0.041 | 0.011 | 0.0056 | |||
| Chromium (trivalent) | Eq. 3 | Eq. 4 | |||||
| Chromium (hexavalent) | 16 | 11 | 1100 | 50 | |||
| Chrysene 1 | Eq. 18 | Eq. 19 | |||||
| Copper | Eq. 5 | Eq. 6 | 4.8 | 3.1 | 1300 (MCL) | ||
| Cyanide (free) | 22 | 5.2 | 1.0 | 1.0 | Eq. 16 | Eq. 17 | |
| 4,4'‑DDD 1 | Eq. 18 | Eq. 19 | |||||
| 4,4'‑DDE 1 | Eq. 18 | Eq. 19 | |||||
| 4,4'‑DDT 1 | 1.1 | 0.001 | 0.13 | 0.001 | Eq. 18 | Eq. 19 | |
| Diazinon | 0.17 | 0.17 | 0.82 | 0.82 | |||
| Dibenzo(a,h)anthracene 1 | Eq. 18 | Eq. 19 | |||||
| 1,2‑Dichlorobenzene | Eq. 16 | Eq. 17 | |||||
| 1,3‑Dichlorobenzene | Eq. 16 | Eq. 17 | |||||
| 1,4‑Dichlorobenzene | Eq. 16 | Eq. 17 | |||||
| 3,3'‑Dichlorobenzidine 1 | Eq. 18 | Eq. 19 | |||||
| Dichlorobromomethane 1 | Eq. 18 | Eq. 19 | |||||
| 1,2‑Dichloroethane 1 | Eq. 18 | Eq. 19 | |||||
| 1,1‑Dichloroethylene | Eq. 16 | Eq. 17 | |||||
| 2,4‑Dichlorophenol | Eq. 16 | Eq. 17 | |||||
| 1,2 Dichloropropane 1 | Eq. 18 | Eq. 19 | |||||
| 1,3 Dichloropropylene 1 | Eq. 18 | Eq. 19 | |||||
| Dieldrin 1 | 0.24 | 0.056 | 0.71 | 0.0019 | Eq. 18 | Eq. 19 | |
| 2,4‑Dimethylphenol | Eq. 16 | Eq. 17 | |||||
| Diethyl phthalate | Eq. 16 | Eq. 17 | |||||
| Dimethyl phthalate | Eq. 16 | Eq. 17 | |||||
| Di‑n‑butyl phthalate | Eq. 16 | Eq. 17 | |||||
| 4,6‑Dinitro‑2‑methylphenol | Eq. 16 | Eq. 17 | |||||
| 2,4 Dinitrotoluene 1 | Eq. 18 | Eq. 19 | |||||
| 2,4‑Dinitrophenol | Eq. 16 | Eq. 17 | |||||
| Dioxin (2,3,7,8‑TCDD) 1 | Eq. 18 | Eq. 19 | |||||
| 1,2‑Diphenylhydrazine 1 | Eq. 18 | Eq. 19 | |||||
| Endosulfan (alpha) | 0.22 | 0.056 | 0.034 | 0.0087 | Eq. 16 | Eq. 17 | |
| Endosulfan (beta) | 0.22 | 0.056 | 0.034 | 0.0087 | Eq. 16 | Eq. 17 | |
| Endosulfan sulfate | Eq. 16 | Eq. 17 | |||||
| Endrin | 0.086 | 0.036 | 0.037 | 0.0023 | Eq. 16 | Eq. 17 | |
| Endrin aldehyde | Eq. 16 | Eq. 17 | |||||
| Ethylbenzene | Eq. 16 | Eq. 17 | |||||
| Fluoranthene | Eq. 16 | Eq. 17 | |||||
| Fluorene | Eq. 16 | Eq. 17 | |||||
| Heptachlor 1 | 0.52 | 0.0038 | 0.053 | 0.0036 | Eq. 18 | Eq. 19 | |
| Heptachlor epoxide 1 | 0.52 | 0.0038 | 0.053 | 0.0036 | Eq. 18 | Eq. 19 | |
| Hexachlorobenzene 1 | Eq. 18 | Eq. 19 | |||||
| Hexachlorobutadiene 1 | Eq. 18 | Eq. 19 | |||||
| Hexachlorocyclohexane (alpha) 1 | Eq. 18 | Eq. 19 | |||||
| Hexachlorocyclohexane (beta) 1 | Eq. 18 | Eq. 19 | |||||
| Hexachlorocyclohexane (gamma) | 0.95 | 0.16 | Eq. 16 | Eq. 17 | |||
| Hexachlorocyclopentadiene | Eq. 16 | Eq. 17 | |||||
| Hexachloroethane 1 | Eq. 18 | Eq. 19 | |||||
| Indeno (1,2,3‑cd) pyrene 1 | Eq. 18 | Eq. 19 | |||||
| Isophorone 1 | Eq. 18 | Eq. 19 | |||||
| Lead | Eq. 7 | Eq. 8 | 210 | 8.1 | |||
| Malathion | 0.1 | 0.1 | |||||
| Mercury (total recoverable) | 2.4 | 0.012 | 2.1 | 0.025 | Eq. 16 | Eq. 17 | |
| Methoxychlor | 0.03 | 0.03 | |||||
| Methyl bromide | Eq. 16 | Eq. 17 | |||||
| Methylene chloride 1 | Eq. 18 | Eq. 19 | |||||
| Mirex | 0.001 | 0.001 | |||||
| Nickel | Eq. 9 | Eq. 10 | 74 | 8.2 | Eq. 16 | Eq. 17 | |
| Nitrobenzene | Eq. 16 | Eq. 17 | |||||
| N‑Nitrosodimethylamine 1 | Eq. 18 | Eq. 19 | |||||
| N‑Nitrosodi‑n‑propylamine 1 | Eq. 18 | Eq. 19 | |||||
| N‑Nitrosodiphenylamine 1 | Eq. 18 | Eq. 19 | |||||
| Parathion | 0.065 | 0.013 | |||||
| PCB‑1016 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1221 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1232 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1242 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1248 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1254 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| PCB‑1260 1,2 | 0.014 | 0.03 | Eq. 18 | Eq. 19 | |||
| Pentachlorophenol 1 | Eq. 11 | Eq. 12 | 13 | 7.9 | Eq. 18 | Eq. 19 | |
| Phenol | Eq. 16 | Eq. 17 | |||||
| Pyrene | Eq. 16 | Eq. 17 | |||||
| Selenium3 | 20 | 5.0 | 290 | 71 | Eq. 16 | Eq. 17 | |
| Silver | Eq. 13 | 1.9 | |||||
| 1,1,2,2‑Tetrachloroethane 1 | Eq. 18 | Eq. 19 | |||||
| Tetrachloroethylene 1 | Eq. 18 | Eq. 19 | |||||
| Thallium | Eq. 16 | Eq. 17 | |||||
| Toluene | Eq. 16 | Eq. 17 | |||||
| Toxaphene 1 | 0.73 | 0.0002 | 0.21 | 0.0002 | Eq. 18 | Eq. 19 | |
| 1,2‑Trans‑dichloroethylene | Eq. 16 | Eq. 17 | |||||
| Tributyltin (TBT) | 0.46 | 0.072 | 0.42 | 0.0074 | |||
| 1,2,4‑Trichlorobenzene | Eq. 16 | Eq. 17 | |||||
| 1,1,2‑Trichloroethane 1 | Eq. 18 | Eq. 19 | |||||
| Trichloroethylene 1 | Eq. 18 | Eq. 19 | |||||
| 2,4,6‑Trichlorophenol 1 | Eq. 18 | Eq. 19 | |||||
| Vinyl chloride 1 | Eq. 18 | Eq. 19 | |||||
| Zinc | Eq. 14 | Eq. 15 | 90 | 81 | Eq. 16 | Eq. 17 |
1 Pollutants considered by EPA to be carcinogenic.
2 The criteria for Polychlorinated Biphenyls (PCBs) apply to total PCBs, which is defined as the sum of the seven particular Aroclors (1016, 1221, 1232, 1242, 1248, 1254, and 1260) listed in this table.
3 The freshwater aquatic life criteria for selenium are expressed in terms of total recoverable metal in the water column.
Author: James E. McIndoe, Chris L. Johnson
Statutory Authority: Code of Ala. 1975, §§22-22-9, 22-22A-5, 22-22A-6, 22-22A-8.
History: Originally Adopted January 24, 1990; Filed January 26 1990; effective March 2, 1990. Amended: Filed February 27, 1991; effective April 3, 1991. Amended: Filed April 23, 1992; effective May 28, 1992. Amended: Filed July 25, 1994; effective August 29, 1994. Amended (Table 1 also): Filed April 25, 1997; effective May 30, 1997. Amended: Filed August 3, 2000; effective September 7, 2000. Amended: Filed December 8, 2000; effective January 12, 2001. Amended: Filed December 10, 2004; effective January 14, 2005. Amended (Table I amended also): Filed August 17, 2005; effective September 21, 2005. Amended (Table I only): Filed April 24, 2007; effective May 29, 2007. Amended (Table 1 also): Filed April 22, 2008; effective May 27, 2008. Amended: Filed February 25, 2014; effective April 1, 2014. Amended: Filed December 7, 2016; effective February 3, 2017. Amended: Published April 30, 2025; effective June 14, 2025.