PUBLIC HEALTH ASSESSMENT
NORTHWEST PIPE AND CASING COMPANY
CLACKAMAS, CLACKAMAS COUNTY, OREGON
FIGURES

Figure 1. General Location Map

Figure 3. On-Site Sample Location Map (December 1989)

Figure 4. SSI On-Site Sample Location Map (July 1988)

Figure 5. Monitoring Well Location Map (February 1990)

Figure 6. Surface Water/Sediment Sample Locations (December 1989)

Figure 7. Off-Site Residential/Background Soil Sample Location Map (December 1989)

Figure 8. Off-Site Groundwater Sample Location Map (Feb 1990)
APPENDICES
APPENDIX A
- ENVIRONMENTAL DATAExplanation of Tables
In the data tables that follow, the listed contaminant does not mean that it will cause adverse health effects from exposures. Instead, the list indicates which contaminants will be evaluated further in the Health Assessment. When selected as a contaminant of concern in one medium, that contaminant will be reported in all media.
The data tables include the following acronyms:
CREG = Cancer Risk Evaluation Guide EMEG = Environmental Media Evaluation Guide LTHA = Lifetime Health Advisory PMCLG = Proposed Maximum Contaminant Level Goal ppb = parts per billion ppm = parts per million RMEG = Reference Dose Media Evaluation Guide
Surface soil samples were included in the tables as follows: split samples were counted as separate samples but replicate samples were not. The data come from the 1988 Site Inspection Report and the 1990 Listing Site Inspection Report (2,4).
ATSDR selects and discusses these contaminants based upon the following factors:
- Concentrations of contaminants on and off the site.
- Field data quality, laboratory data quality, and sample design.
- Comparison of on-site and off-site concentrations with health assessment comparison values for (1) noncarcinogenic endpoints and (2) carcinogenic endpoints.
- Community health concerns.
Health assessment comparison values are contaminant concentrations in specific media that are used to select contaminants for further evaluation. These values include Environmental Media Evaluation Guides (EMEGs), Cancer Risk Evaluation Guides (CREGs), and other relevant guidelines. EMEGs are derived from the Minimal Risk Levels (MRLs), ATSDR-derived estimates of daily human exposure to a chemical that are likely to be without an appreciable risk of deleterious effects (non-carcinogenic) over a specified duration of exposure. MRLs provide a measure of the toxicity of a chemical. CREGs are estimated contaminant concentrations based on a one excess cancer in a million persons exposed over a lifetime. CREGs are calculated from EPA's cancer slope factors. EPA's Maximum Contaminant Level Goal (MCLG) is a drinking water health goal. EPA believes that the MCLG represents a level at which no known or anticipated adverse health effect should occur and allows an adequate margin of safety. Proposed Maximum Contaminant Level Goals (PMCLGs) are MCLGs that are being proposed. Maximum Contaminant Levels (MCLs) represent contaminant concentrations that EPA deems protective of public health (considering the availability and economics of water treatment technology) over a lifetime (70 years) at an exposure rate of 2 liters water per day. While MCLs are regulatory concentrations, PMCLGs and MCLGs are not. EPA's Reference Dose (RfD) is an estimate of the daily exposure to a contaminant that is unlikely to cause adverse health effects. The Reference Dose Media Evaluation Guide (RMEG) is calculated from EPA's Reference Dose. EPA also has a drinking water lifetime health advisory (LTHA) which provides the level of a contaminant at which adverse noncarcinogenic health effects would not be anticipated.
Table 1
|
| |||||
Parcel A and B soils & Background soils Soils 0-6" | |||||
| CONTAMINANT | MAXIMUM CONCEN- TRATION |
YEAR REPORTED | COMPARISON VALUE
(C.V.) FOR INGESTION -CHILD |
FREQ>C.V. (>ND) | |
| PAHs | ppm | ppm | Source | ||
| noncarcinogenic: | |||||
| Acenaphthene | 1300 | 1988 | 3000 | RMEG | 5/52 |
| Acenaphthylene | ND | None | (Unknown) | ||
| Anthracene | 27,000 | 1988 | 20,000 | RMEG | 1/42* |
| Benzo(g,h,i)perylene | 390 J3 | 1989 | None | (34/52) | |
| Fluoranthene | 21,000 | 1988 | 2000 | RMEG | 4/62 |
| Fluorene | 2600 | 1988 | 2000 | RMEG | 2/52 |
| 2-Methylnapthalene | ND | None | (Unknown) | ||
| Naphthalene | 17 J | 1989 | None | (4/41) | |
| Phenanthrene | 16,000 | 1988 | None | (18/46) | |
| Pyrene | 15,000 | 1988 | 2000 | RMEG | 5/62 |
| carcinogenic: | |||||
| Benzo(a)anthracene | 950 | 1988 | None | (6/6)* | |
| Benzo(b)fluoranthene | 800 J3 | 1989 | None | (10/11)* | |
| Benzo(k)fluoranthene | 530 J3 | 1989 | None | (10/11)* | |
| Benzo(a)pyrene | 410 J3 | 1989 | 0.096 | CREG | 42/62 |
| Chrysene | 2100 | 1988 | None | (11/11)* | |
| Dibenzo(a,h)anthracene | 89 J3 | 1989 | None | (8/11)* | |
| Indeno(1,2,3-c,d)pyrene | 250 J3 | 1989 | None | (9/11)* | |
| ND = Not Detected; J = estimated value, tentatively identified compound; J3 = estimated value,
positively identified compound, low bias for the sample (actual concentration may be higher). * Some contaminants could not be separated analytically. Concentrations are reported only if the contaminant could be analyzed on a contaminant specific basis. | |||||
Table 2
|
ON-SITE SOIL (2,4) | ||||
Soils 0-6" | ||||
| CONTAMINANT | MAXIMUM CONCEN- TRATION |
COMPARISON VALUE (C.V.) FOR INGESTION-CHILD |
FREQ>C.V. (>ND) | |
| ppm | ppm | Source | ||
| Benzene | 0.008 | 24 | CREG | 0/41 |
| Bis(2-ethyl hexyl) phthalate | ND | None | (Unknown) | |
| 2-butanone | ND | None | (Unknown) | |
| Carbon Tetrachloride | ND | 40 | RMEG | (Unknown) |
| Chloroform | ND | 500 | EMEG | (Unknown) |
| Dibenzofuran | 830** | 50 | RMEG | 4/11 |
| Di-n-octyl phthalate | ND | None | (Unknown) | |
| Total 1,2 DCE (dichloroethene) |
ND | 1000 | RMEG | (Unknown) |
| Methoxychlor | ND | 300 | RMEG | (Unknown) |
| PCB:Aroclor 1254 | 1000 J | 0.3 | EMEG | 39/56 |
| PCE Tetrachloroethene |
3.2 | 0.036 | CREG | 7/41 |
| 1,1,1 trichloroethane |
0.0056 | None | (1/41) | |
| 1,1,2 trichloroethane |
ND | 200 | RMEG | (Unknown) |
| TCE (trichloroethene) |
0.016 | 64 | CREG | (3/41) |
| Vinyl Chloride | ND | 1 | EMEG | (Unknown) |
| ND= Not Detected J= estimated value, tentatively identified compound. *Most of these organic compounds were detected in soil of Parcel B, but not Parcel A. **1988 value | ||||
Table 3
|
ON-SITE SOIL (4) | |||||
Grid Samples | |||||
| CONTAMINANT | MAXIMUM CONC. | BACKGROUND CONC. (BKGR) |
COMPARISON
VALUE (C.V.) FOR INGESTION -CHILD |
FREQ >C.V. (>BKGR) | |
| ppm | ppm | Source | |||
| Aluminum | 28,400 | 31,300 | None | (0/5) | |
| Antimony | 25.6 | 14.7 J | 20 | RMEG | 1/5 |
| Arsenic | 13.3 J4 | 2.5 J | 0.4 | CREG | 5/5 |
| Barium | 1580 | 154 | 4000 | RMEG | 0/5 |
| Beryllium | 0.66 | ND | 0.16 | CREG | 1/5* |
| Cadmium | ND | ND | 10 | EMEG | 0/5 |
| Chromium (III) | 124 | 29.2 | 50,000 | RMEG | 0/5 |
| Cobalt | 21.7 | 20.8 | None | (1/5) | |
| Copper | 160 | 20.9 | None | (5/5) | |
| Iron | 114,000 J4 | 38,500 J4 | None | (2/5) | |
| Lead | 28.3 J4 | 20.4 J4 | None | (1/5) | |
| Manganese | 950 | 801 | 300 | RMEG | 5/5 |
| Mercury | ND | ND | None | (0/5) | |
| Nickel | 98.9 | 19.6 | None | (4/5) | |
| Selenium | Unusable | Unusable | 100 | EMEG | |
| Vanadium | 115 | 111 | None | (1/5) | |
| Zinc | 807 J4 | 77.5 J4 | None | (4/5) | |
| ND = Not Detected J= estimated value, positively identified compound. J4=estimated value, QC outside control limits * The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. The reported FREQ is the minimum. | |||||
Table 4
All maximum concentrations are from the July 1988 data.|
ON-SITE SEDIMENT (4) | ||||
Drainage Ditches, Sediment 0-6" | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION* | COMPARISON VALUE (C.V.) FOR INGESTION - CHILD |
FREQ>C.V. (>ND) | |
| PAHs | ppm | ppm | Source | |
| noncarcinogenic: | ||||
| Acenaphthene | 0.4 J | 3000 | RMEG | 0/7 |
| Acenaphthylene | ND | None | (0/7) | |
| Anthracene | 20 | 20,000 | RMEG | 0/7 |
| Benzo(g,h,i)perylene | 3.9 J | None | (4/7) | |
| Fluoranthene | 2500* | 2000 | RMEG | 1/7 |
| Fluorene | 2.2 | 2000 | RMEG | 0/7 |
| 2-Methylnapthalene | ND | None | 0/7 | |
| Naphthalene | ND | None | 0/7 | |
| Phenanthrene | 13 | None | (3/10) | |
| Pyrene | 2100* | 2000 | RMEG | 1/10 |
| carcinogenic: | ||||
| Benzo(a)anthracene | 230 J* | None | (4/8)** | |
| Benzo(b)fluoranthene | 10 | None | (5/8)** | |
| Benzo(k)fluoranthene | 6.9 | None | (3/8)** | |
| Benzo(a)pyrene | 56 J* | 0.12 | CREG | 5/8 |
| Chrysene | 280 J* | None | (5/8)** | |
| Dibenzo(a,h)anthracene | 0.76 J | None | (2/3) | |
| Indeno(1,2,3-c,d)pyrene | 4.2 | None | (3/8)** | |
| ND= Not Detected; J= estimated value, positively identified compound; J3 = estimated value,
positively identified compound, low bias for the sample (actual concentration may be higher). *SD1, a background sample, was considered on-site due to contaminants and locality. ** Some contaminants could not be separated analytically. Concentrations are reported only if the contaminant could be analyzed on a contaminant specific basis. | ||||
Table 5
|
ON-SITE SEDIMENT (4) | |||||
Drainage Ditches, Sediment 0-6" | |||||
| CONTAMINANT | MAXIMUMCONCEN- TRATION | YEAR REPORTED | COMPARISON VALUE
(C.V.) FOR INGESTION- CHILD |
FREQ>C.V. (>ND) | |
| ppm | ppm | Source | |||
| Benzene | ND | 1989 | 24 | CREG | 0/6 |
| Bis(2-ethyl hexyl) phthalate | 200 J | 1989 | None | (3/6) | |
| 2-butanone | 19 | 1989 | None | (1/6) | |
| Carbon Tetrachloride | ND | 1989 | 40 | RMEG | 0/6 |
| Chloroform | ND | 1989 | 500 | EMEG | 0/6 |
| Dibenzofuran | 0.52 J | 1988 | 50 | RMEG | 0/6 |
| Di-n-octyl phthalate | ND | 1989 | None | (0/6) | |
| Total 1,2 DCE (dichloroethene) |
43 | 1989 | 1000 | RMEG | 0/6 |
| Methoxychlor | ND | 1989 | 300 | RMEG | 0/6 |
| PCB:Aroclor 1254 | 11 | 1988 | 0.3 | EMEG | 5/6 |
| PCE Tetrachloroethene |
0.23 | 1989 | 0.036 | CREG | 1/6 |
| 1,1,1 trichloroethane |
ND | 1989 | None | 0/6 | |
| 1,1,2 trichloroethane |
ND | 1989 | 200 | RMEG | 0/6 |
| TCE (trichloroethene) |
0.036 | 1989 | 64 | CREG | (2/6) |
| Vinyl Chloride | ND | 1989 | 1 | EMEG | 0/6 |
| *These organic compounds were analyzed in soil of Parcel B. J= estimated value, positively identified compound. | |||||
Table 6
|
ON-SITE SEDIMENT (4) | |||||
Drainage Ditches, Sediment 0-6" | |||||
| CONTAMINANT | MAXIMUM CONC. |
BACKGROUND CONC. (BKGR) |
COMPARISON VALUE (C.V.) FOR INGESTION- CHILD | FREQ >C.V. (>BKGR) | |
| ppm | ppm | Source | |||
| Aluminum | 25,700 | 15,700 | None | (3/4) | |
| Antimony | ND or Unusable |
Unusable | 20 | RMEG | 0/1* |
| Arsenic | 11.8 | 4.9 | 0.4 | CREG | 4/4 |
| Barium | 191 | 138 | 4000 | RMEG | 0/4 |
| Beryllium | ND | ND | 0.16 | CREG | 0/4** |
| Cadmium | ND | ND | 10 | EMEG | 0/4** |
| Chromium (III) | 42 | 27.2 | 50,000 | RMEG | 0/4 |
| Cobalt | 31.3 | 18.3 | None | 2/4 | |
| Copper | 77.0 | 26.6 | None | (3/4) | |
| Iron | 43,200 | 26,500 | None | (2/4) | |
| Lead | 175 J4 | 29.1 | None | (2/4) | |
| Manganese | 1820 | 639 | 300 | RMEG | 4/4 |
| Mercury | 0.28 J4 | ND | None | (1/4) | |
| Nickel | 23.6 | 22.4 | None | (1/4) | |
| Selenium | ND | ND | 100 | EMEG | 0/4 |
| Vanadium | 122 | 68.9 | None | (2/4) | |
| Zinc | 1190 | 153 | None | (3/4) | |
| ND = Not Detected; J= estimated value, positively identified compound; J4=estimated value; QC outside control limits * 3/4 samples were unusable. ** The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. The reported FREQ is the minimum. | |||||
Table 7
No PAHs were detected in surface water. Background surface water samples could not collected because the drainage ditches were dry.|
ON-SITE SURFACE WATER (4) | ||||
Drainage Ditches | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE (C.V.) FOR INGESTION | FREQ>C.V. (>ND) | |
| ppb | ppb | Source | ||
| Benzene | 1 J | 1.2 | CREG | 0/4 |
| Carbon Tetrachloride | ND | 0.27 | CREG | 0/4 |
| Chloroform | ND | 5.7 | CREG | 0/4 |
| Dibenzofuran | ND | 10 | RMEG | 0/4 |
| Total 1,2 DCE (dichloroethene) |
37 | 70 | LTHA | 0/4 |
| PCB:Aroclor 1254 | ND | 0.0045 | CREG | |
| PCE Tetrachloroethene |
53 | 0.67 | CREG | 2/4 |
| 1,1,1 trichloroethane |
ND | None | 0/4 | |
| 1,1,2 trichloroethane |
ND | 0.61 | CREG | 0/4 |
| TCE (trichloroethene) |
13 | 3.2 | CREG | 2/4 |
| Vinyl Chloride | 2.0 J | 0.2 | EMEG | 1/4 |
| ND= Not Detected J= estimated value, positively identified compound. | ||||
Table 8
|
ON-SITE SURFACEWATER (4) | |||||
Drainage Ditches | |||||
| CONTAMINANT | MAXIMUM CONC. | BACKGROUND
CONC. (BKGR) |
COMPARISON VALUE (C.V.) FOR INGESTION |
FREQ >C.V. (>BKGR) | |
| ppb | ppb | Source | |||
| Aluminum | 1830 | 296 UJ1 | None | (1/4) | |
| Antimony | ND | ND | 0.004 | RMEG | (0/4)* |
| Arsenic | ND | ND | 0.003 | RMEG | (0/4)* |
| Barium | 48.9 J | 25.1 J | 0.7 | RMEG | 4/4 |
| Beryllium | 3.5 UJ1 | ND | 8.1 | CREG | 0/4 |
| Cadmium | 3.2 UJ1 | ND | 0.002 | EMEG | (0/4)* |
| Chromium | 7.6 UJ1 | 6 J | 0.05 | RMEG | (0/4)* |
| Cobalt | ND | ND | None | (0/4) | |
| Copper | 31.7 | ND | 1300 | PMCL | 0/4 |
| Iron | 4240 | 585 | None | (1/4) | |
| Lead | 64.8 J4 | 1.3 UJ1, J4 | 0.005 | PMCL | (2/4)* |
| Manganese | 463 | 86.3 | 1.0 | RMEG | 4/4 |
| Mercury | 0.2 | ND | None | (1/4) | |
| Nickel | ND | ND | 0.2 | EMEG | (0/4)* |
| Selenium | 2.8 J | ND | 20 | iEMEG | 0/4 |
| Vanadium | 9.8 J | 3.3 J | 20 | LTHA | 0/4 |
| Zinc | 215 | 38.5 | 2100 | LTHA | 0/4 |
| ND = Not Detected; J= estimated value, positively identified compound; J4=estimated value; QC outside control limits; UJ1=Not detected, the concentration is an estimated/adjusted quantitation limit, blank contamination. * The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. Therefore, the reported FREQ refers to background. | |||||
Table 9
|
ON-SITE GROUNDWATER (2,4) | |||||
| CONTAMINANT | MAXIMUM CONCEN- TRATION |
YEAR REPORTED | COMPARISON VALUE
(C.V.) FOR INGESTION |
FREQ>C.V. (>ND) | |
| PAHs | ppb | ppb | Source | ||
| noncarcinogenic: | |||||
| Acenaphthene | 3400 | 1990 | 600 | RMEG | 2/12 |
| Acenaphthylene | 8 J | 1990 | None | (3/12) | |
| Anthracene | 260 | 1990 | 3000 | RMEG | 0/12 |
| Benzo(g,h,i)perylene | 20 | 1990 | None | (1/8) | |
| Fluoranthene | 2500 | 1990 | 400 | RMEG | 1/12 |
| Fluorene | 1400 | 1990 | 400 | RMEG | 1/8 |
| 2-Methylnapthalene | 110 | 1988 | None | (5/12) | |
| Naphthalene | 680 | 1988 | 20 | LTHA | 1/12 |
| Phenanthrene | 5000 | 1990 | None | (9/12) | |
| Pyrene | 2300 | 1990 | 300 | RMEG | 1/12 |
| carcinogenic: | |||||
| Benzo(a)anthracene | 260 | 1990 | 0.0081 | CREG | 4/12 |
| Benzo(b)fluoranthene | 78 | 1990 | None | (2/8) | |
| Benzo(k)fluoranthene | 38 | 1990 | None | (1/8) | |
| Benzo(a)pyrene | 41 | 1990 | 0.0048 | CREG | 2/8 |
| Chrysene | 210 | 1990 | None | (5/12) | |
| Dibenzo(a,h)anthracene | 10 J | 1990 | None | (1/8) | |
| Indeno(1,2,3-c,d)pyrene | 22 | 1990 | None | (1/8) | |
| J = estimated value, positively identified compound.
The PAH's analyzed as above were all non-detectable in the background well. | |||||
Table 10
|
ON-SITE GROUNDWATER (4) | ||||
MW 1-7, ODOT floor drain | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE (C.V.) FOR INGESTION |
FREQ>C.V. (>ND) | |
| ppb | ppb | Source | ||
| Benzene | 2 J | 1.2 | CREG | 2/8 |
| Carbon Tetrachloride | 41 | 0.27 | CREG | 1/8 |
| Chloroform | 32 | 5.7 | CREG | 1/8 |
| Dibenzofuran | 1200 | 10 | RMEG | 3/8 |
| Total 1,2 DCE (dichloroethene) |
4200 | 70 | LTHA | 4/8 |
| PCB:Aroclor 1254 | 15 | 0.0045 | CREG | 1/8 |
| PCE Tetrachloroethene |
4200 | 0.67 | CREG | 7/8 |
| 1,1,1 trichloroethane |
ND | 200 | LTHA | 0/8 |
| 1,1,2 trichloroethane |
5 J | 0.61 | CREG | 1/8 |
| TCE (trichloroethene) |
1100 | 3.2 | CREG | 5/8 |
| Vinyl Chloride | 91 | 0.2 | EMEG | 5/8 |
| ND= Not Detected J= estimated value, positively identified compound. ODOT = Oregon Department of Transportation MW = Monitoring Well | ||||
Table 11
|
ON-SITE GROUNDWATER (4) | |||||
MW 1-7, ODOT Floor drain | |||||
| CONTAMINANT | MAXIMUM CONC. |
BACKGROUND CONC. (BKGR) |
COMPARISON VALUE (C.V.) FOR INGESTION |
FREQ >C.V. (>BKGR) | |
| ppb | ppb | Source | |||
| Aluminum | 193,000 | ND | None | (8/8) | |
| Antimony | 54.4 J4 | 20 UJ4 | 0.004 | RMEG | 2/8* |
| Arsenic | 31.1 J4 | 1.0 UJ4 | 0.003 | RMEG | 4/8* |
| Barium | 1680 | 21.4 UJ1 | 0.7 | RMEG | 8/8 |
| Beryllium | 10.2 | ND | 8.1 | CREG | 1/8 |
| Cadmium | ND | ND | 0.002 | EMEG | 0/8 |
| Chromium | 293 | ND | 0.05 | RMEG | 6/8* |
| Cobalt | 138 | ND | None | (6/8) | |
| Copper | 334 | ND | 1300 | PMCL | 0/8 |
| Iron | 275,000 | 1040 | None | (8/8) | |
| Lead | 491 J4 | ND | 0.005 | PMCL | 8/8 |
| Manganese | 5930 | 7.6 J | 1.0 | RMEG | 8/8 |
| Mercury | ND | ND | None | (0/8) | |
| Nickel | 155 | ND | 0.2 | EMEG | 5/8* |
| Selenium | Unusable | ||||
| Vanadium | 888 | ND | 20 | LTHA | 6/8 |
| Zinc | 4800 | 263 | 2100 | LTHA | 1/8 |
| ND= Not Detected J= estimated value, positively identified compound. J4=estimated value, QC outside control limits UJ1=Not detected, the concentration is an estimated/adjusted quantitation limit, blank contamination. UJ4= Not detected, the concentration is an estimated/adjusted quantitation limit, QC outside control limits. ODOT = Oregon Department of Transportation * The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. | |||||
Table 12
The frequency column was eliminated because of the minimal number of wells or well involved.|
ON- AND OFF-SITE GROUNDWATER (4) | |||||
City of Milwaukie wells and ODOT well | |||||
| CONTAMINANT | MAXIMUM CONC. | BACKGROUND CONC. | COMPARISON VALUE (C.V.) FOR INGESTION | ||
| ppb | ppb | ppb | Source | ||
| Milwaukie: off-site wells |
ODOT: on-site well |
||||
| Aluminum | ND | ND | ND | None | |
| Antimony | ND | 20 UJ4 | ND | 0.004 | RMEG |
| Arsenic | ND | 8.8 J4 | 1.0 UJ4 | 0.003 | RMEG |
| Barium | 7.6 UJ1 | 74.3 J | 21.4 UJ1 | 0.7 | RMEG |
| Beryllium | ND | ND | ND | 8.1 | CREG |
| Cadmium | ND | ND | ND | 0.002 | EMEG |
| Chromium | ND | ND | ND | 0.05 | RMEG |
| Cobalt | ND | ND | ND | None | |
| Copper | ND | 10.1 J | ND | 1300 | PMCL |
| Iron | 83.4 UJ1 | 4010 | 1040 | None | |
| Lead | ND | 2.4 J | ND or 1J | 0.005 | PMCL |
| Manganese | 27.6 | 1850 | 7.6 J | 1.0 | RMEG |
| Mercury | ND | ND | ND | None | |
| Nickel | ND | ND | ND | 0.2 | EMEG |
| Selenium | Unusable | Unusable | |||
| Vanadium | 6.6J | ND | ND | 20 | LTHA |
| Zinc | 2.4 UJ1 | 1180 | 263 | 2100 | LTHA |
| ND= Not Detected J= estimated value, positively identified compound. J4=estimated value, QC outside control limits UJ1=Not detected, the concentration is an estimated/adjusted quantitation limit, blank contamination. UJ4= Not detected, the concentration is an estimated/adjusted quantitation limit, QC outside control limits. ODOT = Oregon Department of Transportation * The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. | |||||
Table 13
|
OFF-SITE SOILS (4) | ||||
Residential and Background* Samples Soils 0-6" | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE (C.V.) FOR INGESTION -PICA CHILD |
FREQ>C.V. (>ND) | |
| PAHs | ppm | ppm | Source | |
| noncarcinogenic: | ||||
| Acenaphthene | ND | 120 | RMEG | 0/2 |
| Acenaphthylene | ND | None | (Unknown) | |
| Anthracene | ND | 600 | RMEG | 0/2 |
| Benzo(g,h,i)perylene | 0.23 J3 | None | (1/5) | |
| Fluoranthene | 0.31 J3 | 80 | RMEG | 0/5 |
| Fluorene | ND | 80 | RMEG | 0/2 |
| 2-Methylnapthalene | ND | None | (Unknown) | |
| Naphthalene | ND | None | (Unknown) | |
| Phenanthrene | 0.11 J3 | None | (3/5) | |
| Pyrene | 0.32 J3 | 60 | RMEG | 0/5 |
| carcinogenic: | ||||
| Benzo(a)anthracene | 0.21 J3 | None | (2/5) | |
| Benzo(b)fluoranthene | 0.46 J3 | None | (2/5) | |
| Benzo(k)fluoranthene | 0.32 J3 | None | (1/5) | |
| Benzo(a)pyrene | 0.36 J3 | 0.096 | CREG | 3/5 |
| Chrysene | 0.35 J3 | None | (3/5) | |
| Dibenzo(a,h)anthracene | ND | None | (unknown) | |
| Indeno(1,2,3-c,d)pyrene | 0.15 J3 | None | (1/5) | |
| ND= Not Detected J = estimated value, positively identified compound. J3 = estimated value, positively identified compound, low bias for the sample (actual concentration may be higher). * A background sample contained benzo(b)fluoranthene at 0.15 J3 and benzo(a)pyrene at 0.093 J3. | ||||
Table 14
|
OFF-SITE SOIL (4) | ||||
Soils 0-6" | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE (C.V.) FOR INGESTION - PICA CHILD |
FREQ>C.V. (>ND) | |
| ppm | ppm | Source | ||
| Benzene | ND | 24 | CREG | 0/4 |
| Bis(2-ethyl hexyl) phthalate | 120 J | None | (1/4) | |
| 2-butanone | ND | None | (0/4) | |
| Carbon Tetrachloride | ND | 1.4 | CREG | 0/4 |
| Chloroform | ND | 20 | EMEG | 0/4 |
| Dibenzofuran | ND | 2 | RMEG | 0/4 |
| Di-n-octyl phthalate | 53 J3 | None | (1/4) | |
| Total 1,2 DCE (dichloroethene) |
ND | 40 | RMEG | 0/4 |
| Methoxychlor | 68 J3 | 10 | RMEG | (1/4) |
| PCB:Aroclor 1254 | ND | 0.01 | EMEG | 0/4 |
| PCE Tetrachloroethene |
ND | 0.036 | CREG | 0/4 |
| 1,1,1 trichloroethane |
ND | None | (0/4) | |
| 1,1,2 trichloroethane |
ND | 8 | RMEG | 0/4 |
| TCE (trichloroethene) |
ND | 64 | CREG | 0/4 |
| Vinyl Chloride | ND | 0.04 | EMEG | 0/4 |
| ND= Not Detected J= estimated value, tentatively identified compound. J3 = estimated value, positively identified compound, low bias for the sample (actual concentration may be higher). Bis(2-ethylhexyl)phthalate and di-n-octyl phthalate were detected in the background sample. | ||||
Table 15
|
OFF-SITE SOIL (4) | |||||
Residential Soil Samples- 0-6" | |||||
| CONTAMINANT | MAXIMUM CONC. | BACKGROUND CONC. (BKGR) |
COMPARISON VALUE
(C.V.) FOR INGESTION |
FREQ >C.V. (>BKGR) | |
| ppm | ppm | Source | |||
| Aluminum | 33,200 | 31,300 | None | (1/4) | |
| Antimony | ND or unusable | 14.7 J | 0.8 | RMEG | 0/3* |
| Arsenic | 4.8 | 2.5 J | 0.4 | CREG | 4/4 |
| Barium | 299 | 154 | 140 | RMEG | 2/4 |
| Beryllium | ND | ND | 0.16 | CREG | 0/4** |
| Cadmium | ND | ND | 0.4 | EMEG | 0/4** |
| Chromium (III) | 39.7 | 29.2 | 2000 | RMEG | 0/4 |
| Cobalt | 22.5 | 20.8 | None | (1/4) | |
| Copper | 34.7 | 20.9 | None | (2/4) | |
| Iron | 40,900 J4 | 38,500 J4 | None | (1/4) | |
| Lead | 74.5 J4 | 20.4 J4 | None | (3/4) | |
| Manganese | 1310 | 801 | 10 | RMEG | 4/4 |
| Mercury | ND | ND | None | (0/4) | |
| Nickel | 24 | 19.6 | None | (3/4) | |
| Selenium | ND or unusable | Unusable | 4 | EMEG | 0/1* |
| Vanadium | 126 | 111 | None | (1/4) | |
| Zinc | 203 J4 | 77.5 J4 | None | (4/4) | |
| ND= Not Detected; J= estimated value, positively identified compound. J4=estimated value, QC outside control limits * Unusable data reduced the number of samples for comparison. | |||||
Table 16
|
OFF-SITE SEDIMENT (4) | ||||
Drainage ways and Background | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE
(C.V.) FOR INGESTION -PICA CHILD |
FREQ>C.V. (>ND) | |
| PAHs | ppm | ppm | Source | |
| noncarcinogenic: | ||||
| Acenaphthene | 0.18 J | 120 | RMEG | 0/8 |
| Acenaphthylene | ND | None | ||
| Anthracene | 0.35 J | 600 | RMEG | 0/8 |
| Benzo(g,h,i)perylene | 1.40 | None | (4/8) | |
| Fluoranthene | 3.90 | 80 | RMEG | 0/8 |
| Fluorene | 0.14 J | 80 | RMEG | 0/8 |
| 2-Methylnapthalene | ND | None | (0/8) | |
| Naphthalene | ND | None | (0/8) | |
| Phenanthrene | 1.60 | None | (3/8) | |
| Pyrene | 4.50 | 60 | RMEG | 0/8 |
| carcinogenic: | ||||
| Benzo(a)anthracene | 2.20 | None | (4/8) | |
| Benzo(b)fluoranthene | 2.60 | None | (4/8) | |
| Benzo(k)fluoranthene | 2.40 | None | (4/8) | |
| Benzo(a)pyrene | 1.90 | 0.12 | CREG | 4/8 |
| Chrysene | 2.70 | None | (4/8) | |
| Dibenzo(a,h)anthracene | 0.77 J | None | (2/8) | |
| Indeno(1,2,3-c,d)pyrene | 1.40 | None | (4/8) | |
| ND= Not Detected J = estimated value, positively identified compound. *All maximum concentrations are from the December 1989 data. Only one sample from the 1988 data was considered off-site or background. This sample had no detectable organics. No PAH's were detected in the 1989 background sample. | ||||
Table 17
|
OFF-SITE SEDIMENT (4) | ||||
Drainage ways and Background Samples Sediment 0-6" | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION* | COMPARISON VALUE (C.V.) FOR INGESTION - PICA CHILD |
FREQ>C.V. (>ND) | |
| ppm | ppm | Source | ||
| Benzene | ND | 24 | CREG | 0/8 |
| Bis(2-ethyl hexyl) phthalate | 1.30** | None | (7/8) | |
| 2-butanone | 0.008 J** | None | (4/8) | |
| Carbon Tetrachloride | ND | 1.4 | CREG | 0/8 |
| Chloroform | ND | 20 | EMEG | 0/8 |
| Dibenzofuran | ND | 2 | RMEG | 0/8 |
| Di-n-octyl phthalate | 0.47 J | None | (2/8) | |
| Total 1,2 DCE (dichloroethene) |
0.002 | 40 | RMEG | 0/8 |
| Methoxychlor | ND | 10 | RMEG | 0/8 |
| PCB:Aroclor 1254 Aroclor 1260 |
2.50 0.16 J |
0.01 | EMEG | 4/8 1/8 |
| PCE Tetrachloroethene |
0.003 J | 0.036 | RMEG | 0/8 |
| 1,1,1 trichloroethane |
ND | None | 0/8 | |
| 1,1,2 trichloroethane |
ND | 8 | CREG | 0/8 |
| TCE (trichloroethene) |
0.002 J | 64 | CREG | (1/8) |
| Vinyl Chloride | ND | 0.04 | EMEG | 0/8 |
| ND= Not Detected. J= estimated value, positively identified compound. *All reported maximums, except Aroclor 1260, are from the December 1989 data. | ||||
Table 18
|
OFF-SITE SEDIMENT (4) | |||||
Drainage Ditches | |||||
| CONTAMINANT | MAXIMUM CONC. | BACKGROUND
CONC. (BKGR) |
COMPARISON
VALUE (C.V.) FOR INGESTION |
FREQ >C.V. (>BKGR) | |
| ppm | ppm | Source | |||
| Aluminum | 20,800 | 15,700 | None | (3/6) | |
| Antimony | 5.4 J, J4 | Unusable | 0.8 | RMEG | 1/1* |
| Arsenic | 9.4 | 4.9 | 0.4 | CREG | 6/6 |
| Barium | 209 | 138 | 140 | RMEG | 2/6 |
| Beryllium | ND | ND | 0.16 | CREG | 0/6** |
| Cadmium | ND | ND | 0.4 | EMEG | 0/6** |
| Chromium (III) | 59.4 | 27.2 | 2000 | RMEG | 0/6 |
| Cobalt | 36.5 | 18.3 | None | (3/6) | |
| Copper | 365 | 26.6 | None | (3/6) | |
| Iron | 57,300 | 26,500 | None | (3/6) | |
| Lead | 544 | 29.1 | None | (3/6) | |
| Manganese | 1320 | 639 | 10 | RMEG | 6/6 |
| Mercury | 0.16 | ND | None | (1/6) | |
| Nickel | 40.8 | 22.4 | None | (1/6) | |
| Selenium | ND | ND | 4 | EMEG | 0/6 |
| Vanadium | 133 | 68.9 | None | (4/6) | |
| Zinc | 290 | 153 | None | (4/6) | |
| ND= Not Detected; J= estimated value, positively identified compound; J4=estimated value; QC outside control limits. * 5/6 samples were unusable ** The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. The reported FREQ is the minimum. | |||||
Table 19
|
OFF-SITE SURFACE WATER (4) | ||||
Drainage Ditches and Background* | ||||
| CONTAMINANT | MAXIMUM CONCENTRATION | COMPARISON VALUE (C.V.) FOR INGESTION |
FREQ>C.V. (>ND) | |
| ppb | ppb | Source | ||
| Benzene | ND | 1.2 | CREG | 0/5 |
| Carbon Tetrachloride | ND | 0.27 | CREG | 0/5 |
| Chloroform | ND | 5.7 | CREG | 0/5 |
| Dibenzofuran | ND | 10 | RMEG | 0/5 |
| Total 1,2 DCE (dichloroethene) |
2.0 J | 70 | LTHA | 0/5 |
| PCB:Aroclor 1254 | ND | 0.0045 | CREG | 0/5 |
| PCE Tetrachloroethene |
3.0 J | 0.67 | CREG | 1/5 |
| 1,1,1 trichloroethane |
ND | 200 | LTHA | 0/5 |
| 1,1,2 trichloroethane |
ND | 0.61 | CREG | 0/5 |
| TCE (trichloroethene) |
ND | 3.2 | CREG | 0/5 |
| Vinyl Chloride | ND | 0.2 | EMEG | 0/5 |
| ND= Not Detected J= estimated value, positively identified compound. *The concentrations for the above contaminants were not detected in the background sample . | ||||
Table 20
|
OFF-SITE SURFACEWATER (4) | |||||
| CONTAMINANT | MAXIMUM CONC. |
BACKGROUND
CONC. (BKGR) |
COMPARISON VALUE
(C.V.) FOR INGESTION |
FREQ >C.V. (>BKGR) | |
| ppb | ppb | Source | |||
| Aluminum | 1680 | 296 UJ1 | None | (1/4) | |
| Antimony | ND | ND | 0.004 | RMEG | (0/4)* |
| Arsenic | ND | ND | 0.003 | RMEG | (0/4)* |
| Barium | 38.4 J | 25.1 J | 0.7 | RMEG | 4/4 |
| Beryllium | 3.4 UJ1 | ND | 8.1 | CREG | 0/4 |
| Cadmium | 3.7 UJ1 | ND | 0.002 | EMEG | (0/4)* |
| Chromium | 5 UJ1 | 6 J | 0.05 | RMEG | (0/4)* |
| Cobalt | ND | ND | None | (0/4) | |
| Copper | 20.6 J | ND | 1300 | PMCL | 0/4 |
| Iron | 2870 | 585 | None | (3/4) | |
| Lead | 4.6 UJ1 J4 | 1.3 UJ1 | 0.005 | PMCL | (2/4)* |
| Manganese | 248 | 86.3 | 1.0 | RMEG | 4/4 |
| Mercury | ND | ND | None | 0/4 | |
| Nickel | ND | ND | 0.2 | EMEG | (0/4)* |
| Selenium | ND | ND | 20 | EMEG | 0/4 |
| Vanadium | 9.7 J | 3.3 J | 20 | LTHA | 0/4 |
| Zinc | 114 | 38.5 | 2100 | LTHA | 0/4 |
| ND = Not Detected; J= estimated value, positively identified compound; J4=estimated value; QC outside control limits; UJ1=Not detected, the concentration is an estimated/adjusted quantitation limit, blank contamination. * The detection limit is higher than the comparison value, therefore the number of samples exceeding the comparison value is unknown. | |||||
Table 21
The only organic compound exceeding background in off-site wells was TCE. Therefore, no organic tables are presented.|
OFF-SITE GROUNDWATER (4) | ||||||
A= Oregon National Guard/Camp Withycombe wells* B= A Residential Well C= Fire Protection Wells* | ||||||
| CONTAMINANT | MAXIMUM CONC. (ppb) |
BACKGROUND CONC. (BKGR) |
COMPARISON VALUE (C.V.) FOR INGESTION | |||
| A* | B | C* | ppb | ppb | Source | |
| Aluminum | 19,800 | ND | 87 UJ1 | ND | None | |
| Antimony | ND | ND | ND | ND | 0.004 | RMEG |
| Arsenic | ND | ND | ND | 1.0 UJ4 | 0.003 | RMEG |
| Barium | 98.9 J | 5.7 UJ1 | 35.7 J | 21.4 UJ1 | 0.7 | RMEG |
| Beryllium | ND | ND | ND | ND | 8.1 | CREG |
| Cadmium | ND | ND | ND | ND | 0.002 | EMEG |
| Chromium | 9.7 J | ND | ND | ND | 0.05 | RMEG |
| Cobalt | 10.7 J | ND | ND | ND | None | |
| Copper | 28.2 | 28.4 | 18.8 J | ND | 1300 | PMCL |
| Iron | 23,000 | 176 | 2090 | 1040 | None | |
| Lead | 19.8 | 4.8 | 1.5 J | ND or 1J | 0.005 | PMCL |
| Manganese | 932 | 13.1 J | 630 | 7.6 J | 50 | RMEG |
| Mercury | ND | ND | ND | ND | None | |
| Nickel | ND | ND | ND | ND | None | |
| Selenium | Unusable | Unusable | Unusable | |||
| Vanadium | 42.3 J | 3.2 J | ND | ND | 20 | LTHA |
| Zinc | 51.9 | 2280 | 26.4 UJ1 | 263 | 2100 | LTHA |
| ND= Not Detected;J= estimated value, positively identified compound; J4=estimated value; QC outside control limits; UJ1=Not detected, the concentration is an estimated/adjusted quantitation limit, blank contamination; UJ4= Not detected, the concentration is an estimated/adjusted quantitation limit, QC outside control limits. * Not used as drinking water. | ||||||



