PUBLIC HEALTH ASSESSMENT
McCORMICK & BAXTER CREOSOTING COMPANY (PORTLAND) APPENDIX A--SITE MAPS
PORTLAND, MULTNOMAH COUNTY, OREGON
LIST OF FIGURES
APPENDIX B
Figure 2 Principal Site Features
LIST OF TABLES
|
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
COMMENTSThe 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.
ATSDR scientists also need to learn what people in the area know about the site and what
concerns they may have about its impact on their health. Throughout the evaluation process, we
actively gather information and comments from people who live or work near a site. Initally,
community health concerns are usually collected at public availability sessions, which ATSDR
generally holds at the beginning of the site investigation. Community members have further
opportunity to voice their concerns during the public comment period. The community's health
concerns are then addressed in the public health assessment.
The report presents conclusions about the level of health threat, if any, posed by a site. Any
indeterminate health issues, which usually result from an inadequate data base, are also
described. For indeterminate issues that might have an associated substantive public health
connotation, recommendations are made to obtain data that would aid in their future resolution.
| 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.
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.
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. |
Exposure to site-related contaminants and adverse health effects in people
Many studies have been conducted with people occupationally exposed to wood preserving chemicals, as described in the Public Health Implications sections above, and adverse health effects resulting from exposure are known. A health study of this community may not show any additional general information.
Association between exposure and disease in the site community
With no way to determine who was exposed to those chemicals in the community, the only question a study could answer would be, is there a higher rate of a specific disease in the community relative to some standard. Such a study would in no way address the association between exposure and disease. Moreover, such a study would by design substantially underestimate any effect on those truly exposed to chemicals, since the study would be diluted by all the people who lived in the community but who were not exposed.
Exposure to specific chemicals causes specific diseases. Cancer is not a specific disease. Different cancers have different causes and different courses. Some cancers may be caused by exposure to carcinogens; exposure to a carcinogen does not cause many different cancers in different people. An anecdotal report of a rash of cancers does not imply that many people were exposed to carcinogens, although a report of an increase in certain specific cancers could be an indication of exposure.
In addition, a health study of this type simply answers whether there is a statistical association between exposure and disease. Therefore, the study requires a minimum number of exposed participants in order to be statistically valid.
Medical management of an adverse health effect
Recommendations
Individuals and health care providers should be made aware of potential exposures related to the McCormick and Baxter site, as well as the signs and symptoms of exposure to site-specific chemicals, as part of the community and health professionals health education effort recommended in the Recommendations section.
We determined public health hazards posed by the site. We concluded that the site posed a public health hazard for former plant workers, poses a public health hazard for people who might encounter hazardous chemicals along the shoreline, and poses an indeterminate public health hazard for nearby residents because of past, present and future inhalation exposure.
We asked for additional information. We recommended air monitoring, noting that the adverse
lung symptoms reported by people who live near the site are consistent with exposure to
site-related contaminants.
We recommended actions to protect the community's health. We recommended that the site not
be developed or otherwise made accessable by the public until remediation measures are
accomplished in a manner that effectively prevents human exposures from occurring at levels of
public health concern.
As an advisory agency, we cannot require other agencies to follow our recommendations. However, other agencies often rely on our recommendations when taking actions to protect the public's health.
ATSDR concurs, as stated in the Public Health Implications section.
ATSDR will include non-english speaking groups that rely on fish and crayfish for food when conducting a needs assessment of the community.
Without information about exposure, a link between exposure and adverse health effect cannot be established. We did say that the adverse lung symptoms are non-specific symptoms known to be experienced by people with no known exposure to hazardous waste, but they are also consistent with exposure to site-related contaminants.
We recommended that the site be prevented from being developed or otherwise accessed by the public until remediation measures are accomplished in a manner that effectively prevents human exposures from occurring at levels of public health concern. We also have recommended gathering additional data on soil and air.
ATSDR has identified data gaps (including contaminant levels in soil on adjacent industrial property, air quality on site while air-release-related remediation activities are in progress, and ambient air quality where residents continue to express concern about odors) and has requested more information be gathered. As an advisory agency, we cannot require other agencies to follow our recommendations.
ATSDR staff plan to determine appropriate site-specific health education activities for health professionals and community members through a needs assessment. The Public Health Action Plan section of the public health assessment has been revised to reflect this information.