groundwater

Ohio Groundwater Standards - Volatile Organic Compounds (VOCs)

Current Ohio VAP and generic groundwater standards for common VOCs including benzene, TCE, PCE, and vinyl chloride. Cited to OAC 3745-300.

Verified March 20, 2026 Source: Ohio Administrative Code 3745-300

Overview

Ohio’s Voluntary Action Program (VAP) establishes generic cleanup standards for groundwater under OAC 3745-300. The values below are Unrestricted Potable Use Standards (UPUS) - the default and most restrictive groundwater classification, which assumes groundwater is or could be used as a drinking water source.

The UPUS is the lower of the risk-based groundwater concentration and the Safe Drinking Water Act MCL. For most VOCs with MCLs, the MCL governs. For contaminants without MCLs (like MTBE), the risk-based value is the standard.

Other groundwater classifications: If groundwater at your site is classified as restricted potable use (RPUS) or non-potable (RNPUS) under OAC 3745-300-07, less restrictive standards may apply. See the VAP Program Overview for details on groundwater classification and Urban Setting Designations.

VOC Groundwater Standards

Showing 101 of 101 chemicals
Chemical CAS Number VAP UPUS (µg/L) MCL (µg/L)
Acetaldehyde 75-07-0 19 NL
Acetone 67-64-1 18,000 NL
Acetonitrile 75-05-8 130 NL
Acrolein 107-02-8 0.04154 NL
Acrylic Acid 79-10-7 0.41713 NL
Acrylonitrile 107-13-1 0.52327 NL
Allyl Alcohol 107-18-6 80 NL
Allyl Chloride 107-05-1 2.1 NL
Benzene 71-43-2 5 5
Benzotrichloride 98-07-7 0.02996 NL
Benzyl Chloride 100-44-7 0.8924 NL
Bis(2-chloro-1-methylethyl) Ether 108-60-1 710 NL
Bromodichloromethane 75-27-4 80 (b) 80
Bromoform 75-25-2 80 (b) 80
Bromomethane 74-83-9 7.5 NL
Butadiene, 1,3- 106-99-0 0.7077 NL
Butanol, N- 71-36-3 2,000 NL
Butylbenzene, n- 104-51-8 1,000 NL
Carbon Disulfide 75-15-0 810 NL
Carbon Tetrachloride 56-23-5 5 5
Carbonyl Sulfide 463-58-1 210 NL
Chlorobenzene 108-90-7 100 100
Chloro-1,3-butadiene, 2- 126-99-8 0.18718 NL
Chloroform 67-66-3 80 (b) 80
Chloromethane 74-87-3 190 NL
Chloromethyl Methyl Ether 107-30-2 0.06495 NL
Crotonaldehyde, trans- 123-73-9 0.40396 NL
Cumene 98-82-8 450 NL
Cyclohexane 110-82-7 13,000 NL
Cyclohexanone 108-94-1 1,400 NL
Dibromo-3-chloropropane, 1,2- 96-12-8 0.2 0.2
Dibromochloromethane 124-48-1 80 (b) 80 (b)
Dibromoethane, 1,2- 106-93-4 0.05 0.05
Dichloro-2-butene, 1,4- 764-41-0 0.01337 NL
Dichlorodifluoromethane 75-71-8 3,600 NL
Dichloroethane, 1,1- 75-34-3 28 NL
Dichloroethane, 1,2- 107-06-2 5 5
Dichloroethylene, 1,1- 75-35-4 7 7
Dichloroethylene, 1,2-cis- 156-59-2 70 70
Dichloroethylene, 1,2-trans- 156-60-5 100 100
Dichloropropane, 1,2- 78-87-5 5 5
Dichloropropane, 1,3- 142-28-9 370 NL
Dichloropropene, 1,3- 542-75-6 4.7 NL
Dihydrosafrole 94-58-6 3 NL
Dimethylaniline, N,N- 121-69-7 25 NL
Dimethylformamide 68-12-2 61 NL
Dimethylhydrazine, 1,2- 540-73-8 0.00028 NL
Dioxane, 1,4- 123-91-1 4.6 NL
Epoxybutane, 1,2- 106-88-7 42 NL
Ethoxyethanol, 2- 110-80-5 80 NL
Ethyl Acetate 141-78-6 140 NL
Ethyl Acrylate 140-88-5 14 NL
Ethyl Chloride (Chloroethane) 75-00-3 8,300 NL
Ethyl Ether 60-29-7 3,900 NL
Ethyl Methacrylate 97-63-2 630 NL
Ethylbenzene 100-41-4 700 700
Ethylene Diamine 107-15-3 1,800 NL
Ethylene Oxide 75-21-8 0.0067 NL
Ethyleneimine 151-56-4 0.00237 NL
Formaldehyde 50-00-0 3.9 NL
Formic Acid 64-18-6 18,000 NL
Glycidaldehyde 765-34-4 1.7 NL
Hexane, N- 110-54-3 1,500 NL
Hydrazine 302-01-2 0.01098 NL
Isobutyl Alcohol 78-83-1 5,900 NL
Methacrylonitrile 126-98-7 1.9 NL
Methanol 67-56-1 20,000 NL
Methyl Ethyl Ketone (2-Butanone) 78-93-3 5,600 NL
Methyl Hydrazine 60-34-4 20 NL
Methyl Isobutyl Ketone (4-methyl-2-pentanone) 108-10-1 6,300 NL
Methyl Isocyanate 624-83-9 2.1 NL
Methyl Methacrylate 80-62-6 1,400 NL
Methyl tert-Butyl Ether (MTBE) 1634-04-4 140 NL
Methylene Chloride 75-09-2 5 5
Naphthalene 91-20-3 1.2 NL
Nickel Carbonyl 13463-39-3 0.0292 NL
Phosgene 75-44-5 0.62571 NL
Propargyl Alcohol 107-19-7 40 NL
Propionaldehyde 123-38-6 17 NL
Propylene Oxide 75-56-9 2.7 NL
Styrene 100-42-5 100 100
Tetrachlorobenzene, 1,2,4,5- 95-94-3 0.17052 NL
Tetrachloroethane, 1,1,1,2- 630-20-6 5.7 NL
Tetrachloroethane, 1,1,2,2- 79-34-5 0.75736 NL
Tetrachloroethylene 127-18-4 5 5
Toluene 108-88-3 1,000 1,000
Trichloroethane, 1,1,1- 71-55-6 200 200
Trichloroethane, 1,1,2- 79-00-5 5 5
Trichloroethylene 79-01-6 5 5
Trichlorofluoromethane 75-69-4 5,200 NL
Triethylamine 121-44-8 15 NL
Vinyl Acetate 108-05-4 410 NL
Vinyl Bromide 593-60-2 3.7 NL
Vinyl Chloride 75-01-4 2 2
Xylenes 1330-20-7 10,000 10,000
Butylbenzene, sec- 135-98-8 2,000 NL
Butylbenzene, tert- 98-06-6 690 NL
Chloroacetaldehyde, 2- 107-20-0 2.9 NL
Dibromomethane (Methylene Bromide) 74-95-3 8.3 NL
Dimethylhydrazine, 1,1- 57-14-7 0.00416 NL
Propyl benzene 103-65-1 650 NL

† Listed in CIDARS under Supplemental Criteria rather than as an Appendix A generic numerical standard.

Qualifier key:

  • (b) MCL is for Total Trihalomethanes. The 80 µg/L value applies to the sum of the four trihalomethanes, not to each compound individually.

Practical Notes for Consultants

Sampling considerations: When collecting groundwater samples for VOC analysis, use 40 mL glass VOA vials with HCl preservative and zero headspace. Low-flow sampling is the standard method per Ohio EPA guidance - purge at <500 mL/min until field parameters stabilize.

Lab methods: Request EPA Method 8260 (or 8260C) for full VOC analysis. If you only need BTEX, some labs offer a cheaper BTEX-specific package, but 8260 gives you the full chlorinated solvent suite which is almost always worth having at Ohio sites.

Common pitfall: Vinyl chloride is frequently the risk driver at chlorinated solvent sites because its standard (2 µg/L) is tighter than TCE or PCE (both 5 µg/L), and it’s a degradation product that can persist in groundwater. Always include it in your analyte list even if the primary contaminant of concern is TCE or PCE.

BTEX vs. chlorinated solvents: At petroleum UST sites, BTEX compounds are typically the focus. At dry cleaner or industrial sites, the chlorinated solvent suite (TCE, PCE, DCE, vinyl chloride) is more relevant. Many Ohio sites have both - don’t assume one excludes the other.

When These Standards Apply

Ohio VAP generic standards apply to:

  • Properties enrolled in the Ohio Voluntary Action Program
  • Phase II ESA screening level comparisons (common practice even outside VAP)
  • Remediation goal-setting when a property owner elects to use generic standards rather than site-specific risk assessment

They do not directly apply to:

  • RCRA corrective action sites (which use separate OEPA guidance)
  • Federal Superfund (CERCLA) sites (which use EPA RSLs or site-specific values)
  • Drinking water compliance (which uses MCLs under the Safe Drinking Water Act)
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Ohio VAP generic groundwater standards for VOCs - ready for your report appendix.

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