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PUBLIC HEALTH ASSESSMENT

WASTE INC. LANDFILL
MICHIGAN CITY, LA PORTE COUNTY, INDIANA



APPENDICES

APPENDIX A


Figure 1. Site Location Map


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



APPENDIX B

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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


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
* No comparison value available


APPENDIX C

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.

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