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PRELIMINARY PUBLIC HEALTH ASSESSMENT

MONARCH TILE, INC., FLORENCE DIVISION
LAUDERDALE COUNTY, ALABAMA



APPENDIX A


Figure 1. Area Location Map


Figure 2. City Location Map


Figure 3. Site Location Map


Figure 4. Sediment Sampling Location Map


Figure 5. Drainage Patterns



APPENDIX B

Contaminants of Concern Tables

Table 1. Contaminants of Concern in On-site Surface Water

Contaminant
Levels
(ppb)
Reference
Comparison Value
ppb Source
Arsenic 5
5
0.02 CREG
Barium 7,210
5
2000 Adult RMEG
Chromium 328
200 Adult RMEG
Lead 1,060
5


Nickel 1,920
5
700 Adult RMEG



Table 2. Contaminants of Concern in On-site Sediment

Contaminant
Levels
(ppm)
Reference
Comparison Value
ppm Source
Arsenic 14.2
3,4
0.4 CREG
Lead 994.2
3,4





Table 3. Contaminants of Concern in Off-site Sediment

Contaminant
Levels
(ppm)
Reference Comparison Value
ppm Source
Arsenic 11.3 4 0.4 CREG
Barium 186.4 4 100 RMEG
Pica Child
Cadmium 19.8 4 1.0 Chronic EMEG
Pica Child
Chromium 29.7 4 10.0 Chronic EMEG
Pica Child
Lead 1,328.6 4

Nickel 69.4 4 40 RMEG
Zinc 10,410.5 4 600 RMEG
Pica Child



APPENDIX C

Pathways Tables

Table 4. Potential Exposure Pathways

Pathway
Exposure Pathway Elements
Time
Source
Environment
Point of
Route
Exposure
Sediment Monarch sediment Southern &
Northern
drainage
pathways
ingestion,
inhalation,
dermal
children past,
present,
future
Soil Monarch soil On-site,
residences
near plant
ingestion,
inhalation,
dermal
workers,
adults,
children
past,
present,
future
Ambient Air Monarch air On-site,
residences
near plant
inhalation workers,
adults,
children
past



APPENDIX D

RESPONSE TO PUBLIC COMMENTS

The following comments were offered by Walston, Stabler, Wells, Anderson & Bains on behalf of Monarch Tile, Inc.:

  1. Cover sheets; P. iii; P. 1, 1st ¶, 1st line; P. 2, Part A, 1st ¶; P. 15, 3rd ¶; and P. 16, last ¶: substitute "Rickwood Road/Cox Creek Site: for "Monarch Tile, Inc." where the name of the CERCLA site which is the subject of the proposed NPL listing is intended. Where the plant facility is meant, refer specifically to it. Otherwise delete all references to "Monarch Tile, Inc." (See text of letter below re name change.)

    Response: At this time, EPA has not decided on a new name for this site. ATSDR will track this site by the name of Monarch Tile, Inc.; therefore, we retain the use of "Monarch Tile, Inc." for this site.

  2. P. 1, ¶1, 5th line: delete "lead, barium and cadmium." See affidavit of Henry Stamper, attached as Exhibit 2 to the Comments submitted on July 9, 1993 to the Environmental Protection Agency Office of Emergency and Remedial Response (hereafter "Comments"). Mr. Stamper stated the "the facility did not use barium, cadmium or lead as a colorant." An accurate statement would be: "Former operations included the use of glaze materials containing compounds of zinc, lead, and barium." As Mr. Stamper reported, to his knowledge the facility did not use cadmium-based compounds in its processes.

    Response: As suggested, the statement was changed to read, "Former operations included the use of glaze materials containing compounds of zinc, lead, and barium." Regardless of the origin of the compound, cadmium is an environmental contaminant of concern both on and off site and as such, was evaluated in this report.

  3. P. 1, ¶1, 8th line: replace the first "1980" with 1976. In 1976, all discharge from the settling basins was routed to the city sewer pursuant to a State Indirect Discharge permit issued by the Alabama Department of Environmental Management.

    Response: The suggested change was made in the document.

  4. P. 1, ¶1, 8th line, last sentence: replace "1980" with "1979." See Affidavit of Henry Stamper, Comments, Exhibit 2. After 1979, use of barium carbonate was discontinued. After 1979, use of lead compounds stopped.

    Response: The suggested change was made in the document.

  5. P. 2, part A, 3rd ¶;, last line: replace "1989" with "1988."

    Response: The suggested change was made in the document.

  6. P. 2, Part A, last ¶, 6th line: replace "eastern drainage ditch" with "east drainage channel" to be consistent with Figure 3.

    Response: The suggested change was made throughout the document.

  7. P. 3, Part B, 3rd bullet, 1st line: insert after "ditch," "which was dry and overgrown at the time of the visit."

    Response: The inspection of the area outside the facility property behind Plant 1 was not sufficiently detailed to justify a determination that the ditch was "dry and overgrown" along its entire length. Therefore, this change was not made in the document.

  8. P. 3, Part B, 3rd bullet, 5th line: add "or the creek" to the end of the sentence.

    Response: The item denoted by the 3rd bullet refers only to the ditch, not the creek; therefore, this change was not made in the document.

  9. P. 4, last line, and P. 5, 1st line: delete "either southwest or northwest" and insert "southwest." See E&E, p. 2-7 (6).

    Response: The suggested change was made in the document.

  10. P. 5, first full ¶, 1st line: replace "drainage ditch" with "facility."

    Response: The suggested change was made in the document.

  11. P. 5, first full ¶, 4th line: insert "designated as" before "suitable."

    Response: The suggested change was made in the document.

  12. Pp. 6-9, Environmental Contamination and Other Hazards (this comment applies to this entire section with respect to contaminants of concern, and particularly to the listing of on-site and off-site contaminants of concern on P. 6). Based on background concentrations reported in the Background Sampling Analysis Report by ENSR Consulting and Engineering, August 1994, submitted to EPA Region IV, contaminants of concern at the site should be limited to barium, lead, nickel and zinc. Based on the Hazard Ranking System Guidance Manual, any contaminant within three times background concentration would not be considered as a release. Section 5.1, p. 58. Since cadmium was never used at the site and since cadmium concentrations measured at the site are within three times established background, Monarch believes it should not be listed as a contaminant of concern. Other metals (except lead, nickel, barium, and zinc) were within background concentrations reported at the site. See Background Sampling Analysis Report, Tables 6-1 and 6-2. A copy of this report is included.

    Response: ATSDR's protocol for PHAs requires evaluation of all contaminants of concern at a site by comparing them to established comparison values. All available environmental data are to be included. Any substances present at concentrations above the comparison values are classified as contaminants of concern.

  13. P. 8: add available information on "Offsite Surface Water," as follows:

    "As reported in ENSR's August 1994 report submitted to EPA, Stormwater Runoff Sampling Report, metals analyses conducted on runoff samples collected from offsite ditches during a rain event indicate that metals did not exceed MCLs, with the exception of two samples which were barely above the MCLs. ENSR conducted stormwater runoff sampling in both the north and south ditches on May 26, 1994, during a significant rain event. Samples were analyzed for arsenic, barium, cadmium, chromium, lead, nickel and zinc. All tested parameters in the north ditch were below drinking water MCLs, with the exception of one sample which tested at 10 ppb lead (4 ppb above the MCL). That sample, 5/26-W-1, was collected from the north ditch where it discharges into Cox Creek, and may reflect other potential contaminant sources. All tested parameters in the south ditch were below MCLs with the exception of the lead concentration in sample 5/26-W-3, which was only 2 ppb over the MCL."

    A copy of ENSR's August 1994 report is included.

    Response: The above information does not substantially change the findings or conclusions of the document. It reinforces the information reported in Eliminated Pathways, Public Water Supply and Biota Pathways, p 11. However, the finding of lead in the surface water runoff strengthens the conclusion that the sediment pathway is a potential exposure pathway in that lead is migrating off site.

  14. P. 8, Onsite Groundwater: E&E installed five groundwater monitoring wells in 1987. Groundwater analysis of samples from the wells in 1987 indicated that metals concentrations were below MCLs. (6)

    Response: Comment noted.

  15. P. 9, Sediment, ¶ 1: Monarch contends that contaminants of concern should be limited to barium, lead and zinc on the south ditch, and to barium, lead, nickel and zinc on the north ditch sediments. Refer to the Background Sampling Analysis Report. Cadmium should not be included, as discussed above (item 12).

    Response: See response to Comment 12.

  16. P. 11, Biota Pathway: Monarch concurs with the conclusion that sediments are highly unlikely to migrate in sufficient quantity to pose a health risk, and concurs that sediment concentrations are unlikely to pose any health threat. ADPH could cite as supporting data ENSR's recent study of watershed dilution factors, which supports ADPH's conclusion concerning the migration of sediments from the ditches to the respective creeks. ENSR calculates that flow in the north ditch is diluted by a factor of over 100 when it reaches Cox Creek (ratio of north ditch to Cox Creek is 0.009, or 1 to 111.1); similarly, flow in the south ditch is diluted by a factor of almost seven (ratio of south ditch to Sweetwater Creek is 0.147, or 1 to 6.8). Engineering Evaluation and Cost Analysis Work Plan, Appendix A, July 1994, ENSR Consulting and Engineering. A copy of Appendix A is included.

    Response: See response to Comment 12.

  17. P. 12, 1st sentence: Monarch objects to this statement. Substitute: "The monitoring wells around the settling basins indicate no leaching of the material from the settling basins into adjacent groundwater." Analytical results of groundwater samples obtained from upgradient wells were the same or higher than results of downgradient wells in all sampling events. Therefore, there is no basis to indicate any leaching of material from the settling basins into groundwater. Furthermore, the electromagnetic conductivity study conducted by E&E in 1987 indicated there was no leaching of materials from the settling basins. (6)

    Response: The sentence has been changed to read, "The monitoring wells around the settlement basins indicate very little if any leaching of the material into the adjacent groundwater."

  18. P. 12, Section A: The Toxicological Evaluation should only address contaminants of concern, consistent with item 12 above, which would limit the metals to barium, nickel, lead and zinc.

    Response: See response to Comment 12.

  19. P. 12, Section A, 2nd ¶: Monarch contends the Comparison Values contained in Appendix B to the Public Health Assessment are excessively conservative based on the chemical structures and physical properties of the compounds used at the facility (fritted and calcined metals). As indicated by the Comments submitted by Monarch on the proposed NPL listing, metals were used at the site only in a calcined and/or fritted form. Metals in such forms exhibit far lower bioavailability, and are therefore less toxic, than elemental metals or metal oxides. Refer to Comments, Section F.1 and throughout, and Exhibit 1 to the Comments (ENSR Consulting), Comment 15, Comment 18, Comment 21, and references (including references in the Comments) cited therein. With respect to Minimal Risk Levels, metals at the site are not found in the forms for which the MRLs were established. Furthermore, the Comparison Values contained in Appendix B to the Public Health Assessment are for the elemental forms of the metals listed.

    Response: ATSDR's protocol requires the use of these comparison values.

  20. P. 15, 2nd ¶, 3rd line: In 1973, Monarch did not purchase the facility, but leased it.

    Response: The suggested change was made in the document.

  21. P. 15, 2nd ¶, 4th line: Monarch ceased using such compounds in 1979.

    Response: The suggested change was made in the document.

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