Tables: N.J.A.C. 7:9B - Surface Water Quality Standards¶
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1. Table 1¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 28
| Substance | Criteria | Classifications |
|---|---|---|
| 1. (ml) | Bacterial quality (Counts/100 | i. Shellfish Harvesting: Bacterial Indicators shall not exceed, in all shellfish waters, the standard for approved shellfish waters as established by the National Shellfish Sanitation Program as set forth in its current manual of operations. |
| ii. Primary Contact Recreation: (1) Enterococci levels shall not exceed a geometric mean of 30/100 ml over a 90-day period and a Statistical Threshold Value of 110/100 ml, which shall not be greater than 10 percent excursion frequency over a 90-day period. |
||
| (2) E. coli levels shall not exceed a geometric mean of 100/100 ml over a 90-day period and a Statistical Threshold Value of 320/100 ml, which shall not be greater than 10 percent excursion frequency over a 90-day period. | ||
| iii. Secondary Contact Recreation: (1) Fecal coliform levels shall not exceed a geometric mean of 770/100 ml. |
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| (2) Fecal coliform levels shall not exceed a geometric mean of 1500/100ml. | ||
| 2. | Dissolved oxygen (mg/L) | i. Not less than 7.0 at any time; |
| ii. 24 hour average not less than 6.0. Not less than 5.0 at any time (see paragraph viii below); |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | 1. (ml) | Bacterial quality (Counts/100 | i. Shellfish Harvesting: Bacterial Indicators shall not exceed, in all shellfish waters, the standard for approved shellfish waters as established by the National Shellfish Sanitation Program as set forth in its current manual of operations. | | | | ii. Primary Contact Recreation:(1) Enterococci levels shall not exceed a geometric mean of 30/100 ml over a 90-day period and a Statistical Threshold Value of 110/100 ml, which shall not be greater than 10 percent excursion frequency over a 90-day period. | | | | (2) E. coli levels shall not exceed a geometric mean of 100/100 ml over a 90-day period and a Statistical Threshold Value of 320/100 ml, which shall not be greater than 10 percent excursion frequency over a 90-day period. | | | | iii. Secondary Contact Recreation:
(1) Fecal coliform levels shall not exceed a geometric mean of 770/100 ml. | | | | (2) Fecal coliform levels shall not exceed a geometric mean of 1500/100ml. | | 2. | Dissolved oxygen (mg/L) | i. Not less than 7.0 at any time; | | | | ii. 24 hour average not less than 6.0. Not less than 5.0 at any time (see paragraph viii below); | 27
2. Table 2¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 29
| Substance | Criteria | Classifications |
|---|---|---|
| iii. 24 hour average not less than 5.0, but not less than 4.0 at any time (see paragraph viii below); | FW2-NT (except as in iv below), SE1 | |
| iv. Not less than 4.0 at any time; | Tidal portions of FW2-NT tributaries to the Delaware River, between Rancocas Creek and Big Timber Creek inclusive. | |
| v. Not less than 5.0 at any time; | SC | |
| vi. Not less than 4.0 at any time; | SE2 | |
| vii. Not less than 3.0 at any time; and | SE3 | |
| viii. Supersaturated dissolved oxygen values shall be expressed as their corresponding 100 percent saturation values for purposes of calculating 24 hour averages. | FW2-TM, FW2-NT, SE1 | |
| 3. Floating, colloidal, color and settleable solids; petroleum hydrocarbons and other oils and grease | i. None noticeable in the water or deposited along the shore or on the aquatic substrata in quantities detrimental to the natural biota. None which would render the waters unsuitable for the designated uses. | All Classifications |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | | iii. 24 hour average not less than 5.0, but not less than 4.0 at any time (see paragraph viii below); | FW2-NT (except as in iv below), SE1 | | | iv. Not less than 4.0 at any time; | Tidal portions of FW2-NT tributaries to the Delaware River, between Rancocas Creek and Big Timber Creek inclusive. | | | v. Not less than 5.0 at any time; | SC | | | vi. Not less than 4.0 at any time; | SE2 | | | vii. Not less than 3.0 at any time; and | SE3 | | | viii. Supersaturated dissolved oxygen values shall be expressed as their corresponding 100 percent saturation values for purposes of calculating 24 hour averages. | FW2-TM, FW2-NT, SE1 | | 3. Floating, colloidal, color and settleable solids; petroleum hydrocarbons and other oils and grease | i. None noticeable in the water or deposited along the shore or on the aquatic substrata in quantities detrimental to the natural biota. None which would render the waters unsuitable for the designated uses. | All Classifications | 283. Table 3¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 30
| Substance | Criteria | Classifications |
|---|---|---|
| 4. Nutrients | i. Except as due to natural conditions, nutrients shall not be allowed in concentrations that render the waters unsuitable for the existing or designated uses due to objectionable algal densities, nuisance aquatic vegetation, diurnal fluctuations in dissolved oxygen or pH indicative of excessive photosynthetic activity, detrimental changes to the composition of aquatic ecosystems, or other indicators of use impairment caused by nutrients. | All Classifications |
| ii. Phosphorus (mg/L)* | ||
| (1) Non Tidal Streams: Concentrations of total P shall not exceed 0.1 in any stream, unless site-specific criteria or watershed-specific translators are established pursuant to N.J.A.C. 7:9B-1.5(g)2 or if the Department determines that concentrations do not render the waters unsuitable in accordance with (d)4i. above. | FW2 | |
| (2) Lakes: Concentrations of total P shall not exceed 0.05 in any lake, pond or reservoir, or in a tributary at the point where it enters such bodies of water, unless site-specific criteria or watershed-specific translators are developed pursuant to N.J.A.C. 7:9B-1.5(g)2 or if the Department determines that concentrations do not render the waters unsuitable in accordance with (d)4i. above. | FW2 |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | 4. Nutrients | i. Except as due to natural conditions, nutrients shall not be allowed in concentrations that render the waters unsuitable for the existing or designated uses due to objectionable algal densities, nuisance aquatic vegetation, diurnal fluctuations in dissolved oxygen or pH indicative of excessive photosynthetic activity, detrimental changes to the composition of aquatic ecosystems, or other indicators of use impairment caused by nutrients. | All Classifications | | | ii. Phosphorus (mg/L)* | | | | (1) Non Tidal Streams: Concentrations of total P shall not exceed 0.1 in any stream, unless site-specific criteria or watershed-specific translators are established pursuant to N.J.A.C. 7:9B-1.5(g)2 or if the Department determines that concentrations do not render the waters unsuitable in accordance with (d)4i. above. | FW2 | | | (2) Lakes: Concentrations of total P shall not exceed 0.05 in any lake, pond or reservoir, or in a tributary at the point where it enters such bodies of water, unless site-specific criteria or watershed-specific translators are developed pursuant to N.J.A.C. 7:9B-1.5(g)2 or if the Department determines that concentrations do not render the waters unsuitable in accordance with (d)4i. above. | FW2 | 294. Table 4¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 31
| Substance | Criteria | Classifications |
|---|---|---|
| 5. pH (Standard Units) | i. 6.5-8.5 | FW2 waters listed at 1.15(d), (f), (g) and (i), All SE |
| ii. 4.5 – 7.5 | FW2 waters listed at 1.15(c), (e) and (h) | |
| iii. Natural pH conditions shall prevail. | SC | |
| 6. Radioactivity | i. Prevailing regulations including all amendments and future supplements thereto adopted by the U.S. Environmental Protection Agency pursuant to Sections 1412, 1445, and 1450 of the Public Health Services Act, as amended by the Safe Drinking Water Act (PL 93-523) | All Classifications |
| 7. Solids, Suspended (mg/L) (Non-filterable residue) | i. 25.0 | FW2-TP, FW2-TM |
| ii. 40.0 | FW2-NT | |
| iii. None of which would render the water unsuitable for the designated uses. | All SE, SC | |
| 8. Solids, Total Dissolved (mg/L) (Filterable Residue) | i. No increase in background which may adversely affect the survival, growth or propagation of the aquatic biota. Compliance with water quality-based WET limitations or LC_{50} ≥ 50 percent, whichever is more stringent, shall be deemed to meet this requirement. | FW2 |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | 5. pH (Standard Units) | i. 6.5-8.5 | FW2 waters listed at 1.15(d), (f), (g) and (i), All SE | | | ii. 4.5 – 7.5 | FW2 waters listed at 1.15(c), (e) and (h) | | | iii. Natural pH conditions shall prevail. | SC | | 6. Radioactivity | i. Prevailing regulations including all amendments and future supplements thereto adopted by the U.S. Environmental Protection Agency pursuant to Sections 1412, 1445, and 1450 of the Public Health Services Act, as amended by the Safe Drinking Water Act (PL 93-523) | All Classifications | | 7. Solids, Suspended (mg/L) (Non-filterable residue) | i. 25.0 | FW2-TP, FW2-TM | | | ii. 40.0 | FW2-NT | | | iii. None of which would render the water unsuitable for the designated uses. | All SE, SC | | 8. Solids, Total Dissolved (mg/L) (Filterable Residue) | i. No increase in background which may adversely affect the survival, growth or propagation of the aquatic biota. Compliance with water quality-based WET limitations or LC_{50} ≥ 50 percent, whichever is more stringent, shall be deemed to meet this requirement. | FW2 | 305. Table 5¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 32
| Substance | Criteria | Classifications |
|---|---|---|
| ii. No increase in background which would interfere with the designated or existing uses, or 500 mg/L, whichever is more stringent. | FW2 | |
| iii. None which would render the water unsuitable for the designated uses. | All SE | |
| 9. Sulfate (mg/L) | i. 250 | FW2 |
| 10. Taste and odor producing substances | i. None offensive to humans or which would produce offensive taste or odors in water supplies and biota used for human consumption. None which would render the water unsuitable for the designated uses. | All Classifications |
| 11. Temperature | i. Temperatures shall not exceed a daily maximum of 22 degrees Celsius or rolling seven-day average of the daily maximum of 19 degrees Celsius, unless due to natural conditions | FW2-TP |
| ii. Temperatures shall not exceed a daily maximum of 25 degrees Celsius or rolling seven-day average of the daily maximum of 23 degrees Celsius, unless due to natural conditions | FW2-TM | |
| iii. Temperatures shall not exceed a daily maximum of 31 degrees Celsius or rolling seven-day average of the daily maximum of 28 degrees Celsius, unless due to natural conditions | FW2-NT | |
| iv. No thermal alterations which would cause temperatures to exceed 29.4 degrees Celsius (85 degree Fahrenheit) Summer seasonal average | SE |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | | ii. No increase in background which would interfere with the designated or existing uses, or 500 mg/L, whichever is more stringent. | FW2 | | | iii. None which would render the water unsuitable for the designated uses. | All SE | | 9. Sulfate (mg/L) | i. 250 | FW2 | | 10. Taste and odor producing substances | i. None offensive to humans or which would produce offensive taste or odors in water supplies and biota used for human consumption. None which would render the water unsuitable for the designated uses. | All Classifications | | 11. Temperature | i. Temperatures shall not exceed a daily maximum of 22 degrees Celsius or rolling seven-day average of the daily maximum of 19 degrees Celsius, unless due to natural conditions | FW2-TP | | | ii. Temperatures shall not exceed a daily maximum of 25 degrees Celsius or rolling seven-day average of the daily maximum of 23 degrees Celsius, unless due to natural conditions | FW2-TM | | | iii. Temperatures shall not exceed a daily maximum of 31 degrees Celsius or rolling seven-day average of the daily maximum of 28 degrees Celsius, unless due to natural conditions | FW2-NT | | | iv. No thermal alterations which would cause temperatures to exceed 29.4 degrees Celsius (85 degree Fahrenheit) Summer seasonal average | SE | 316. Table 6¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 33
| Substance | Criteria | Classifications |
|---|---|---|
| 12. Toxic Substances (general) | v. No thermal alterations which would cause temperatures to exceed 26.7 degrees Celsius (80 degree Fahrenheit) Summer seasonal average | SC |
| i. None, either alone or in combination with other substances, in such concentrations as to affect humans or be detrimental to the natural aquatic biota, produce undesirable aquatic life, or which would render the waters unsuitable for the designated uses. | All Classifications | |
| ii. None which would cause standards for drinking water to be exceeded after appropriate treatment. | FW2 | |
| iii. Toxic substances shall not be present in concentrations that cause acute or chronic toxicity to aquatic biota, or bioaccumulate within an organism to concentrations that exert a toxic effect on that organism or render it unfit for consumption. | All Classifications | |
| iv. The concentrations of nonpersistent toxic substances in the State's waters shall not exceed one-twentieth (0.05) of the acute definitive LC_{50} or EC_{50} value, as determined by appropriate bioassays conducted in accordance with N.J.A.C. 7:18. | All Classifications | |
| v. The concentration of persistent toxic substances in the State's waters shall not exceed one-hundredth (0.01) of the acute definitive LC_{50} or EC_{50} value, as determined by appropriate bioassays conducted in accordance with N.J.A.C. 7:18. | All Classifications |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | 12. Toxic Substances (general) | v. No thermal alterations which would cause temperatures to exceed 26.7 degrees Celsius (80 degree Fahrenheit) Summer seasonal average | SC | | | i. None, either alone or in combination with other substances, in such concentrations as to affect humans or be detrimental to the natural aquatic biota, produce undesirable aquatic life, or which would render the waters unsuitable for the designated uses. | All Classifications | | | ii. None which would cause standards for drinking water to be exceeded after appropriate treatment. | FW2 | | | iii. Toxic substances shall not be present in concentrations that cause acute or chronic toxicity to aquatic biota, or bioaccumulate within an organism to concentrations that exert a toxic effect on that organism or render it unfit for consumption. | All Classifications | | | iv. The concentrations of nonpersistent toxic substances in the State's waters shall not exceed one-twentieth (0.05) of the acute definitive LC_{50} or EC_{50} value, as determined by appropriate bioassays conducted in accordance with N.J.A.C. 7:18. | All Classifications | | | v. The concentration of persistent toxic substances in the State's waters shall not exceed one-hundredth (0.01) of the acute definitive LC_{50} or EC_{50} value, as determined by appropriate bioassays conducted in accordance with N.J.A.C. 7:18. | All Classifications | 327. Table 7¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 34
| Substance | Criteria | Classifications |
|---|---|---|
| 13. Turbidity (Nephelometric Turbidity Unit-NTU) | i. Maximum 30-day average of 15 NTU, a maximum of 50 NTU at any time. | FW2, SE3 |
| ii. Maximum 30-day average of 10 NTU, a maximum of 30 NTU at any time. | SE1, SE2 | |
| iii. Levels shall not exceed 10.0 NTU. | SC |
Source context and notes
7:9B-1.14(d) General Surface Water Quality Criteria for FW2, SE and SC Waters: (Expressed as Maximum concentrations unless otherwise noted) | Substance | Criteria | Classifications | | --- | --- | --- | | 13. Turbidity (Nephelometric Turbidity Unit-NTU) | i. Maximum 30-day average of 15 NTU, a maximum of 50 NTU at any time. | FW2, SE3 | | | ii. Maximum 30-day average of 10 NTU, a maximum of 30 NTU at any time. | SE1, SE2 | | | iii. Levels shall not exceed 10.0 NTU. | SC | * See N.J.A.C. 7:9B-1.14(g) for site-specific criteria. 338. Table 8¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 35
| CAS Number | Criteria | Classification |
|---|---|---|
| 1. Ammonia, un-ionized (mg NH₃-N/L) 7664-41-7 | i. at pH < 8.30 0.23810⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (acute) 0.06110⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (chronic) |
PL |
| ii. 0.115 (acute); 0.030 (chronic) | All SE | |
| iii. 0.094 (acute); 0.024 (chronic) | SC |
Source context and notes
(e) Surface Water Quality Criteria for Ammonia are derived in accordance with the formulas set forth below. Acute criteria are expressed as three-hour average using MA1CD10 flow and chronic criteria are expressed as 30-day average using MA30CD10 flow. No exceedance of criteria shall be permitted at or above the design flows specified. | CAS Number | Criteria | Classification | | --- | --- | --- | | 1. Ammonia, un-ionized (mg NH₃-N/L) 7664-41-7 | i. at pH < 8.300.238*10⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (acute)
0.061*10⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (chronic) | PL | | | ii. 0.115 (acute); 0.030 (chronic) | All SE | | | iii. 0.094 (acute); 0.024 (chronic) | SC | 2. Ammonia, Total (mg TAN/L) - Acute criteria are expressed as one-hour average using MA1CD10 flow, chronic criteria are expressed as 30-day rolling average using MA30CD10 flow and the highest four-day average within the 30-day averaging period should not be more than 2.5 times of chronic criteria. No exceedance of criteria shall be permitted at or above the design flows specified. | CAS Number | Criteria applicable in FW2 waters | Classifications | | --- | --- | --- | | 3. Ammonia, total (mg TAN/L) 7664-41-7 | i. MIN $\left(\frac{0.275}{1 + 10^{7.204 - pH}} + \frac{39.0}{1 + 10^{pH - 7.204}}\right),$ $\left(0.7249 \times \left(\frac{0.0114}{1 + 10^{7.204 - pH}} + \frac{1.6181}{1 + 10^{pH - 7.204}}\right) \times (23.12 \times 10^{0.036 \times (20 - T)})\right)$ (acute) ii. 0.7249 $\times \left(\frac{0.0114}{1 + 10^{7.204 - pH}} + \frac{1.6181}{1 + 10^{pH - 7.204}}\right) \times MIN\left(51.93,23.12 \times 10^{0.036 \times (20 - T)}\right)$ (acute)
9. Table 9¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 35
| CAS Number | Criteria applicable in FW2 waters | Classifications |
|---|---|---|
Source context and notes
| CAS Number | Criteria | Classification | | --- | --- | --- | | 1. Ammonia, un-ionized (mg NH₃-N/L) 7664-41-7 | i. at pH < 8.300.238*10⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (acute)
0.061*10⁰.⁰²⁶(Temp-20) + 0.41 (pH-7.80) (chronic) | PL | | | ii. 0.115 (acute); 0.030 (chronic) | All SE | | | iii. 0.094 (acute); 0.024 (chronic) | SC | 2. Ammonia, Total (mg TAN/L) - Acute criteria are expressed as one-hour average using MA1CD10 flow, chronic criteria are expressed as 30-day rolling average using MA30CD10 flow and the highest four-day average within the 30-day averaging period should not be more than 2.5 times of chronic criteria. No exceedance of criteria shall be permitted at or above the design flows specified. | CAS Number | Criteria applicable in FW2 waters | Classifications | | --- | --- | --- | | 3. Ammonia, total (mg TAN/L) 7664-41-7 | i. MIN $\left(\frac{0.275}{1 + 10^{7.204 - pH}} + \frac{39.0}{1 + 10^{pH - 7.204}}\right),$ $\left(0.7249 \times \left(\frac{0.0114}{1 + 10^{7.204 - pH}} + \frac{1.6181}{1 + 10^{pH - 7.204}}\right) \times (23.12 \times 10^{0.036 \times (20 - T)})\right)$ (acute) ii. 0.7249 $\times \left(\frac{0.0114}{1 + 10^{7.204 - pH}} + \frac{1.6181}{1 + 10^{pH - 7.204}}\right) \times MIN\left(51.93,23.12 \times 10^{0.036 \times (20 - T)}\right)$ (acute) iii. 0.8876 $\times \left(\frac{0.0278}{1 + 10^{7.688 - pH}} + \frac{1.1994}{1 + 10^{pH - 7.688}}\right) \times \left(2.126 \times 10^{0.028 \times (20 - MAX(T,7))}\right)$ (chronic) | FW2-TP, FW2-TM
10. Table 10¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 38
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | Saline Water (SE & SC) Criteria | ||||
|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | ||||
| Acute | Chronic | Acute | Chronic | ||||
| Acenaphthene | 83-32-9 | 670(h) | 990(h) | ||||
| Acrolein | 107-02-8 | 6.1(h) | 9.3(h) | ||||
| Acrylonitrile | 107-13-1 | 0.051(hc) | 0.25(hc) | ||||
| Aldrin | 309-00-2 | 3.0 | 0.000049(hc) | 1.3 | 0.000050(hc) | ||
| Ammonia, un-ionized | 7664-41-7 | See N.J.A.C. 7:9B-1.14(e) | See N.J.A.C. 7:9B-1.14(e) | ||||
| Anthracene | 120-12-7 | 8,300(h) | 40,000(h) | ||||
| Antimony | 7440-36-0 | 5.6(h)(T) | 640(h)(T) | ||||
| Arsenic | 7440-38-2 | 340(d)(s) | 150(d)(s) | 0.017(hc)(T) | 69(d)(s) | 36(d)(s) | 0.061(hc)(T) |
| Asbestos | 1332-21-4 | 7x10^6fibers/L >10μm(h) | |||||
| Barium | 7440-39-3 | 2,000(h)(T) | |||||
| Benz(a)anthracene | 56-55-3 | 0.038(hc) | 0.18(hc) | ||||
| Benzene | 71-43-2 | 0.15(hc) | 3.3(hc) | ||||
| Benzidine | 92-87-5 | 0.000086(hc) | 0.00020(hc) | ||||
| 3,4-Benzofluoranthene (Benzo(b)fluoranthene) | 205-99-2 | 0.038(hc) | 0.18(hc) | ||||
| Benzo(k)fluoranthene | 207-08-9 | 0.38(hc) | 1.8(hc) | ||||
| Benzo(a)pyrene (BaP) | 50-32-8 | 0.0038(hc) | 0.018(hc) | ||||
| Beryllium | 7440-41-7 | 6.0(h)(T) | 42(h)(T) | ||||
| alpha-BHC (alpha-HCH) | 319-84-6 | 0.0026(hc) | 0.0049(hc) | ||||
| beta-BHC (beta-HCH) | 319-85-7 | 0.0091(hc) | 0.017(hc) | ||||
| gamma-BHC (gamma-HCH/Lindane) | 58-89-9 | 0.95 | 0.98(h) | 0.16 | 1.8(h) | ||
| Bis(2-chloroethyl) ether | 111-44-4 | 0.030(hc) | 0.53(hc) | ||||
| Bis(2-chloroisopropyl) ether | 108-60-1 | 1,400(h) | 65,000(h) | ||||
| Bis(2-ethylhexyl) phthalate | 117-81-7 | 1.2(hc) | 2.2(hc) | ||||
| Bromodichloromethane (Dichlorobromomethane) | 75-27-4 | 0.55(hc) | 17(hc) | ||||
| Bromoform | 75-25-2 | 4.3(hc) | 140(hc) | ||||
| Butyl benzyl phthalate | 85-68-7 | 150(h) | 190(h) | ||||
| Cadmium | 7440-43-9 | (a) | (a) | 3.4(h)(T) | 40(d)(s) | 8.8(d)(s) | 16(h)(T) |
| Carbon tetrachloride | 56-23-5 | 0.33(hc) | 2.3(hc) | ||||
| Chlordane | 57-74-9 | 2.4 | 0.0043 | 0.00010(hc) | 0.09 | 0.0040 | 0.00011(hc) |
Source context and notes
7. SURFACE WATER QUALITY CRITERIA FOR TOXIC SUBSTANCES: $(\mu \mathrm{g} / \mathrm{L})$ | Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | | | Saline Water (SE & SC) Criteria | | | | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | Acute | Chronic | | Acute | Chronic | | | Acenaphthene | 83-32-9 | | | 670(h) | | | 990(h) | | Acrolein | 107-02-8 | | | 6.1(h) | | | 9.3(h) | | Acrylonitrile | 107-13-1 | | | 0.051(hc) | | | 0.25(hc) | | Aldrin | 309-00-2 | 3.0 | | 0.000049(hc) | 1.3 | | 0.000050(hc) | | Ammonia, un-ionized | 7664-41-7 | See N.J.A.C. 7:9B-1.14(e) | | | See N.J.A.C. 7:9B-1.14(e) | | | | Anthracene | 120-12-7 | | | 8,300(h) | | | 40,000(h) | | Antimony | 7440-36-0 | | | 5.6(h)(T) | | | 640(h)(T) | | Arsenic | 7440-38-2 | 340(d)(s) | 150(d)(s) | 0.017(hc)(T) | 69(d)(s) | 36(d)(s) | 0.061(hc)(T) | | Asbestos | 1332-21-4 | | | 7x10^6fibers/L >10μm(h) | | | | | Barium | 7440-39-3 | | | 2,000(h)(T) | | | | | Benz(a)anthracene | 56-55-3 | | | 0.038(hc) | | | 0.18(hc) | | Benzene | 71-43-2 | | | 0.15(hc) | | | 3.3(hc) | | Benzidine | 92-87-5 | | | 0.000086(hc) | | | 0.00020(hc) | | 3,4-Benzofluoranthene (Benzo(b)fluoranthene) | 205-99-2 | | | 0.038(hc) | | | 0.18(hc) | | Benzo(k)fluoranthene | 207-08-9 | | | 0.38(hc) | | | 1.8(hc) | | Benzo(a)pyrene (BaP) | 50-32-8 | | | 0.0038(hc) | | | 0.018(hc) | | Beryllium | 7440-41-7 | | | 6.0(h)(T) | | | 42(h)(T) | | alpha-BHC (alpha-HCH) | 319-84-6 | | | 0.0026(hc) | | | 0.0049(hc) | | beta-BHC (beta-HCH) | 319-85-7 | | | 0.0091(hc) | | | 0.017(hc) | | gamma-BHC (gamma-HCH/Lindane) | 58-89-9 | 0.95 | | 0.98(h) | 0.16 | | 1.8(h) | | Bis(2-chloroethyl) ether | 111-44-4 | | | 0.030(hc) | | | 0.53(hc) | | Bis(2-chloroisopropyl) ether | 108-60-1 | | | 1,400(h) | | | 65,000(h) | | Bis(2-ethylhexyl) phthalate | 117-81-7 | | | 1.2(hc) | | | 2.2(hc) | | Bromodichloromethane (Dichlorobromomethane) | 75-27-4 | | | 0.55(hc) | | | 17(hc) | | Bromoform | 75-25-2 | | | 4.3(hc) | | | 140(hc) | | Butyl benzyl phthalate | 85-68-7 | | | 150(h) | | | 190(h) | | Cadmium | 7440-43-9 | (a) | (a) | 3.4(h)(T) | 40(d)(s) | 8.8(d)(s) | 16(h)(T) | | Carbon tetrachloride | 56-23-5 | | | 0.33(hc) | | | 2.3(hc) | | Chlordane | 57-74-9 | 2.4 | 0.0043 | 0.00010(hc) | 0.09 | 0.0040 | 0.00011(hc) |11. Table 11¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 39
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | Saline Water (SE & SC) Criteria | ||||
|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | ||||
| Acute | Chronic | Acute | Chronic | ||||
| Chloride | 16887-00-6 | 860,000 | 230,000 | 250,000(ol) | |||
| Chlorine Produced Oxidants (CPO) | 7782-50-5 | 19 | 11 | 13 | 7.5 | ||
| Chlorobenzene | 108-90-7 | 210(h) | 2,500(h) | ||||
| Chloroform | 67-66-3 | 68(h) | 2,100(h) | ||||
| 2-Chloronaphthalene | 91-58-7 | 1,000(h) | 1,600(h) | ||||
| 2-Chlorophenol | 95-57-8 | 81(h) | 150(h) | ||||
| Chlorpyrifos | 2921-88-2 | 0.083 | 0.041 | 0.011 | 0.0056 | ||
| Chromium | 7440-47-3 | 92(h)(T) | 750(h)(T) | ||||
| Chromium+3 | 16065-83-1 | (a) | (a) | ||||
| Chromium+6 | 18540-29-9 | 15(d)(s) | 10(d)(s) | 1,100(d)(s) | 50(d)(s) | ||
| Chrysene | 218-01-9 | 3.8(hc) | 18(hc) | ||||
| Copper* | 7440-50-8 | (a) | (a) | 1,300(h)(T) | 4.8(d)(s) | 3.1(d)(s) | |
| Cyanide (Total) | 57-12-5 | 22(fc) | 5.2(fc) | 140(h) | 2.7(fc) | 2.7(fc) | 140(h) |
| 4,4'-DDD (p,p'-TDE) | 72-54-8 | 0.00031(hc) | 0.00031(hc) | ||||
| 4,4'-DDE | 72-55-9 | 0.00022(hc) | 0.00022(hc) | ||||
| 4,4'-DDT | 50-29-3 | 1.1 | 0.0010 | 0.00022(hc) | 0.13 | 0.0010 | 0.00022(hc) |
| Demeton | 8065-48-3 | 0.1 | 0.1 | ||||
| Dibenz(a,h)anthracene | 53-70-3 | 0.0038(hc) | 0.018(hc) | ||||
| Dibromochloromethane (Chlorodibromomethane) | 124-48-1 | 0.40(hc) | 13(hc) | ||||
| Di-n-butyl phthalate | 84-74-2 | 2,000(h) | 4,500(h) | ||||
| 1,2-Dichlorobenzene | 95-50-1 | 2,000(h) | 6,200(h) | ||||
| 1,3-Dichlorobenzene | 541-73-1 | 2,200(h) | 8,300(h) | ||||
| 1,4-Dichlorobenzene | 106-46-7 | 550(h) | 2,200(h) | ||||
| 3,3'-Dichlorobenzidine | 91-94-1 | 0.021(hc) | 0.028(hc) | ||||
| 1,2-Dichloroethane | 107-06-2 | 0.29(hc) | 28(hc) | ||||
| 1,1-Dichloroethylene | 75-35-4 | 4.7(h) | 100(h) | ||||
| trans-1,2-Dichloroethylene | 156-60-5 | 590(h) | 43,000(h) | ||||
| 2,4-Dichlorophenol | 120-83-2 | 77(h) | 290(h) | ||||
| 1,2-Dichloropropane | 78-87-5 | 0.50(hc) | 15(hc) | ||||
| 1,3-Dichloropropene (cis and trans) | 542-75-6 | 0.34(hc) | 21(hc) |
Source context and notes
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | | | Saline Water (SE & SC) Criteria | | | | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | Acute | Chronic | | Acute | Chronic | | | Chloride | 16887-00-6 | 860,000 | 230,000 | 250,000(ol) | | | | | Chlorine Produced Oxidants (CPO) | 7782-50-5 | 19 | 11 | | 13 | 7.5 | | | Chlorobenzene | 108-90-7 | | | 210(h) | | | 2,500(h) | | Chloroform | 67-66-3 | | | 68(h) | | | 2,100(h) | | 2-Chloronaphthalene | 91-58-7 | | | 1,000(h) | | | 1,600(h) | | 2-Chlorophenol | 95-57-8 | | | 81(h) | | | 150(h) | | Chlorpyrifos | 2921-88-2 | 0.083 | 0.041 | | 0.011 | 0.0056 | | | Chromium | 7440-47-3 | | | 92(h)(T) | | | 750(h)(T) | | Chromium+3 | 16065-83-1 | (a) | (a) | | | | | | Chromium+6 | 18540-29-9 | 15(d)(s) | 10(d)(s) | | 1,100(d)(s) | 50(d)(s) | | | Chrysene | 218-01-9 | | | 3.8(hc) | | | 18(hc) | | Copper* | 7440-50-8 | (a) | (a) | 1,300(h)(T) | 4.8(d)(s) | 3.1(d)(s) | | | Cyanide (Total) | 57-12-5 | 22(fc) | 5.2(fc) | 140(h) | 2.7(fc) | 2.7(fc) | 140(h) | | 4,4'-DDD (p,p'-TDE) | 72-54-8 | | | 0.00031(hc) | | | 0.00031(hc) | | 4,4'-DDE | 72-55-9 | | | 0.00022(hc) | | | 0.00022(hc) | | 4,4'-DDT | 50-29-3 | 1.1 | 0.0010 | 0.00022(hc) | 0.13 | 0.0010 | 0.00022(hc) | | Demeton | 8065-48-3 | | 0.1 | | | 0.1 | | | Dibenz(a,h)anthracene | 53-70-3 | | | 0.0038(hc) | | | 0.018(hc) | | Dibromochloromethane (Chlorodibromomethane) | 124-48-1 | | | 0.40(hc) | | | 13(hc) | | Di-n-butyl phthalate | 84-74-2 | | | 2,000(h) | | | 4,500(h) | | 1,2-Dichlorobenzene | 95-50-1 | | | 2,000(h) | | | 6,200(h) | | 1,3-Dichlorobenzene | 541-73-1 | | | 2,200(h) | | | 8,300(h) | | 1,4-Dichlorobenzene | 106-46-7 | | | 550(h) | | | 2,200(h) | | 3,3'-Dichlorobenzidine | 91-94-1 | | | 0.021(hc) | | | 0.028(hc) | | 1,2-Dichloroethane | 107-06-2 | | | 0.29(hc) | | | 28(hc) | | 1,1-Dichloroethylene | 75-35-4 | | | 4.7(h) | | | 100(h) | | trans-1,2-Dichloroethylene | 156-60-5 | | | 590(h) | | | 43,000(h) | | 2,4-Dichlorophenol | 120-83-2 | | | 77(h) | | | 290(h) | | 1,2-Dichloropropane | 78-87-5 | | | 0.50(hc) | | | 15(hc) | | 1,3-Dichloropropene (cis and trans) | 542-75-6 | | | 0.34(hc) | | | 21(hc) | 3812. Table 12¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 40
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | Saline Water (SE & SC) Criteria | ||||
|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | ||||
| Acute | Chronic | Acute | Chronic | ||||
| Dieldrin | 60-57-1 | 0.24 | 0.056 | 0.000052(hc) | 0.71 | 0.0019 | 0.000054(hc) |
| Diethyl phthalate | 84-66-2 | 17,000(h) | 44,000(h) | ||||
| 2,4-Dimethyl phenol | 105-67-9 | 380(h) | 850(h) | ||||
| 4,6-Dinitro-o-cresol | 534-52-1 | 13(h) | 280(h) | ||||
| 2,4-Dinitrophenol | 51-28-5 | 69(h) | 5,300(h) | ||||
| 2,4-Dinitrotoluene | 121-14-2 | 0.11(hc) | 3.4(hc) | ||||
| 1,2-Diphenylhydrazine | 122-66-7 | 0.036(hc) | 0.20(hc) | ||||
| Endosulfans (alpha and beta) | 115-29-7 | 0.22 | 0.056 | 62(h) | 0.034 | 0.0087 | 89(h) |
| Endosulfan sulfate | 1031-07-8 | 62(h) | 89(h) | ||||
| Endrin | 72-20-8 | 0.086 | 0.036 | 0.059(h) | 0.037 | 0.0023 | 0.060(h) |
| Endrin aldehyde | 7421-93-4 | 0.059(h) | 0.060(h) | ||||
| Ethylbenzene | 100-41-4 | 530(h) | 2,100(h) | ||||
| Fluoranthene | 206-44-0 | 130(h) | 140(h) | ||||
| Fluorene | 86-73-7 | 1,100(h) | 5,300(h) | ||||
| Guthion | 86-50-0 | 0.01 | 0.01 | ||||
| Heptachlor | 76-44-8 | 0.52 | 0.0038 | 0.000079(hc) | 0.053 | 0.0036 | 0.000079(hc) |
| Heptachlor epoxide | 1024-57-3 | 0.52 | 0.0038 | 0.000039(hc) | 0.053 | 0.0036 | 0.000039(hc) |
| Hexachlorobenzene | 118-74-1 | 0.00028(hc) | 0.00029(hc) | ||||
| Hexachlorobutadiene | 87-68-3 | 0.44(hc) | 18(hc) | ||||
| Hexachlorocyclopenta-diene | 77-47-4 | 40(h) | 1,100(h) | ||||
| Hexachloroethane | 67-72-1 | 1.4(hc) | 3.3(hc) | ||||
| Indeno(1,2,3-cd)pyrene | 193-39-5 | 0.038(hc) | 0.18(hc) | ||||
| Isophorone | 78-59-1 | 35(hc) | 960(hc) | ||||
| Lead | 7439-92-1 | 38(d)(s) | 5.4(d)(s) | 5.0(h)(T) | 210(d)(s) | 24(d)(s) | |
| Malathion | 121-75-5 | 0.1 | 0.1 | ||||
| Manganese | 7439-96-5 | 100(h)(T) | |||||
| Mercury | 7439-97-6 | 1.4(d)(s) | 0.77(d)(s) | 0.050(h)(T) | 1.8(d)(s) | 0.94(d)(s) | 0.051(h)(T) |
| Methoxychlor | 72-43-5 | 0.03 | 40(h) | 0.03 | |||
| Methyl bromide (bromomethane) | 74-83-9 | 47(h) | 1,500(h) | ||||
| Methyl t-butyl ether (MTBE) | 1634-04-4 | 70(h) |
Source context and notes
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | | | Saline Water (SE & SC) Criteria | | | | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | Acute | Chronic | | Acute | Chronic | | | Dieldrin | 60-57-1 | 0.24 | 0.056 | 0.000052(hc) | 0.71 | 0.0019 | 0.000054(hc) | | Diethyl phthalate | 84-66-2 | | | 17,000(h) | | | 44,000(h) | | 2,4-Dimethyl phenol | 105-67-9 | | | 380(h) | | | 850(h) | | 4,6-Dinitro-o-cresol | 534-52-1 | | | 13(h) | | | 280(h) | | 2,4-Dinitrophenol | 51-28-5 | | | 69(h) | | | 5,300(h) | | 2,4-Dinitrotoluene | 121-14-2 | | | 0.11(hc) | | | 3.4(hc) | | 1,2-Diphenylhydrazine | 122-66-7 | | | 0.036(hc) | | | 0.20(hc) | | Endosulfans (alpha and beta) | 115-29-7 | 0.22 | 0.056 | 62(h) | 0.034 | 0.0087 | 89(h) | | Endosulfan sulfate | 1031-07-8 | | | 62(h) | | | 89(h) | | Endrin | 72-20-8 | 0.086 | 0.036 | 0.059(h) | 0.037 | 0.0023 | 0.060(h) | | Endrin aldehyde | 7421-93-4 | | | 0.059(h) | | | 0.060(h) | | Ethylbenzene | 100-41-4 | | | 530(h) | | | 2,100(h) | | Fluoranthene | 206-44-0 | | | 130(h) | | | 140(h) | | Fluorene | 86-73-7 | | | 1,100(h) | | | 5,300(h) | | Guthion | 86-50-0 | | 0.01 | | | 0.01 | | | Heptachlor | 76-44-8 | 0.52 | 0.0038 | 0.000079(hc) | 0.053 | 0.0036 | 0.000079(hc) | | Heptachlor epoxide | 1024-57-3 | 0.52 | 0.0038 | 0.000039(hc) | 0.053 | 0.0036 | 0.000039(hc) | | Hexachlorobenzene | 118-74-1 | | | 0.00028(hc) | | | 0.00029(hc) | | Hexachlorobutadiene | 87-68-3 | | | 0.44(hc) | | | 18(hc) | | Hexachlorocyclopenta-diene | 77-47-4 | | | 40(h) | | | 1,100(h) | | Hexachloroethane | 67-72-1 | | | 1.4(hc) | | | 3.3(hc) | | Indeno(1,2,3-cd)pyrene | 193-39-5 | | | 0.038(hc) | | | 0.18(hc) | | Isophorone | 78-59-1 | | | 35(hc) | | | 960(hc) | | Lead | 7439-92-1 | 38(d)(s) | 5.4(d)(s) | 5.0(h)(T) | 210(d)(s) | 24(d)(s) | | | Malathion | 121-75-5 | | 0.1 | | | 0.1 | | | Manganese | 7439-96-5 | | | | | | 100(h)(T) | | Mercury | 7439-97-6 | 1.4(d)(s) | 0.77(d)(s) | 0.050(h)(T) | 1.8(d)(s) | 0.94(d)(s) | 0.051(h)(T) | | Methoxychlor | 72-43-5 | | 0.03 | 40(h) | | 0.03 | | | Methyl bromide (bromomethane) | 74-83-9 | | | 47(h) | | | 1,500(h) | | Methyl t-butyl ether (MTBE) | 1634-04-4 | | | 70(h) | | | |13. Table 13¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 41
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | Saline Water (SE & SC) Criteria | ||||
|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | ||||
| Acute | Chronic | Acute | Chronic | ||||
| Methylene chloride | 75-09-2 | 2.5(hc) | 310(hc) | ||||
| Mirex | 2385-85-5 | 0.001 | 0.001 | ||||
| Nickel | 7440-02-0 | (a) | (a) | 500(h)(T) | 64(d)(s) | 22(d)(s) | 1,700(h)(T) |
| Nitrate (as N) | 14797-55-8 | 10,000(h) | |||||
| Nitrobenzene | 98-95-3 | 17(h) | 690(h) | ||||
| N-Nitrosodi-n-butylamine | 924-16-3 | 0.0063(hc) | 0.22(hc) | ||||
| N-Nitrosodiethylamine | 55-18-5 | 0.00023(hc) | 0.13(hc) | ||||
| N-Nitrosodimethylamine | 62-75-9 | 0.00069(hc) | 3.0(hc) | ||||
| N-Nitrosodiphenylamine | 86-30-6 | 3.3(hc) | 6.0(hc) | ||||
| N-Nitrosodi-n-propylamine (Di-n-propylnitrosamine) | 621-64-7 | 0.0050(hc) | 0.51(hc) | ||||
| N-Nitrosopyrrolidine | 930-55-2 | 0.016(hc) | 34(hc) | ||||
| Parathion | 56-38-2 | 0.065 | 0.013 | ||||
| Pentachlorobenzene | 608-93-5 | 1.4(h) | 1.5(h) | ||||
| Pentachlorophenol | 87-86-5 | (b) | (b) | 0.27(hc) | 13 | 7.9 | 3.0(hc) |
| Phenol | 108-95-2 | 10,000(h) | 860,000(h) | ||||
| Phosphorous (yellow) | 7723-14-0 | 0.1 | |||||
| Polychlorinated biphenyls (PCBs) | 1336-36-3 | 0.014 | 0.000064(hc) | 0.030 | 0.000064(hc) | ||
| Pyrene | 129-00-0 | 830(h) | 4,000(h) | ||||
| Selenium | 7782-49-2 | 20(s) | 5.0(s) | 170(h)(T) | 290(d)(s) | 71(d)(s) | 4,200(h)(T) |
| Silver | 7440-22-4 | (a) | 170(h)(T) | 1.9(d)(s) | 40,000(h)(T) | ||
| Sulfide-hydrogen sulfide (undissociated) | 7783-06-4 | 2 | 2 | ||||
| 1,2,4,5-Tetrachlorobenzene | 95-94-3 | 0.97(h) | 1.1(h) | ||||
| 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) | 1746-01-6 | 0.0000000050(hc) | 0.0000000051(hc) | ||||
| 1,1,2,2-Tetrachloroethane | 79-34-5 | 4.7(h) | 110(h) | ||||
| Tetrachloroethylene | 127-18-4 | 0.34(hc) | 1.6(hc) | ||||
| Thallium | 7440-28-0 | 0.24(h)(T) | 0.47(h)(T) | ||||
| Toluene | 108-88-3 | 1,300(h) | 15,000(h) | ||||
| Toxaphene | 8001-35-2 | 0.73 | 0.0002 | 0.00028(hc) | 0.21 | 0.0002 | 0.00028(hc) |
| 1,2,4-Trichlorobenzene | 120-82-1 | 21(h) | 42(h) |
Source context and notes
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | | | Saline Water (SE & SC) Criteria | | | | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | Acute | Chronic | | Acute | Chronic | | | Methylene chloride | 75-09-2 | | | 2.5(hc) | | | 310(hc) | | Mirex | 2385-85-5 | | 0.001 | | | 0.001 | | | Nickel | 7440-02-0 | (a) | (a) | 500(h)(T) | 64(d)(s) | 22(d)(s) | 1,700(h)(T) | | Nitrate (as N) | 14797-55-8 | | | 10,000(h) | | | | | Nitrobenzene | 98-95-3 | | | 17(h) | | | 690(h) | | N-Nitrosodi-n-butylamine | 924-16-3 | | | 0.0063(hc) | | | 0.22(hc) | | N-Nitrosodiethylamine | 55-18-5 | | | 0.00023(hc) | | | 0.13(hc) | | N-Nitrosodimethylamine | 62-75-9 | | | 0.00069(hc) | | | 3.0(hc) | | N-Nitrosodiphenylamine | 86-30-6 | | | 3.3(hc) | | | 6.0(hc) | | N-Nitrosodi-n-propylamine (Di-n-propylnitrosamine) | 621-64-7 | | | 0.0050(hc) | | | 0.51(hc) | | N-Nitrosopyrrolidine | 930-55-2 | | | 0.016(hc) | | | 34(hc) | | Parathion | 56-38-2 | 0.065 | 0.013 | | | | | | Pentachlorobenzene | 608-93-5 | | | 1.4(h) | | | 1.5(h) | | Pentachlorophenol | 87-86-5 | (b) | (b) | 0.27(hc) | 13 | 7.9 | 3.0(hc) | | Phenol | 108-95-2 | | | 10,000(h) | | | 860,000(h) | | Phosphorous (yellow) | 7723-14-0 | | | | | 0.1 | | | Polychlorinated biphenyls (PCBs) | 1336-36-3 | | 0.014 | 0.000064(hc) | | 0.030 | 0.000064(hc) | | Pyrene | 129-00-0 | | | 830(h) | | | 4,000(h) | | Selenium | 7782-49-2 | 20(s) | 5.0(s) | 170(h)(T) | 290(d)(s) | 71(d)(s) | 4,200(h)(T) | | Silver | 7440-22-4 | (a) | | 170(h)(T) | 1.9(d)(s) | | 40,000(h)(T) | | Sulfide-hydrogen sulfide (undissociated) | 7783-06-4 | | 2 | | | 2 | | | 1,2,4,5-Tetrachlorobenzene | 95-94-3 | | | 0.97(h) | | | 1.1(h) | | 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) | 1746-01-6 | | | 0.0000000050(hc) | | | 0.0000000051(hc) | | 1,1,2,2-Tetrachloroethane | 79-34-5 | | | 4.7(h) | | | 110(h) | | Tetrachloroethylene | 127-18-4 | | | 0.34(hc) | | | 1.6(hc) | | Thallium | 7440-28-0 | | | 0.24(h)(T) | | | 0.47(h)(T) | | Toluene | 108-88-3 | | | 1,300(h) | | | 15,000(h) | | Toxaphene | 8001-35-2 | 0.73 | 0.0002 | 0.00028(hc) | 0.21 | 0.0002 | 0.00028(hc) | | 1,2,4-Trichlorobenzene | 120-82-1 | | | 21(h) | | | 42(h) |14. Table 14¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 42
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | Saline Water (SE & SC) Criteria | ||||
|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | ||||
| Acute | Chronic | Acute | Chronic | ||||
| 1,1,1-Trichloroethane | 71-55-6 | 120(h) | 2,600(h) | ||||
| 1,1,2-Trichloroethane | 79-00-5 | 13(h) | 350(h) | ||||
| Trichloroethylene | 79-01-6 | 1.0(hc) | 12(hc) | ||||
| 2,4,5-Trichlorophenol | 95-95-4 | 1,800(h) | 3,600(h) | ||||
| 2,4,6-Trichlorophenol | 88-06-2 | 0.58(hc) | 1.0(hc) | ||||
| Vinyl chloride | 75-01-4 | 0.082(hc) | 8.1(hc) | ||||
| Zinc | 7440-66-6 | (a) | (a) | 7,400(h)(T) | 90(d)(s) | 81(d)(s) | 26,000(h)(T) |
Source context and notes
| Toxic Substance | CAS Number | Fresh Water (FW2) Criteria | | | Saline Water (SE & SC) Criteria | | | | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | Acute | Chronic | | Acute | Chronic | | | 1,1,1-Trichloroethane | 71-55-6 | | | 120(h) | | | 2,600(h) | | 1,1,2-Trichloroethane | 79-00-5 | | | 13(h) | | | 350(h) | | Trichloroethylene | 79-01-6 | | | 1.0(hc) | | | 12(hc) | | 2,4,5-Trichlorophenol | 95-95-4 | | | 1,800(h) | | | 3,600(h) | | 2,4,6-Trichlorophenol | 88-06-2 | | | 0.58(hc) | | | 1.0(hc) | | Vinyl chloride | 75-01-4 | | | 0.082(hc) | | | 8.1(hc) | | Zinc | 7440-66-6 | (a) | (a) | 7,400(h)(T) | 90(d)(s) | 81(d)(s) | 26,000(h)(T) | (a) Criteria as listed at (f)3 above as formula (b) Criteria as listed at (f)4 above as formula (d) Criterion is expressed as a function of the Water Effect Ratio (WER). For criterion in the table, WER equates to the default value of 1.0. (fc) Criteria expressed as free cyanide (as CN)/L (h) Human health noncarcinogen (hc) Human health carcinogen (ol) Organoleptic effect-based criterion with no frequency of exceedance at or above the MA7CD10 flow (s) Dissolved criterion (T) Total recoverable criterion * See N.J.A.C. 7:9B-1.14(g) for site-specific criteria.15. Table 15¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 43
| Toxic Substance | CAS Number | Freshwater Criteria | Saline water Criteria | Waterbodies | ||||
|---|---|---|---|---|---|---|---|---|
| Aquatic | Human Health | Aquatic | Human Health | |||||
| Acute | Chronic | Acute | Chronic | |||||
| Copper (μg/L dissolved) | 7440508 | 7.9 | 5.6 | Newark Bay, Raritan Bay, Arthur Kill, Kill Van Kull, saline portions of the Passaic, Hackensack, and Hudson Rivers and saline portions of tributaries to all of these waters. |
Source context and notes
(g) Site-specific surface water quality criteria listed below apply to specific waterbodies that supersede the State-wide criteria listed at (d), (e), and (f) above. Any site-specific criterion developed through a Total Maximum Daily Load (TMDL) adopted as an amendment to the Statewide Water Quality Management Plan or the applicable Areawide Water Quality Management Plan in accordance with N.J.A.C. 7:15-5.4 shall be incorporated into this section. The Department shall publish a notice of administrative change in the New Jersey Register. 1. | Toxic Substance | CAS Number | Freshwater Criteria | | | Saline water Criteria | | | Waterbodies | | --- | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | | Acute | Chronic | | Acute | Chronic | | | | Copper (μg/L dissolved) | 7440508 | | | | 7.9 | 5.6 | | Newark Bay, Raritan Bay, Arthur Kill, Kill Van Kull, saline portions of the Passaic, Hackensack, and Hudson Rivers and saline portions of tributaries to all of these waters. | 2. | Substance | Criteria | Duration | Waterbody | Associated HUC14 Name | Associated HUC14 Number | | --- | --- | --- | --- | --- | --- | | Total Phosphorus (mg/L)(A) | 0.050 | Annual average | Carnegie Lake (Mercer & Middlesex Counties) | Stony Bk (Princeton) | 02030105090090 | | | | | | Millstone R (Rt. 1 to Cranbury Bk) | 02030105100140 | | | | | | Millstone R (Heathcote Bk to Harrison St.) | 02030105110020 | | | 0.053 | Annual average | Gordon Pond (Middlesex County) | Devils Brook | 02030105100110 | | | 0.040 | Annual average | Grovers Mill Pond (Mercer County) | Bear Brook (below Trenton Road) | 02030105100130 | | | 0.059 | Annual average | Peddie Lake (Mercer County) | Rocky Brook (below Monmouth Co line) | 02030105100050 | | | 0.043 | Annual average | Plainsboro Pond (Middlesex County) | Cranbury Brook (below NJ Turnpike) | 02030105100090 | (A) In accordance with the Amendment to the Lower Raritan/Middlesex, Mercer County, Monmouth County, Northeast, Upper Delaware and Upper Raritan Water Quality Management Plans; Total Maximum Daily Load Report for the Non-Tidal Raritan River Basin Addressing Total Phosphorus, Dissolved Oxygen, pH and Total Suspended Solids Impairments Watershed Management Areas 8, 9 and 10; adopted May 24, 2016 at 48 N.J.R. 1321(a)). The TMDL Report may be downloaded at https://www.nj.gov/dep/wms/bears/docs/raritan_tmdl_adopted.pdf.16. Table 16¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 43
| Substance | Criteria | Duration | Waterbody | Associated HUC14 Name | Associated HUC14 Number |
|---|---|---|---|---|---|
| Total Phosphorus (mg/L)(A) | 0.050 | Annual average | Carnegie Lake (Mercer & Middlesex Counties) | Stony Bk (Princeton) | 02030105090090 |
| Millstone R (Rt. 1 to Cranbury Bk) | 02030105100140 | ||||
| Millstone R (Heathcote Bk to Harrison St.) | 02030105110020 | ||||
| 0.053 | Annual average | Gordon Pond (Middlesex County) | Devils Brook | 02030105100110 | |
| 0.040 | Annual average | Grovers Mill Pond (Mercer County) | Bear Brook (below Trenton Road) | 02030105100130 | |
| 0.059 | Annual average | Peddie Lake (Mercer County) | Rocky Brook (below Monmouth Co line) | 02030105100050 | |
| 0.043 | Annual average | Plainsboro Pond (Middlesex County) | Cranbury Brook (below NJ Turnpike) | 02030105100090 |
Source context and notes
| Toxic Substance | CAS Number | Freshwater Criteria | | | Saline water Criteria | | | Waterbodies | | --- | --- | --- | --- | --- | --- | --- | --- | --- | | | | Aquatic | | Human Health | Aquatic | | Human Health | | | | | Acute | Chronic | | Acute | Chronic | | | | Copper (μg/L dissolved) | 7440508 | | | | 7.9 | 5.6 | | Newark Bay, Raritan Bay, Arthur Kill, Kill Van Kull, saline portions of the Passaic, Hackensack, and Hudson Rivers and saline portions of tributaries to all of these waters. | 2. | Substance | Criteria | Duration | Waterbody | Associated HUC14 Name | Associated HUC14 Number | | --- | --- | --- | --- | --- | --- | | Total Phosphorus (mg/L)(A) | 0.050 | Annual average | Carnegie Lake (Mercer & Middlesex Counties) | Stony Bk (Princeton) | 02030105090090 | | | | | | Millstone R (Rt. 1 to Cranbury Bk) | 02030105100140 | | | | | | Millstone R (Heathcote Bk to Harrison St.) | 02030105110020 | | | 0.053 | Annual average | Gordon Pond (Middlesex County) | Devils Brook | 02030105100110 | | | 0.040 | Annual average | Grovers Mill Pond (Mercer County) | Bear Brook (below Trenton Road) | 02030105100130 | | | 0.059 | Annual average | Peddie Lake (Mercer County) | Rocky Brook (below Monmouth Co line) | 02030105100050 | | | 0.043 | Annual average | Plainsboro Pond (Middlesex County) | Cranbury Brook (below NJ Turnpike) | 02030105100090 | (A) In accordance with the Amendment to the Lower Raritan/Middlesex, Mercer County, Monmouth County, Northeast, Upper Delaware and Upper Raritan Water Quality Management Plans; Total Maximum Daily Load Report for the Non-Tidal Raritan River Basin Addressing Total Phosphorus, Dissolved Oxygen, pH and Total Suspended Solids Impairments Watershed Management Areas 8, 9 and 10; adopted May 24, 2016 at 48 N.J.R. 1321(a)). The TMDL Report may be downloaded at https://www.nj.gov/dep/wms/bears/docs/raritan_tmdl_adopted.pdf.17. Table 17¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 44
| Substance | Criteria | Duration | Waterbody | Associated HUC14 Name | Associated HUC14 Number |
|---|---|---|---|---|---|
| Chlorophyll a (μg/L)^{(B)} | 20 | Seasonal average (June 15^{th} to September 1^{st}) | Dundee Lake | Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 |
| 10 | Seasonal average (June 15^{th} to September 1^{st}) | Wanaque Lake | Wanaque Reservoir (below Monks gage) | 02030103070050 |
Source context and notes
3. | Substance | Criteria | Duration | Waterbody | Associated HUC14 Name | Associated HUC14 Number | | --- | --- | --- | --- | --- | --- | | Chlorophyll a (μg/L)^{(B)} | 20 | Seasonal average (June 15^{th} to September 1^{st}) | Dundee Lake | Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 | | | 10 | Seasonal average (June 15^{th} to September 1^{st}) | Wanaque Lake | Wanaque Reservoir (below Monks gage) | 02030103070050 | (B) Chlorophyll $a$ is a watershed-specific translator applicable for the lakes identified above where the total phosphorus criterion of $0.1 \, \mathrm{mg/L}$ does not apply to the upstream waterbodies identified in Table (i) below in accordance with the Amendment to the Northeast, Upper Raritan, Sussex County and Upper Delaware Water Quality Management Plans; Total Maximum Daily Load Report for the Non-Tidal Passaic River Basin Addressing Phosphorus Impairments. Watershed Management Areas 3, 4 and 6; adopted April 24, 2008 at 40 N.J.R. 2574(b)). The TMDL Report may be downloaded at https://www.nj.gov/dep/wms/bears/docs/passaic_tmdl.pdf. i. The total phosphorus criterion of $0.1\mathrm{mg / L}$ at N.J.A.C. 7:9B-1.14(d)4ii(1) does not apply to the following waterbodies: | Waterbody | Associated HUC14 Name | Associated HUC14 Number | | --- | --- | --- | | Passaic River from source to Dundee Lake Dam, including all named and unnamed tributaries | Passaic R Upr (above Osborn Mills) | 02030103010010 | | | Passaic R Upr (Dead R to Osborn Mills) | 02030103010070 | | | Passaic R Upr (Plainfield Rd to Dead R) | 02030103010110 | | | Passaic R Upr (Snyder to Plainfield Rd) | 02030103010120 | | | Passaic R Upr (40d 45m to Snyder Ave) | 02030103010130 | | | Passaic R Upr (Columbia Rd to 40d 45m) | 02030103010150 | | | Passaic R Upr (Hanover RR to Columbia Rd) | 02030103010160 | | | Passaic R Upr (Rockaway to Hanover RR) | 02030103010170 | | | Passaic R Upr (Pine Bk br to Rockaway) | 02030103010180 | | | Passaic R Upr (Pompton R to Pine Bk) | 02030103040010 | | | Passaic R Lwr (pump stn to Pompton R) | 02030103120100 | | | Passaic R Lwr (Goffle Bk to pump stn) | 02030103120110 | | | Passaic R Lwr (Fair Lawn Ave to Goffle) | 02030103120070 | | | Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 | | High Mountain Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 | | Meadow Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 | | Wanaque River from Wanaque Reservoir dam to Pequannock River including all named and unnamed tributaries | Meadow Brook/High Mountain Brook | 02030103070060 | | | Wanaque R/Posts Bk (below reservoir) | 02030103070070 | | Posts Brook including all named and unnamed tributaries | Wanaque R/Posts Bk (below reservoir) | 02030103070070 |18. Table 18¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 44
| Waterbody | Associated HUC14 Name | Associated HUC14 Number |
|---|---|---|
| Passaic River from source to Dundee Lake Dam, including all named and unnamed tributaries | Passaic R Upr (above Osborn Mills) | 02030103010010 |
| Passaic R Upr (Dead R to Osborn Mills) | 02030103010070 | |
| Passaic R Upr (Plainfield Rd to Dead R) | 02030103010110 | |
| Passaic R Upr (Snyder to Plainfield Rd) | 02030103010120 | |
| Passaic R Upr (40d 45m to Snyder Ave) | 02030103010130 | |
| Passaic R Upr (Columbia Rd to 40d 45m) | 02030103010150 | |
| Passaic R Upr (Hanover RR to Columbia Rd) | 02030103010160 | |
| Passaic R Upr (Rockaway to Hanover RR) | 02030103010170 | |
| Passaic R Upr (Pine Bk br to Rockaway) | 02030103010180 | |
| Passaic R Upr (Pompton R to Pine Bk) | 02030103040010 | |
| Passaic R Lwr (pump stn to Pompton R) | 02030103120100 | |
| Passaic R Lwr (Goffle Bk to pump stn) | 02030103120110 | |
| Passaic R Lwr (Fair Lawn Ave to Goffle) | 02030103120070 | |
| Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 | |
| High Mountain Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 |
| Meadow Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 |
| Wanaque River from Wanaque Reservoir dam to Pequannock River including all named and unnamed tributaries | Meadow Brook/High Mountain Brook | 02030103070060 |
| Wanaque R/Posts Bk (below reservoir) | 02030103070070 | |
| Posts Brook including all named and unnamed tributaries | Wanaque R/Posts Bk (below reservoir) | 02030103070070 |
Source context and notes
| --- | --- | --- | --- | --- | --- | | Chlorophyll a (μg/L)^{(B)} | 20 | Seasonal average (June 15^{th} to September 1^{st}) | Dundee Lake | Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 | | | 10 | Seasonal average (June 15^{th} to September 1^{st}) | Wanaque Lake | Wanaque Reservoir (below Monks gage) | 02030103070050 | (B) Chlorophyll $a$ is a watershed-specific translator applicable for the lakes identified above where the total phosphorus criterion of $0.1 \, \mathrm{mg/L}$ does not apply to the upstream waterbodies identified in Table (i) below in accordance with the Amendment to the Northeast, Upper Raritan, Sussex County and Upper Delaware Water Quality Management Plans; Total Maximum Daily Load Report for the Non-Tidal Passaic River Basin Addressing Phosphorus Impairments. Watershed Management Areas 3, 4 and 6; adopted April 24, 2008 at 40 N.J.R. 2574(b)). The TMDL Report may be downloaded at https://www.nj.gov/dep/wms/bears/docs/passaic_tmdl.pdf. i. The total phosphorus criterion of $0.1\mathrm{mg / L}$ at N.J.A.C. 7:9B-1.14(d)4ii(1) does not apply to the following waterbodies: | Waterbody | Associated HUC14 Name | Associated HUC14 Number | | --- | --- | --- | | Passaic River from source to Dundee Lake Dam, including all named and unnamed tributaries | Passaic R Upr (above Osborn Mills) | 02030103010010 | | | Passaic R Upr (Dead R to Osborn Mills) | 02030103010070 | | | Passaic R Upr (Plainfield Rd to Dead R) | 02030103010110 | | | Passaic R Upr (Snyder to Plainfield Rd) | 02030103010120 | | | Passaic R Upr (40d 45m to Snyder Ave) | 02030103010130 | | | Passaic R Upr (Columbia Rd to 40d 45m) | 02030103010150 | | | Passaic R Upr (Hanover RR to Columbia Rd) | 02030103010160 | | | Passaic R Upr (Rockaway to Hanover RR) | 02030103010170 | | | Passaic R Upr (Pine Bk br to Rockaway) | 02030103010180 | | | Passaic R Upr (Pompton R to Pine Bk) | 02030103040010 | | | Passaic R Lwr (pump stn to Pompton R) | 02030103120100 | | | Passaic R Lwr (Goffle Bk to pump stn) | 02030103120110 | | | Passaic R Lwr (Fair Lawn Ave to Goffle) | 02030103120070 | | | Passaic R Lwr (Dundee Dam to F.L. Ave) | 02030103120080 | | High Mountain Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 | | Meadow Brook, entire length | Meadow Brook/High Mountain Brook | 02030103070060 | | Wanaque River from Wanaque Reservoir dam to Pequannock River including all named and unnamed tributaries | Meadow Brook/High Mountain Brook | 02030103070060 | | | Wanaque R/Posts Bk (below reservoir) | 02030103070070 | | Posts Brook including all named and unnamed tributaries | Wanaque R/Posts Bk (below reservoir) | 02030103070070 |19. Table 19¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 45
| Ramapo River from Pompton Lake to Pompton River including all named and unnamed tributaries | Ramapo R (below Crystal Lake bridge) P | 02030103100070 P |
|---|---|---|
| Pompton River from confluence with Pequannock River to Passaic River, including all named and unnamed all tributaries | Pequannock R (below Macopin gage) P | 02030103050080 P |
| Pompton River | 02030103110020 | |
| Beaver Brook including all named and unnamed all tributaries | Lincoln Park trips (Pompton River) | 02030103110010 |
| Preakness (Singac) Brook, entire length | Preakness Brook / Naachtpunkt Brook | 02030103120030 |
| Goffle Brook, entire length | Goffle Brook | 02030103120050 |
| Molly Ann Brook, entire length | Molly Ann Brook | 02030103120040 |
| Deepavaal Brook, entire length | Deepavaal Brook | 02030103120060 |
| Peckman River, entire length | Peckman River (above CG Res trip) | 02030103120010 |
| Peckman River (below CG Res trip) | 02030103120020 | |
| Canoe Brook, entire length | Canoe Brook | 02030103010140 |
| Slough Brook, entire length | Slough Brook | 02030103010190 |
| Crooked Brook including all named and unnamed all tributaries | Montville trips. | 02030103030160 |
| Rockaway River, from downstream boundary of Jersey City (Boonton) Reservoir to Passaic River including all named and unnamed tributaries | Rockaway R (Passaic R to Boonton dam) | 02030103030170 |
| Whippany River from Washington Valley Road to Passaic River including all named and unnamed all tributaries | Greystone / Watnong Mtn trips | 02030103020030 |
| Whippany R (Lk Pocahontas to Wash Val Rd) | 02030103020040 | |
| Whippany R (Malapardis to Lk Pocahontas) | 02030103020050 | |
| Whippany R (Rockaway R to Malapardis Bk) | 02030103020100 | |
| Dead River, entire length | Dead River (above Harrisons Brook) | 02030103010080 |
| Dead River (below Harrisons Brook) | 02030103010100 | |
| Harrisons Brook, entire length | Harrisons Brook | 02030103010090 |
| Primrose Brook, entire length | Primrose Brook | 02030103010020 |
| Loantaka Brook, entire length | Loantaka Brook | 02030103010040 |
| Great Brook including all named and unnamed all tributaries | Great Brook (above Green Village Rd) | 02030103010030 |
| Great Brook (below Green Village Rd) | 02030103010050 | |
| Malapardis Brook, entire length | Malapardis Brook | 02030103020060 |
| Black Brook, entire length | Black Brook (Hanover) | 02030103020070 |
| Black Brook including all named and unnamed all tributaries | Black Brook (Great Swamp NWR) | 02030103010060 |
| Troy Brook including all named and unnamed tributaries | Troy Brook (above Reynolds Ave) | 02030103020080 |
| Troy Brook (below Reynolds Ave) | 02030103020090 |
Source context and notes
| Ramapo River from Pompton Lake to Pompton River including all named and unnamed tributaries | Ramapo R (below Crystal Lake bridge) P | 02030103100070 P | | --- | --- | --- | | Pompton River from confluence with Pequannock River to Passaic River, including all named and unnamed all tributaries | Pequannock R (below Macopin gage) P | 02030103050080 P | | | Pompton River | 02030103110020 | | Beaver Brook including all named and unnamed all tributaries | Lincoln Park trips (Pompton River) | 02030103110010 | | Preakness (Singac) Brook, entire length | Preakness Brook / Naachtpunkt Brook | 02030103120030 | | Goffle Brook, entire length | Goffle Brook | 02030103120050 | | Molly Ann Brook, entire length | Molly Ann Brook | 02030103120040 | | Deepavaal Brook, entire length | Deepavaal Brook | 02030103120060 | | Peckman River, entire length | Peckman River (above CG Res trip) | 02030103120010 | | | Peckman River (below CG Res trip) | 02030103120020 | | Canoe Brook, entire length | Canoe Brook | 02030103010140 | | Slough Brook, entire length | Slough Brook | 02030103010190 | | Crooked Brook including all named and unnamed all tributaries | Montville trips. | 02030103030160 | | Rockaway River, from downstream boundary of Jersey City (Boonton) Reservoir to Passaic River including all named and unnamed tributaries | Rockaway R (Passaic R to Boonton dam) | 02030103030170 | | Whippany River from Washington Valley Road to Passaic River including all named and unnamed all tributaries | Greystone / Watnong Mtn trips | 02030103020030 | | | Whippany R (Lk Pocahontas to Wash Val Rd) | 02030103020040 | | | Whippany R (Malapardis to Lk Pocahontas) | 02030103020050 | | | Whippany R (Rockaway R to Malapardis Bk) | 02030103020100 | | Dead River, entire length | Dead River (above Harrisons Brook) | 02030103010080 | | | Dead River (below Harrisons Brook) | 02030103010100 | | Harrisons Brook, entire length | Harrisons Brook | 02030103010090 | | Primrose Brook, entire length | Primrose Brook | 02030103010020 | | Loantaka Brook, entire length | Loantaka Brook | 02030103010040 | | Great Brook including all named and unnamed all tributaries | Great Brook (above Green Village Rd) | 02030103010030 | | | Great Brook (below Green Village Rd) | 02030103010050 | | Malapardis Brook, entire length | Malapardis Brook | 02030103020060 | | Black Brook, entire length | Black Brook (Hanover) | 02030103020070 | | Black Brook including all named and unnamed all tributaries | Black Brook (Great Swamp NWR) | 02030103010060 | | Troy Brook including all named and unnamed tributaries | Troy Brook (above Reynolds Ave) | 02030103020080 | | | Troy Brook (below Reynolds Ave) | 02030103020090 | P Partial HUC1420. Table 20¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 49
| Waterbody | Classification |
|---|---|
| ABRAMS CREEK (Marmora) - Entire length, except portion outside the boundaries of the MacNamara Wildlife Management Area |
FW2-NT/SE1(C1) |
| (Griscom) - Portions of the Creek and tributaries outside of the MacNamara Wildlife Management Area | FW2-NT/SE1 |
| ABSECON BAY (Absecon) - All waters within Absecon Wildlife Management Area | SE1(C1) |
| ABSECON CREEK (Egg Harbor) - North and South Branches from their origins downstream to the boundary of the Pinelands Protection and Preservation Area |
PL |
| (Absecon) - Boundary of the Pinelands Protection and Preservation Area to Mill Road Dam | FW2-NT |
| (Absecon) - Mill Road Dam to Absecon Bay, except portions within Absecon Wildlife Management Area | SE1 |
| ARNOLD POND (Barnegat) | FW2-NT/SE1(C1) |
| ATLANTIC OCEAN (Offshore) - Waters from the shoreline out to the three mile limit, except areas described below |
SC |
| (Beach Haven) - Waters of the Atlantic Ocean out to the State's three mile limit from Beach Haven Inlet to Cape May Point, excluding waters classified as Prohibited in accordance with N.J.A.C. 7:12 | SC(C1) |
| TRIBUTARIES, ATLANTIC OCEAN (New Jersey Coast) - All those streams or segments of streams that flow directly into the Atlantic Ocean or into back bays of the Ocean which are not included elsewhere in this list, are not within the boundaries of the Pinelands Protection or Preservation Areas |
FW2-NT/SE1 |
| (Pinelands) - All streams or segments of streams which flow directly into the Atlantic Ocean or into back bays of the Ocean, are within the boundaries of the Pinelands Protection and Preservation Areas and are not classified as FW1 in this Table | PL |
| (New Jersey Coast) - All streams or segments of streams which flow directly into the Atlantic Ocean or into back bays of the Ocean, are not trout maintenance waters, and are not classified as FW1 in this Table | FW2-NT/SE1(C1) |
| BABCOCK CREEK (Marmora) - Entire length | FW2-NT/SE1(C1) |
| BALLANGER CREEK |
Source context and notes
(c) The following surface water classifications are for waters of the Atlantic Coastal Basin: | Waterbody | Classification | | --- | --- | | ABRAMS CREEK(Marmora) - Entire length, except portion outside the boundaries of the MacNamara Wildlife Management Area | FW2-NT/SE1(C1) | | (Griscom) - Portions of the Creek and tributaries outside of the MacNamara Wildlife Management Area | FW2-NT/SE1 | | ABSECON BAY (Absecon) - All waters within Absecon Wildlife Management Area | SE1(C1) | | ABSECON CREEK
(Egg Harbor) - North and South Branches from their origins downstream to the boundary of the Pinelands Protection and Preservation Area | PL | | (Absecon) - Boundary of the Pinelands Protection and Preservation Area to Mill Road Dam | FW2-NT | | (Absecon) - Mill Road Dam to Absecon Bay, except portions within Absecon Wildlife Management Area | SE1 | | ARNOLD POND (Barnegat) | FW2-NT/SE1(C1) | | ATLANTIC OCEAN
(Offshore) - Waters from the shoreline out to the three mile limit, except areas described below | SC | | (Beach Haven) - Waters of the Atlantic Ocean out to the State's three mile limit from Beach Haven Inlet to Cape May Point, excluding waters classified as Prohibited in accordance with N.J.A.C. 7:12 | SC(C1) | | TRIBUTARIES, ATLANTIC OCEAN
(New Jersey Coast) - All those streams or segments of streams that flow directly into the Atlantic Ocean or into back bays of the Ocean which are not included elsewhere in this list, are not within the boundaries of the Pinelands Protection or Preservation Areas | FW2-NT/SE1 | | (Pinelands) - All streams or segments of streams which flow directly into the Atlantic Ocean or into back bays of the Ocean, are within the boundaries of the Pinelands Protection and Preservation Areas and are not classified as FW1 in this Table | PL | | (New Jersey Coast) - All streams or segments of streams which flow directly into the Atlantic Ocean or into back bays of the Ocean, are not trout maintenance waters, and are not classified as FW1 in this Table | FW2-NT/SE1(C1) | | BABCOCK CREEK (Marmora) - Entire length | FW2-NT/SE1(C1) | | BALLANGER CREEK | |
21. Table 21¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 62
| Waterbody | Classification |
|---|---|
| ALEXAUKEN CREEK (Lambertville) - Entire length, including all tributaries | FW2-TM(C1) |
| ALLAMUCHY CREEK (Allamuchy) - Entire length | FW2-NT(C1) |
| ALLAMUCHY POND (Allamuchy) | FW2-NT(C1) |
| ALLAMUCHY POND TRIBUTARIES (Allamuchy) - All tributaries that are located entirely within the boundaries of Allamuchy State Park and that flow into Allamuchy Pond | FW1 |
| ALMS HOUSE BROOK (Hampton) - Source to, but not including, County Farm Pond |
FW2-TM |
| (Frankford) - County Farm Pond to Paulins Kill | FW2-NT |
| AMWELL LAKES (Lambertville) | FW2-NT(C1) |
| ANDOVER JUNCTION BROOK (Andover) - Source to Valentines Pond |
FW2-TM |
| (Andover) - Valentines Pond to Kymer Brook | FW2-TM(C1) |
| ANDOVER JUNCTION BROOK LAKES (Andover) - All unlisted lakes greater than five acres | FW2-NT(C1) |
| ASHROE LAKE (Stokes State Forest) | FW2-NT(C1) |
| ASHROE LAKE TRIBUTARIES (Stokes State Forest) -Tributary to the Lake from Deer Lake and portion of southernmost tributary to Ashroe Lake outside of the Stokes State Forest boundary |
FW2-TP(C1) |
| (Stokes State Forest) - Southernmost tributary to the Lake from its source to the Stokes State Forest boundary | FW1(tp) |
| ASSUNPINK CREEK (Trenton) - Source to confluence with the Delaware River, except segments described separately below |
FW2-NT |
| (Roosevelt) - Creek and those tributaries within the boundaries of the Assunpink Wildlife Management Area | FW2-NT(C1) |
| (Quaker Bridge) - Portions of the creek within the boundaries of Van Ness Refuge | FW2-NT(C1) |
| BARKERS MILL BROOK (Independence) - Entire length | FW2-TP(C1) |
| BEAR BROOK (Johnsonburg) - Entire length | FW2-TP(C1) |
| BEAR CREEK (Johnsonburg) - Mud Pond to the Erie-Lackawanna Railroad trestle north of Johnsonburg |
FW1(tm) |
| (Frelinghuysen) - Erie-Lackawanna Railroad trestle to confluence with Trout Brook, including all unnamed and unlisted tributaries | FW2-TM(C1) |
Source context and notes
(d) The following surface water classifications are for waters of the Upper Delaware River Basin: | Waterbody | Classification | | --- | --- | | ALEXAUKEN CREEK (Lambertville) - Entire length, including all tributaries | FW2-TM(C1) | | ALLAMUCHY CREEK (Allamuchy) - Entire length | FW2-NT(C1) | | ALLAMUCHY POND (Allamuchy) | FW2-NT(C1) | | ALLAMUCHY POND TRIBUTARIES (Allamuchy) - All tributaries that are located entirely within the boundaries of Allamuchy State Park and that flow into Allamuchy Pond | FW1 | | ALMS HOUSE BROOK(Hampton) - Source to, but not including, County Farm Pond | FW2-TM | | (Frankford) - County Farm Pond to Paulins Kill | FW2-NT | | AMWELL LAKES (Lambertville) | FW2-NT(C1) | | ANDOVER JUNCTION BROOK
(Andover) - Source to Valentines Pond | FW2-TM | | (Andover) - Valentines Pond to Kymer Brook | FW2-TM(C1) | | ANDOVER JUNCTION BROOK LAKES (Andover) - All unlisted lakes greater than five acres | FW2-NT(C1) | | ASHROE LAKE (Stokes State Forest) | FW2-NT(C1) | | ASHROE LAKE TRIBUTARIES
(Stokes State Forest) -Tributary to the Lake from Deer Lake and portion of southernmost tributary to Ashroe Lake outside of the Stokes State Forest boundary | FW2-TP(C1) | | (Stokes State Forest) - Southernmost tributary to the Lake from its source to the Stokes State Forest boundary | FW1(tp) | | ASSUNPINK CREEK
(Trenton) - Source to confluence with the Delaware River, except segments described separately below | FW2-NT | | (Roosevelt) - Creek and those tributaries within the boundaries of the Assunpink Wildlife Management Area | FW2-NT(C1) | | (Quaker Bridge) - Portions of the creek within the boundaries of Van Ness Refuge | FW2-NT(C1) | | BARKERS MILL BROOK (Independence) - Entire length | FW2-TP(C1) | | BEAR BROOK (Johnsonburg) - Entire length | FW2-TP(C1) | | BEAR CREEK
(Johnsonburg) - Mud Pond to the Erie-Lackawanna Railroad trestle north of Johnsonburg | FW1(tm) | | (Frelinghuysen) - Erie-Lackawanna Railroad trestle to confluence with Trout Brook, including all unnamed and unlisted tributaries | FW2-TM(C1) |
22. Table 22¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 64
| Steeny Kill Lake that originate in High Point State Park downstream to their confluence with Clove Brook or to the High Point State Park Boundaries (High Point State Park) - Those northerly tributaries to Mill Brook that are located due west of Steeny Kill Lake, within the boundaries of High Point State Park |
FW1(tp) |
|---|---|
| COOPERMINE BROOK (Pahaquarry) - Entire length | FW1 |
| COWBOY CREEK (Byram) – Entire length | FW2-NT(C1) |
| CRANBERRY LAKE (Byram) | FW2-TM(C1) |
| CRANBERRY LAKE OUTLET STREAM (Byram) - Entire length within Cranberry Lake State Park |
FW2-NT(C1) |
| (Byram) - Stream outside of Cranberry Lake State Park | FW2-NT |
| CRISS BROOK (Stokes State Forest) - Entire length within the boundaries of Stokes State Forest | FW1(tp) |
| CULVER'S CREEK (Frankford) - Entire length | FW2-TM |
| CULVER'S LAKE (Frankford) | FW2-TM |
| DEER LAKE (Sandyston) | FW2-NT(C1) |
| DEER PARK POND (Allamuchy) - Pond and tributaries to the pond within Allamuchy State Park, except those tributaries classified as FW1, below |
FW2-NT(C1) |
| (Allamuchy) - All tributaries to the Pond and to its outlet stream that are located entirely with the boundaries of Allamuchy State Park | FW1 |
| (Allamuchy) - Deer Park Pond outlet stream downstream to Musconetcong River | FW2-TM(C1) |
| DELAWANNA CREEK (Delaware) - Source downstream to, but not including, Delaware Lake |
FW2-TM |
| (Delaware) – Delaware Lake dam downstream to Delaware River, including tributaries | FW2-TP(C1) |
| DELAWARE AND RARITAN CANAL (Lambertville) - Entire length | FW2-NT |
| DELAWARE RIVER TRIBUTARIES (Holland) - Entire length |
FW2-TP(C1) |
| (Port Jervis) - Unnamed or unlisted direct tributaries that are north of Big Timber Creek, are outside of the Pinelands Protection and Preservation Areas, and are not mapped as C1 waters by the Department | FW2-NT |
| (Knowlton) - Source, north of Hope-Delaware Road, to confluence with the Delaware River 0.5 mile south of Ramseysburg | FW2-TP(C1) |
| (Titusville) - Unnamed tributaries through Washington Crossing State Park | FW2-NT(C1) |
| DONKEY'S CORNER BROOK (Delaware Water Gap) - Entire length | FW1 |
| DRY BROOK (Branchville) - Entire length | FW2-NT |
Source context and notes
| Steeny Kill Lake that originate in High Point State Park downstream to their confluence with Clove Brook or to the High Point State Park Boundaries(High Point State Park) - Those northerly tributaries to Mill Brook that are located due west of Steeny Kill Lake, within the boundaries of High Point State Park | FW1(tp) | | --- | --- | | COOPERMINE BROOK (Pahaquarry) - Entire length | FW1 | | COWBOY CREEK (Byram) – Entire length | FW2-NT(C1) | | CRANBERRY LAKE (Byram) | FW2-TM(C1) | | CRANBERRY LAKE OUTLET STREAM
(Byram) - Entire length within Cranberry Lake State Park | FW2-NT(C1) | | (Byram) - Stream outside of Cranberry Lake State Park | FW2-NT | | CRISS BROOK (Stokes State Forest) - Entire length within the boundaries of Stokes State Forest | FW1(tp) | | CULVER'S CREEK (Frankford) - Entire length | FW2-TM | | CULVER'S LAKE (Frankford) | FW2-TM | | DEER LAKE (Sandyston) | FW2-NT(C1) | | DEER PARK POND
(Allamuchy) - Pond and tributaries to the pond within Allamuchy State Park, except those tributaries classified as FW1, below | FW2-NT(C1) | | (Allamuchy) - All tributaries to the Pond and to its outlet stream that are located entirely with the boundaries of Allamuchy State Park | FW1 | | (Allamuchy) - Deer Park Pond outlet stream downstream to Musconetcong River | FW2-TM(C1) | | DELAWANNA CREEK
(Delaware) - Source downstream to, but not including, Delaware Lake | FW2-TM | | (Delaware) – Delaware Lake dam downstream to Delaware River, including tributaries | FW2-TP(C1) | | DELAWARE AND RARITAN CANAL (Lambertville) - Entire length | FW2-NT | | DELAWARE RIVER TRIBUTARIES
(Holland) - Entire length | FW2-TP(C1) | | (Port Jervis) - Unnamed or unlisted direct tributaries that are north of Big Timber Creek, are outside of the Pinelands Protection and Preservation Areas, and are not mapped as C1 waters by the Department | FW2-NT | | (Knowlton) - Source, north of Hope-Delaware Road, to confluence with the Delaware River 0.5 mile south of Ramseysburg | FW2-TP(C1) | | (Titusville) - Unnamed tributaries through Washington Crossing State Park | FW2-NT(C1) | | DONKEY'S CORNER BROOK (Delaware Water Gap) - Entire length | FW1 | | DRY BROOK (Branchville) - Entire length | FW2-NT | 60
23. Table 23¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 73
| Waterbody | Classification |
|---|---|
| ALLOWAY CREEK (Alloways) – Source to Greenwich Street, including all tributaries and Alloway Lake (Quinton) – Greenwich Street to Delaware Bay (Quinton) – All named and unnamed tributaries of Alloway Creek from Greenwich Street to Delaware Bay |
FW2-NT SE1 FW2-NT/SE1 |
| ASSISCUNK CREEK (Columbus) - Headwaters to confluence with Barkers Brook, including all tributaries (Burlington) - Confluence with Barkers Brook to the Delaware River |
FW2-NT/C1 FW2-NT |
| BALDRIDGE CREEK (Salem Creek) - Entire length, except segments described below (Salem Creek) - Segments outside the boundaries of the Supawna National Wildlife Refuge |
FW2-NT/SE1(C1) FW2-NT/SE1 |
| BAY PONDS (Egg Island) BEADONS CREEK (Fortescue) - Entire length |
FW2-NT/SE1(C1) SE1(C1) |
| BEAVERDAM BRANCH (Glassboro) - Source to boundary of the Glassboro Wildlife Management Area (Glassboro) - Within the boundaries of Glassboro Wildlife Management Area |
FW2-NT FW2-NT |
| BIG TIMBER CREEK (Westville) - Entire length | FW2-NT |
| BLACKBIRD GUT (Newport) - Entire length | SE1(C1) |
| BLACKS CREEK (Bordentown) - Entire length | FW2-NT |
| BLACKWATER BRANCH (Vineland) – Entire length |
FW2-NT |
| BOILER DITCH (Egg Island) - Entire length | FW2-NT/SE1(C1) |
| BUCKS DITCH (Mad Horse Creek) - Entire length | SE1(C1) |
| BUCKSHUTEM CREEK (Centre Grove) - Entire length, except segments described separately below (Edward G. Bevan) - Creek and tributaries within the boundaries of Edward G. Bevan Wildlife Management Area, except those tributaries described separately below (Edward G. Bevan) - Joshua and Pine Branches to their confluence with Buckshutem Creek |
FW2-NT FW2-NT/C1 FW1 |
Source context and notes
(e) The following surface water classifications are for waters of the Lower Delaware River Basin: | Waterbody | Classification | | --- | --- | | ALLOWAY CREEK(Alloways) – Source to Greenwich Street, including all tributaries and Alloway Lake
(Quinton) – Greenwich Street to Delaware Bay
(Quinton) – All named and unnamed tributaries of Alloway Creek from Greenwich Street to Delaware Bay | FW2-NT
SE1
FW2-NT/SE1 | | ASSISCUNK CREEK
(Columbus) - Headwaters to confluence with Barkers Brook, including all tributaries
(Burlington) - Confluence with Barkers Brook to the Delaware River | FW2-NT/C1
FW2-NT | | BALDRIDGE CREEK
(Salem Creek) - Entire length, except segments described below
(Salem Creek) - Segments outside the boundaries of the Supawna National Wildlife Refuge | FW2-NT/SE1(C1)
FW2-NT/SE1 | | BAY PONDS (Egg Island)
BEADONS CREEK (Fortescue) - Entire length | FW2-NT/SE1(C1)
SE1(C1) | | BEAVERDAM BRANCH
(Glassboro) - Source to boundary of the Glassboro Wildlife Management Area
(Glassboro) - Within the boundaries of Glassboro Wildlife Management Area | FW2-NT
FW2-NT | | BIG TIMBER CREEK (Westville) - Entire length | FW2-NT | | BLACKBIRD GUT (Newport) - Entire length | SE1(C1) | | BLACKS CREEK (Bordentown) - Entire length | FW2-NT | | BLACKWATER BRANCH
(Vineland) – Entire length | FW2-NT | | BOILER DITCH (Egg Island) - Entire length | FW2-NT/SE1(C1) | | BUCKS DITCH (Mad Horse Creek) - Entire length | SE1(C1) | | BUCKSHUTEM CREEK
(Centre Grove) - Entire length, except segments described separately below
(Edward G. Bevan) - Creek and tributaries within the boundaries of Edward G. Bevan Wildlife Management Area, except those tributaries described separately below
(Edward G. Bevan) - Joshua and Pine Branches to their confluence with Buckshutem Creek | FW2-NT
FW2-NT/C1
FW1 |
24. Table 24¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 84
| Waterbody | Classification |
|---|---|
| AMES LAKE (Hibernia) | FW2-NT(C1) |
| APSHAWA BROOK (Macopin) - Entire length | FW2-TP(C1) |
| ARTHUR KILL | |
| (Perth Amboy) - The Kill and its saline New Jersey tributaries between the Outerbridge Crossing and a line connecting Ferry Pt., Perth Amboy to Wards Pt., Staten Island, New York | SE2 |
| (Elizabeth) - From an east-west line connecting Elizabethport with Bergen Pt., Bayonne to the Outerbridge Crossing | SE3 |
| (Woodbridge) - All freshwater tributaries | FW2-NT |
| BEAR BROOK | |
| (Washington) - Source to Spring Valley Road | FW2-NT(C1) |
| (Washington) - Spring Valley Road to Woodcliff Lake, including all tributaries | FW2-TM(C1) |
| BEAR SWAMP BROOK (Mahwah) - Entire length | FW2-TP(C1) |
| BEAR SWAMP LAKE (Ringwood State Park) | FW2-NT(C1) |
| BEAVER BROOK | |
| (Meriden) - From Splitrock Reservoir Dam downstream to Meriden Road Bridge | FW2-TP(C1) |
| (Denville) - Meriden Road Bridge to Rockaway River, including Mount Hope and White Meadow Lakes and all unnamed and unlisted tributaries | FW2-NT(C1) |
| TRIBUTARIES | |
| (Meriden) - Two tributaries located approximately three quarters of a mile southwest of Meriden | FW2-TP(C1) |
| BEECH BROOK | |
| (West Milford) - From State line downstream to Monksville Reservoir, including all tributaries | FW2-TP(C1) |
| BELCHER CREEK (W. Milford) - Entire length | FW2-NT |
| BERRYS CREEK (Secaucus) - Entire length | FW2-NT/SE2 |
| BLACK BROOK | |
| (Meyersville) - Entire length, except segment described below | FW2-NT |
| (Great Swamp) - Segment and tributaries within the Great Swamp National Wildlife Refuge | FW2-NT(C1) |
| BLUE MINE BROOK | |
| (Wanaque) - Headwaters downstream to lower Snake Den Road bridge | FW2-TP(C1) |
Source context and notes
(f) The following surface water classifications are for waters of the Passaic, Hackensack and New York Harbor Complex Basin: | Waterbody | Classification | | --- | --- | | AMES LAKE (Hibernia) | FW2-NT(C1) | | APSHAWA BROOK (Macopin) - Entire length | FW2-TP(C1) | | ARTHUR KILL | | | (Perth Amboy) - The Kill and its saline New Jersey tributaries between the Outerbridge Crossing and a line connecting Ferry Pt., Perth Amboy to Wards Pt., Staten Island, New York | SE2 | | (Elizabeth) - From an east-west line connecting Elizabethport with Bergen Pt., Bayonne to the Outerbridge Crossing | SE3 | | (Woodbridge) - All freshwater tributaries | FW2-NT | | BEAR BROOK | | | (Washington) - Source to Spring Valley Road | FW2-NT(C1) | | (Washington) - Spring Valley Road to Woodcliff Lake, including all tributaries | FW2-TM(C1) | | BEAR SWAMP BROOK (Mahwah) - Entire length | FW2-TP(C1) | | BEAR SWAMP LAKE (Ringwood State Park) | FW2-NT(C1) | | BEAVER BROOK | | | (Meriden) - From Splitrock Reservoir Dam downstream to Meriden Road Bridge | FW2-TP(C1) | | (Denville) - Meriden Road Bridge to Rockaway River, including Mount Hope and White Meadow Lakes and all unnamed and unlisted tributaries | FW2-NT(C1) | | TRIBUTARIES | | | (Meriden) - Two tributaries located approximately three quarters of a mile southwest of Meriden | FW2-TP(C1) | | BEECH BROOK | | | (West Milford) - From State line downstream to Monksville Reservoir, including all tributaries | FW2-TP(C1) | | BELCHER CREEK (W. Milford) - Entire length | FW2-NT | | BERRYS CREEK (Secaucus) - Entire length | FW2-NT/SE2 | | BLACK BROOK | | | (Meyersville) - Entire length, except segment described below | FW2-NT | | (Great Swamp) - Segment and tributaries within the Great Swamp National Wildlife Refuge | FW2-NT(C1) | | BLUE MINE BROOK | | | (Wanaque) - Headwaters downstream to lower Snake Den Road bridge | FW2-TP(C1) |25. Table 25¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 94
| Waterbody | Classification |
|---|---|
| ALLERTON CREEK (Allerton) - Entire length | FW2-NT |
| AMBROSE BROOK (Piscataway) - Entire length | FW2-NT |
| AMWELL LAKE (Syndertown) | FW2-NT(C1) |
| ASSISCONG CREEK (Flemington) - Entire length | FW2-NT |
| BACK BROOK (Vanliew's Corners) - Entire length | FW2-NT |
| BALDWINS CREEK | |
| (Pennington) - Entire length, except segment described separately below | FW2-NT |
| (Baldwin) - Segment within the boundaries of Baldwin Lake Wildlife Management Area | FW2-NT(C1) |
| BEAVER BROOK | |
| (Cokesbury) - Source to Reformatory Road bridge | FW2-TP(C1) |
| (Annandale) - Reformatory Rd. bridge to Beaver Ave., bridge | FW2-TM |
| (Annandale) - Beaver Ave. bridge downstream to South Branch Raritan River, including all tributaries | FW2-TP(C1) |
| BEDEN BROOK (Montgomery) - Entire length | FW2-NT |
| BLACK BROOK (Polktown) - Entire length | FW2-TP(C1) |
| BLACK RIVER - See LAMINGTON RIVER | |
| BLUE BROOK (Mountainside) - Entire length | FW2-NT |
| BOULDER HILL BROOK (Tewksbury) - Entire length | FW2-TP(C1) |
| BOUND BROOK (Dunellen) - Entire length | FW2-NT |
| BUDD LAKE (Mt. Olive) | FW2-NT(C1) |
| TRIBUTARIES | |
| (E. of Budd Lake) - Entire Length | FW2-TM |
| (W. of Budd Lake) - Entire Length | FW2-NT |
| BURNETT BROOK (Ralston) - Entire length | FW2-TP(C1) |
| BUSHKILL BROOK | |
| (Flemington) - Source and tributary downstream to Rt. 31 Bridge | FW2-TM |
| (Flemington) - Rt. 31 bridge downstream to South Branch Raritan River | FW2-NT |
| CAPOOLONG (CAKEPOULIN) CREEK (Sydney) - Entire length | FW2-TP(C1) |
| CHAMBERS BROOK (Whitehouse) - Entire length | FW2-NT |
| COLD BROOK (Oldwick) - Entire length | FW2-TP(C1) |
| CRAMERS CREEK (Hamden) - Entire length | FW2-NT |
| CRUSER BROOK (Montgomery) - Entire length | FW2-NT |
| CUCKELS BROOK (Bridgewater) - Entire length | FW2-NT |
| DAWSONS BROOK (Ironia) - Entire length | FW2-TP(C1) |
| DRAKES BROOK |
Source context and notes
(g) The following surface water classifications are for waters of the Upper Raritan River and Raritan Bay Basin: | Waterbody | Classification | | --- | --- | | ALLERTON CREEK (Allerton) - Entire length | FW2-NT | | AMBROSE BROOK (Piscataway) - Entire length | FW2-NT | | AMWELL LAKE (Syndertown) | FW2-NT(C1) | | ASSISCONG CREEK (Flemington) - Entire length | FW2-NT | | BACK BROOK (Vanliew's Corners) - Entire length | FW2-NT | | BALDWINS CREEK | | | (Pennington) - Entire length, except segment described separately below | FW2-NT | | (Baldwin) - Segment within the boundaries of Baldwin Lake Wildlife Management Area | FW2-NT(C1) | | BEAVER BROOK | | | (Cokesbury) - Source to Reformatory Road bridge | FW2-TP(C1) | | (Annandale) - Reformatory Rd. bridge to Beaver Ave., bridge | FW2-TM | | (Annandale) - Beaver Ave. bridge downstream to South Branch Raritan River, including all tributaries | FW2-TP(C1) | | BEDEN BROOK (Montgomery) - Entire length | FW2-NT | | BLACK BROOK (Polktown) - Entire length | FW2-TP(C1) | | BLACK RIVER - See LAMINGTON RIVER | | | BLUE BROOK (Mountainside) - Entire length | FW2-NT | | BOULDER HILL BROOK (Tewksbury) - Entire length | FW2-TP(C1) | | BOUND BROOK (Dunellen) - Entire length | FW2-NT | | BUDD LAKE (Mt. Olive) | FW2-NT(C1) | | TRIBUTARIES | | | (E. of Budd Lake) - Entire Length | FW2-TM | | (W. of Budd Lake) - Entire Length | FW2-NT | | BURNETT BROOK (Ralston) - Entire length | FW2-TP(C1) | | BUSHKILL BROOK | | | (Flemington) - Source and tributary downstream to Rt. 31 Bridge | FW2-TM | | (Flemington) - Rt. 31 bridge downstream to South Branch Raritan River | FW2-NT | | CAPOOLONG (CAKEPOULIN) CREEK (Sydney) - Entire length | FW2-TP(C1) | | CHAMBERS BROOK (Whitehouse) - Entire length | FW2-NT | | COLD BROOK (Oldwick) - Entire length | FW2-TP(C1) | | CRAMERS CREEK (Hamden) - Entire length | FW2-NT | | CRUSER BROOK (Montgomery) - Entire length | FW2-NT | | CUCKELS BROOK (Bridgewater) - Entire length | FW2-NT | | DAWSONS BROOK (Ironia) - Entire length | FW2-TP(C1) | | DRAKES BROOK | | 9026. Table 26¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 100
| Waterbody | Classification |
|---|---|
| BARCLAY BROOK (Redshaw Corners) - Entire length | FW2-NT |
| BEAR BROOK (West Windsor) - Entire length | FW2-NT |
| BIG BROOK (Vanderberg) - Entire length, including all tributaries and lakes | FW2-NT(C1) |
| BLACKBERRY CREEK | |
| (Oceanport) - Source to a line beginning on the easternmost extent of Gooseneck Point and bearing approximately 162 degrees True North to its terminus on the westernmost extent of an unnamed point of land in the vicinity of the western extent of Cayuga Ave. in Oceanport | SE1 |
| (Oceanport) - Creek below the line described above | SE1(C1) |
| BRANCHPORT CREEK | |
| (Long Branch) - Source to a line beginning on the northernmost extent of an unnamed point of land lying north of Pocano Ave. in Oceanport and bearing approximately 055 degrees True North to its terminus on the westernmost extent of the northern bulkhead at the lagoon located between France Rd. and Lori Rd. in Monmouth Beach | FW2-NT/SE1 |
| (Monmouth Beach) - Creek below line described above | SE1(C1) |
| CEDAR BROOK (Spotswood) - Entire length | FW2-NT |
| CHEESEQUAKE STATE PARK WATERS (S. Amboy) - Fresh waters within the park upstream of the limits of tidal influence | FW2-NT(C1) |
| CLAYPIT CREEK | |
| (Navesink) - Source to widening of the Creek near Linden Ave. and just north to the Locust Ave. bridge in Navesink | FW2-NT/SE1 |
| (Navesink) - Widening of Creek to Navesink River | SE1(C1) |
| CRANBURY BROOK (Old Church) - Entire length | FW2-NT |
| DEEP RUN (Old Bridge) - Entire length | FW2-NT |
| DEVILS BROOK (Schalks) - Entire length | FW2-NT |
| GANDER BROOK (Manalapan) - Entire length | FW2-NT |
| GREAT DITCH (S. Brunswick) - That portion of Great Ditch and its tributaries within Pigeon Swamp State Park | FW2-NT(C1) |
| IRELAND BROOK (Paulus Corners) - Entire length | FW2-NT |
| IRESICK BROOK (Spotswood) - Entire length | FW2-NT |
| LAWRENCE BROOK | |
| (Deans) - Source to the intake of the New Brunswick Water Department at Weston's Mill Dam | FW2-NT |
Source context and notes
(h) The following surface water classifications are for waters of the Lower Raritan River and Raritan Bay Basin: | Waterbody | Classification | | --- | --- | | BARCLAY BROOK (Redshaw Corners) - Entire length | FW2-NT | | BEAR BROOK (West Windsor) - Entire length | FW2-NT | | BIG BROOK (Vanderberg) - Entire length, including all tributaries and lakes | FW2-NT(C1) | | BLACKBERRY CREEK | | | (Oceanport) - Source to a line beginning on the easternmost extent of Gooseneck Point and bearing approximately 162 degrees True North to its terminus on the westernmost extent of an unnamed point of land in the vicinity of the western extent of Cayuga Ave. in Oceanport | SE1 | | (Oceanport) - Creek below the line described above | SE1(C1) | | BRANCHPORT CREEK | | | (Long Branch) - Source to a line beginning on the northernmost extent of an unnamed point of land lying north of Pocano Ave. in Oceanport and bearing approximately 055 degrees True North to its terminus on the westernmost extent of the northern bulkhead at the lagoon located between France Rd. and Lori Rd. in Monmouth Beach | FW2-NT/SE1 | | (Monmouth Beach) - Creek below line described above | SE1(C1) | | CEDAR BROOK (Spotswood) - Entire length | FW2-NT | | CHEESEQUAKE STATE PARK WATERS (S. Amboy) - Fresh waters within the park upstream of the limits of tidal influence | FW2-NT(C1) | | CLAYPIT CREEK | | | (Navesink) - Source to widening of the Creek near Linden Ave. and just north to the Locust Ave. bridge in Navesink | FW2-NT/SE1 | | (Navesink) - Widening of Creek to Navesink River | SE1(C1) | | CRANBURY BROOK (Old Church) - Entire length | FW2-NT | | DEEP RUN (Old Bridge) - Entire length | FW2-NT | | DEVILS BROOK (Schalks) - Entire length | FW2-NT | | GANDER BROOK (Manalapan) - Entire length | FW2-NT | | GREAT DITCH (S. Brunswick) - That portion of Great Ditch and its tributaries within Pigeon Swamp State Park | FW2-NT(C1) | | IRELAND BROOK (Paulus Corners) - Entire length | FW2-NT | | IRESICK BROOK (Spotswood) - Entire length | FW2-NT | | LAWRENCE BROOK | | | (Deans) - Source to the intake of the New Brunswick Water Department at Weston's Mill Dam | FW2-NT |27. Table 27¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 104
| Waterbody | Classification |
|---|---|
| BEARFORT WATERS (Wawayanda) | FW2-NT(C1) |
| BEAVER RUN (Wantage) - Entire length, except tributaries that originate in Wantage Township | FW2-NT(C1) |
| BLACK CREEK | |
| (McAfee) - Source to Rt. 94 bridge, except those tributaries described separately, below | FW2-TM |
| (Vernon) - Rt. 94 bridge to Pochuck Creek | FW2-NT |
| TRIBUTARIES | |
| (Hamburg) - Three tributaries to Black Creek which originate in the former Hamburg Mtn. Wildlife Management Area from their sources to the former Management Area boundaries | FW1(tm) |
| (Rudeville) - Tributaries within the former Hamburg Mtn. Wildlife Management Area not classified as FW1, above | FW2-TM(C1) |
| (McAfee) - Entire length | FW2-TP(C1) |
| (Vernon Valley) - Entire length | FW2-NT |
| BLUE HERON LAKE (Sparta) | FW2-NT(C1) |
| CEDAR SWAMP - See RUTGERS CREEK | |
| CLOVE CREEK (Colesville) - Entire length | FW2-TM |
| CLOVE BROOK | |
| (Wantage) - Source to, confluence with tributary originating from south of Mt. Salem, including all tributaries, except those tributaries described separately below | FW2-TM(C1) |
| (Wantage) — Tributary originating from south of Mt. Salem to Clove Acres Lake | FW2-TM |
| (Sussex) - Clove Acres Lake to Papakating Creek | FW2-NT |
| (High Point) - Those portions of the two northernmost tributaries located entirely within High Point State Park boundaries, immediately east of Lake Marcia | FW1(tp) |
| FRANKLIN POND (Hamburg Mtn.) | FW2-NT |
| TRIBUTARY (Franklin) - Southeastern tributary to Franklin Pond | FW2-NT(C1) |
| FRANKLIN POND CREEK | |
| (Hardyston) - Source to, but not including, Franklin Pond | FW2-TP(C1) |
| (Hamburg Mtn.) - Tributaries within the Hamburg Mtn. Wildlife Management Area | FW2-TM(C1) |
| TRIBUTARY (Hamburg Mtn.) - The first tributary to Franklin Pond Creek just south of Hamburg Mountain, flowing toward the Wallkill River and located entirely within the former Hamburg Mtn. Wildlife Management Area | FW1(tm) |
Source context and notes
(i) The following surface water classifications are for waters of the Wallkill River Basin: | Waterbody | Classification | | --- | --- | | BEARFORT WATERS (Wawayanda) | FW2-NT(C1) | | BEAVER RUN (Wantage) - Entire length, except tributaries that originate in Wantage Township | FW2-NT(C1) | | BLACK CREEK | | | (McAfee) - Source to Rt. 94 bridge, except those tributaries described separately, below | FW2-TM | | (Vernon) - Rt. 94 bridge to Pochuck Creek | FW2-NT | | TRIBUTARIES | | | (Hamburg) - Three tributaries to Black Creek which originate in the former Hamburg Mtn. Wildlife Management Area from their sources to the former Management Area boundaries | FW1(tm) | | (Rudeville) - Tributaries within the former Hamburg Mtn. Wildlife Management Area not classified as FW1, above | FW2-TM(C1) | | (McAfee) - Entire length | FW2-TP(C1) | | (Vernon Valley) - Entire length | FW2-NT | | BLUE HERON LAKE (Sparta) | FW2-NT(C1) | | CEDAR SWAMP - See RUTGERS CREEK | | | CLOVE CREEK (Colesville) - Entire length | FW2-TM | | CLOVE BROOK | | | (Wantage) - Source to, confluence with tributary originating from south of Mt. Salem, including all tributaries, except those tributaries described separately below | FW2-TM(C1) | | (Wantage) — Tributary originating from south of Mt. Salem to Clove Acres Lake | FW2-TM | | (Sussex) - Clove Acres Lake to Papakating Creek | FW2-NT | | (High Point) - Those portions of the two northernmost tributaries located entirely within High Point State Park boundaries, immediately east of Lake Marcia | FW1(tp) | | FRANKLIN POND (Hamburg Mtn.) | FW2-NT | | TRIBUTARY (Franklin) - Southeastern tributary to Franklin Pond | FW2-NT(C1) | | FRANKLIN POND CREEK | | | (Hardyston) - Source to, but not including, Franklin Pond | FW2-TP(C1) | | (Hamburg Mtn.) - Tributaries within the Hamburg Mtn. Wildlife Management Area | FW2-TM(C1) | | TRIBUTARY (Hamburg Mtn.) - The first tributary to Franklin Pond Creek just south of Hamburg Mountain, flowing toward the Wallkill River and located entirely within the former Hamburg Mtn. Wildlife Management Area | FW1(tm) |28. Table 28¶
N.J.A.C. 7:9B - Surface Water Quality Standards, PDF p. 107
| (Franklin) - Sparta Glen Brook to, but not including, Franklin Pond, including all unnamed and unlisted tributaries | FW2-TM(C1) |
|---|---|
| (Wantage) - Outlet of Franklin Pond to confluence with Beaver Run, including all unnamed and unlisted tributaries | FW2-NT(C1) |
| (Wantage) - Confluence with Beaver Run to Glenwood Road | FW2-NT |
| (Wantage) - Glenwood Road to confluence with Wantage Brook, including all unnamed and unlisted tributaries | FW2-NT(C1) |
| (Wantage) - Confluence with Wantage Brook to State line | FW2-NT |
| TRIBUTARIES | |
| (Sparta) - Entire length but not including Lake Saginaw | FW2-TP(C1) |
| (Sparta) - Unnamed standalone stream South of Pimple Hills | FW2-NT(C1) |
| (Ogdensburg) - Entire length | FW2-TP(C1) |
| (East of Quarryville) - Unnamed standalone stream segment east of Willow (Quarryville) Brook | FW2-NT(C1) |
| WANTAGE BROOK (Wantage) - Entire length, including all tributaries | FW2-NT |
| WAWAYANDA CREEK | |
| (Vernon) - State line to Pochuck Creek, except unnamed tributary described below | FW2-TM |
| TRIBUTARIES | |
| (Wawayanda) - Source to State line | FW2-NT |
| (Wawayanda State Park) - Segments within State Park boundaries, except Livingston Ponds Brook as noted above | FW2-NT(C1) |
| WAWAYANDA LAKE (Wawayanda) | FW2-TM(C1) |
| WHITE LAKE (Sparta) | FW2-TM(C1) |
| WILDCAT BROOK (Franklin) - Entire length, including all tributaries | FW2-NT(C1) |
| WILDWOOD LAKE (Hamburg Mountain) | FW2-NT(C1) |
| WILLOW (QUARRYVILLE) BROOK (Wantage) - Entire length, including all tributaries | FW2-TM |