PUBLIC HEALTH ASSESSMENT
WASTE INC. LANDFILL
MICHIGAN CITY, LA PORTE COUNTY, INDIANA

Figure 2. Soil Sample Locations

Figure 3. Round One Monitoring Well Locations

Figure 4. Round Two Monitoring Well Locations

Figure 5. Rain Water and Storm Runoff/Leachate Sample Locations

Figure 6. Stream Sampling Cross Sections
On-Site Subsurface Soil Sample Results, August/October 1989
| Chemical | Sample No. |
Sample Depth (Feet) |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | ||||
| acenaphthene | WIE041S WI0031S |
2-4 | 70-250 | 100,000 | RMEG |
| acenaphthylene | WI0031S | 2-4 | 63 | - | * |
| acetone | WIN071S | 30.5-33 | 32-140 | 400,000 | RMEG |
| anthracene | WIF011S WI0031S |
0-4 | 49-410 | 600,000 | RMEG |
| aroclor-1242 | WI0031S | 2-4 | 4,400 | 100 | RMEG |
| aroclor-1260 | WI0031S | 2-4 | 2,200 | 100 | RMEG |
| benzene | WIH131S | 30.5-33 | 7 | 20,000 | CREG |
| benzo(a)anthracene | WII011S WII0031S |
2-5 | 60-1,400 | - | * |
| benzo(b)fluoranthene | WII011S WII0031S |
2-10 | 98-2,000 | - | * |
| benzo(k)fluoranthene | WII011S WII0031S |
2-10 | 98-2,000 | - | * |
| benzo(g,h,i)perylene | WII011S WI0031S |
2-10 | 53-470 | - | * |
| benzoic acid | WIF011SR WIL111S |
0-7 | 44-490 | 8,000,000 | RMEG |
| bis(2-ethylhexyl) phthalate |
WIH131S WI0031S |
2-33 | 550-6,200 | 50,000 | CREG |
| chloroform | WIF101S | 2-5 | 3 | 20,000 | EMEG |
| chrysene | WIF101S WII0031S |
2-4 | 65-1,100 | - | * |
| dibenzofuran | WIE041S WI0031S |
2-4 | 79-190 | - | * |
| 1,2-dichloroethene (total) | WIH131S | 30.5-33 | 37 | 46,000 | RMEG |
| 2,4-dimethylphenol | WI0031S | 2-4 | 52 | 40,000 | RMEG |
| di-n-butylphthalate | WIE041S | 2-4 | 2,700 | 1,000,000 | EMEG |
| Chemical | Sample No. |
Sample Depth (Feet) |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | ||||
| ethylbenzene | WIH131S WIH131SDL |
30.5-33 | 1,400-230,000 | 200,000 | RMEG |
| fluoranthene | WII011S WI0031S |
2-10 | 100-2,100 | 80,000 | RMEG |
| fluorene | WIE041S WI0031S |
2-4 | 100-240 | 80,000 | RMEG |
| 2-methylnaphthalene | WIM011S WIH131S |
8-33 | 43-670 | - | * |
| 2-methylphenol | WIE041S | 2-4 | 81 | - | * |
| 4-methylphenol | WIE041S WIH131S |
2-33 | 89-300 | 5,000 | OSHA |
| naphthalene | WIM011S WIH131S |
8-33 | 43-2,500 | 10,000 | OSHA |
| 3-nitroaniline | WI0031S | 2-4 | 2,000 | - | * |
| 4-nitrophenol | WIN071S | 2-4 | 240 | - | * |
| n-nitrosodiphenylamine | WIF011SR | 0-2 | 86 | 100,000 | CREG |
| phenanthrene | WIM011S WI0031S |
2-10 | 51-1,900 | - | * |
| phenol | WI0031S WIE041S |
2-4 | 190-360 | 1,000,000 | RMEG |
| pyrene | WIF101S WI0031S |
2-5 | 94-2,400 | 60,000 | RMEG |
| toluene | WIH131SDL | 30.5-33 | 82,000 | 400,000 | RMEG |
| total xylenes | WIE041S WIH131SDL |
2-33 | 3-890,000 | 400,000 | EMEG |
| trichloroethene | WIH131S | 30.5-33 | 31 | 100,000 | OSHA |
| (ppm) | |||||
| aluminum | WIL111S WI0031S |
2-7 | 1,100-15,000 | - | * |
| antimony | WIL111S WI0031S |
2-4 | 16 | 0.8 | RMEG |
| Chemical | Sample No. |
Sample Depth (Feet) |
Concentration Range - ppm |
Comparison Value | |
| ppm | Source | ||||
| arsenic | WIF011S WI0031S |
0-4 | 3-12 | 0.6 | EMEG |
| barium | WIN071S WIH131S |
2-33 | 54-206 | 100 | RMEG |
| beryllium | WIF011SR | 0-2 | 1 | 0.2 | CREG |
| cadmium | WIF011SP WI0031S |
0-4 | 2-28 | 1 | EMEG |
| calcium | WII011S WI0031S |
2-10 | 2,050-325,000 | - | * |
| chromium | WIL111S WI0031S |
2-7 | 3-115 | 10 | RMEG |
| cobalt | WI0031S | 2-4 | 22 | - | * |
| copper | WIH131S WI0031S |
2-33 | 9-1,670 | - | * |
| cyanide | WI0031S | 2-4 | 2 | 40 | RMEG |
| iron | WIL111S WI0031S |
2-7 | 3,740-94,000 | - | * |
| lead | WIM011S WI0031S |
2-7 | 9-624 | - | * |
| magnesium | WIE041S WIN071S |
2-4 | 4,350-18,200 | - | * |
| manganese | WIL111S WI0031S |
2-7 | 69-1,280 | 10 | RMEG |
| mercury | WIM011S WI0031S |
2-10 | <1-8 | - | * |
| nickel | WIN071S WI0031S |
2-4 | 17-156 | 40 | RMEG |
| potassium | WIN071S | 2-4 | 2,200 | - | * |
| vanadium | WIF011S WIF101S |
0-5 | 11-36 | 6 | EMEG |
| zinc | WIL111S WI0031S |
2-7 | 23-1,960 | 600 | RMEG |
On-Site Groundwater Sample Results, Rounds I & II, May 1990/January 1991.
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| (Round I) | ||||
| benzene | WIMW5D | 11 | 1 | CREG |
| bis(2-ethylhexyl) phthalate |
WIMW5D | 2 | 3 | CREG |
| chloroethane | WIMW5D | 47 | - | * |
| diethylphthalate | WIMW10D | 3 | 8,000 | RMEG |
| methylene chloride | WIMW1D WIMW2S |
2-29 | 600 | EMEG |
| toluene | WIMW8S | 2 | 2,000 | RMEG |
| (Round II) | ||||
| acenaphthene | WIMW4I | 9 | 600 | RMEG |
| acetone | WIMW82D | 6 | 2,000 | EMEG |
| anthracene | WIMW4I | 3 | 3,000 | RMEG |
| aroclor-1254 | WIMW8S | 2 | 0.7 | RMEG |
| benzo(a)anthracene | WIMW4I | 6 | 0.1 | MCL |
| benzo(b)fluoranthene | WIMW4I | 7 | 0.2 | MCL |
| benzoic acid | WIMW3S WIMW5S |
2-17 | 40,000 | RMEG |
| chrysene | WIMW4I | 9 | 0.2 | MCL |
| dibenzofuran | WIMW4I | 7 | - | * |
| 1,2-dichloroethene (total) | WIMW10S | 2 | 200 | RMEG |
| ethylbenzene | WIMW3D | 4 | 1,000 | RMEG |
| fluoranthene | WIMW4I | 11 | 400 | RMEG |
| fluorene | WIMW4I | 7 | 400 | RMEG |
| 2-methylnaphthalene | WIMW4I | 16 | - | * |
| 4-methylphenol | WIMW4I WIMW5S |
2-4 | - | * |
| naphthalene | WIMW4I | 9 | 20 | LTHA |
| n-nitrosodiphenylamine | WIMW4I | 16 | 7 | CREG |
| phenanthrene | WIMW4I2 | 22 | - | * |
| pyrene | WIMW4I | 11 | 300 | RMEG |
| 1,1,1-trichloroethane | WIMW10S | 9 | 200 | LTHA |
| total xylenes | WIMW4I | 19 | 2,000 | EMEG |
On-Site Groundwater Sample Results for Dissolved Inorganic
Chemicals (Rounds I & II), May 1990/January 1991
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| (Round I) | ||||
| aluminum | WIMW1S WIMW1S |
338 | - | * |
| barium | WIMW5D WIMW8S |
472 | 700 | RMEG |
| calcium | WIMW1S WIMW2S |
25,600-110,000 | - | * |
| iron | WIMW8D WIMW5D |
190 | - | * |
| magnesium | WIMW1S WIMW6D WIMW5D |
5,010-68,100 | - | * |
| manganese | WIMW1S WIMW10S |
29-980 | 50 | RMEG |
| nickel | WIMW5D | 45 | 200 | RMEG |
| potassium | WIMW10S WIMW5D |
6,640-66,400 | - | * |
| sodium | WIMW1D WIMW5D |
9,520-178,000 | 20,000 | MEMO |
| (Round II) | ||||
| aluminum | WIMW8D WIMW1S |
39-1,890 | - | * |
| arsenic | WIMW5I WIMW4I |
3-219 | 3 | EMEG |
| barium | WIMW8D WIMW6D WIMW6I WIMW8S |
2-594 | 700 | RMEG |
| calcium | WIMW3D WIMW6D WIMW6I WIMW2S |
65-179,000 | - | * |
| cobalt | WIMW5S | 10 | - | * |
| copper | WIMW1S WIMW3D |
3-9 | 1,300 | MCL |
| iron | WIMW5I WIMW2I |
43-31,100 | - | * |
| magnesium | WIMW8D WIMW6D WIMW6I WIMW4I |
59-86,000 | - | * |
| manganese | WIMW8D WIMW6I WIMW2S |
1-1,900 | 50 | RMEG |
| nickel | WIMW3I WIMW4I |
11-86 | 200 | RMEG |
| sodium | WIMW3D WIMW6D WIMW6I WIMW4I |
731-306,000 | 20,000 | MEMO |
| vanadium | WIMW10S | 7 | 30 | EMEG |
On-Site Groundwater Sample Results for Total Inorganic Chemicals (Rounds I & II), May 1990/January 1991
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| (Round I) | ||||
| aluminum | WIMW5D WIMW1S |
1,040-230,000 | - | * |
| arsenic | WIMW8S WIMW1S |
21-445 | 3 | EMEG |
| barium | WIMW10S WIMW8S |
364-1,370 | 700 | RMEG |
| beryllium | WIMW1S | 13-15 | 0.008 | CREG |
| chromium | WIMW1D WIMW1S |
10-409 | 100 | LTHA |
| cobalt | WIMW10S WIMW1S |
53-247 | - | * |
| copper | WIMW10D WIMW8S |
31-1,740 | 1,300 | MCL |
| iron | WIMW8D MIMW1S |
7,420-515,000 | - | * |
| lead | WIMW5D WIMW6D WIMW8S |
6-1,900 | 15 | MCL |
| magnesium | WIMW8D WIMW5S |
23,900-107,000 | - | * |
| mercury | WIMW10D | <1 | - | * |
| nickel | WIMW5S WIMW1S |
44-505 | 200 | RMEG |
| potassium | WIMW1D WIMW5D |
5,340-83,900 | - | * |
| silver | WIMW8S | 11 | 50 | RMEG |
| sodium | WIMW1D WIMW6D WIMW5D |
12,600-231,000 | 20,000 | MEMO |
| vanadium | WIMW10S WIMW1S |
98-592 | 30 | EMEG |
| zinc | WIMW8D WIMW8S |
60-3,600 | 3,000 | RMEG |
| (Round II) | ||||
| antimony | WIMW4I | 65 | 4 | RMEG |
| cyanide | WIMW4I | 15 | 200 | RMEG |
| potassium | WIMW3D WIMW6I WIMW4I |
2,840-96,200 | - | * |
| sodium | WIMW3D WIMW6I WIMW4I |
466-292,000 | 20,000 | MEMO |
| zinc | WIMW3D WIMW6I WIMW4I |
20-7,070 | 3,000 | RMEG |
Off-Site Storm Water Runoff and Leachate Sample Results, May 1990.
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| DISSOLVED INORGANIC CHEMICALS | ||||
| arsenic | WISW51L | 11 | 3 | EMEG |
| barium | WISW31L WISW51L |
273-427 | 700 | RMEG |
| calcium | WISW21L WISW31L |
61,500-81,600 | - | * |
| iron | WISW21L WISW51L |
299-5,300 | - | * |
| magnesium | WISW21L WISW41L |
29,900-134,000 | - | * |
| manganese | WISW21L WISW31L |
182-659 | 50 | RMEG |
| nickel | WISW31L WISW41L |
87-120 | 200 | RMEG |
| potassium | WISW21L WISW51L |
9,790-139,000 | - | * |
| sodium | WISW21L WISW51L |
85,100-750,000 | 20,000 | MEMO |
| TOTAL INORGANIC CHEMICALS | ||||
| aluminum | WISW21L WISW51L |
232-281 | - | * |
| arsenic | WISW51L | 25 | 3 | EMEG |
| barium | WISW31L WISW51L |
382-821 | 700 | RMEG |
| calcium | WISW21L WISW31L |
61,900-77,500 | - | * |
| copper | WISW31L | 82 | 1,300 | MCL |
| cyanide | WISW31L WISW41L |
23-162 | 200 | RMEG |
| iron | WISW41L WISW51L |
5,720-32,000 | - | * |
| lead | WISW41L WISW31L |
4-8 | 15 | MCL |
| magnesium | WISW21L WISW41L |
28,600-125,000 | - | * |
| manganese | WISW21L WISW31L |
211-687 | 50 | RMEG |
| nickel | WISW41L WISW51L |
101-114 | 200 | RMEG |
| potassium | WISW21L WISW51L |
9,670-134,000 | - | * |
| sodium | WISW21L WISW51L |
81,300-706,000 | 20,000 | MEMO |
| zinc | WISW41L WISW31L |
106-482 | 3,000 | RMEG |
Off-Site Surface Water Sample Results, June 1987
| Chemical | Cross Section |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| aluminum | 2 & 1 | 55-434 | - | * |
| arsenic | 2 | 4 | 3 | EMEG |
| barium | 2 & 8 | 56-72 | 700 | RMEG |
| bis(2-ethylhexyl)phthalate | 8-7 | 4-7 | 3 | CREG |
| calcium | 1 & 8 | 64,300-74,000 | - | * |
| chromium | 1 | 44 | 100 | LTHA |
| copper | 2 & 1 | 9-15 | 1,300 | MCL |
| cyanide | 1 & 2 | 21 | 200 | RMEG |
| iron | 1 | 1,390 | - | * |
| lead | 2 & 3 | 3-63 | 15 | MCL |
| magnesium | 1 & 8 | 19,700-23,400 | - | * |
| manganese | 8 & 1 | 49-141 | 50 | RMEG |
| mercury | 7 & 1 | <1-1 | - | * |
| nickel | 1 & 2 | 32 | 200 | RMEG |
| sodium | 8 & 2 | 14,550-26,300 | 20,000 | MEMO |
| zinc | 7 & 1 | 15-68 | 3,000 | RMEG |
Off-Site Stream Sediment Organic Chemicals Sample Results, June 1987
| Chemical | Cross Section |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| acenaphthene | 3 & 1 | 77-92 | 100,000 | RMEG |
| anthracene | 2 | 71 | 600,000 | RMEG |
| benzo(a)anthracene | 1 | 210 | - | * |
| benzo(a)pyrene | 3 & 1 | 110-400 | - | * |
| benzo(k)fluoranthene | 1 | 1,000 | - | * |
| benzoic acid | 3 | 3,500 | 8,000 | RMEG |
| bis(2-ethylhexyl)phthalate | 3 & 1 | 1,400-11,000 | 50,000 | CREG |
| 2-butanone | 1 & 2 | 10-17 | - | * |
| butylbenzylphthalate | 1 | 180 | 400,000 | RMEG |
| chloroform | 6 | 2 | 20,000 | EMEG |
| chrysene | 3 & 1 | 160-540 | - | * |
| 4,4'-DDD | 1 | 65 | 20,000 | EMEG |
| fluoranthene | 1 | 940 | 80,000 | RMEG |
| fluorene | 2 & 1 | 64-220 | 80,000 | RMEG |
| 2-methylnaphthalene | 3 & 1 | 100-540 | - | * |
| 2-methylphenol | 1 | 100 | - | * |
| 4-methylphenol | 2 | 1,800 | 5,000 | OSHA |
| naphthalene | 3 & 1 | 150-400 | - | * |
| phenanthrene | 1 | 740 | - | * |
| phenol | 2 & 3 | 160-1,200 | 1,000,000 | RMEG |
| pyrene | 1 | 900 | 60,000 | RMEG |
| toluene | 1 | 250 | 400,000 | RMEG |
Off-Site Stream Sediment Inorganic Chemical Sample Results, June 1987
| Chemical | Cross Section | Concentration Range - ppm |
Comparison Value | |
| ppm | Source | |||
| aluminum | 2 & 1 | 2,430-6,260 | - | * |
| arsenic | 2 & 5 | 3 - 10 | 0.6 | EMEG |
| barium | 6 & 1 | 31 - 257 | 100 | RMEG |
| beryllium | 1 | 1 | 0.2 | CREG |
| cadmium | 3 & 1 | 7-47 | 1 | EMEG |
| calcium | 6 | 2,700 | - | * |
| chromium | 7 & 1 | 15-137 | 10 | RMEG |
| copper | 6 & 1 | 20-201 | - | * |
| cyanide | 2 & 1 | 4-19 | 40 | RMEG |
| iron | 2 & 7 | 9,870-29,300 | - | * |
| lead | 5 & 1 | 28-72 | - | * |
| magnesium | 2 & 1 | 5,030-11,700 | - | * |
| manganese | 2 & 7 | 337-1,500 | 10 | RMEG |
| mercury | 1 & 2 | <1 | - | * |
| nickel | 6 & 1 | 14-37 | 40 | RMEG |
| vanadium | 2 | 5 | 6 | EMEG |
| zinc | 6 & 1 | 95-974 | 600 | RMEG |
Off-Site Groundwater Sample Results, January 1991 (Rounds I & II)
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| benzoic acid | WIMW6I | 11 | 40,000 | RMEG |
| bis(2-ethylhexyl)phthalate | WIMW13S | 5 | 3 | CREG |
| butylbenzyl phthalate | WIMW13S | 5 | 2,000 | RMEG |
Off-Site Groundwater Sample Results for Dissolved Inorganic Chemicals (Rounds I & II)
May 1990/January 1991.
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| arsenic | MW13D MW14D |
3-4 | 3 | EMEG |
| barium | MW13S MW14I |
17-88 | 700 | RMEG |
| calcium | MW13D MW14I |
33,400-71,300 | - | * |
| iron | MW13D MW13S |
23-100 | - | * |
| magnesium | MW13D MW14D |
9,200-25,700 | - | * |
| manganese | MW13D MW14I |
11-285 | 50 | RMEG |
| potassium | WIMW13D WIMW4I |
933-3,470 | - | * |
| sodium | MW13S MW6D |
12,400-37,960 | 20,000 | MEMO |
| zinc | WIMW13S | 4 | 3,000 | RMEG |
Off-Site Groundwater Sample Results for Total Inorganic Chemicals (Rounds I & II) May 1990/January 1991
| Chemical | Sample No. |
Concentration Range - ppb |
Comparison Value | |
| ppb | Source | |||
| aluminum | MW6D MW13S |
3,320-277,000 | - | * |
| arsenic | MW14D MW13S |
25-466 | 3 | EMEG |
| barium | MW13D MW13S |
102-1,570 | 700 | RMEG |
| beryllium | MW13S | 16 | 0.008 | CREG |
| cadmium | MW6D MW13S |
7-9 | 7 | EMEG |
| calcium | MW13S MW14D |
68,900-402,000 | - | * |
| chromium | MW13D MW13S |
13-507 | 100 | LTHA |
| cobalt | MW6I MW13S |
15-295 | - | * |
| copper | MW14I MW13S |
92-539 | 1,300 | MCL |
| iron | MW6D MW13S |
7,980-900,000 | - | * |
| lead | MW13S | 6-569 | 15 | MCL |
| magnesium | MW6I MW14D |
27,500-162,000 | - | * |
| manganese | MW6D MW13S WIMW1SGW |
290-25,000 | 50 | RMEG |
| mercury | MW13S | 1 | - | * |
| nickel | MW13D MW13S |
13-553 | 200 | RMEG |
| potassium | MW6I MW13S |
570-34,400 | - | * |
| sodium | MW13S MW14I |
6,220-32,300 | 20,000 | MEMO |
| vanadium | MW13D MW13S |
23-868 | 30 | EMEG |
| zinc | MW6D MW13S |
113-2,220 | 3,000 | RMEG |
COMMENTS & RESPONSES
| 1. | COMMENT | If you know that this site is not the cause of cancer increase,
please identify what the cause for our increased cancer rate. |
|
RESPONSE |
The data that we reviewed did not indicate that individuals
exposed at the estimated exposure doses would experience any significant
increase in cancer. However, please recall that we identified data gaps
(page 37). Although we are concerned about the health of the community,
it is important to note that the focus and purpose of this document is to
determine the adverse health effects caused by this site on the community.
|
|
|
2. |
COMMENT | We urge you to find resources to continue the monitoring of
fish tissues. |
|
RESPONSE |
We agree that there is the continued need for fish tissue
sampling in all Indiana rivers and streams; however, this request is beyond
the scope and purpose of this document. |
|
|
3. |
COMMENT | The residence within 100 yards of the site should
be included in the background section on page 2. |
| RESPONSE | Wherever appropriate, this residence has been added to the
document. |
|
|
4. |
COMMENT | We request a copy of the Court Order (Injunction) in 1993
which closed the site. |
|
RESPONSE |
We do not have a copy of the Court Order. As this order was
probably initiated by IDEM, I would suggest contacting the IDEM to obtain
a copy. |
|
|
5. |
COMMENT | Why were no new samples required by ATSDR to confirm the allegations
of illegal dumping occurring in 1988? |
|
RESPONSE |
The recommendations made by ATSDR included collecting further
sampling information which would pass acceptable quality control/quality
assurance procedures, and obtaining additional information on site-related
chemicals and any chemicals released off-site. Please see page 4 paragraph
1. |
|
|
6. |
COMMENT | Why were no samples taken of the drums seen on-site? |
|
RESPONSE |
The drums that were seen throughout the site were all empty.
The drums seen in the old office building contained decontamination water
from drilling/sampling. In the event that we would like to know the contents
of a drum or barrel, we would request either IDEM or EPA to sample for us.
We do not perform any environmental sampling. |
|
|
7. |
COMMENT | Samples of the oil-type sheen observed on Trail Creek should
be taken, and the storm sewer must be replaced. |
|
RESPONSE |
The sampling of this media would not change the conclusions
and recommendations of this Public Health Assessment. There is a fish advisory
on Trail Creek, and we recommend that necessary actions be taken to prevent
local population exposure to site-related contaminants (see page 38). |
|
|
8. |
COMMENT | The results of the door-to-door survey by the Minority Health
Coalition of LaPorte County should be included. Also, the well at International
Friendship Gardens should be tested. |
|
RESPONSE |
We will request this information from the organization.
However, it will not be a part of this document as the public comment period
for this document is over. Please see page 7 regarding the well at International
Friendship Gardens. |
|
|
9. |
COMMENT | The odd childhood cancers reported during the last public
meeting should be investigated. |
|
RESPONSE |
A health study is planned for this community to investigate
adverse health effects, including odd childhood cancers. |
|
| 10. | COMMENT | What about the Indiana Cancer Registry? |
|
RESPONSE |
Data from the Indiana Cancer Registry was reviewed. The results
of this review are contained on page 31. |
|
|
11. |
COMMENT | Where did you get the off-site comparisons? |
|
RESPONSE |
The location of the off-site sample data is noted in the document.
(Please see page 15, OFF-SITE CONTAMINATION.) |
|
| 12. | COMMENT | Please identify the companies described on page 9, especially
the one that showed emissions of either chromium in groundwater or nickel
compounds in the air. |
|
RESPONSE |
Please contact your local EPA office and request the latest
publication of their Toxic Release Inventory. The specific companies are
listed in this publication. |
|
|
13. |
COMMENT | Please identify the scientific basis for identifying "chemicals
of concern". |
|
RESPONSE |
This is discussed on page 8 of the document. |
|
|
14. |
COMMENT | Please identify the suspected source of dibenzofuran. |
|
RESPONSE |
That is beyond the scope of this document. We have identified
that the chemical was found in the on-site well; its source is unknown at
this time. |
|
|
16. |
COMMENT | Why were only two rounds of sampling taken? |
|
RESPONSE |
The ISDH does not determine the number of rounds of sampling
that other agencies performs at a site. This document only reports the information
that was available to us at the time of the writing of this document. We
suggest referring this comment to the EPA. |
|
|
17. |
COMMENT | If intermediate wells were installed after Round I, how were
21 SVOCs detected during Rounds I and II? |
|
RESPONSE |
The information was reviewed and appropriate changes were
made to the document. |
|
|
18. |
COMMENT | Are all organic chemicals of concern on page 14? |
|
RESPONSE |
Please see the first paragraph under Deep Wells. |
|
|
19. |
COMMENT | Your description of detection of no chemicals at levels of
concern in storm water and leachate contradicts all previous site descriptions,
why? Please provide us with your analysis of these values with Indiana Water
Quality Standards. |
|
RESPONSE |
The data was reviewed and appropriate changes were made to
the document. Comparison values are provided to us by the ATSDR. These values
are not compared to the Indiana Water Quality Standards. We select contaminants
of concern based on comparative analyses with health guidelines, multi-media
exposures, interactive effects, and community health concerns. |
|
|
21. |
COMMENT | We understand that there were problems with the original sediment
samples as part of the RI/FS test of the Confined Disposal Facility. Please
explain why some of the samples were unacceptable. |
|
RESPONSE |
It is our understanding that there were some sediment samples
taken by IDEM prior to the Remedial Investigation (RI); therefore, it would
not have been included in the RI. This information will be requested and
evaluated. Please note, however, that the results from this data would more
than likely not change the conclusions and recommendations of this document
as sediment is already considered a completed exposure pathway for individuals
who eat fish taken from Trail Creek and those who participate in recreational
activities at Trail Creek. |
|
|
22. |
COMMENT |
Since deep groundwater flow is to Lake Michigan, the lead
found in the deep well may be from the site. |
|
RESPONSE |
This comment was reviewed and appropriate changes were made
to the document. |
|
|
23. |
COMMENT | Please include the test results for lead. This information
should be included along with the other chemicals identified in fish tissue
samples from Trail Creek. |
|
RESPONSE |
This information has been reviewed and appropriate changes
made. |
|
|
24. |
COMMENT | There should be a discussion of bioaccumulation as an exposure route. |
|
RESPONSE |
In determining exposures, bioaccumulation was taken into consideration.
|
|
|
25. |
COMMENT | All fish tissue was sampled for chlordane, dieldrin, lead,
DDT, DDE and other compounds; this information should be included. |
|
RESPONSE |
This information was reviewed and the relevant section in
the document was re-written. |
|
|
26. |
COMMENT | Air sampling should be done. |
|
RESPONSE |
We agree with this comment. (Please see the Conclusions section
of the Public Health Assessment.) |
|
|
27. |
COMMENT | How can your calculations include a child drinking 1 liter
per day for 43 years? That sure would be an old child. |
|
RESPONSE |
The narrative was reviewed, and appropriate changes were made
to the document. |
|
|
28. |
COMMENT | Please identify the areas where background soil has 10,000
- 300,000 ppb lead. |
|
RESPONSE |
These numbers were obtained from the United States Geological
Survey Table. This table gives mean concentrations, deviations, and ranges
of elements in samples of soil in the conterminous United States. |
|
|
29. |
COMMENT | Please review Dr. Rotkin's Cancer study on LaPorte County,
especially the soft tissue, rare cancers he identified. |
|
RESPONSE |
This study was reviewed as stated under the Community Health Concerns Evaluation section of the document. |
|
|
30. |
COMMENT | The information from the public relating to childhood cancer
should be included. |
|
RESPONSE |
This most valuable information will be added to the document
and will be used in the Planned Community Health Study. |
|
|
31. |
COMMENT | It should be documented that heptachlor was detected by the
FIT in both the on-site well and the raw water intake for Michigan City.
|
|
RESPONSE |
The FIT report of December 14, 1983, indicates that the results
of 2 weeks of samples showed the presence of heptachlor above EPA drinking
water standards. It also indicates that this chemical is not attributed
to the industrial work of this site because it is an insecticide widely
used by midwest farmers. |
|
|
32. |
COMMENT | Please provide us with the review of Dr. Rotkin's report by
experts in the cancer field. |
|
RESPONSE |
A copy of the review will be provided. |
|
|
33. |
COMMENT | Please include an estimate for exposure to people eating produce from gardens. |
|
RESPONSE |
One of the data gaps mentioned in the Public Health Assessment
is the lack of off-site surface soil samples. Estimated ingestion exposure
doses cannot be determined without this information. |
|
|
34. |
COMMENT |
Please put signs along the waterway warning people of the fish consumption
advisory. |
|
RESPONSE |
Although this may appear to be the solution to warning the
community about the fish in Trail Creek, there are some practical and economical
reasons why this is not done. We have found that signs along waterways prove
more to be targets for vandalism than anything else. We do not have the
funds to purchase warning signs, nor do we have the staff to install and
maintain any warning signs. Individuals are warned, however, through the
fish advisory which is given to each person getting their license to fish. |
|
|
35. |
COMMENT | Please let drinking water well users know about this issue. |
|
RESPONSE |
It is our understanding that there are no private wells within
a 1-mile radius that are being used for drinking water. We will, however,
contact all owners of private wells and inform them of the potential dangers
of using their wells for drinking purposes. |
|
|
36. |
COMMENT | The Indiana State Department of Health must support the cleanup
alternative most protective of public health and the environment. |
|
RESPONSE |
Our role is not one of risk management, but of protecting
human health. It would be inappropriate for this agency to support one cleanup
alternative over another. The role of the Environmental Epidemiology Section
of the Indiana State Department of Health is to make recommendations to
the appropriate agencies to ensure that the health of a community is not
adversely affected by toxic chemicals emitted, spilled, or naturally occurring
in the environment. |