Indiana Groundwater Published Levels - SVOCs and PAHs
IDEM Published Level Table 1 groundwater standards for SVOCs and PAHs in Indiana. 202 chemicals. No commercial/industrial groundwater levels published.
Overview
These are Indiana’s Published Level Table 1 groundwater standards for semi-volatile organic compounds (SVOCs) and polycyclic aromatic hydrocarbons (PAHs), from the IDEM Remediation Closure Guide (WASTE-0046-R2), effective March 28, 2025.
Risk basis: Indiana’s published levels use a 1E-05 cancer risk (1 in 100,000) and HQ of 1.0 - 10 times less conservative than EPA’s default 1E-06. For carcinogenic SVOCs and PAHs, Indiana’s groundwater values are approximately 10 times higher than default EPA Regional Screening Levels.
Residential values only: IDEM does not publish commercial/industrial groundwater screening levels (Remediation Closure Guide, Section 3.3). Groundwater is evaluated under a single residential use scenario.
Qualifier key:
- C = Carcinogenic
- N = Noncarcinogenic
- M = MCL-based
- D = Detection limit-based
Blank cells indicate no published level for that chemical - not zero.
Groundwater Published Levels - SVOCs and PAHs
| Chemical | CAS Number | Residential (µg/L) | Q |
|---|---|---|---|
| Acenaphthene | 83-32-9 | 500 | N |
| Acetophenone | 98-86-2 | 2,000 | N |
| Acetylaminofluorene, 2- | 53-96-3 | 0.2 | C |
| Aminobiphenyl, 4- | 92-67-1 | 0.03 | C |
| Aminophenol, m- | 591-27-5 | 2,000 | N |
| Aminophenol, o- | 95-55-6 | 80 | N |
| Aminophenol, p- | 123-30-8 | 400 | N |
| Aniline | 62-53-3 | 100 | C |
| Anthracene | 120-12-7 | 2,000 | N |
| Anthraquinone, 9,10- | 84-65-1 | 10 | C |
| Auramine | 492-80-8 | 0.8 | C |
| Azobenzene | 103-33-3 | 1 | C |
| Azodicarbonamide | 123-77-3 | 20,000 | N |
| Benz[a]anthracene | 56-55-3 | 0.3 | C |
| Benzaldehyde | 100-52-7 | 200 | C |
| Benzenethiol | 108-98-5 | 20 | N |
| Benzidine | 92-87-5 | 0.001 | C |
| Benzo[a]pyrene | 50-32-8 | 0.2 | M |
| Benzo[b]fluoranthene | 205-99-2 | 3 | C |
| Benzo[e]pyrene | 192-97-2 | 2 | N |
| Benzo[j]fluoranthene | 205-82-3 | 0.7 | C |
| Benzo[k]fluoranthene | 207-08-9 | 30 | C |
| Benzofluorene, 2,3- | 243-17-4 | 100 | N |
| Benzoic Acid | 65-85-0 | 80,000 | N |
| Benzotrichloride | 98-07-7 | 0.03 | C |
| Benzyl Alcohol | 100-51-6 | 2,000 | N |
| Biphenyl, 1,1'- | 92-52-4 | 0.8 | N |
| Bis(2-ethylhexyl)phthalate | 117-81-7 | 6 | M |
| Bisphenol A | 80-05-7 | 800 | N |
| Bromo-3-fluorobenzene, 1- | 1073-06-9 | 5 | N |
| Bromo-4-fluorobenzene, 1- | 460-00-4 | 5 | N |
| Butyl Benzyl Phthalate | 85-68-7 | 200 | C |
| Chloro-2-methylaniline HCl, 4- | 3165-93-3 | 2 | C |
| Chloro-2-methylaniline, 4- | 95-69-2 | 7 | C |
| Chloroaniline, p- | 106-47-8 | 4 | C |
| Chlorobenzene sulfonic acid, p- | 98-66-8 | 2,000 | N |
| Chlorobenzoic Acid, p- | 74-11-3 | 500 | N |
| Chloronaphthalene, Beta- | 91-58-7 | 800 | N |
| Chloronitrobenzene, o- | 88-73-3 | 2 | C |
| Chloronitrobenzene, p- | 100-00-5 | 10 | C |
| Chlorophenol, 2- | 95-57-8 | 90 | N |
| Chrysene | 218-01-9 | 300 | C |
| Cresol, m- | 108-39-4 | 900 | N |
| Cresol, o- | 95-48-7 | 900 | N |
| Cresol, p- | 106-44-5 | 400 | N |
| Cresol, p-chloro-m- | 59-50-7 | 1,000 | N |
| Cresols | 1319-77-3 | 2,000 | N |
| Cupferron | 135-20-6 | 4 | C |
| Cyclohexane, 1,2,3,4,5-pentabromo-6-chloro- | 87-84-3 | 30 | C |
| Decabromodiphenyl ether, 2,2',3,3',4,4',5,5',6,6'- (BDE-209) | 1163-19-5 | 100 | N |
| Dibenz[a,h]anthracene | 53-70-3 | 0.3 | C |
| Dibenzo[a,e]pyrene | 192-65-4 | 0.07 | C |
| Dibenzofuran | 132-64-9 | 8 | N |
| Dibromobenzene, 1,3- | 108-36-1 | 5 | N |
| Dibromobenzene, 1,4- | 106-37-6 | 100 | N |
| Dibutyl Phthalate | 84-74-2 | 900 | N |
| Dichlorobenzene, 1,2- | 95-50-1 | 600 | M |
| Dichlorobenzene, 1,4- | 106-46-7 | 75 | M |
| Dichlorobenzidine, 3,3'- | 91-94-1 | 1 | C |
| Dichlorophenol, 2,4- | 120-83-2 | 50 | N |
| Diethyl Phthalate | 84-66-2 | 20,000 | N |
| Dihydrosafrole | 94-58-6 | 3 | C |
| Dimethoxybenzidine, 3,3'- | 119-90-4 | 0.2 | C |
| Dimethylamino azobenzene [p-] | 60-11-7 | 0.05 | C |
| Dimethylaniline HCl, 2,4- | 21436-96-4 | 1 | C |
| Dimethylaniline, 2,4- | 95-68-1 | 4 | C |
| Dimethylaniline, N,N- | 121-69-7 | 30 | C |
| Dimethylbenz[a]anthracene, 7,12- | 57-97-6 | 0.001 | C |
| Dimethylbenzidine, 3,3'- | 119-93-7 | 0.02 | C |
| Dimethylformamide | 68-12-2 | 60 | N |
| Dimethylhydrazine, 1,1- | 57-14-7 | 0.004 | N |
| Dimethylhydrazine, 1,2- | 540-73-8 | 0.0003 | C |
| Dimethylphenol, 2,4- | 105-67-9 | 400 | N |
| Dimethylphenol, 2,6- | 576-26-1 | 10 | N |
| Dimethylphenol, 3,4- | 95-65-8 | 20 | N |
| Dimethylterephthalate | 120-61-6 | 2,000 | N |
| Dinitroaniline, 3,5- | 618-87-1 | 8 | N |
| Dinitrobenzene, 1,2- | 528-29-0 | 2 | N |
| Dinitrobenzene, 1,3- | 99-65-0 | 2 | N |
| Dinitrobenzene, 1,4- | 100-25-4 | 2 | N |
| Dinitro-o-cresol, 4,6- | 534-52-1 | 2 | N |
| Dinitro-o-cyclohexyl Phenol, 4,6- | 131-89-5 | 20 | N |
| Dinitrophenol, 2,4- | 51-28-5 | 40 | N |
| Dinitrotoluene Mixture, 2,4/2,6- | E1615210 | 1 | C |
| Dinitrotoluene, 2,4- | 121-14-2 | 2 | C |
| Dinitrotoluene, 2,6- | 606-20-2 | 0.5 | C |
| Dinitrotoluene, 2-Amino-4,6- | 35572-78-2 | 2 | N |
| Dinitrotoluene, 4-Amino-2,6- | 19406-51-0 | 2 | N |
| Dinitrotoluene, Technical grade | 25321-14-6 | 1 | C |
| Dioxins: Hexachlorodibenzo-p-dioxin, Mixture | 34465-46-8 | 0.0001 | C |
| Dioxins: TCDD, 2,3,7,8- | 1746-01-6 | 0.00003 | M |
| Diphenyl Ether | 101-84-8 | 0.8 | N |
| Diphenyl Sulfone | 127-63-9 | 20 | N |
| Diphenylamine | 122-39-4 | 1,000 | N |
| Diphenylhydrazine, 1,2- | 122-66-7 | 0.8 | C |
| Direct Black 38 | 1937-37-7 | 0.1 | C |
| Direct Blue 6 | 2602-46-2 | 0.1 | C |
| Direct Brown 95 | 16071-86-6 | 0.1 | C |
| Fluoranthene | 206-44-0 | 800 | N |
| Fluorene | 86-73-7 | 300 | N |
| Furan | 110-00-9 | 20 | N |
| Hexabromobenzene | 87-82-1 | 40 | N |
| Hexabromodiphenyl ether, 2,2',4,4',5,5'- (BDE-153) | 68631-49-2 | 4 | N |
| Hexachlorobenzene | 118-74-1 | 1 | M |
| Hexachlorobutadiene | 87-68-3 | 1 | C |
| Hexachlorocyclohexane, Alpha- | 319-84-6 | 0.07 | C |
| Hexachlorocyclohexane, Beta- | 319-85-7 | 0.3 | C |
| Hexachlorocyclohexane, Delta- | 319-86-8 | 0.0007 | N |
| Hexachlorocyclohexane, Technical | 608-73-1 | 0.3 | C |
| Hexachlorocyclopentadiene | 77-47-4 | 50 | M |
| Hexachloroethane | 67-72-1 | 3 | C |
| Hexachlorophene | 70-30-4 | 6 | N |
| Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) | 121-82-4 | 10 | C |
| Hexamethylene Diisocyanate, 1,6- | 822-06-0 | 0.02 | N |
| Hexanedioic Acid | 124-04-9 | 40,000 | N |
| Hydroquinone | 123-31-9 | 10 | C |
| Indeno[1,2,3-cd]pyrene | 193-39-5 | 3 | C |
| Isophorone | 78-59-1 | 800 | C |
| Lewisite | 541-25-3 | 0.09 | N |
| Maleic Anhydride | 108-31-6 | 2,000 | N |
| Maleic Hydrazide | 123-33-1 | 10,000 | N |
| Mercaptobenzothiazole, 2- | 149-30-4 | 60 | C |
| Methoxy-5-nitroaniline, 2- | 99-59-2 | 20 | C |
| Methyl-5-Nitroaniline, 2- | 99-55-8 | 80 | C |
| Methylaniline Hydrochloride, 2- | 636-21-5 | 6 | C |
| Methylene-bis(2-chloroaniline), 4,4'- | 101-14-4 | 2 | C |
| Methylene-bis(N,N-dimethyl) Aniline, 4,4'- | 101-61-1 | 7 | C |
| Methylnaphthalene, 1- | 90-12-0 | 0.06 | D |
| Methylnaphthalene, 2- | 91-57-6 | 40 | N |
| Monomethylaniline | 100-61-8 | 40 | N |
| N,N'-Diphenyl-1,4-benzenediamine | 74-31-7 | 4 | N |
| Naphtha, High Flash Aromatic (HFAN) | 64742-95-6 | 200 | N |
| Naphthalene | 91-20-3 | 1 | C |
| Naphthylamine, 2- | 91-59-8 | 0.4 | C |
| Nitroaniline, 2- | 88-74-4 | 200 | N |
| Nitroaniline, 4- | 100-01-6 | 40 | C |
| Nitrobenzene | 98-95-3 | 1 | C |
| Nitrocellulose | 9004-70-0 | 60,000,000 | N |
| Nitrofurantoin | 67-20-9 | 1,000 | N |
| Nitroglycerin | 55-63-0 | 2 | N |
| Nitropyrene, 4- | 57835-92-4 | 0.2 | C |
| Nitrosodiethanolamine, N- | 1116-54-7 | 0.3 | C |
| Nitrosodiethylamine, N- | 55-18-5 | 0.002 | C |
| Nitrosodimethylamine, N- | 62-75-9 | 0.001 | C |
| Nitrosodiphenylamine, N- | 86-30-6 | 100 | C |
| Nitrosomorpholine [N-] | 59-89-2 | 0.1 | C |
| Nitrosopiperidine [N-] | 100-75-4 | 0.08 | C |
| Nitrosopyrrolidine, N- | 930-55-2 | 0.4 | C |
| Nitrotoluene, m- | 99-08-1 | 2 | N |
| Nitrotoluene, o- | 88-72-2 | 3 | C |
| Nitrotoluene, p- | 99-99-0 | 40 | C |
| Octabromodiphenyl Ether | 32536-52-0 | 60 | N |
| Octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX) | 2691-41-0 | 1,000 | N |
| Octyl Phthalate, di-N- | 117-84-0 | 200 | N |
| Pentabromodiphenyl Ether | 32534-81-9 | 40 | N |
| Pentabromodiphenyl ether, 2,2',4,4',5- (BDE-99) | 60348-60-9 | 2 | N |
| Pentachlorobenzene | 608-93-5 | 3 | N |
| Pentachloronitrobenzene | 82-68-8 | 1 | C |
| Pentachlorophenol | 87-86-5 | 1 | M |
| Perylene | 198-55-0 | 2 | N |
| Phenacetin | 62-44-2 | 300 | C |
| Phenol | 108-95-2 | 6,000 | N |
| Phenol, 2-(1-methylethoxy)-, methylcarbamate | 114-26-1 | 80 | N |
| Phenothiazine | 92-84-2 | 4 | N |
| Phenylenediamine, m- | 108-45-2 | 100 | N |
| Phenylenediamine, o- | 95-54-5 | 2 | C |
| Phenylenediamine, p- | 106-50-3 | 20 | N |
| Phenylphenol, 2- | 90-43-7 | 300 | C |
| Phthalic Acid, p- | 100-21-0 | 9,000 | N |
| Phthalic Anhydride | 85-44-9 | 40,000 | N |
| Picramic Acid (2-Amino-4,6-dinitrophenol) | 96-91-3 | 2 | N |
| Picric Acid (2,4,6-Trinitrophenol) | 88-89-1 | 40 | N |
| Polybrominated Biphenyls | 36355-01-8 | 0.03 | C |
| Pyrene | 129-00-0 | 100 | N |
| Pyridine | 110-86-1 | 20 | N |
| Quinoline | 91-22-5 | 0.2 | C |
| Safrole | 94-59-7 | 1 | C |
| Sulfonylbis(4-chlorobenzene), 1,1'- | 80-07-9 | 10 | N |
| Tetrabromodiphenyl ether, 2,2',4,4'- (BDE-47) | 5436-43-1 | 2 | N |
| Tetrachlorobenzene, 1,2,4,5- | 95-94-3 | 0.2 | N |
| Tetrachlorophenol, 2,3,4,6- | 58-90-2 | 200 | N |
| Tetrahydrofuran | 109-99-9 | 3,000 | N |
| Thiodiglycol | 111-48-8 | 1,000 | N |
| Toluene-2,6-diisocyanate | 91-08-7 | 0.02 | N |
| Toluenediamine, 2,3- | 2687-25-4 | 2 | N |
| Toluenediamine, 2,5- | 95-70-5 | 4 | N |
| Toluenediamine, 3,4- | 496-72-0 | 2 | N |
| Toluic Acid, p- | 99-94-5 | 90 | N |
| Toluidine, o- (Methylaniline, 2-) | 95-53-4 | 50 | C |
| Toluidine, p- | 106-49-0 | 30 | C |
| Triacetin | 102-76-1 | 2,000,000 | N |
| Tribromobenzene, 1,2,4- | 615-54-3 | 50 | N |
| Tribromophenol, 2,4,6- | 118-79-6 | 100 | N |
| Trichloroaniline HCl, 2,4,6- | 33663-50-2 | 30 | C |
| Trichloroaniline, 2,4,6- | 634-93-5 | 0.4 | N |
| Trichlorobenzene, 1,2,3- | 87-61-6 | 7 | N |
| Trichlorobenzene, 1,2,4- | 120-82-1 | 70 | M |
| Trichlorophenol, 2,4,5- | 95-95-4 | 1,000 | N |
| Trichlorophenol, 2,4,6- | 88-06-2 | 10 | N |
| Trinitrobenzene, 1,3,5- | 99-35-4 | 600 | N |
| Trinitrotoluene, 2,4,6- | 118-96-7 | 10 | N |
| Urethane | 51-79-6 | 0.3 | C |
No results found.
Practical Notes
PAHs in groundwater are common at manufactured gas plant (MGP) sites, coal tar impacted properties, and sites with weathered petroleum contamination. Because many PAHs have very low aqueous solubility, dissolved-phase concentrations in groundwater may be low even when soil concentrations are elevated. PAH groundwater detections above published levels are often found near NAPL source zones.
Naphthalene is the most soluble and mobile PAH and typically has the highest dissolved-phase concentrations in groundwater at petroleum or coal tar sites. It is frequently the groundwater risk driver among the PAH group.
Phthalates (especially DEHP) can be laboratory contaminants introduced through sample containers or processing equipment. Confirm with your laboratory that phthalate detections in groundwater represent real site contamination before comparing to published levels.
Soil relationship: SVOCs in soil can leach to groundwater, particularly at high concentrations or on permeable, low-organic-matter soils. Compare soil results to Indiana Soil - SVOCs and PAHs and groundwater results to this page as part of a complete pathway evaluation.