The file's text, extracted by GovTribe without its formatting.
COMP A
| Newark Bay - Upland |
| Newark Bay - Upland - COMP A - Sediment Volatiles |
| Volatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | #20220312 | | #20220312 | | |
| Limit Exceedance Qualifier | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | A COMP A | Q | A COMP A | Q | |
| Chloromethane (Methyl Chloride) | | | | | | | 4 | 12 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromomethane | 10 | 1 | | | | | 25 | 59 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Vinyl chloride | 0.08 | 1 | 0.21 | 0.9 | 13 | 27 | 0.7 | 2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Chloroethane | | | | | | | 220 | 1100 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Methylene chloride (Dichloromethane) | 3 | 1 | 51 | 100 | 500 | 1000 | 46 | 230 | | | 0.012 | U | 0.01 | U | 21 | B | 12 |
| Acetone | 6000 | 10 | 100 | 100 | 500 | 1000 | 70000 | | | | 0.047 | U | 0.041 | U | 18 | | 2 |
| Carbon disulfide | 700 | 1 | | | | | 7800 | 110000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1-Dichloroethene | | | 100 | 100 | 500 | 1000 | 11 | 150 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1-Dichloroethane | 50 | 1 | 19 | 26 | 240 | 480 | 8 | 24 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (total) | | | | | | | | | | | 0.024 | U | 0.02 | U | 2 | U | |
| Chloroform | 70 | 1 | 10 | 49 | 350 | 700 | 0.6 | 2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethane | 0.3 | 2 | 2.3 | 3.1 | 30 | 60 | 0.9 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 2-Butanone (MEK) | 300 | 2 | 100 | 100 | 500 | 1000 | 3100 | 44000 | | | 0.012 | U | 0.01 | U | 5 | U | |
| 1,1,1-Trichloroethane | 30 | 1 | 100 | 100 | 500 | 1000 | 160000 | | | | 0.012 | U | 0.01 | U | 1 | U | |
| Carbon tetrachloride | 0.4 | 1 | 1.4 | 2.4 | 22 | 44 | 2 | 4 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromodichloromethane | 0.6 | 1 | | | | | 1 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloropropane | 0.5 | 1 | | | | | 2 | 5 | | | 0.012 | U | 0.01 | U | 1 | U | |
| cis-1,3-Dichloropropene | | | | | | | 2 | 7 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Trichloroethene | 1 | 1 | 10 | 21 | 200 | 400 | 3 | 10 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Dibromochloromethane | 0.4 | 1 | | | | | 3 | 8 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1,2-Trichloroethane | 3 | 2 | | | | | 2 | 6 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Benzene | 0.2 | 1 | 2.9 | 4.8 | 44 | 89 | 2 | 5 | 0.59 | 2.16 | 0.012 | U | 0.01 | U | 1 | U | |
| trans-1,3-dichloropropene | | | | | | | 2 | 7 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromoform | 4 | 0.8 | | | | | 81 | 280 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 4-Methyl-2-pentanone (MIBK) | | | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| 2-Hexanone | 40 | 1 | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| Tetrachloroethene | 0.4 | 1 | 5.5 | 19 | 150 | 300 | 43 | 1500 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1,2,2-Tetrachloroethane | 1 | 1 | | | | | 1 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Toluene | 600 | 1 | 100 | 100 | 500 | 1000 | 6300 | 91000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Chlorobenzene | 50 | 1 | 100 | 100 | 500 | 1000 | 510 | 7400 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Ethyl benzene | 700 | 2 | 30 | 41 | 390 | 780 | 7800 | 110000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Styrene | 100 | 2 | | | | | 90 | 260 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Xylenes(Total) | 1000 | 2 | 100 | 100 | 500 | 1000 | 12000 | 170000 | | | 0.024 | U | 0.02 | U | 2 | U | |
| Acrolein | 4 | 5 | | | | | 0.5 | 1 | | | 0.24 | U | 0.2 | U | 20 | U | |
| Acrylonitrile | 0.06 | 2 | | | | | 0.9 | 3 | | | 0.12 | U | 0.1 | U | 20 | U | |
| 1,2-Dibromo-3-chloropropane | 0.02 | 0.02 | | | | | 0.08 | 0.2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dibromoethane | 0.0004 | 0.03 | | | | | 0.008 | 0.04 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Dichlorodifluoromethane | 1000 | 2 | | | | | 490 | 230000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (cis) | | | 59 | 100 | 500 | 1000 | 230 | 560 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (trans) | | | 100 | 100 | 500 | 1000 | 300 | 720 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Methyl acetate | 7000 | 0.5 | | | | | 78000 | | | | 0.059 | U | 0.051 | U | 5 | U | |
| Methyl tert-butyl ether (MTBE) | 70 | 1 | 62 | 100 | 500 | 1000 | 110 | 320 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Tertiary butyl alcohol (TBA) | 100 | 2 | | | | | 1400 | 11000 | | | 0.12 | U | 0.1 | U | 40 | U | |
| Trichlorofluoromethane | 2000 | 1 | | | | | 23000 | 340000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Combined 1,3-dichloropropenes (SUM) cis + trans | 0.4 | 1 | | | | | | | | | | | | | | | |
| 1,4-dioxane | 0.4 | 0.1 | 9.8 | 13 | 130 | 250 | | | | | 0.78 | U | 0.67 | U | 2 | U | |
| n-propylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| sec-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| tert-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2,4-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,3,5-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| n-Butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
Newark Bay - Upland - COMP A - Sediment Semivolatiles
| Semivolatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | #20220312 | | #20220312 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | A COMP A | Q | A COMP A | Q |
| Phenol | 2000 | 10 | 100 | 100 | 500 | 1000 | 18000 | 210000 | | | 0.38 | U | 0.33 | U | 0.74 | J |
| bis(2-Chloroethyl)ether | 0.03 | 7 | | | | | 0.4 | 2 | | | 0.078 | U | 0.067 | U | 0.19 | U |
| 2-Chlorophenol | 40 | 20 | | | | | 310 | 2200 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 1,3-Dichlorobenzene | 600 | 5 | 17 | 49 | 280 | 560 | 5300 | 59000 | | | 0.012 | U | 0.01 | U | 1 | U |
| 1,4-Dichlorobenzene | 75 | 5 | 9.8 | 13 | 130 | 250 | 5 | 13 | | | 0.012 | U | 0.01 | U | 1 | U |
| 1,2-Dichlorobenzene | 600 | 5 | 100 | 100 | 500 | 1000 | 5300 | 59000 | | | 0.012 | U | 0.01 | U | 1 | U |
| 2-Methylphenol (o-cresol) | | | 100 | 100 | 500 | 1000 | 310 | 3400 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 1-Chloropropane-2,2'-oxybis/ bis(2-chloroisopropyl)ether | 300 | 10 | | | | | 23 | 67 | | | 0.078 | U | 0.067 | U | 0.19 | U |
| 4-Methylphenol (p-cresol) (co-elutes with 3-methylphenol (m-cresol)) | | | 34 | 100 | 500 | 1000 | 31 | 340 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| N-Nitroso-Di-N-Propylamine | 0.005 | 10 | | | | | 0.2 | 0.3 | | | 0.078 | U | 0.067 | U | 0.19 | U |
| Hexachloroethane | 2 | 7 | | | | | 12 | 48 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| Nitrobenzene | 4 | 6 | | | | | 5 | 14 | | | 0.78 | U | 0.67 | U | 2 | U |
| Isophorone | 40 | 10 | | | | | 510 | 2000 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 2-Nitrophenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dimethylphenol | 100 | 20 | | | | | 1200 | 14000 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| bis(2-Chloroethoxy)methane | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dichlorophenol | 20 | 10 | | | | | 180 | 2100 | | | 0.078 | U | 0.067 | U | 0.19 | U |
| 1,2,4-Trichlorobenzene | 9 | 1 | | | | | 73 | 820 | | | 0.012 | U | 0.01 | U | 1 | U |
| Naphthalene | 300 | 2 | 100 | 100 | 500 | 1000 | 6 | 17 | | | 0.04 | J | 0.051 | J | 0.19 | U |
| 4-Chloroaniline | 30 | 10 | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Hexachloro-1,3-butadiene | 0.4 | 1 | | | | | 6 | 25 | | | 0.078 | U | 0.067 | U | 0.19 | U |
| 4-Chloro-3-methylphenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2-Methylnaphthalene | 30 | 10 | | | | | 230 | 2400 | | | 0.03 | J | 0.034 | J | 0.19 | U |
| Hexachlorocyclopentadiene | 40 | 0.5 | | | | | 45 | 110 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 2,4,6-Trichlorophenol | 1 | 20 | | | | | 19 | 74 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 2,4,5-Trichlorophenol | 700 | 10 | | | | | 6100 | 68000 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 2-Chloronaphthalene | 600 | 10 | | | | | | | | | | | | | 0.19 | U |
| 2-Nitroaniline | | | | | | | 39 | 23000 | | | 2 | U | 1.7 | U | 4.9 | U |
| Dimethylphthalate | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Acenaphthylene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.082 | | 0.085 | | 0.19 | U |
| 2,6-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.38 | U | 0.33 | U | 0.98 | U |
| 3-Nitroaniline | | | | | | | | | | | | | 0 | 0 | | |
| Newark Bay - Upland - COMP A - Sediment Semivolatiles, con't. | | | | | | | | | | | | | | | | |
| Semivolatiles, continued | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: mg/kg) | | Threshold Exceedances | Amended Sediment (Units: mg/kg) | | Threshold Exceedances | SPLP | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | | #20220312 | | | #20220312 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | | A COMP A | Q | | A COMP A | Q |
| Acenaphthene | 400 | 10 | 100 | 100 | 500 | 1000 | 3400 | 37000 | | | 0.024 | J | | 0.028 | J | | 0.19 | U |
| 2,4-Dinitrophenol | 10 | 40 | | | | | 120 | 1400 | | | 3.8 | U | | 3.3 | U | | 9.8 | U |
| 4-Nitrophenol | | | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| Dibenzofuran | | | 14 | 59 | 350 | 1000 | | | | | 0.38 | U | | 0.33 | U | | | |
| 2,4-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| Diethylphthalate | 6000 | 1 | | | | | 49000 | 550000 | | | 0.38 | U | | 0.33 | U | | 0.58 | J |
| 4-Chlorophenyl-phenylether | | | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| Fluorene | 300 | 1 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.039 | J | | 0.045 | J | | 0.19 | U |
| 4-Nitroaniline | | | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| 4,6-Dinitro-2-methylphenol | 0.7 | 0.03 | | | | | 6 | 68 | | | 2 | U | | 1.7 | U | | 4.9 | U |
| N-Nitrosodiphenylamine | 7 | 10 | | | | | 99 | 390 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| 4-Bromophenyl-phenylether | | | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| Hexachlorobenzene | 0.02 | 0.02 | 0.33 | 1.2 | 6 | 12 | 0.3 | 1 | | | 0.078 | U | | 0.067 | U | | 0.19 | U |
| Pentachlorophenol | 0.3 | 0.1 | 2.4 | 6.7 | 6.7 | 55 | 0.9 | 3 | | | 2 | U | | 1.7 | U | | 4.9 | U |
| Phenanthrene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.12 | | | 0.15 | | | 0.094 | J |
| Anthracene | 2000 | 10 | 100 | 100 | 500 | 1000 | 17000 | 30000 | | | 0.13 | | | 0.14 | | | 0.19 | U |
| Carbazole | | | | | | | 24 | 96 | | | 0.032 | J | | 0.024 | J | | 0.19 | U |
| Di-n-butylphthalate | | | | | | | 6100 | 68000 | | | 0.38 | U | | 0.33 | U | | 2.4 | B |
| Fluoranthene | 300 | 10 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.25 | | | 0.31 | | | 0.19 | U |
| Pyrene | 200 | 0.1 | 100 | 100 | 500 | 1000 | 1700 | 18000 | | | 0.36 | | | 0.41 | | | 0.19 | U |
| Butylbenzylphthalate | 100 | 1 | | | | | 1200 | 14000 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| 3,3'-Dichlorobenzidine | 0.08 | 30 | | | | | 1 | 4 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| Benzo(a)anthracene | 0.05 | 0.1 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.2 | | | 0.23 | | | 0.19 | U |
| Chrysene | 5 | 0.2 | 1 | 3.9 | 56 | 110 | 450 | 1700 | | | 0.23 | | | 0.28 | | | 0.19 | U |
| bis(2-Ethylhexyl)phthalate | 2 | 3 | | | | | 35 | 140 | | | 3.8 | U | | 0.36 | J | | 9.8 | U |
| DI-n-octylphthalate | 100 | 10 | | | | | 2400 | 27000 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| Benzo(b)fluoranthene | 0.05 | 0.2 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.26 | | | 0.28 | | | 0.19 | U |
| Benzo(k)fluoranthene | 0.5 | 0.3 | 1 | 3.9 | 56 | 110 | 45 | 170 | | | 0.096 | | | 0.12 | | | 0.19 | U |
| Benzo(a)pyrene | 0.005 | 0.1 | 1 | 1 | 1 | 1.1 | 0.5 | 2 | | | 0.25 | | | 0.28 | | | 0.19 | U |
| Indeno(1,2,3-cd)pyrene | 0.05 | 0.2 | 0.5 | 0.5 | 5.6 | 11 | 5 | 17 | | | 0.17 | | | 0.22 | | | 0.19 | U |
| Dibenzo(a,h)anthracene | 0.005 | 0.3 | 0.33 | 0.33 | 0.56 | 1.1 | 0.5 | 2 | | | 0.055 | J | | 0.066 | J | | 0.19 | U |
| Benzo(ghi)perylene | | | 100 | 100 | 500 | 1000 | 380000 | 30000 | | | 0.2 | | | 0.2 | | | 0.19 | U |
| Pyridine | | | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| Acetophenone | 700 | 10 | | | | | 2 | 5 | | | 0.78 | U | | 0.67 | U | | 0.28 | J |
| Atrazine | 3 | 0.1 | | | | | 210 | 2400 | | | 0.78 | U | | 0.67 | U | | 0.98 | U |
| Benzaldehyde | | | | | | | 6100 | 68000 | | | 0.78 | U | | 0.049 | J | | 2.1 | |
| Benzidine | 0.0002 | 20 | | | | | 0.7 | 0.7 | | | 7.8 | U | | 6.7 | U | | 20 | U |
| 1,1'-Biphenyl | 400 | 10 | | | | | 61 | 240 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| Caprolactam | 4000 | 60 | | | | | 31000 | 340000 | | | 2 | U | | 1.7 | U | | 0.96 | J B |
| 1,2-Diphenylhydrazine | 0.04 | 20 | | | | | 0.7 | 2 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| N-Nitrosodimethylamine | 0.0007 | 0.8 | | | | | 0.7 | 0.7 | | | 0.38 | U | | 0.33 | U | | 0.98 | U |
| Total Cresol | 50 | 0.1 | | | | | | | | | 0 | 0 | | 0 | 0 | | | |
| Newark Bay - Upland - COMP A - Pesticides/Aroclors | | | | | | | | | | | | | | | | | | |
| Pesticides/Aroclors | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | | #20220312 | | #20220312 | | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | | A COMP A | Q | A COMP A | Q | |
| alpha-BHC | 0.006 | 0.02 | 0.097 | 0.48 | 3.4 | 6.8 | 0.1 | 0.5 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| beta-BHC | 0.02 | 0.04 | 0.072 | 0.36 | 3 | 14 | 0.4 | 2 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| delta-BHC | | | 100 | 100 | 500 | 1000 | | | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| gamma-BHC (Lindane) | 0.03 | 0.02 | 0.28 | 1.3 | 9.2 | 23 | 0.4 | 2 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Heptachlor | 0.008 | 0.05 | 0.42 | 2.1 | 15 | 29 | 0.1 | 0.7 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Aldrin | 0.002 | 0.04 | 0.019 | 0.097 | 0.68 | 1.4 | 0.04 | 0.2 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Heptachlor epoxide | 0.004 | 0.2 | | | | | 0.07 | 0.3 | | | 0.00067 | p | | 0.0004 | J p | 0.0013 | U | |
| Endosulfan I | 40 | 0.02 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Dieldrin | 0.002 | 0.03 | 0.039 | 0.2 | 1.4 | 2.8 | 0.04 | 0.2 | 0.11 | 0.48 | 0.00045 | J | | 0.00036 | J | 0.0013 | U | |
| 4,4'-DDE | 0.1 | 0.01 | 1.8 | 8.9 | 62 | 120 | 2 | 9 | | | 0.004 | | | 0.0026 | | 0.0013 | U | |
| Endrin | 2 | 0.03 | 2.2 | 11 | 89 | 410 | 23 | 340 | | | 0.0018 | | | 0.0011 | | 0.0013 | U | |
| Endosulfan II | 40 | 0.04 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| 4,4'-DDD | 0.1 | 0.02 | 2.6 | 13 | 92 | 180 | 3 | 13 | | | 0.0016 | p | | 0.0012 | p | 0.0013 | U | |
| Endosulfan sulfate | 40 | 0.02 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.00049 | U | | 0.00019 | J p | 0.0013 | U | |
| 4,4'-DDT | 0.1 | 0.1 | 1.7 | 7.9 | 47 | 94 | 2 | 8 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Methoxychlor | 40 | 0.1 | | | | | 390 | 5700 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Endrin ketone | | | | | | | | | | | | | | | | | | |
| Endrin aldehyde | | | | | | | | | | | | | | | | 0.0013 | U | |
| alpha-Chlordane | | | 0.91 | 4.2 | 24 | 47 | 0.2 | 1 | | | 0.00048 | J | | 0.00034 | J | 0.0013 | U | |
| gamma-Chlordane | | | | | | | 0.2 | 1 | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Toxaphene | 0.03 | 2 | | | | | 0.6 | 3 | | | 0.019 | U | | 0.017 | U | 0.096 | U | |
| Mirex | 0.1 | 0.08 | | | | | | | | | 0.00049 | U | | 0.00042 | U | 0.0013 | U | |
| Aroclor-1016 | | | | | | | | | | | 0.0097 | U F2 | | 0.0083 | U | 0.0096 | U | |
| Aroclor-1221 | | | | | | | | | | | 0.0097 | U | | 0.0083 | U | 0.0096 | U | |
| Aroclor-1232 | | | | | | | | | | | 0.0097 | U | | 0.0083 | U | 0.0096 | U | |
| Aroclor-1242 | | | | | | | | | | | 0.0097 | U | | 0.0083 | U | 0.0096 | U | |
| Aroclor-1248 | | | | | | | | | | | 0.093 | | | 0.016 | | 0.0096 | U | |
| Aroclor-1254 | | | | | | | | | | | 0.0097 | U | | 0.0083 | U | 0.0096 | U | |
| Aroclor-1260 | | | | | | | | | | | 0.047 | F2 F1 | | 0.0092 | | 0.0096 | U | |
| Total Aroclor(SUM) | 0.02 | 0.5 | 1 | 1 | 1 | 25 | 0.2 | 1 | 0.1 | 1 | 0.1885 | | 9 | 0.0667 | | 0.0672 | | 1 |
Newark Bay - Upland - COMP A - Herbicides
| Herbicides | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | #20220312 | | #20220312 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | A COMP A | Q | A COMP A | Q |
| 2,4,5-TP (Silvex) | 60 | 0.6 | 58 | 100 | 500 | 1000 | | | | | 0.047 | U | 0.041 | U | 0.98 | U |
| 2,4-D | 70 | 2 | | | | | | | | | 0.19 | U | 0.16 | U | 3.9 | U |
Newark Bay - Upland - COMP A - Metals
| Metals | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | | #20220312 | | | #20220312 | | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | | A COMP A | Q | | A COMP A | Q | |
| Aluminum | 200 | 30 | | | | | 78000 | | | | 9400 | | | 11000 | | | 780 | | 12 |
| Antimony | 6 | 3 | | | | | 31 | 450 | | | 0.35 | F1 | | 0.63 | | | 0.78 | J | |
| Arsenic | 0.02 | 3 | 16 | 16 | 16 | 16 | 19 | 19 | 8.2 | 53 | 8.8 | | 9 | 12 | | 9 | 1.8 | | 1 |
| Barium | 6000 | 200 | 350 | 400 | 400 | 10000 | 16000 | 59000 | | | 48 | | | 64 | | | 78 | | |
| Beryllium | 1 | 1 | 14 | 72 | 590 | 2700 | 16 | 140 | | | 0.54 | | | 0.65 | | | 1 | U | |
| Cadmium | 4 | 0.5 | 2.5 | 4.3 | 9.3 | 60 | 78 | 78 | 1.2 | 9.5 | 0.31 | | | 0.39 | | | 1 | U | |
| Calcium | | | | | | | | | | | | | | | | | | | |
| Chromium | 70 | 1 | | | | | | | | | 38 | | | 44 | | | 8.6 | | 2 |
| Hexavalent Chromium | | | 22 | 110 | 400 | 800 | | | | | 0.92 | U | | 0.8 | U | | 0.01 | U | |
| Trivalent Chromium | | | 36 | 180 | 1500 | 6800 | | | | | 38 | | 3 | 44 | | 3 | 8.6 | J | |
| Cobalt | 100 | 0.5 | | | | | 1600 | 590 | | | 7.8 | | | 9.4 | | | 3.2 | | 2 |
| Copper | 1300 | 4 | 270 | 270 | 270 | 10000 | 3100 | 45000 | 33 | 270 | 50 | | 9 | 70 | | 9 | 150 | | 2 |
| Iron | 300 | 20 | | | | | | | | | | | | | | | | | |
| Lead | 5 | 5 | 400 | 400 | 1000 | 3900 | 400 | 800 | 47 | 218 | 58 | | 9 | 59 | | 9 | 1 | U | |
| Magnesium | | | | | | | | | | | | | | | | | | | |
| Manganese | 50 | 0.4 | 2000 | 2000 | 10000 | 10000 | 11000 | 5900 | | | 470 | | | 480 | | | 5 | U | |
| Mercury | 2 | 0.05 | 0.81 | 0.81 | 2.8 | 5.7 | 23 | 65 | 0.17 | 1.6 | 0.82 | H | 349 | 0.85 | | 349 | 0.2 | U | |
| Nickel | 100 | 4 | 140 | 310 | 310 | 10000 | 1600 | 23000 | | | 25 | | | 28 | | | 18 | | 2 |
| Potassium | | | | | | | | | | | | | | | | | | | |
| Selenium | 40 | 4 | 36 | 180 | 1500 | 6800 | 390 | 5700 | | | 0.35 | J F1 | | 0.4 | J | | 2 | J | |
| Silver | 40 | 1 | 36 | 180 | 1500 | 6800 | 390 | 5700 | | | 0.86 | | | 0.84 | | | 1 | U | |
| Sodium | 50000 | 400 | | | | | | | | | | | | | | | | | |
| Thallium | 0.5 | 2 | | | | | | | | | | | | | | | 1 | U | |
| Vanadium | | | | | | | 78 | 1100 | | | 25 | | | 26 | | | 6.6 | | |
| Zinc | 2000 | 10 | 2200 | 10000 | 10000 | 10000 | 23000 | 110000 | | | 120 | | | 210 | | | 16 | | 2 |
| Cyanide, total | | | 27 | 27 | 27 | 10000 | 47 | 680 | | | 0.47 | U F1 | | 0.39 | U | | 10 | U | |
| %Solids | | | | | | | | | | | 42.5 | | | 49.2 | | | | | |
Newark Bay - Upland - COMP A - Dioxin/Furan
| Dioxin/Furan | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: pg/g) | | Threshold Exceedances | Amended Sediment | | | | |
| (Units: pg/g) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | |
| (Units: pg/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | pg/g | pg/g | #20220182 | | | #20220312 | | | #20220312 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | | A COMP A | Q | | A COMP A | Q |
| 2,3,7,8-TCDD | | | | | | | | | 4.5 | 50 | 10 | | 9 | 8.6 | | 9 | 9.6 | U |
| 1,2,3,7,8-PeCDD | | | | | | | | | | | 2.1 | J q | | 1.8 | J q | | 48 | U |
| 1,2,3,4,7,8-HxCDD | | | | | | | | | | | 3.1 | J B | | 2.7 | J B | | 1.4 | J B q |
| 1,2,3,6,7,8-HxCDD | | | | | | | | | | | 11 | B | | 10 | B | | 0.69 | J B q |
| 1,2,3,7,8,9-HxCDD | | | | | | | | | | | 8.4 | S B | | 7.7 | S B | | 0.87 | J B q |
| 1,2,3,4,6,7,8-HpCDD | | | | | | | | | | | 190 | | | 250 | | | 48 | U |
| OCDD | | | | | | | | | | | 1900 | B | | 2800 | B | | 2.8 | J B q |
| 2,3,7,8-TCDF | | | | | | | | | | | 11 | | | 11 | | | 9.6 | U |
| 1,2,3,7,8-PeCDF | | | | | | | | | | | 4.1 | J | | 3.7 | J | | 48 | U |
| 2,3,4,7,8-PeCDF | | | | | | | | | | | 6.7 | B | | 6.1 | B | | 48 | U |
| 1,2,3,4,7,8-HxCDF | | | | | | | | | | | 15 | | | 14 | | | 48 | U |
| 1,2,3,6,7,8-HxCDF | | | | | | | | | | | 7.6 | I | | 6.2 | I | | 48 | U |
| 2,3,4,6,7,8-HxCDF | | | | | | | | | | | 3.6 | J | | 3.6 | J | | 48 | U |
| 1,2,3,7,8,9-HxCDF | | | | | | | | | | | 5.9 | U | | 5.0 | U | | 48 | U |
| 1,2,3,4,6,7,8-HpCDF | | | | | | | | | | | 89 | B | | 87 | B | | 48 | U |
| 1,2,3,4,7,8,9-HpCDF | | | | | | | | | | | 4.4 | J B | | 3.8 | J B | | 48 | U |
| OCDF | | | | | | | | | | | 120 | B | | 150 | B | | 1.5 | J B q |
Newark Bay - Upland - COMP A - TOGS Totals
| TOGS Table 2 Totals | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | |
| (Units: mg/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220182 | | | #20220312 | | | #20220312 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP A | Q | | A COMP A | Q | | A COMP A | Q |
| Total BTEX | | | | | | | | | 0.96 | 5.9 | 0.06 | | | 0.05 | | | | |
| Total PAH | | | | | | | | | 4 | 45 | 2.506 | | | 2.895 | | | | |
| Total DDx | | | | | | | | | 0.003 | 0.03 | 0.00609 | | 9 | 0.00422 | | 9 | | |
| Total Chlordane | | | | | | | | | 0.003 | 0.036 | 0.00097 | | | 0.00076 | | | | |
| NJ Threshold values (solids) are for the sum of trans-1,3-dichloropropene and cis-1,3-dichloropropene | | | | | | | | | | | | | | | | | | |
| NY Threshold values (solids) are presented for m-cresol and p-cresol separately. These two analytes co-elute. The lower of the two values is reported as the threshold value when they differ. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values (solids) are presented for p-cresol only. M-cresol and p-cresol co-elute. The sum of the two concentration values are compared to threshold value when detected. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values for Endosulfan I and Endosulfan II are the sum of these two analytes. The Endo I and Endo II are compared to this value individualy. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values for Chlordane are presented as a sum of the alpha and gamma isomers. The individual isomers are compared to the threshold values. | | | | | | | | | | | | | | | | | | |
| a Totals: | | | | | | | | | | | | | | | | | | |
| 1) include estimated values, those reported with a J qualifier | | | | | | | | | | | | | | | | | | |
| 2) If a concentration of a specific contaminant is reported as 'non-detect' or less than, and the method detection limit was not achieved, then the reported detection limit is used as an estimate of the maximum possible concentration. | | | | | | | | | | | | | | | | | | |
| 3) If a concentration of a specific contaminant is reported as 'non-detect' or less than, and the detection limit achieved was at or below the method detection limit, then half the achieved detection limit is used as an estimate of the concentration | | | | | | | | | | | | | | | | | | |
COMP B
| Newark Bay - Upland |
| Newark Bay - Upland - COMP B - Sediment Volatiles |
| Volatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | #20220313 | | #20220313 | | |
| Limit Exceedance Qualifier | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | A COMP B | Q | A COMP B | Q | |
| Chloromethane (Methyl Chloride) | | | | | | | 4 | 12 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromomethane | 10 | 1 | | | | | 25 | 59 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Vinyl chloride | 0.08 | 1 | 0.21 | 0.9 | 13 | 27 | 0.7 | 2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Chloroethane | | | | | | | 220 | 1100 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Methylene chloride (Dichloromethane) | 3 | 1 | 51 | 100 | 500 | 1000 | 46 | 230 | | | 0.012 | U | 0.01 | U | 15 | B | 12 |
| Acetone | 6000 | 10 | 100 | 100 | 500 | 1000 | 70000 | | | | 0.037 | J | 0.17 | | 16 | | 2 |
| Carbon disulfide | 700 | 1 | | | | | 7800 | 110000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1-Dichloroethene | | | 100 | 100 | 500 | 1000 | 11 | 150 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1-Dichloroethane | 50 | 1 | 19 | 26 | 240 | 480 | 8 | 24 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (total) | | | | | | | | | | | 0.024 | U | 0.02 | U | 2 | U | |
| Chloroform | 70 | 1 | 10 | 49 | 350 | 700 | 0.6 | 2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethane | 0.3 | 2 | 2.3 | 3.1 | 30 | 60 | 0.9 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 2-Butanone (MEK) | 300 | 2 | 100 | 100 | 500 | 1000 | 3100 | 44000 | | | 0.026 | | 0.19 | | 2.8 | J | 2 |
| 1,1,1-Trichloroethane | 30 | 1 | 100 | 100 | 500 | 1000 | 160000 | | | | 0.012 | U | 0.01 | U | 1 | U | |
| Carbon tetrachloride | 0.4 | 1 | 1.4 | 2.4 | 22 | 44 | 2 | 4 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromodichloromethane | 0.6 | 1 | | | | | 1 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloropropane | 0.5 | 1 | | | | | 2 | 5 | | | 0.012 | U | 0.01 | U | 1 | U | |
| cis-1,3-Dichloropropene | | | | | | | 2 | 7 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Trichloroethene | 1 | 1 | 10 | 21 | 200 | 400 | 3 | 10 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Dibromochloromethane | 0.4 | 1 | | | | | 3 | 8 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1,2-Trichloroethane | 3 | 2 | | | | | 2 | 6 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Benzene | 0.2 | 1 | 2.9 | 4.8 | 44 | 89 | 2 | 5 | 0.59 | 2.16 | 0.012 | U | 0.01 | U | 1 | U | |
| trans-1,3-dichloropropene | | | | | | | 2 | 7 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Bromoform | 4 | 0.8 | | | | | 81 | 280 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 4-Methyl-2-pentanone (MIBK) | | | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| 2-Hexanone | 40 | 1 | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| Tetrachloroethene | 0.4 | 1 | 5.5 | 19 | 150 | 300 | 43 | 1500 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,1,2,2-Tetrachloroethane | 1 | 1 | | | | | 1 | 3 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Toluene | 600 | 1 | 100 | 100 | 500 | 1000 | 6300 | 91000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Chlorobenzene | 50 | 1 | 100 | 100 | 500 | 1000 | 510 | 7400 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Ethyl benzene | 700 | 2 | 30 | 41 | 390 | 780 | 7800 | 110000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Styrene | 100 | 2 | | | | | 90 | 260 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Xylenes(Total) | 1000 | 2 | 100 | 100 | 500 | 1000 | 12000 | 170000 | | | 0.024 | U | 0.02 | U | 2 | U | |
| Acrolein | 4 | 5 | | | | | 0.5 | 1 | | | 0.24 | U | 0.2 | U | 20 | U | |
| Acrylonitrile | 0.06 | 2 | | | | | 0.9 | 3 | | | 0.12 | U | 0.1 | U | 20 | U | |
| 1,2-Dibromo-3-chloropropane | 0.02 | 0.02 | | | | | 0.08 | 0.2 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dibromoethane | 0.0004 | 0.03 | | | | | 0.008 | 0.04 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Dichlorodifluoromethane | 1000 | 2 | | | | | 490 | 230000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (cis) | | | 59 | 100 | 500 | 1000 | 230 | 560 | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2-Dichloroethene (trans) | | | 100 | 100 | 500 | 1000 | 300 | 720 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Methyl acetate | 7000 | 0.5 | | | | | 78000 | | | | 0.061 | U | 0.05 | U | 5 | U | |
| Methyl tert-butyl ether (MTBE) | 70 | 1 | 62 | 100 | 500 | 1000 | 110 | 320 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Tertiary butyl alcohol (TBA) | 100 | 2 | | | | | 1400 | 11000 | | | 0.12 | U | 0.1 | U | 40 | U | |
| Trichlorofluoromethane | 2000 | 1 | | | | | 23000 | 340000 | | | 0.012 | U | 0.01 | U | 1 | U | |
| Combined 1,3-dichloropropenes (SUM) cis + trans | 0.4 | 1 | | | | | | | | | | | | | | | |
| 1,4-dioxane | 0.4 | 0.1 | 9.8 | 13 | 130 | 250 | | | | | 0.8 | U | 0.67 | U | 1.9 | U | |
| n-propylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| sec-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| tert-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,2,4-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| 1,3,5-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
| n-Butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.012 | U | 0.01 | U | 1 | U | |
Newark Bay - Upland - COMP B - Sediment Semivolatiles
| Semivolatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | #20220313 | | #20220313 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | A COMP B | Q | A COMP B | Q |
| Phenol | 2000 | 10 | 100 | 100 | 500 | 1000 | 18000 | 210000 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| bis(2-Chloroethyl)ether | 0.03 | 7 | | | | | 0.4 | 2 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| 2-Chlorophenol | 40 | 20 | | | | | 310 | 2200 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 1,3-Dichlorobenzene | 600 | 5 | 17 | 49 | 280 | 560 | 5300 | 59000 | | | 0.012 | U | 0.01 | U | 1 | U |
| 1,4-Dichlorobenzene | 75 | 5 | 9.8 | 13 | 130 | 250 | 5 | 13 | | | 0.012 | U | 0.01 | U | 1 | U |
| 1,2-Dichlorobenzene | 600 | 5 | 100 | 100 | 500 | 1000 | 5300 | 59000 | | | 0.012 | U | 0.01 | U | 1 | U |
| 2-Methylphenol (o-cresol) | | | 100 | 100 | 500 | 1000 | 310 | 3400 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 1-Chloropropane-2,2'-oxybis/ bis(2-chloroisopropyl)ether | 300 | 10 | | | | | 23 | 67 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| 4-Methylphenol (p-cresol) (co-elutes with 3-methylphenol (m-cresol)) | | | 34 | 100 | 500 | 1000 | 31 | 340 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| N-Nitroso-Di-N-Propylamine | 0.005 | 10 | | | | | 0.2 | 0.3 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| Hexachloroethane | 2 | 7 | | | | | 12 | 48 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Nitrobenzene | 4 | 6 | | | | | 5 | 14 | | | 0.8 | U | 0.67 | U | 1.9 | U |
| Isophorone | 40 | 10 | | | | | 510 | 2000 | | | 0.39 | U | 0.33 | U | 0.34 | J |
| 2-Nitrophenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dimethylphenol | 100 | 20 | | | | | 1200 | 14000 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| bis(2-Chloroethoxy)methane | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dichlorophenol | 20 | 10 | | | | | 180 | 2100 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| 1,2,4-Trichlorobenzene | 9 | 1 | | | | | 73 | 820 | | | 0.012 | U | 0.01 | U | 1 | U |
| Naphthalene | 300 | 2 | 100 | 100 | 500 | 1000 | 6 | 17 | | | 0.041 | J | 0.02 | J | 0.18 | U |
| 4-Chloroaniline | 30 | 10 | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Hexachloro-1,3-butadiene | 0.4 | 1 | | | | | 6 | 25 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| 4-Chloro-3-methylphenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2-Methylnaphthalene | 30 | 10 | | | | | 230 | 2400 | | | 0.033 | J | 0.067 | U | 0.18 | U |
| Hexachlorocyclopentadiene | 40 | 0.5 | | | | | 45 | 110 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 2,4,6-Trichlorophenol | 1 | 20 | | | | | 19 | 74 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 2,4,5-Trichlorophenol | 700 | 10 | | | | | 6100 | 68000 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 2-Chloronaphthalene | 600 | 10 | | | | | | | | | 0 | 0 | 0 | 0 | 0.18 | U |
| 2-Nitroaniline | | | | | | | 39 | 23000 | | | 2 | U | 1.7 | U | 4.8 | U |
| Dimethylphthalate | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Acenaphthylene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.1 | | 0.034 | J | 0.18 | U |
| 2,6-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 3-Nitroaniline | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Newark Bay - Upland - COMP B - Sediment Semivolatiles, con't. | | | | | | | | | | | | | | | | |
| Semivolatiles, continued | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | #20220313 | | #20220313 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | A COMP B | Q | A COMP B | |
| Acenaphthene | 400 | 10 | 100 | 100 | 500 | 1000 | 3400 | 37000 | | | 0.029 | J | 0.067 | U | 0.18 | U |
| 2,4-Dinitrophenol | 10 | 40 | | | | | 120 | 1400 | | | 3.9 | U | 3.3 | U | 9.6 | U |
| 4-Nitrophenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Dibenzofuran | | | 14 | 59 | 350 | 1000 | | | | | 0.39 | U | 0.33 | U | | |
| 2,4-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Diethylphthalate | 6000 | 1 | | | | | 49000 | 550000 | | | 0.21 | J | 0.33 | U | 0.96 | U |
| 4-Chlorophenyl-phenylether | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Fluorene | 300 | 1 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.049 | J | 0.067 | U | 0.18 | U |
| 4-Nitroaniline | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 4,6-Dinitro-2-methylphenol | 0.7 | 0.03 | | | | | 6 | 68 | | | 2 | U | 1.7 | U | 4.8 | U |
| N-Nitrosodiphenylamine | 7 | 10 | | | | | 99 | 390 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 4-Bromophenyl-phenylether | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Hexachlorobenzene | 0.02 | 0.02 | 0.33 | 1.2 | 6 | 12 | 0.3 | 1 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| Pentachlorophenol | 0.3 | 0.1 | 2.4 | 6.7 | 6.7 | 55 | 0.9 | 3 | | | 2 | U | 1.7 | U | 4.8 | U |
| Phenanthrene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.15 | | 0.063 | J | 0.18 | U |
| Anthracene | 2000 | 10 | 100 | 100 | 500 | 1000 | 17000 | 30000 | | | 0.25 | | 0.068 | | 0.18 | U |
| Carbazole | | | | | | | 24 | 96 | | | 0.066 | J | 0.017 | J | 0.18 | U |
| Di-n-butylphthalate | | | | | | | 6100 | 68000 | | | 0.39 | U | 0.33 | U | 1 | B |
| Fluoranthene | 300 | 10 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.31 | | 0.14 | | 0.18 | U |
| Pyrene | 200 | 0.1 | 100 | 100 | 500 | 1000 | 1700 | 18000 | | | 0.39 | | 0.15 | | 0.18 | U |
| Butylbenzylphthalate | 100 | 1 | | | | | 1200 | 14000 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| 3,3'-Dichlorobenzidine | 0.08 | 30 | | | | | 1 | 4 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Benzo(a)anthracene | 0.05 | 0.1 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.24 | | 0.089 | | 0.18 | U |
| Chrysene | 5 | 0.2 | 1 | 3.9 | 56 | 110 | 450 | 1700 | | | 0.3 | | 0.11 | | 0.18 | U |
| bis(2-Ethylhexyl)phthalate | 2 | 3 | | | | | 35 | 140 | | | 3.9 | U | 3.3 | U | 9.6 | U |
| DI-n-octylphthalate | 100 | 10 | | | | | 2400 | 27000 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Benzo(b)fluoranthene | 0.05 | 0.2 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.26 | | 0.13 | | 0.18 | U |
| Benzo(k)fluoranthene | 0.5 | 0.3 | 1 | 3.9 | 56 | 110 | 45 | 170 | | | 0.12 | | 0.052 | J | 0.18 | U |
| Benzo(a)pyrene | 0.005 | 0.1 | 1 | 1 | 1 | 1.1 | 0.5 | 2 | | | 0.31 | | 0.12 | | 0.18 | U |
| Indeno(1,2,3-cd)pyrene | 0.05 | 0.2 | 0.5 | 0.5 | 5.6 | 11 | 5 | 17 | | | 0.14 | | 0.074 | | 0.18 | U |
| Dibenzo(a,h)anthracene | 0.005 | 0.3 | 0.33 | 0.33 | 0.56 | 1.1 | 0.5 | 2 | | | 0.08 | U | 0.067 | U | 0.18 | U |
| Benzo(ghi)perylene | | | 100 | 100 | 500 | 1000 | 380000 | 30000 | | | 0.15 | | 0.092 | | 0.18 | U |
| Pyridine | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Acetophenone | 700 | 10 | | | | | 2 | 5 | | | 0.8 | U | 0.67 | U | 0.96 | U |
| Atrazine | 3 | 0.1 | | | | | 210 | 2400 | | | 0.8 | U | 0.67 | U | 0.96 | U |
| Benzaldehyde | | | | | | | 6100 | 68000 | | | 0.8 | U | 0.67 | U | 0.9 | J |
| Benzidine | 0.0002 | 20 | | | | | 0.7 | 0.7 | | | 8 | U | 6.7 | U | 19 | U |
| 1,1'-Biphenyl | 400 | 10 | | | | | 61 | 240 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Caprolactam | 4000 | 60 | | | | | 31000 | 340000 | | | 2 | U | 1.7 | U | 4.8 | U |
| 1,2-Diphenylhydrazine | 0.04 | 20 | | | | | 0.7 | 2 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| N-Nitrosodimethylamine | 0.0007 | 0.8 | | | | | 0.7 | 0.7 | | | 0.39 | U | 0.33 | U | 0.96 | U |
| Total Cresol | 50 | 0.1 | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Newark Bay - Upland - COMP B - Pesticides/Aroclors | | | | | | | | | | | | | | | | |
| Pesticides/Aroclors | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | | #20220313 | | | #20220313 | | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | | A COMP B | Q | | A COMP B | Q | |
| alpha-BHC | 0.006 | 0.02 | 0.097 | 0.48 | 3.4 | 6.8 | 0.1 | 0.5 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| beta-BHC | 0.02 | 0.04 | 0.072 | 0.36 | 3 | 14 | 0.4 | 2 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| delta-BHC | | | 100 | 100 | 500 | 1000 | | | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| gamma-BHC (Lindane) | 0.03 | 0.02 | 0.28 | 1.3 | 9.2 | 23 | 0.4 | 2 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Heptachlor | 0.008 | 0.05 | 0.42 | 2.1 | 15 | 29 | 0.1 | 0.7 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Aldrin | 0.002 | 0.04 | 0.019 | 0.097 | 0.68 | 1.4 | 0.04 | 0.2 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Heptachlor epoxide | 0.004 | 0.2 | | | | | 0.07 | 0.3 | | | 0.00067 | p | | 0.00032 | J p | | 0.0013 | U | |
| Endosulfan I | 40 | 0.02 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Dieldrin | 0.002 | 0.03 | 0.039 | 0.2 | 1.4 | 2.8 | 0.04 | 0.2 | 0.11 | 0.48 | 0.00045 | J | | 0.00018 | J p | | 0.0013 | U | |
| 4,4'-DDE | 0.1 | 0.01 | 1.8 | 8.9 | 62 | 120 | 2 | 9 | | | 0.0038 | | | 0.0018 | | | 0.0013 | U | |
| Endrin | 2 | 0.03 | 2.2 | 11 | 89 | 410 | 23 | 340 | | | 0.0018 | | | 0.00085 | | | 0.0013 | U | |
| Endosulfan II | 40 | 0.04 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| 4,4'-DDD | 0.1 | 0.02 | 2.6 | 13 | 92 | 180 | 3 | 13 | | | 0.0018 | p | | 0.0031 | | | 0.0013 | U | |
| Endosulfan sulfate | 40 | 0.02 | 4.8 | 24 | 200 | 920 | 470 | 6800 | | | 0.00025 | J p | | 0.00041 | U | | 0.0013 | U | |
| 4,4'-DDT | 0.1 | 0.1 | 1.7 | 7.9 | 47 | 94 | 2 | 8 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Methoxychlor | 40 | 0.1 | | | | | 390 | 5700 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Endrin ketone | | | | | | | | | | | | | | | | | | | |
| Endrin aldehyde | | | | | | | | | | | | | | | | | 0.0013 | U | |
| alpha-Chlordane | | | 0.91 | 4.2 | 24 | 47 | 0.2 | 1 | | | 0.00054 | | | 0.00027 | J | | 0.0013 | U | |
| gamma-Chlordane | | | | | | | 0.2 | 1 | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Toxaphene | 0.03 | 2 | | | | | 0.6 | 3 | | | 0.02 | U | | 0.017 | U | | 0.096 | U | |
| Mirex | 0.1 | 0.08 | | | | | | | | | 0.0005 | U | | 0.00041 | U | | 0.0013 | U | |
| Aroclor-1016 | | | | | | | | | | | 0.01 | U | | 0.0083 | U | | 0.0096 | U | |
| Aroclor-1221 | | | | | | | | | | | 0.01 | U | | 0.0083 | U | | 0.0096 | U | |
| Aroclor-1232 | | | | | | | | | | | 0.01 | U | | 0.0083 | U | | 0.0096 | U | |
| Aroclor-1242 | | | | | | | | | | | 0.01 | U | | 0.0083 | U | | 0.0096 | U | |
| Aroclor-1248 | | | | | | | | | | | 0.092 | | | 0.042 | | | 0.0096 | U | |
| Aroclor-1254 | | | | | | | | | | | 0.01 | U | | 0.0083 | U | | 0.0096 | U | |
| Aroclor-1260 | | | | | | | | | | | 0.059 | | | 0.02 | | | 0.0096 | U | |
| Total Aroclor(SUM) | 0.02 | 0.5 | 1 | 1 | 1 | 25 | 0.2 | 1 | 0.1 | 1 | 0.201 | | 79 | 0.1035 | | 9 | 0.0672 | | 1 |
Newark Bay - Upland - COMP B - Herbicides
| Herbicides | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | #20220313 | | #20220313 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | A COMP B | Q | A COMP B | Q |
| 2,4,5-TP (Silvex) | 60 | 0.6 | 58 | 100 | 500 | 1000 | | | | | 0.048 | U | 0.04 | U | 0.98 | U |
| 2,4-D | 70 | 2 | | | | | | | | | 0.19 | U | 0.16 | U | 3.9 | U |
Newark Bay - Upland - COMP B - Metals
| Metals | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | | #20220313 | | | #20220313 | | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | | A COMP B | Q | | A COMP B | Q | |
| Aluminum | 200 | 30 | | | | | 78000 | | | | 12000 | | | 13000 | | | 620 | | 12 |
| Antimony | 6 | 3 | | | | | 31 | 450 | | | 0.33 | | | 0.63 | F1 | | 0.69 | J | |
| Arsenic | 0.02 | 3 | 16 | 16 | 16 | 16 | 19 | 19 | 8.2 | 53 | 13 | | 9 | 13 | | 9 | 1.9 | | 1 |
| Barium | 6000 | 200 | 350 | 400 | 400 | 10000 | 16000 | 59000 | | | 57 | | | 65 | | | 46 | | |
| Beryllium | 1 | 1 | 14 | 72 | 590 | 2700 | 16 | 140 | | | 0.73 | | | 0.71 | | | 1 | U | |
| Cadmium | 4 | 0.5 | 2.5 | 4.3 | 9.3 | 60 | 78 | 78 | 1.2 | 9.5 | 0.39 | | | 0.36 | F1 | | 1 | U | |
| Calcium | | | | | | | | | | | | | | | | | | | |
| Chromium | 70 | 1 | | | | | | | | | 46 | | | 44 | F1 | | 9.2 | | 2 |
| Hexavalent Chromium | | | 22 | 110 | 400 | 800 | | | | | 0.96 | U | | 0.81 | U | | 0.01 | U F1 | |
| Trivalent Chromium | | | 36 | 180 | 1500 | 6800 | | | | | 46 | | 3 | 44 | | 3 | 9.2 | J | |
| Cobalt | 100 | 0.5 | | | | | 1600 | 590 | | | 9.9 | | | 10 | | | 3.5 | | 2 |
| Copper | 1300 | 4 | 270 | 270 | 270 | 10000 | 3100 | 45000 | 33 | 270 | 60 | | 9 | 71 | F1 | 9 | 170 | | 2 |
| Iron | 300 | 20 | | | | | | | | | | | | | | | | | |
| Lead | 5 | 5 | 400 | 400 | 1000 | 3900 | 400 | 800 | 47 | 218 | 71 | | 9 | 61 | F1 | 9 | 1.6 | | |
| Magnesium | | | | | | | | | | | | | | | | | | | |
| Manganese | 50 | 0.4 | 2000 | 2000 | 10000 | 10000 | 11000 | 5900 | | | 700 | | | 570 | | | 5 | U | |
| Mercury | 2 | 0.05 | 0.81 | 0.81 | 2.8 | 5.7 | 23 | 65 | 0.17 | 1.6 | 0.79 | H | 9 | 0.66 | H | 9 | 0.2 | U | |
| Nickel | 100 | 4 | 140 | 310 | 310 | 10000 | 1600 | 23000 | | | 31 | | | 29 | | | 20 | | 2 |
| Potassium | | | | | | | | | | | | | | | | | | | |
| Selenium | 40 | 4 | 36 | 180 | 1500 | 6800 | 390 | 5700 | | | 0.48 | J | | 0.44 | J F1 | | 2.2 | J | |
| Silver | 40 | 1 | 36 | 180 | 1500 | 6800 | 390 | 5700 | | | 1 | | | 0.83 | | | 1 | U | |
| Sodium | 50000 | 400 | | | | | | | | | | | | | | | | | |
| Thallium | 0.5 | 2 | | | | | | | | | | | | | | | 1 | U | |
| Vanadium | | | | | | | 78 | 1100 | | | 31 | | | 28 | F1 | | 4.1 | | |
| Zinc | 2000 | 10 | 2200 | 10000 | 10000 | 10000 | 23000 | 110000 | | | 150 | | | 220 | | | 5 | U | |
| Cyanide, total | | | 27 | 27 | 27 | 10000 | 47 | 680 | | | 0.48 | U | | 0.36 | J | | 10 | U | |
| %Solids | | | | | | | | | | | 41.3 | | | 49.6 | | | | | |
Newark Bay - Upland - COMP B - Dioxin/Furan
| Dioxin/Furan | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: pg/g) | | Threshold Exceedances | Amended Sediment | | | | |
| (Units: pg/g) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | |
| (Units: pg/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | pg/g | pg/g | #20220183 | | | #20220313 | | | #20220313 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | | A COMP B | Q | | A COMP B | Q |
| 2,3,7,8-TCDD | | | | | | | | | 4.5 | 50 | 12 | | 9 | 7.6 | | 9 | 9.9 | U |
| 1,2,3,7,8-PeCDD | | | | | | | | | | | 2.4 | J | | 1.8 | J q | | 50 | U |
| 1,2,3,4,7,8-HxCDD | | | | | | | | | | | 3.4 | J B | | 2.7 | J q B | | 1.5 | J B q |
| 1,2,3,6,7,8-HxCDD | | | | | | | | | | | 11 | B | | 10 | B | | 0.41 | J B q |
| 1,2,3,7,8,9-HxCDD | | | | | | | | | | | 9.3 | S B | | 7.1 | S B | | 1.2 | J B q |
| 1,2,3,4,6,7,8-HpCDD | | | | | | | | | | | 200 | | | 210 | | | 50 | U |
| OCDD | | | | | | | | | | | 2100 | B | | 2100 | B | | 4.6 | J B |
| 2,3,7,8-TCDF | | | | | | | | | | | 12 | | | 9.9 | | | 9.9 | U |
| 1,2,3,7,8-PeCDF | | | | | | | | | | | 4.2 | J | | 3.4 | J | | 0.82 | J B |
| 2,3,4,7,8-PeCDF | | | | | | | | | | | 6.7 | B | | 5.6 | B | | 50 | U |
| 1,2,3,4,7,8-HxCDF | | | | | | | | | | | 15 | | | 13 | | | 50 | U |
| 1,2,3,6,7,8-HxCDF | | | | | | | | | | | 7.6 | I | | 5.7 | I | | 50 | U |
| 2,3,4,6,7,8-HxCDF | | | | | | | | | | | 3.7 | J | | 3.1 | J | | 50 | U |
| 1,2,3,7,8,9-HxCDF | | | | | | | | | | | 6.0 | U | | 5.0 | U | | 50 | U |
| 1,2,3,4,6,7,8-HpCDF | | | | | | | | | | | 90 | B | | 80 | B | | 0.9 | J B q |
| 1,2,3,4,7,8,9-HpCDF | | | | | | | | | | | 4.3 | J B | | 3.4 | J B | | 0.64 | J B q |
| OCDF | | | | | | | | | | | 120 | B | | 93 | B | | 2.5 | J B q |
Newark Bay - Upland - COMP B - TOGS Totals
| TOGS Table 2 Totals | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220183 | | | #20220313 | | | #20220313 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP B | Q | | A COMP B | Q | | A COMP B | Q |
| Total BTEX | | | | | | | | | 0.96 | 5.9 | 0.06 | | | 0.05 | | | | |
| Total PAH | | | | | | | | | 4 | 45 | 2.919 | | | 1.343 | | | | |
| Total DDx | | | | | | | | | 0.003 | 0.03 | 0.0061 | | 9 | 0.00531 | | 9 | | |
| Total Chlordane | | | | | | | | | 0.003 | 0.036 | 0.00104 | | | 0.00068 | | | | |
| NJ Threshold values (solids) are for the sum of trans-1,3-dichloropropene and cis-1,3-dichloropropene | | | | | | | | | | | | | | | | | | |
| NY Threshold values (solids) are presented for m-cresol and p-cresol separately. These two analytes co-elute. The lower of the two values is reported as the threshold value when they differ. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values (solids) are presented for p-cresol only. M-cresol and p-cresol co-elute. The sum of the two concentration values are compared to threshold value when detected. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values for Endosulfan I and Endosulfan II are the sum of these two analytes. The Endo I and Endo II are compared to this value individualy. | | | | | | | | | | | | | | | | | | |
| NJ Threshold values for Chlordane are presented as a sum of the alpha and gamma isomers. The individual isomers are compared to the threshold values. | | | | | | | | | | | | | | | | | | |
| a Totals: | | | | | | | | | | | | | | | | | | |
| 1) include estimated values, those reported with a J qualifier | | | | | | | | | | | | | | | | | | |
| 2) If a concentration of a specific contaminant is reported as 'non-detect' or less than, and the method detection limit was not achieved, then the reported detection limit is used as an estimate of the maximum possible concentration. | | | | | | | | | | | | | | | | | | |
| 3) If a concentration of a specific contaminant is reported as 'non-detect' or less than, and the detection limit achieved was at or below the method detection limit, then half the achieved detection limit is used as an estimate of the concentration | | | | | | | | | | | | | | | | | | |
COMP C
| Newark Bay - Upland |
| Newark Bay - Upland - COMP C - Sediment Volatiles |
| Volatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220184 | | #20220314 | | #20220314 | | |
| Limit Exceedance Qualifier | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP C | Q | A COMP C | Q | A COMP C | Q | |
| Chloromethane (Methyl Chloride) | | | | | | | 4 | 12 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Bromomethane | 10 | 1 | | | | | 25 | 59 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Vinyl chloride | 0.08 | 1 | 0.21 | 0.9 | 13 | 27 | 0.7 | 2 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Chloroethane | | | | | | | 220 | 1100 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Methylene chloride (Dichloromethane) | 3 | 1 | 51 | 100 | 500 | 1000 | 46 | 230 | | | 0.013 | U | 0.011 | U | 14 | B | 12 |
| Acetone | 6000 | 10 | 100 | 100 | 500 | 1000 | 70000 | | | | 0.028 | J | 0.25 | | 15 | | 2 |
| Carbon disulfide | 700 | 1 | | | | | 7800 | 110000 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,1-Dichloroethene | | | 100 | 100 | 500 | 1000 | 11 | 150 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,1-Dichloroethane | 50 | 1 | 19 | 26 | 240 | 480 | 8 | 24 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dichloroethene (total) | | | | | | | | | | | 0.026 | U | 0.021 | U | 2 | U | |
| Chloroform | 70 | 1 | 10 | 49 | 350 | 700 | 0.6 | 2 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dichloroethane | 0.3 | 2 | 2.3 | 3.1 | 30 | 60 | 0.9 | 3 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 2-Butanone (MEK) | 300 | 2 | 100 | 100 | 500 | 1000 | 3100 | 44000 | | | 0.013 | U | 0.24 | | 5 | U | |
| 1,1,1-Trichloroethane | 30 | 1 | 100 | 100 | 500 | 1000 | 160000 | | | | 0.013 | U | 0.011 | U | 1 | U | |
| Carbon tetrachloride | 0.4 | 1 | 1.4 | 2.4 | 22 | 44 | 2 | 4 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Bromodichloromethane | 0.6 | 1 | | | | | 1 | 3 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dichloropropane | 0.5 | 1 | | | | | 2 | 5 | | | 0.013 | U | 0.011 | U | 1 | U | |
| cis-1,3-Dichloropropene | | | | | | | 2 | 7 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Trichloroethene | 1 | 1 | 10 | 21 | 200 | 400 | 3 | 10 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Dibromochloromethane | 0.4 | 1 | | | | | 3 | 8 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,1,2-Trichloroethane | 3 | 2 | | | | | 2 | 6 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Benzene | 0.2 | 1 | 2.9 | 4.8 | 44 | 89 | 2 | 5 | 0.59 | 2.16 | 0.013 | U | 0.011 | U | 1 | U | |
| trans-1,3-dichloropropene | | | | | | | 2 | 7 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Bromoform | 4 | 0.8 | | | | | 81 | 280 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 4-Methyl-2-pentanone (MIBK) | | | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| 2-Hexanone | 40 | 1 | | | | | | | | | 0 | 0 | 0 | 0 | | | |
| Tetrachloroethene | 0.4 | 1 | 5.5 | 19 | 150 | 300 | 43 | 1500 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,1,2,2-Tetrachloroethane | 1 | 1 | | | | | 1 | 3 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Toluene | 600 | 1 | 100 | 100 | 500 | 1000 | 6300 | 91000 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Chlorobenzene | 50 | 1 | 100 | 100 | 500 | 1000 | 510 | 7400 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Ethyl benzene | 700 | 2 | 30 | 41 | 390 | 780 | 7800 | 110000 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Styrene | 100 | 2 | | | | | 90 | 260 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Xylenes(Total) | 1000 | 2 | 100 | 100 | 500 | 1000 | 12000 | 170000 | | | 0.026 | U | 0.021 | U | 2 | U | |
| Acrolein | 4 | 5 | | | | | 0.5 | 1 | | | 0.26 | U | 0.21 | U | 20 | U | |
| Acrylonitrile | 0.06 | 2 | | | | | 0.9 | 3 | | | 0.13 | U | 0.11 | U | 20 | U | |
| 1,2-Dibromo-3-chloropropane | 0.02 | 0.02 | | | | | 0.08 | 0.2 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dibromoethane | 0.0004 | 0.03 | | | | | 0.008 | 0.04 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Dichlorodifluoromethane | 1000 | 2 | | | | | 490 | 230000 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dichloroethene (cis) | | | 59 | 100 | 500 | 1000 | 230 | 560 | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2-Dichloroethene (trans) | | | 100 | 100 | 500 | 1000 | 300 | 720 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Methyl acetate | 7000 | 0.5 | | | | | 78000 | | | | 0.064 | U | 0.053 | U | 5 | U | |
| Methyl tert-butyl ether (MTBE) | 70 | 1 | 62 | 100 | 500 | 1000 | 110 | 320 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Tertiary butyl alcohol (TBA) | 100 | 2 | | | | | 1400 | 11000 | | | 0.13 | U | 0.11 | U | 40 | U | |
| Trichlorofluoromethane | 2000 | 1 | | | | | 23000 | 340000 | | | 0.013 | U | 0.011 | U | 1 | U | |
| Combined 1,3-dichloropropenes (SUM) cis + trans | 0.4 | 1 | | | | | | | | | | | | | | | |
| 1,4-dioxane | 0.4 | 0.1 | 9.8 | 13 | 130 | 250 | | | | | 0.85 | U | 0.7 | U | 1.9 | U | |
| n-propylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
| sec-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
| tert-butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,2,4-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
| 1,3,5-trimethylbenzene | | | 47 | 52 | 190 | 380 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
| n-Butylbenzene | | | 100 | 100 | 500 | 1000 | | | | | 0.013 | U | 0.011 | U | 1 | U | |
Newark Bay - Upland - COMP C - Sediment Semivolatiles
| Semivolatiles | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220184 | | #20220314 | | #20220314 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP C | Q | A COMP C | Q | A COMP C | Q |
| Phenol | 2000 | 10 | 100 | 100 | 500 | 1000 | 18000 | 210000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| bis(2-Chloroethyl)ether | 0.03 | 7 | | | | | 0.4 | 2 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| 2-Chlorophenol | 40 | 20 | | | | | 310 | 2200 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 1,3-Dichlorobenzene | 600 | 5 | 17 | 49 | 280 | 560 | 5300 | 59000 | | | 0.013 | U | 0.011 | U | 1 | U |
| 1,4-Dichlorobenzene | 75 | 5 | 9.8 | 13 | 130 | 250 | 5 | 13 | | | 0.013 | U | 0.011 | U | 1 | U |
| 1,2-Dichlorobenzene | 600 | 5 | 100 | 100 | 500 | 1000 | 5300 | 59000 | | | 0.013 | U | 0.011 | U | 1 | U |
| 2-Methylphenol (o-cresol) | | | 100 | 100 | 500 | 1000 | 310 | 3400 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 1-Chloropropane-2,2'-oxybis/ bis(2-chloroisopropyl)ether | 300 | 10 | | | | | 23 | 67 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| 4-Methylphenol (p-cresol) (co-elutes with 3-methylphenol (m-cresol)) | | | 34 | 100 | 500 | 1000 | 31 | 340 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| N-Nitroso-Di-N-Propylamine | 0.005 | 10 | | | | | 0.2 | 0.3 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| Hexachloroethane | 2 | 7 | | | | | 12 | 48 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| Nitrobenzene | 4 | 6 | | | | | 5 | 14 | | | 0.85 | U | 0.7 | U | 1.9 | U |
| Isophorone | 40 | 10 | | | | | 510 | 2000 | | | 0.42 | U | 0.35 | U | 0.33 | J |
| 2-Nitrophenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dimethylphenol | 100 | 20 | | | | | 1200 | 14000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| bis(2-Chloroethoxy)methane | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2,4-Dichlorophenol | 20 | 10 | | | | | 180 | 2100 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| 1,2,4-Trichlorobenzene | 9 | 1 | | | | | 73 | 820 | | | 0.013 | U | 0.011 | U | 1 | U |
| Naphthalene | 300 | 2 | 100 | 100 | 500 | 1000 | 6 | 17 | | | 0.051 | J | 0.038 | J | 0.18 | U |
| 4-Chloroaniline | 30 | 10 | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Hexachloro-1,3-butadiene | 0.4 | 1 | | | | | 6 | 25 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| 4-Chloro-3-methylphenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 2-Methylnaphthalene | 30 | 10 | | | | | 230 | 2400 | | | 0.035 | J | 0.024 | J | 0.18 | U |
| Hexachlorocyclopentadiene | 40 | 0.5 | | | | | 45 | 110 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 2,4,6-Trichlorophenol | 1 | 20 | | | | | 19 | 74 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 2,4,5-Trichlorophenol | 700 | 10 | | | | | 6100 | 68000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 2-Chloronaphthalene | 600 | 10 | | | | | | | | | 0 | 0 | 0 | 0 | 0.18 | U |
| 2-Nitroaniline | | | | | | | 39 | 23000 | | | 2.2 | U | 1.8 | U | 4.9 | U |
| Dimethylphthalate | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Acenaphthylene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.1 | | 0.076 | | 0.18 | U |
| 2,6-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 3-Nitroaniline | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Newark Bay - Upland - COMP C - Sediment Semivolatiles, con't. | | | | | | | | | | | | | | | | |
| Semivolatiles, continued | New Jersey Ground Water Quality Criterion | New Jersey Practical Quantitation Level (PQL)* | New York Residential | New York Restricted-Residential | New York Commercial | New York Industrial | New Jersey Residential Direct Contact Soil Remediation Standard | New Jersey Non-Residential Direct Contact Soil Remediation Standard | New York TOGS Class B | New York TOGS Class C | Unamended Sediment | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | Amended Sediment | | | | | | | | | | | | | | |
| (Units: mg/kg) | | Threshold Exceedances | SPLP | | | | | | | | | | | | | | |
| (Units: ug/L) | | Threshold Exceedances | | | | | | | | | | | | | | | |
| ASI ID # | ug/L | ug/L | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | ppm (mg/kg) | mg/kg | mg/kg | mg/kg | mg/kg | #20220184 | | #20220314 | | #20220314 | |
| | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | COMP C | Q | A COMP C | Q | A COMP C | Q |
| Acenaphthene | 400 | 10 | 100 | 100 | 500 | 1000 | 3400 | 37000 | | | 0.031 | J | 0.021 | J | 0.18 | U |
| 2,4-Dinitrophenol | 10 | 40 | | | | | 120 | 1400 | | | 4.2 | U | 3.5 | U | 9.7 | U |
| 4-Nitrophenol | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Dibenzofuran | | | 14 | 59 | 350 | 1000 | | | | | 0.42 | U | 0.35 | U | | |
| 2,4-Dinitrotoluene | 0.05 | 10 | | | | | 0.7 | 3 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| Diethylphthalate | 6000 | 1 | | | | | 49000 | 550000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 4-Chlorophenyl-phenylether | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Fluorene | 300 | 1 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.04 | J | 0.03 | J | 0.18 | U |
| 4-Nitroaniline | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| 4,6-Dinitro-2-methylphenol | 0.7 | 0.03 | | | | | 6 | 68 | | | 2.2 | U | 1.8 | U | 4.9 | U |
| N-Nitrosodiphenylamine | 7 | 10 | | | | | 99 | 390 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 4-Bromophenyl-phenylether | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
| Hexachlorobenzene | 0.02 | 0.02 | 0.33 | 1.2 | 6 | 12 | 0.3 | 1 | | | 0.086 | U | 0.071 | U | 0.18 | U |
| Pentachlorophenol | 0.3 | 0.1 | 2.4 | 6.7 | 6.7 | 55 | 0.9 | 3 | | | 2.2 | U | 1.8 | U | 4.9 | U |
| Phenanthrene | | | 100 | 100 | 500 | 1000 | | 300000 | | | 0.14 | | 0.12 | | 0.18 | U |
| Anthracene | 2000 | 10 | 100 | 100 | 500 | 1000 | 17000 | 30000 | | | 0.13 | | 0.1 | | 0.18 | U |
| Carbazole | | | | | | | 24 | 96 | | | 0.024 | J | 0.022 | J | 0.18 | U |
| Di-n-butylphthalate | | | | | | | 6100 | 68000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| Fluoranthene | 300 | 10 | 100 | 100 | 500 | 1000 | 2300 | 24000 | | | 0.34 | | 0.24 | | 0.18 | U |
| Pyrene | 200 | 0.1 | 100 | 100 | 500 | 1000 | 1700 | 18000 | | | 0.46 | | 0.27 | | 0.18 | U |
| Butylbenzylphthalate | 100 | 1 | | | | | 1200 | 14000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| 3,3'-Dichlorobenzidine | 0.08 | 30 | | | | | 1 | 4 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| Benzo(a)anthracene | 0.05 | 0.1 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.25 | | 0.17 | | 0.18 | U |
| Chrysene | 5 | 0.2 | 1 | 3.9 | 56 | 110 | 450 | 1700 | | | 0.32 | | 0.19 | | 0.18 | U |
| bis(2-Ethylhexyl)phthalate | 2 | 3 | | | | | 35 | 140 | | | 4.2 | U | 3.5 | U | 9.7 | U |
| DI-n-octylphthalate | 100 | 10 | | | | | 2400 | 27000 | | | 0.42 | U | 0.35 | U | 0.97 | U |
| Benzo(b)fluoranthene | 0.05 | 0.2 | 1 | 1 | 5.6 | 11 | 5 | 17 | | | 0.34 | | 0.24 | | 0.18 | U |
| Benzo(k)fluoranthene | 0.5 | 0.3 | 1 | 3.9 | 56 | 110 | 45 | 170 | | | 0.13 | | 0.078 | | 0.18 | U |
| Benzo(a)pyrene | 0.005 | 0.1 | 1 | 1 | 1 | 1.1 | 0.5 | 2 | | | 0.33 | | 0.22 | | 0.18 | U |
| Indeno(1,2,3-cd)pyrene | 0.05 | 0.2 | 0.5 | 0.5 | 5.6 | 11 | 5 | 17 | | | 0.18 | | 0.13 | | 0.18 | U |
| Dibenzo(a,h)anthracene | 0.005 | 0.3 | 0.33 | 0.33 | 0.56 | 1.1 | 0.5 | 2 | | | 0.087 | | 0.071 | U | 0.18 | U |
| Benzo(ghi)perylene | | | 100 | 100 | 500 | 1000 | 380000 | 30000 | | | 0.26 | | 0.16 | | 0.18 | U |
| Pyridine | | | | | | | | | | | 0 | 0 | 0 | 0 | | |
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