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PUBLIC HEALTH ASSESSMENT

McCORMICK & BAXTER CREOSOTING COMPANY (PORTLAND)
PORTLAND, MULTNOMAH COUNTY, OREGON


APPENDIX A--SITE MAPS

LIST OF FIGURES

Figure 1. Site Location Map.
Figure 1 Site Location Map

Figure 2. Principal Site Features.
Figure 2 Principal Site Features





APPENDIX B--CONTAMINANT AND PATHWAY TABLES

LIST OF TABLES

Table 1
Table 2
Table 3
Table 4
Table 5
Table 6
Table 7
Table 8
Table 9
Table 10
Contaminants--On-Site Surface Soils
Contaminants--On-Site Subsurface Soils
Contaminants--On-Site Groundwater
Contaminants--On-Site NAPL (Below Ground)
Contaminants--On-Site Storm Water (Unfiltered)
Contaminants--Off-Site Surface Soils
Contaminants--Off-Site Sediment
Contaminants--Off-Site: Crayfish, Large Scale Sucker
Summary--Completed Pathways and Associated Health-Related Information
Summary--Potential Pathways and Associated Health-Related Information

ACRONYMS, ABBREVIATIONS

ND
ppm
ppb
E
M
LM
L
EMEG
CREG
RMEG
PMCL
LTHA
AL
NAPL
PCDD/PCDF
not detected
parts per million
parts per billion
estimated value
mean value
might be less than the stated mean value
less than the stated value
Environmental Media Evaluation Guide
Cancer Risk Evaluation Guide for 1x10-6 excess cancer risk
Reference Dose Media Evaluation Guide
Proposed Maximum Contaminant Level
Lifetime Health Advisory
Action Level
nonaqueous-phase liquids
polychlorinated dibenzodioxins and polychlorinated dibenzofurans,presented as 2,3,7,8-tetrachlorodibenzo-p-dioxin toxicequivalents. See discussion under Environmental Contamination and Other Hazards section.

Table 1 Contaminants--On-Site Surface Soils

Contaminants Maximum
Concentration
(ppm)
Sample
(year)
Comparison Values
ppm Source
acenaphthylene 50 1990 none
benz(a)anthracene 420E 1990 none
benzo(a)pyrene 210 1990 0.1 CREG
benzo(e)pyrene 620E 1990 none
benzo(ghi)perylene 66 1990 none
benzofluoranthenes 1,000E 1990 none
carbazole 1,200E 1990 none
chrysene 1,900E 1990 none
dibenz(a,h)anthracene 22 1990 none
dibenzofuran 290E 1990 none
indeno(1,2,3-cd)pyrene 56 1990 none
2-methylnaphthalene 140 1990 none
naphthalene 42 1990 none
PCDD/PCDF
(toxic equivalents *)
0.38 1990 0.0007 CREG
pentachlorophenol 4,800E 1990 6 CREG
phenanthrene 4,900 1990 none
2,3,4,5-tetrachlorophenol 65E 1990 none
arsenic 5,100 1990 0.4 CREG
beryllium 0.58 1990 0.2 CREG
lead 150 1990 none
Ref. (1)



Table 2 Contaminants--On-Site Subsurface Soils

Contaminants Maximum
Concentration
(ppm)
Sample
(year)
Comparison Values
ppm Source
acenaphthylene 13 1992 none
benz(a)anthracene 570E 1992 none
benzo(a)pyrene 170 1992 0.1 CREG
benzo(e)pyrene 150 1992 none
benzo(ghi)perylene 30 1992 none
benzofluoranthenes 460 1992 none
carbazole 460E 1992 none
chrysene 770E 1992 none
dibenz(a,h)anthracene 22 1992 none
indeno(1,2,3-cd)pyrene 64 1992 none
naphthalene 23,000 1992 none
PCDD/PCDF (toxic equiv-alents) 0.037 1992 0.0007 CREG
pentachlorophenol 5,200E 1992 6 CREG
phenanthrene 3,600 1992 none
arsenic 61,000 1992 0.4 CREG
copper 19,000 1992 none
Ref. (1)



Table 3 Contaminants--On-Site Groundwater

Contaminants Maximum
Concentration
(ppb)
Sample
(year)
Comparison Values
ppb Source
acenaphthene 2,000,000 1991 600 RMEG
acenaphthylene 150,000 1991 none
anthracene 620,000 1991 3,000 RMEG
benz(a)anthracene 240,000 1991 0.1 PMCL
benzo(a)pyrene 100,000 1991 0.005 CREG
benzo(e)pyrene 5,300 1991 none
benzo(ghi)perylene 20,000 1991 none
benzofluoranthenes 160,000 1991 0.2 PMCL
chrysene 190,000 1991 none
dibenz(a,h)anthracene 17,000 1991 0.3 PMCL
fluorene 1,800,000 1991 400 RMEG
fluoranthene 2,000,000 1991 400 RMEG
indeno(1,2,3-cd)pyrene 5,200 1991 0.4 PMCL
naphthalene 2,400,000 1991 20 LTHA
PCDD/PCDF (toxic equivalents) 0.20 1991 0.00001 CREG
pentachlorophenol 1,200,000 1991 0.3 CREG
phenanthrene 3,900,000 1991 none
pyrene 1,100,000 1991 300 RMEG
2,3,4,5-tetrachlorophenol 190E 1991 none
arsenic 9,000 1991 3 EMEG
chromium 12,000 1991 10,000 RMEG
chromium +6 120 1991 50 RMEG
copper 5,400 1991 1,300 AL
zinc 260,000 1991 3,000 RMEG
Ref. (1)



Table 4 Contaminants--On-Site NAPL Below Ground

Contaminants Maximum
Concentration
(ppb)
Sample
(year)
Comparison Values
ppb Source
acenapthene 30,000,000 1991 600 RMEG
acenaphthylene 490,000 1991 none
anthracene 820,000 1991 none
benz(a)anthracene 610,000 1991 0.1 PMCL
benzofluoranthenes 170,000 1991 0.2 PMCL
carbazole 160,000 1991 none
fluoranthene 32,000,000 1991 400 RMEG
fluorene 36,000,000 1991 400 RMEG
naphthalene 90,000,000 1991 20 LTHA
pentachlorophenol 830,000 1991 0.3 CREG
phenanthrene 88,000,000 1991 none
pyrene 30,000,000 1991 300 RMEG
Ref. (1)



Table 5 Contaminants--On-Site Storm Water (Unfiltered)

Contaminants Maximum
Concentration
(ppb)
Sample
(year)
Comparison Values
ppb Source
PCDD/PCDF (toxic equivalents) 0.024 1991 0.00001 CREG
pentachlorophenol 1,700 1991 0.3 CREG
tetrachlorophenols 68E 1991 none
arsenic 7,600M 1991 3 EMEG
copper 15,000M 1991 1,300 AL
zinc 8,200M 1991 3,000 RMEG
Ref. (1)



Table 6 Contaminants--Off-Site Surface Soils

Contaminants Maximum
Concentration
(ppm)
Sample
(year)
Comparison Values
ppm Source
benz(a)anthracene A- ND
B- 0.21E
C- 0.055E
D- 0.33
E- ND
1991 none
benzo(a)pyrene A- ND
B- 0.28
C- 0.30E
D- 0.26
E- ND
1991 0.1 CREG
benzo(e)pyrene A- ND
B- 0.32
C- 0.21E
D- 0.70
E- ND
1991 none
benzo(ghi)perylene A- ND
B- 0.24
C- 0.17E
D- 0.26
E- ND
1991 none
benzofluoranthenes A- ND
B- 0.47
C- 0.35E
D- 1.3
E- ND
1991 none
carbazole A- ND
B- 0.022
C- ND
D- 0.052
E- ND
1991 none
chrysene A- ND
B- 0.36
C- 0.31E
D- 1.1
E- ND
1991 none
dibenz(a,h)anthracene A- ND
B- ND
C- ND
D- 0.098
E- ND
1991 none
indeno(1,2,3-cd)pyrene A- ND
B- 0.3
C- 0.20E
D- 0.042
E- ND
1991 none
naphthalene A- 0.056E
B- 0.025
C- 0.11E
D- 0.035
E- ND
1991 none
PCDD/PCDF (toxic equivalents) A- 0.0000081L
B- 0.0005
C- 0.000054L
D- 0.0011
E- 0.000012L
1991 0.000002 EMEG
phenanthrene A- 0.054E
B- 0.16
C- 0.12E
D- 0.27
E- ND
1991 none
arsenic A- 3.4E
B- 11M
C- 6.2
D- 17
E- 2.7E
1991 0.4 CREG
Table 6. Contaminants-Off-Site Surface Soils, notes
A- Samples from residential area beyond top of bluff
B- Samples from access road
C- Samples from adjacent industrial property to the north and from slope of bluff
D- Single sample taken on site beside south property line that might represent conditions off-site in that area.
E- Background sample taken near university
Ref. (1)



Table 7 Contaminants--Off-Site River Sediment

Contaminants Maximum
Concentration
(ppm)
Sample
(year)
Comparison Values
ppm Source
acenaphthylene 17 1990 none
benz(a)anthracene 170 1990 none
benzo(a)pyrene 58 1990 0.1 CREG
benzo(e)pyrene 50 1990 none
benzofluoranthenes 170 1990 none
chrysene 170 1990 none
dibenz(a,h)anthracene 87 1990 none
dibenzofuran 620 1990 none
1,4-dichlorobenzene 0.53 1990 none
2,6-dinitro-toluene 22 1990 none
endrin aldehyde 0.00056E 1990 none
indeno(1,2,3-cd)pyrene 87 1990 none
2-methylnaphthalene 1,300 1990 none
4-methylphenol 0.90M 1990 none
naphthalene 3,500E 1990 none
PCDD/PCDF (toxic equiv-alents) 0.0027 1990 0.00005 EMEG
pentachloro-phenol 7.2 1990 6 CREG
phenanthrene 1,900E 1990 none
arsenic 18E 1990 0.4 CREG
beryllium 0.9 1990 0.2 CREG
lead 44 1990 none
manganese 690 1990 300 RMEG
Ref. (1)



Table 8 Contaminants--Off-Site: Crayfish, Large Scale Sucker

Contaminants Maximum Concentration
(via wet weight)
(organic compounds--ppb)
(metals--ppm)
Comparison
Value
Crayfish Sucker
acenaphthylene 21 57 none
fluorene ND 46 none
naphthalene 57 78M none
PCDD/PCDF
(toxic equiv-alents)
0.0056LM 0.0055LM none
pyrene ND 17E none
arsenic 0.24E ND none
chromium 1.6 0.55 none
copper 13 0.5 none
zinc 15M 7.4 none
Sample date not reported
Ref. (1)



Table 9 Summary--Completed Pathways and Associated Health-Related Information

PATHWAY NAME: Air (on site)
during operations
Air (off site)
during operations
Process chemicals, wastes, soils
(on site) during operations
Soils
(on site)
Soils (off site)
Source: McCormick & Baxter McCormick & Baxter McCormick & Baxter McCormick & Baxter McCormick & Baxter
Medium: Air Air Chemicals, wastes,
soils
Surface soils Surface soils
Exposure Point: On site Off site On site On site Off site
Exposure Route: Inhalation Inhalation Skin contact, ingestion Skin contact,
ingestion
Skin contact,

ingestion

Receptor Population: Workers, visitors,
trespassers
Nearby residents, nearby workers Workers Trespassers Nearby residents, nearby

workers

Exposure Period: Past Past Past Present, future Past, present, future
Number Exposed: Workers--about 50 employed at any one time Unknown About 50 employed at any one time Unknown Unknown
Contaminants at Levels of Public Health Concern: Unknown Unknown Arsenic, pentachlorophenol, dioxins/furans, creosote None None
Exposure Duration: Maximum of 47 years (operating time of site) Maximum of 47 years (operating time of site) Maximum of 47 years (operating time of site)

Potential Health Effects: cannot determine, see Toxicologic Evaluation section discussion cannot determine, see Community Health Concerns Evaluation section discussion various organs: cancer or other disorders, see Toxicologic Evaluation section discussion

Source: McCormick & Baxter, possibly others upstream McCormick & Baxter, possibly others along river McCormick & Baxter, possibly others upstream McCormick & Baxter or others
Medium: Sediment Aquatic biota Surface water Air
Exposure Point: On and off site Off site Off site Off site
Exposure Route: Skin contact Ingestion Skin contact, ingestion Inhalation
Receptor Population: Trespassers, children, former workers Area fishermen Shoreline users, fishermen, water skiers, swimmers Nearby residents, on-site and nearby workers
Exposure Period: Past, present, future for trespassers, children
Past for former workers
Past, present, future Past, present, future Past, present, future
Number Exposed: Workers--about 50 employed at any one time Unknown Unknown Unknown
Contaminants at Levels of Public Health Concern: Unknown None Unknown Unknown
Exposure Duration: Temporary
Temporary Unknown
Potential Health Effects: Unknown
Unknown, none likely Unknown



Table 10 Summary--Potential Pathways and Associated Health-Related Information

PATHWAY NAME: Soils (on site) Air (on site) Sediment (on site and off site)
Source: McCormick & Baxter McCormick & Baxter McCormick & Baxter
Medium: Soils Air Sediment
Exposure Point: On site On site On site, off site
Exposure Route: Ingestion, skin contact, inhalation Inhalation Skin contact
Receptor Population: Remedial workers,
future site users
Site users Shoreline users
Exposure Period: Present, future Future Future
Number Exposed: Unknown Unknown Unknown
Contaminants at Levels of Public Health Concern: Unknown Unknown Unknown
Exposure Duration: Unknown Unknown Temporary
Potential Health Effects: Cannot determine Cannot determine Cannot determine

APPENDIX C-PUBLIC COMMENTS

The McCormick and Baxter public health assessment was available for public review and comment in the local library and local neighborhood association office for a 60-day period ending April 10, 1995. The public comment period was announced in local newspapers. In addition, the public health assessment was sent to one individual. Several sets of commments were received. Specific comments and responses are summarized below. When duplicate comments on specific and particular issues were received, we responded only once.

  1. Comment: Many comments seem to address, in part, elements of the methods that are inherent in our health assessment process (which was described in the Forward of the health assessment document). Thus, as a preliminary to answering specific questions, it seems appropriate to briefly summarize the assessment process.




2A. Comment: It is imperative that, because of recreational uses of the Willamette River and concentrations of pollutants due to multiple sources, the community should be able to assess the full level of pollution as well as the residual and ongoing effects of the McCormick & Baxter contaminants--thus, the assessment should be expanded to include river water quality data.
    Response:

    ATSDR reported in the assessment that there was no river water quality data for the site vicinity. We have no reason to expect that the low exposure doses associated with incidental ingestion during recreational activities would result in definable human health effects. Therefore, river sampling was not recommended, because we believe that the additional information would not substantively enhance our assessment of the site and community effects.

    The document has not been changed.
2B. Comment: People use the river to feed their families. No testing was done of fish other than the large scale sucker and crayfish. It is imperative that, because of recreational uses of the Willamette River and concentrations of pollutants due to multiple sources, the community should be able to assess the full level of pollution as well as the residual and ongoing effects of the McCormick & Baxter contaminants--thus, the assessment should be expanded to include more thorough testing of other species of fish which recreational fishermen might encounter.

    Response:

    ATSDR reported the crayfish and fish data and associated subsistence consumption health consequences. We have no reason to expect that exposure doses associated with eating fish other than those already sampled would result in additional definable health effects. Therefore, we did not recommend sampling for other species because we believe that the additional information would not substantively enhance our assessment of the site and community effects.

    The document has not been changed.
  1. Comment: The assessment states that not enough soil sample information is available to make a representative judgement of the true contamination levels in the off site area. The community and future users of the land surrounding the site should be apprised of the true contamination levels. Further soil sampling must take place.



  2. Comment: How long will the riverbank be dangerous to the health of the public?



  3. Comment: On Page 1 and 22, the document says: "Site should not be developed until contamination levels have been reduced below levels of health concern". Are there standards for each contaminant and, if so, how do the standards compare with what is on site and compare with data in the report tables. Cleanup should be thorough and should go beyond the minimum standard to allow for the possibility of more stringent standards occurring in the future.



  4. Why wasn't a door-to-door survey conducted of people who live on the ridge above the site, as well as a search for and survey of former residents? Residents have had concerns about the plant and its odors for years.



  5. Anecdotal evidence of considerable community health erosion, including a rash of cancers in the neighborhood, warrants further investigation.

    Exposure to site-related contaminants and adverse health effects in people

    Association between exposure and disease in the site community

    Medical management of an adverse health effect

    Recommendations



  6. Why wasn't a health study conducted on former McCormick and Baxter employees and their families?



  7. The public health assessment recommends that individuals concerned about chronic bronchitis and lung tissue damage should discuss potential chemical exposure with their physicians; however, individuals may not know to mention McCormick and Baxter as a possible contributor to health concerns.



  8. ATSDR would not have conducted the public health assessment if the health of the public was not in danger.



  9. The public comment period was too short.



  10. Since the report indicates that there are few problems due lack of data, only minor cleanup will be conducted and the site will continue to pose a health hazard.



  11. The commentor's personal experience with wood preserving chemicals indicates that exposure does not have to be intense and over many years to have serious detrimental effects.



  12. Signs and warning in a variety of languages should be provided to the resource agencies that work with non-english speaking groups that fish the slough and rivers for food.



  13. The report concludes that lung symptoms are consistent with exposure to site-related contaminants, but did not collect information from residents about lung-related problems in an orderly fashion. Depending upon insufficient data will result in a report that does not safeguard health.



  14. The report indicates that, should additional information become available, conclusions will be revised, but is unclear how additional data will be made available. ATSDR needs to require additional study in order to have a meaningful response.



  15. How will health professionals and members of the community receive recommended education?

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