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Plastics Materials And Resins, major discharger, Marietta, Ohio. NPDES permit OH0003905, in force until Aug 31, 2031. Last 12 months: no values over a limit. Source: EPA ECHO, Oct 22, 2026.
| Parameter | Statistic | Limit | Months | Outfall |
|---|---|---|---|---|
| Temperature, water deg. centigrade | monthly average | report only (deg C) | all year | 001 |
| Temperature, water deg. centigrade | daily maximum | report only (deg C) | all year | 001 |
| pH | daily minimum | ≥ 6.5 SU | all year | 001 |
| pH | daily maximum | ≤ 9 SU | all year | 001 |
| Flow, in conduit or thru treatment plant | monthly average | report only (MGD) | all year | 001 |
| Flow, in conduit or thru treatment plant | daily maximum | report only (MGD) | all year | 001 |
| Chlorine, total residual | daily maximum | ≤ .038 mg/L | Mar, Jun, Sep, Dec | 001 |
| BOD, 5-day, 20 deg. C | monthly average | ≤ 15.84 mg/L | all year | 002 |
| BOD, 5-day, 20 deg. C | daily maximum | ≤ 42.24 mg/L | all year | 002 |
| BOD, 5-day, 20 deg. C | monthly average | ≤ 60.8 kg/d | all year | 002 |
| BOD, 5-day, 20 deg. C | daily maximum | ≤ 162.1 kg/d | all year | 002 |
| Solids, total suspended | monthly average | ≤ 26.4 mg/L | all year | 002 |
| Solids, total suspended | daily maximum | ≤ 85.8 mg/L | all year | 002 |
| Solids, total suspended | monthly average | ≤ 101.3 kg/d | all year | 002 |
| Solids, total suspended | daily maximum | ≤ 329.3 kg/d | all year | 002 |
| Oil and grease, hexane extr method | daily maximum | ≤ 10 mg/L | all year | 002 |
| Cyanide, total [as CN] | monthly average | ≤ .277 mg/L | Sep | 002 |
| Cyanide, total [as CN] | daily maximum | ≤ .792 mg/L | Sep | 002 |
| Cyanide, total [as CN] | monthly average | ≤ 1.064 kg/d | Sep | 002 |
| Cyanide, total [as CN] | daily maximum | ≤ 3.04 kg/d | Sep | 002 |
| Chromium, total [as Cr] | monthly average | ≤ 732.6 ug/L | Sep | 002 |
| Chromium, total [as Cr] | daily maximum | ≤ 1828.2 ug/L | Sep | 002 |
| Chromium, total [as Cr] | monthly average | ≤ 2.812 kg/d | Sep | 002 |
| Chromium, total [as Cr] | daily maximum | ≤ 7.017 kg/d | Sep | 002 |
| Lead, total [as Pb] | monthly average | ≤ 211.2 ug/L | Sep | 002 |
| Lead, total [as Pb] | daily maximum | ≤ 455.4 ug/L | Sep | 002 |
| Lead, total [as Pb] | monthly average | ≤ .811 kg/d | Sep | 002 |
| Lead, total [as Pb] | daily maximum | ≤ 1.748 kg/d | Sep | 002 |
| Nickel, total [as Ni] | monthly average | ≤ 1115.4 ug/L | Sep | 002 |
| Nickel, total [as Ni] | daily maximum | ≤ 2626.8 ug/L | Sep | 002 |
| Nickel, total [as Ni] | monthly average | ≤ 4.281 kg/d | Sep | 002 |
| Nickel, total [as Ni] | daily maximum | ≤ 10.082 kg/d | Sep | 002 |
| Zinc, total [as Zn] | monthly average | ≤ 693 ug/L | Sep | 002 |
| Zinc, total [as Zn] | daily maximum | ≤ 1722.6 ug/L | Sep | 002 |
| Zinc, total [as Zn] | monthly average | ≤ 2.66 kg/d | Sep | 002 |
| Zinc, total [as Zn] | daily maximum | ≤ 6.612 kg/d | Sep | 002 |
| Copper, total recoverable | daily maximum | ≤ 234 ug/L | Sep | 002 |
| Copper, total recoverable | daily maximum | ≤ .898 kg/d | Sep | 002 |
| Coliform, fecal MF, MFC broth, 44.5 C | monthly geometric mean | ≤ 1000 #/100mL | Jan, Feb, Mar, Apr, Nov, Dec | 002 |
| Coliform, fecal MF, MFC broth, 44.5 C | weekly geometric mean | ≤ 2000 #/100mL | Jan, Feb, Mar, Apr, Nov, Dec | 002 |
| E. coli, MTEC-MF | monthly geometric mean | ≤ 126 MPN/100mL | May–Oct | 002 |
| E. coli, MTEC-MF | weekly geometric mean | ≤ 240 MPN/100mL | May–Oct | 002 |
| Carbon tetrachloride | monthly average | ≤ 11.88 ug/L | Sep | 002 |
| Carbon tetrachloride | daily maximum | ≤ 25.08 ug/L | Sep | 002 |
| Carbon tetrachloride | monthly average | ≤ .046 kg/d | Sep | 002 |
| Carbon tetrachloride | daily maximum | ≤ .096 kg/d | Sep | 002 |
| 1,2-Dichloroethane | monthly average | ≤ 44.88 ug/L | Sep | 002 |
| 1,2-Dichloroethane | daily maximum | ≤ 139.26 ug/L | Sep | 002 |
| 1,2-Dichloroethane | monthly average | ≤ .172 kg/d | Sep | 002 |
| 1,2-Dichloroethane | daily maximum | ≤ .535 kg/d | Sep | 002 |
| Chloroform | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| Chloroform | daily maximum | ≤ 30.36 ug/L | Sep | 002 |
| Chloroform | monthly average | ≤ .053 kg/d | Sep | 002 |
| Chloroform | daily maximum | ≤ .117 kg/d | Sep | 002 |
| Toluene | monthly average | ≤ 17.16 ug/L | Sep | 002 |
| Toluene | daily maximum | ≤ 52.8 ug/L | Sep | 002 |
| Toluene | monthly average | ≤ .066 kg/d | Sep | 002 |
| Toluene | daily maximum | ≤ .203 kg/d | Sep | 002 |
| Benzene | monthly average | ≤ 24.42 ug/L | Sep | 002 |
| Benzene | daily maximum | ≤ 89.76 ug/L | Sep | 002 |
| Benzene | monthly average | ≤ .094 kg/d | Sep | 002 |
| Benzene | daily maximum | ≤ .345 kg/d | Sep | 002 |
| Acenaphthylene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Acenaphthylene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Acenaphthylene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Acenaphthylene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Acenaphthene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Acenaphthene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Acenaphthene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Acenaphthene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Acrylonitrile | monthly average | ≤ 63.36 ug/L | Sep | 002 |
| Acrylonitrile | daily maximum | ≤ 159.72 ug/L | Sep | 002 |
| Acrylonitrile | monthly average | ≤ .243 kg/d | Sep | 002 |
| Acrylonitrile | daily maximum | ≤ .613 kg/d | Sep | 002 |
| Anthracene | daily maximum | ≤ 2.49 ug/L | Sep | 002 |
| Anthracene | daily maximum | ≤ .0096 kg/d | Sep | 002 |
| Benzo[b]fluoranthene | monthly average | ≤ 15.18 ug/L | Sep | 002 |
| Benzo[b]fluoranthene | daily maximum | ≤ 40.26 ug/L | Sep | 002 |
| Benzo[b]fluoranthene | monthly average | ≤ .058 kg/d | Sep | 002 |
| Benzo[b]fluoranthene | daily maximum | ≤ .155 kg/d | Sep | 002 |
| Benzo[k]fluoranthene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Benzo[k]fluoranthene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Benzo[k]fluoranthene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Benzo[k]fluoranthene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Benzo[a]pyrene | monthly average | ≤ 2.4 ug/L | Sep | 002 |
| Benzo[a]pyrene | daily maximum | ≤ 40.26 ug/L | Sep | 002 |
| Benzo[a]pyrene | monthly average | ≤ .0092 kg/d | Sep | 002 |
| Benzo[a]pyrene | daily maximum | ≤ .155 kg/d | Sep | 002 |
| Chlorobenzene | monthly average | ≤ 9.9 ug/L | Sep | 002 |
| Chlorobenzene | daily maximum | ≤ 18.48 ug/L | Sep | 002 |
| Chlorobenzene | monthly average | ≤ .038 kg/d | Sep | 002 |
| Chlorobenzene | daily maximum | ≤ .071 kg/d | Sep | 002 |
| Chrysene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Chrysene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Chrysene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Chrysene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Diethyl phthalate | monthly average | ≤ 53.46 ug/L | Sep | 002 |
| Diethyl phthalate | daily maximum | ≤ 133.98 ug/L | Sep | 002 |
| Diethyl phthalate | monthly average | ≤ .205 kg/d | Sep | 002 |
| Diethyl phthalate | daily maximum | ≤ .514 kg/d | Sep | 002 |
| Dimethyl phthalate | monthly average | ≤ 12.54 ug/L | Sep | 002 |
| Dimethyl phthalate | daily maximum | ≤ 31.02 ug/L | Sep | 002 |
| Dimethyl phthalate | monthly average | ≤ .048 kg/d | Sep | 002 |
| Dimethyl phthalate | daily maximum | ≤ .119 kg/d | Sep | 002 |
| Ethylbenzene | monthly average | ≤ 21.12 ug/L | Sep | 002 |
| Ethylbenzene | daily maximum | ≤ 71.28 ug/L | Sep | 002 |
| Ethylbenzene | monthly average | ≤ .081 kg/d | Sep | 002 |
| Ethylbenzene | daily maximum | ≤ .274 kg/d | Sep | 002 |
| Fluoranthene | monthly average | ≤ 16.5 ug/L | Sep | 002 |
| Fluoranthene | daily maximum | ≤ 44.88 ug/L | Sep | 002 |
| Fluoranthene | monthly average | ≤ .063 kg/d | Sep | 002 |
| Fluoranthene | daily maximum | ≤ .172 kg/d | Sep | 002 |
| Fluorene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Fluorene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Fluorene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Fluorene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Hexachloroethane | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| Hexachloroethane | daily maximum | ≤ 35.64 ug/L | Sep | 002 |
| Hexachloroethane | monthly average | ≤ .053 kg/d | Sep | 002 |
| Hexachloroethane | daily maximum | ≤ .137 kg/d | Sep | 002 |
| Methyl chloride [Chloromethane] | monthly average | ≤ 56.76 ug/L | Sep | 002 |
| Methyl chloride [Chloromethane] | daily maximum | ≤ 125.4 ug/L | Sep | 002 |
| Methyl chloride [Chloromethane] | monthly average | ≤ .218 kg/d | Sep | 002 |
| Methyl chloride [Chloromethane] | daily maximum | ≤ .481 kg/d | Sep | 002 |
| Methylene chloride | monthly average | ≤ 26.4 ug/L | Sep | 002 |
| Methylene chloride | daily maximum | ≤ 58.74 ug/L | Sep | 002 |
| Methylene chloride | monthly average | ≤ .101 kg/d | Sep | 002 |
| Methylene chloride | daily maximum | ≤ .225 kg/d | Sep | 002 |
| Nitrobenzene | monthly average | ≤ 17.82 ug/L | Sep | 002 |
| Nitrobenzene | daily maximum | ≤ 44.88 ug/L | Sep | 002 |
| Nitrobenzene | monthly average | ≤ .068 kg/d | Sep | 002 |
| Nitrobenzene | daily maximum | ≤ .172 kg/d | Sep | 002 |
| Phenanthrene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Phenanthrene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Phenanthrene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Phenanthrene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Pyrene | monthly average | ≤ 16.5 ug/L | Sep | 002 |
| Pyrene | daily maximum | ≤ 44.22 ug/L | Sep | 002 |
| Pyrene | monthly average | ≤ .063 kg/d | Sep | 002 |
| Pyrene | daily maximum | ≤ .17 kg/d | Sep | 002 |
| Tetrachloroethylene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Tetrachloroethylene | daily maximum | ≤ 36.96 ug/L | Sep | 002 |
| Tetrachloroethylene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Tetrachloroethylene | daily maximum | ≤ .142 kg/d | Sep | 002 |
| 1,1-Dichloroethane | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| 1,1-Dichloroethane | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| 1,1-Dichloroethane | monthly average | ≤ .056 kg/d | Sep | 002 |
| 1,1-Dichloroethane | daily maximum | ≤ .149 kg/d | Sep | 002 |
| 1,1-Dichloroethylene | monthly average | ≤ 10.56 ug/L | Sep | 002 |
| 1,1-Dichloroethylene | daily maximum | ≤ 16.5 ug/L | Sep | 002 |
| 1,1-Dichloroethylene | monthly average | ≤ .041 kg/d | Sep | 002 |
| 1,1-Dichloroethylene | daily maximum | ≤ .063 kg/d | Sep | 002 |
| 1,1,1-Trichloroethane | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| 1,1,1-Trichloroethane | daily maximum | ≤ 35.64 ug/L | Sep | 002 |
| 1,1,1-Trichloroethane | monthly average | ≤ .053 kg/d | Sep | 002 |
| 1,1,1-Trichloroethane | daily maximum | ≤ .137 kg/d | Sep | 002 |
| 1,1,2-Trichloroethane | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| 1,1,2-Trichloroethane | daily maximum | ≤ 35.64 ug/L | Sep | 002 |
| 1,1,2-Trichloroethane | monthly average | ≤ .053 kg/d | Sep | 002 |
| 1,1,2-Trichloroethane | daily maximum | ≤ .137 kg/d | Sep | 002 |
| Benzo[a]anthracene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Benzo[a]anthracene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Benzo[a]anthracene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Benzo[a]anthracene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| 1,2-Dichlorobenzene | monthly average | ≤ 50.82 ug/L | Sep | 002 |
| 1,2-Dichlorobenzene | daily maximum | ≤ 107.58 ug/L | Sep | 002 |
| 1,2-Dichlorobenzene | monthly average | ≤ .195 kg/d | Sep | 002 |
| 1,2-Dichlorobenzene | daily maximum | ≤ .413 kg/d | Sep | 002 |
| 1,2-Dichloropropane | monthly average | ≤ 100.98 ug/L | Sep | 002 |
| 1,2-Dichloropropane | daily maximum | ≤ 151.8 ug/L | Sep | 002 |
| 1,2-Dichloropropane | monthly average | ≤ .388 kg/d | Sep | 002 |
| 1,2-Dichloropropane | daily maximum | ≤ .583 kg/d | Sep | 002 |
| trans-1,2-Dichloroethylene | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| trans-1,2-Dichloroethylene | daily maximum | ≤ 35.64 ug/L | Sep | 002 |
| trans-1,2-Dichloroethylene | monthly average | ≤ .053 kg/d | Sep | 002 |
| trans-1,2-Dichloroethylene | daily maximum | ≤ .137 kg/d | Sep | 002 |
| 1,2,4-Trichlorobenzene | monthly average | ≤ 44.88 ug/L | Sep | 002 |
| 1,2,4-Trichlorobenzene | daily maximum | ≤ 92.4 ug/L | Sep | 002 |
| 1,2,4-Trichlorobenzene | monthly average | ≤ .172 kg/d | Sep | 002 |
| 1,2,4-Trichlorobenzene | daily maximum | ≤ .355 kg/d | Sep | 002 |
| 1,3-Dichlorobenzene | monthly average | ≤ 20.46 ug/L | Sep | 002 |
| 1,3-Dichlorobenzene | daily maximum | ≤ 29.04 ug/L | Sep | 002 |
| 1,3-Dichlorobenzene | monthly average | ≤ .079 kg/d | Sep | 002 |
| 1,3-Dichlorobenzene | daily maximum | ≤ .111 kg/d | Sep | 002 |
| 1,4-Dichlorobenzene | monthly average | ≤ 9.9 ug/L | Sep | 002 |
| 1,4-Dichlorobenzene | daily maximum | ≤ 18.48 ug/L | Sep | 002 |
| 1,4-Dichlorobenzene | monthly average | ≤ .038 kg/d | Sep | 002 |
| 1,4-Dichlorobenzene | daily maximum | ≤ .071 kg/d | Sep | 002 |
| 2-Chlorophenol | monthly average | ≤ 20.46 ug/L | Sep | 002 |
| 2-Chlorophenol | daily maximum | ≤ 64.68 ug/L | Sep | 002 |
| 2-Chlorophenol | monthly average | ≤ .079 kg/d | Sep | 002 |
| 2-Chlorophenol | daily maximum | ≤ .248 kg/d | Sep | 002 |
| 2-Nitrophenol | monthly average | ≤ 27.06 ug/L | Sep | 002 |
| 2-Nitrophenol | daily maximum | ≤ 45.54 ug/L | Sep | 002 |
| 2-Nitrophenol | monthly average | ≤ .104 kg/d | Sep | 002 |
| 2-Nitrophenol | daily maximum | ≤ .175 kg/d | Sep | 002 |
| 2,4-Dichlorophenol | monthly average | ≤ 25.74 ug/L | Sep | 002 |
| 2,4-Dichlorophenol | daily maximum | ≤ 73.92 ug/L | Sep | 002 |
| 2,4-Dichlorophenol | monthly average | ≤ .099 kg/d | Sep | 002 |
| 2,4-Dichlorophenol | daily maximum | ≤ .284 kg/d | Sep | 002 |
| 2,4-Dimethylphenol | monthly average | ≤ 11.88 ug/L | Sep | 002 |
| 2,4-Dimethylphenol | daily maximum | ≤ 23.76 ug/L | Sep | 002 |
| 2,4-Dimethylphenol | monthly average | ≤ .046 kg/d | Sep | 002 |
| 2,4-Dimethylphenol | daily maximum | ≤ .091 kg/d | Sep | 002 |
| 2,4-Dinitrotoluene | monthly average | ≤ 74.58 ug/L | Sep | 002 |
| 2,4-Dinitrotoluene | daily maximum | ≤ 188.1 ug/L | Sep | 002 |
| 2,4-Dinitrotoluene | monthly average | ≤ .285 kg/d | Sep | 002 |
| 2,4-Dinitrotoluene | daily maximum | ≤ .722 kg/d | Sep | 002 |
| 2,4-Dinitrophenol | monthly average | ≤ 46.86 ug/L | Sep | 002 |
| 2,4-Dinitrophenol | daily maximum | ≤ 81.18 ug/L | Sep | 002 |
| 2,4-Dinitrophenol | monthly average | ≤ .18 kg/d | Sep | 002 |
| 2,4-Dinitrophenol | daily maximum | ≤ .312 kg/d | Sep | 002 |
| 2,6-Dinitrotoluene | monthly average | ≤ 168.3 ug/L | Sep | 002 |
| 2,6-Dinitrotoluene | daily maximum | ≤ 423.06 ug/L | Sep | 002 |
| 2,6-Dinitrotoluene | monthly average | ≤ .646 kg/d | Sep | 002 |
| 2,6-Dinitrotoluene | daily maximum | ≤ 1.624 kg/d | Sep | 002 |
| 4-Nitrophenol | monthly average | ≤ 47.52 ug/L | Sep | 002 |
| 4-Nitrophenol | daily maximum | ≤ 81.84 ug/L | Sep | 002 |
| 4-Nitrophenol | monthly average | ≤ .182 kg/d | Sep | 002 |
| 4-Nitrophenol | daily maximum | ≤ .314 kg/d | Sep | 002 |
| 4,6-Dinitro-o-cresol | monthly average | ≤ 51.48 ug/L | Sep | 002 |
| 4,6-Dinitro-o-cresol | daily maximum | ≤ 182.82 ug/L | Sep | 002 |
| 4,6-Dinitro-o-cresol | monthly average | ≤ .198 kg/d | Sep | 002 |
| 4,6-Dinitro-o-cresol | daily maximum | ≤ .702 kg/d | Sep | 002 |
| Phenol | monthly average | ≤ 9.9 ug/L | Sep | 002 |
| Phenol | daily maximum | ≤ 17.16 ug/L | Sep | 002 |
| Phenol | monthly average | ≤ .038 kg/d | Sep | 002 |
| Phenol | daily maximum | ≤ .066 kg/d | Sep | 002 |
| Naphthalene | monthly average | ≤ 14.52 ug/L | Sep | 002 |
| Naphthalene | daily maximum | ≤ 38.94 ug/L | Sep | 002 |
| Naphthalene | monthly average | ≤ .056 kg/d | Sep | 002 |
| Naphthalene | daily maximum | ≤ .149 kg/d | Sep | 002 |
| Di[2-ethylhexyl] phthalate [DEHP] | monthly average | ≤ 67.98 ug/L | Sep | 002 |
| Di[2-ethylhexyl] phthalate [DEHP] | daily maximum | ≤ 184.14 ug/L | Sep | 002 |
| Di[2-ethylhexyl] phthalate [DEHP] | monthly average | ≤ .261 kg/d | Sep | 002 |
| Di[2-ethylhexyl] phthalate [DEHP] | daily maximum | ≤ .707 kg/d | Sep | 002 |
| Di-n-butyl phthalate | monthly average | ≤ 17.82 ug/L | Sep | 002 |
| Di-n-butyl phthalate | daily maximum | ≤ 37.62 ug/L | Sep | 002 |
| Di-n-butyl phthalate | monthly average | ≤ .068 kg/d | Sep | 002 |
| Di-n-butyl phthalate | daily maximum | ≤ .144 kg/d | Sep | 002 |
| Vinyl chloride | monthly average | ≤ 68.64 ug/L | Sep | 002 |
| Vinyl chloride | daily maximum | ≤ 176.88 ug/L | Sep | 002 |
| Vinyl chloride | monthly average | ≤ .263 kg/d | Sep | 002 |
| Vinyl chloride | daily maximum | ≤ .679 kg/d | Sep | 002 |
| Trichloroethylene | monthly average | ≤ 13.86 ug/L | Sep | 002 |
| Trichloroethylene | daily maximum | ≤ 35.64 ug/L | Sep | 002 |
| Trichloroethylene | monthly average | ≤ .053 kg/d | Sep | 002 |
| Trichloroethylene | daily maximum | ≤ .137 kg/d | Sep | 002 |
| Hexachlorobenzene | monthly average | ≤ .00079 ug/L | Sep | 002 |
| Hexachlorobenzene | daily maximum | ≤ 18.48 ug/L | Sep | 002 |
| Hexachlorobenzene | monthly average | ≤ .000003 kg/d | Sep | 002 |
| Hexachlorobenzene | daily maximum | ≤ .071 kg/d | Sep | 002 |
| Hexachlorobutadiene | monthly average | ≤ .1 ug/L | Sep | 002 |
| Hexachlorobutadiene | daily maximum | ≤ 32.34 ug/L | Sep | 002 |
| Hexachlorobutadiene | monthly average | ≤ .00038 kg/d | Sep | 002 |
| Hexachlorobutadiene | daily maximum | ≤ .125 kg/d | Sep | 002 |
| Flow, in conduit or thru treatment plant | monthly average | report only (MGD) | all year | 002 |
| Flow, in conduit or thru treatment plant | daily maximum | report only (MGD) | all year | 002 |
| Toxicity [acute], Ceriodaphnia dubia | monthly average | report only (tox acute) | Mar, Sep | 002 |
| Toxicity [acute], Ceriodaphnia dubia | daily maximum | report only (tox acute) | Mar, Sep | 002 |
| Toxicity [acute], Pimephales promelas [Fathead Minnow] | monthly average | report only (tox acute) | Sep | 002 |
| Toxicity [acute], Pimephales promelas [Fathead Minnow] | daily maximum | report only (tox acute) | Sep | 002 |
| pH, maximum | daily maximum | report only (SU) | all year | 002 |
| pH, minimum | daily minimum | report only (SU) | all year | 002 |
| Solids, total dissolved- 180 deg. C | monthly average | report only (mg/L) | all year | 002 |
| Solids, total dissolved- 180 deg. C | daily maximum | report only (mg/L) | all year | 002 |
| 1,3-Dichloropropene | monthly average | ≤ 19.14 ug/L | Sep | 002 |
| 1,3-Dichloropropene | daily maximum | ≤ 29.04 ug/L | Sep | 002 |
| 1,3-Dichloropropene | monthly average | ≤ .073 kg/d | Sep | 002 |
| 1,3-Dichloropropene | daily maximum | ≤ .111 kg/d | Sep | 002 |
| pH range excursions, > 60 minutes | daily maximum | ≤ 0 occur/d | all year | 002 |
| pH range excursions, monthly total accum | daily maximum | ≤ 446 min | all year | 002 |
| Chloroethane | monthly average | ≤ 68.64 ug/L | Sep | 002 |
| Chloroethane | daily maximum | ≤ 176.88 ug/L | Sep | 002 |
| Chloroethane | monthly average | ≤ .263 kg/d | Sep | 002 |
| Chloroethane | daily maximum | ≤ .679 kg/d | Sep | 002 |
| %Effect Static Renewal 48Hr Acute Ceriodaphnia dubia | monthly average | report only (%) | Mar, Sep | 801 |
| %Effect Static Renewal 48Hr Acute Ceriodaphnia dubia | daily maximum | report only (%) | Mar, Sep | 801 |
| %Effect Static Renewal 96Hr Acute Pimephales promelas | monthly average | report only (%) | Sep | 801 |
| %Effect Static Renewal 96Hr Acute Pimephales promelas | daily maximum | report only (%) | Sep | 801 |
Cited limits by parameter: Ohio's rules and the federal ones.
Same industry: the 68 Chemicals and Allied Products permits in Ohio.
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