This listing represents
the combination of Tables 3-2 and 7-1 from the Department of Environmental
Protection and Energy’s February 3, 1992 proposed rule entitled
Cleanup Standards for Contaminated Sites, N.J.A.C. 7:26D, as corrected
based upon errors identified by the Department during or subsequent
to the comment period as well as new toxicological or other information
obtained since the rule proposal. Please refer to the respective footnotes
for more detail. Notwithstanding, where the following criteria are
based on human health impacts, the Department shall still consider
environmental impacts when establishing site-specific cleanup criteria.
This along with other site-specific factors including background conditions
may result in site specific cleanup criteria which differ from the
criteria listed below. Therefore, this list shall not be assumed to
represent approval by the Department of any remedial action or to
represent the Department’s opinion that a site requires remediation.
Note: Material bracketed [thus]
is deleted and material underlined thus is added
| |
Residential Direct Contact Soil Cleanup
Criteria (a) (b ) |
Non- Residential Direct Contact Soil Cleanup Criteria (a) (b) |
Impact to Ground water Soil Cleanup Criteria (b)
|
| Contaminant |
CASRN |
(RDCSCC) |
(NRDCSCC) |
(IGWSCC) |
| Acenaphthene |
83-32-9 |
3400 |
10000(c) |
100 |
| Acetone (2-propanone) |
67-64-1 |
1000(d) |
1000(d) |
100 |
| Acrylonitrile |
107-13-1 |
1 |
5 |
1 |
| Aldrin |
309-00-2 |
0.040 |
0.17 |
50 |
| Anthracene |
120-12-7 |
10000(c) |
10000(c) |
100 |
| Antimony |
7440-36-0 |
14 |
340 |
(h) |
| Arsenic |
7440-38-2 |
20 (e) |
20 (e) |
(h) |
| Barium |
7440-39-3 |
700 |
47000(n) |
(h) |
| Benzene |
71-43-2 |
3 |
13 |
1 |
| Benzo(b)fluoranthene (3,4-Benzofluoranthene) |
205-99-2 |
0.9 |
4 |
50 |
| Benzo(a)anthracene (1,2-Benzanthracene) |
56-55-3 |
0.9 |
4 |
500 |
| Benzo(a)pyrene (BaP) |
50-32-8 |
0.66(f) |
0.66(f) |
100 |
| Benzo(k)fluoranthene |
207-08-9 |
0.9 |
4 |
500 |
| Benzyl Alcohol |
100-51-6 |
10000(c) |
10000(c) |
50 |
| Beryllium |
7440-41-7 |
[1(f)] 2 (e) |
[1(f)] 2 (e) |
(h) |
| Bis(2-chloroethyl) ether |
111-44-4 |
0.66(f) |
3 |
10 |
| Bis(2-chloroisopropyl)ether |
108-60-1 |
2300 |
10000(c) |
10 |
| Bis(2-ethylhexyl) phthalate |
117-81-7 |
49
|
210 |
100 |
| Bromodichloromethane (Dichlorobromomethane) |
75-27-4 |
11 |
46 |
1 |
| Bromoform |
75-25-2 |
86 |
370 |
1 |
| Bromomethane (Methyl bromide) |
74-83-9 |
79 |
1000 (d) |
1 |
| 2-Butanone (Methyl ethyl ketone) (MEK) |
78-93-3 |
1000 (d) |
1000 (d) |
50 |
| Butylbenzyl phthalate |
85-68-7 |
1100 |
10000 (c) |
100 |
| Cadmium |
7440-43-9 |
[1] 39 |
100 |
(h) |
| Carbon tetrachloride |
56-23-5 |
2 (k) |
4 (k) |
1 |
| 4-Chloroaniline (p-Chloroaniline) |
106-47-8 |
230 |
4200 |
(r) |
Chlorobenzene
|
108-90-7 |
37 |
680 |
1 |
| Chloroform |
67-66-3
|
19 (k) |
28 (k) |
1 |
| 4-Chloro-3-methyl phenol (p-Chloro-m-cresol) |
59-50-7 |
10000 (c) |
10000 (c) |
100 |
| Chloromethane (Methyl chloride) |
74-87-3 |
520 |
1000 (d) |
10 |
| 2-Chlorophenol (o-Chlorophenol) |
95-57-8 |
280 |
5200 |
10 |
Chromium – hexavalent (VI)
|
18540-29-9 |
240; 270 (g); (i) |
6100; 20 (g); (i) |
(h) |
| Chromium – trivalent (III) |
16065-83-1 |
120,000 |
(j) |
(l) |
| Chrysene |
218-01-9 |
9 |
40 |
500 |
| Copper |
7440-50-8 |
600 (m) |
600 (m) |
(h) |
| Cyanide |
57-12-5 |
1100 |
21000 (o) |
(h) |
4,4'-DDD (p,p'-TDE)
|
72-54-8 |
3 |
12 |
50 |
| 4,4'-DDE (p,p’-DDX) |
72-55-9 |
2 |
9 |
50 |
| 4,4'-DDT |
50-29-3 |
2 |
9 |
500 |
| Dibenz(a,h)anthracene |
53-70-3 |
0.66 (f) |
0.66 (f) |
100 |
| Dibromochloromethane (Chlorodibromomethane) |
124-48-1 |
110 |
1000 (d) |
1 |
| Di-n-butyl phthalate |
84-74-2 |
5700 |
10000 (c) |
100 |
| Di-n-octyl phthalate |
117-84-0 |
1100 |
10000 (c) |
100 |
| 1,2-Dichlorobenzene (o-Dichlorobenzene) |
95-50-1 |
5100 |
10000 (c) |
50 |
1,3-Dichlorobenzene (m-Dichlorobenzene)
|
541-73-1 |
5100 |
10000 (c) |
100 |
| 1,4-Dichlorobenzene (p-Dichlorobenzene) |
106-46-7 |
570 |
10000 (c) |
100 |
| 3,3'-Dichlorobenzidine |
91-94-1 |
2 |
6 |
100 |
| 1,1-Dichloroethane |
75-34-3 |
570 |
1000 (d) |
10 |
| 1,2-Dichloroethane |
107-06-2 |
6 |
24 |
1 |
| 1,1-Dichloroethene |
75-35-4 |
8 |
150 |
10 |
| 1,2-Dichloroethene (trans) |
156-60-5 |
1000 (d) |
1000 (d) |
50 |
1,2-Dichloroethene (cis)
|
156-59-2 |
79 |
1000 (d) |
1 |
| 2,4-Dichlorophenol |
120-83-2 |
170 |
3100 |
10 |
| 1,2-Dichloropropane |
78-87-5 |
10 |
43 |
(r) |
| 1,3-Dichloropropene(cis and trans) |
542-75-6 |
4 |
5 (k) |
1 |
| Dieldrin |
60-57-1 |
0.042 |
0.18 |
50 |
| Diethyl phthalate |
84-66-2 |
10000 (c) |
10000 (c) |
50 |
| 2,4-Dimethyl phenol |
105-67-9 |
1100 |
10000 (c) |
10 |
| Dimethyl phthalate |
131-11-3 |
10000 (c) |
10000 (c) |
50 |
2,4-Dinitrophenol
|
51-28-5 |
110 |
2100 |
10 |
| Dinitrotoluene(2,4-/2,6-mixture) |
25321-14-6 |
1 (l) |
4 (l) |
10 (l) |
| Endosulfan |
115-29-7 |
340 |
6200 |
50 |
| Endrin |
72-20-8 |
17 |
310 |
50 |
| Ethylbenzene |
100-41-4 |
1000 (d) |
1000 (d) |
100 |
| Fluoranthene |
206-44-0 |
2300 |
10000 (c) |
100 |
| Fluorene |
86-73-7 |
2300 |
10000 (c) |
100 |
| Heptachlor |
76-44-8 |
0.15 |
0.65 |
50 |
| Hexachlorobenzene |
118-74-1 |
0.66 (f) |
2 |
100 |
| Hexachlorobutadiene |
87-68-3 |
1 |
21 |
100 |
| Hexachlorocyclopentadiene |
77-47-4 |
400 |
7300 |
100 |
| Hexachloroethane |
67-72-1 |
6 |
100 |
100 |
| Indeno(1,2,3-cd)pyrene |
193-39-5 |
0.9 |
4 |
500 |
Isophorone
|
78-59-1 |
1100 |
10000 (c) |
50 |
| Lead |
7439-92-1 |
400 (p) |
600 (q) |
(h) |
| Lindane (gamma BHC) (gamma HCH) |
58-89-9 |
0.52 |
2.2 |
50 |
| 2-Methylphenol (o-creosol) |
95-48-7 |
2800 |
10000 (c) |
(r) |
| 4-Methylphenol (p-creosol) |
106-44-5 |
2800 |
10000 (c) |
(r) |
Methoxychlor
|
72-43-5 |
280 |
5200 |
50 |
| Mercury |
7439-97-6 |
14 |
270 |
(h) |
| 4-Methyl-2-pentanone (MIBK) |
108-10-1 |
1000 (d) |
1000 (d) |
50 |
| Methylene chloride (Dichloromethane) |
75-09-2 |
49 |
210 |
1 |
| Naphthalene |
91-20-3 |
230 |
4200 |
100 |
| Nickel |
7440-02-0 |
250 |
2400 (k) (n) |
(h) |
| Nitrobenzene |
98-95-3 |
28 |
520 |
10 |
| N-Nitrosodiphenylamine |
86-30-6 |
140 |
600 |
100 |
| N-Nitrosodi-n-propylamine |
621-64-7 |
0.66 (f) |
0.66 (f) |
10 |
| PCBs (Polychlorinated biphenyls) |
1336-36-3 |
0.49 |
2 |
50 |
| Pentachlorophenol |
87-86-5 |
6 |
24 |
100 |
| Phenol |
108-95-2 |
10000 (c) |
10000 (c) |
50 |
| Pyrene |
129-00-0 |
1700 |
10000 (c) |
100 |
| Selenium |
7782-49-2 |
63 |
3100 (n) |
(h) |
| Silver |
7440-22-4 |
110 |
4100 (n) |
(h) |
| Styrene |
100-42-5 |
23 |
97 |
100 |
| 1,1,1,2-Tetrachloroethane |
630-20-6 |
170 |
310 |
1 |
| 1,1,2,2-Tetrachloroethane |
79-34-5 |
34 |
70 (k) |
1 |
| Tetrachloroethene (Tetrachloroethylene) (PCE) |
127-18-4 |
4 (k) |
6 (k) |
1 |
| Thallium |
7440-28-0 |
2 (f) |
2 (f) |
(h) |
| Toluene |
108-88-3 |
1000 (d) |
1000 (d) |
500 |
| Toxaphene |
8001-35-2 |
0.10 (k) |
0.2 (k) |
50 |
| 1,2,4-Trichlorobenzene |
120-82-1 |
68 |
1200 |
100 |
1,1,1-Trichloroethane
|
71-55-6 |
210 |
1000 (d) |
50 |
| 1,1,2-Trichloroethane |
79-00-5 |
22 |
420 |
1 |
| Trichloroethene (Trichloroethylene) (TCE) |
79-01-6 |
23 |
54 (k) |
1 |
| 2,4,5-Trichlorophenol |
95-95-4 |
5600 |
10000 (c) |
50 |
| 2,4,6-Trichlorophenol |
88-06-2 |
62 |
270 |
10 |
| Vanadium |
7440-62-2 |
370 |
7100 (n) |
(h) |
| Vinyl chloride |
75-01-4 |
2 |
7 |
10 |
| Xylenes (Total) |
1330-20-7 |
410 |
1000 (d) |
[10] 67 (s) |
| Zinc |
7440-66-6 |
1500 (m) |
1500 (m) |
(h) |
Footnotes:
(a) Criteria are health based using an incidental ingestion exposure
pathway except where noted below.
(b) Criteria are subject to change based on site specific factors
(e.g., aquifer classification, soil type, natural background, environmental
impacts, etc.).
(c) Health based criterion exceeds the 10,000 mg/kg maximum for
total organic contaminants.
(d) Health based criterion exceeds the 1000 mg/kg maximum for total
volatile organic contaminants.
(e) Cleanup standard proposal was based on natural background.
(f) Health based criterion is lower than analytical limits; cleanup
criterion based on practical quantitation level.
(g) Criterion based on the inhalation exposure pathway.
(h) The impact to ground water values for inorganic constituents
will be developed based upon site specific chemical and physical
parameters.
(i) Site specific determination required for SCC for the allergic
contact dermatitis exposure pathway.
(j) Contaminant not regulated for this exposure pathway.
(k) Criteria based on inhalation exposure pathway, which yielded
a more stringent criterion than the incidental ingestion exposure
pathway.
(l) No criterion derived for this contaminant.
(m) Criterion based on ecological (phytotoxicity) effects.
(n) Level of the human health based criterion is such that evaluation
for potential environmental impacts on a site by site basis is recommended.
(o) Level of the criterion is such that evaluation for potential
acute exposure hazard is recommended.
(p) Criterion based on the USEPA Integrated Exposure Uptake Biokinetic
(IEUBK) model utilizing the default parameters. The concentration
is considered to protect 95% of target population (children) at
a blood lead level of 10 ug/dl.
(q) Criteria were derived from a model developed by the Society
for Environmental Geochemistry and Health (SEGH) and were designed
to be protective for adults in the workplace.
(r) Insufficient information available to calculate impact to ground
water criteria.
(s) Criterion based on new drinking water standard.
|
