PUBLIC HEALTH ASSESSMENT
CENTRAL WOOD PRESERVING COMPANY
SLAUGHTER, EAST FELICIANA PARISH, LOUISIANA

Figure 1. Demographic Statistics
Table 1. Maximum Concentrations in On-Site Soil. ( 0-2 feet depth). Presented in Site Inspection Report, Ecology and Environment, Inc., 1993, 1994, 1995 and 1999. Central Wood Preserving, East Feliciana Parish, Louisiana.
| Contaminants of Concern | South Property | North Property | Comparison Values | |||
| Max. conc. detected (mg/kg)1 | Background | Max. conc. detected (mg/kg) | Background | mg/kg | Source | |
| Inorganics | ||||||
| arsenic | 430 | 14 | 6900 | 14 | 20 | child EMEG3 |
| chromium, total | 610 | 22 | 3500 | 22 | 200 | RMEG4 |
| copper | 360 | 5.3 | 4400 | 5.3 | 20 | [15] |
| PAHs | ||||||
| benzo(a)pyrene | 1.5 | N/A2 | 260 | N/A | 0.1 | CREG |
1mg/kg - milligrams per kilogram
2N/A= Not available
3child EMEG= Environmental Media Evaluation Guide
4RMEG= Reference Dose Media Evaluation
[15]= EPA Region 6 Web site
Table 2. Toxicity Equivalency Calculation for Polycyclic
Aromatic Hydrocarbons detected in On-Site Soil (0 to 2 feet depth). Presented
in Baseline Human Health Risk Assessment, 1993, 1994, 1995 and 1999. Central
Wood Preserving, East Feliciana Parish, Louisiana.
| Contaminants of Concern | Max. conc. detected (mg/kg)1 | Toxic Equivalency Factor | Products | ||
| South Property | North Property | South Property | North Property | ||
| PAHs | |||||
| Dibenzo(a,h)anthracene | 20 | 1.2 | 5 | 100 | 6 |
| Benzo(a)pyrene | 1.5 | 260 | 1 | 1.5 | 260 |
| benzo(a)anthracene | 2.0 | 280 | 0.1 | 0.2 | 28 |
| benzo(b)fluoranthene | 2.4 | 440 | 0.1 | 0.24 | 44 |
| benzo(k)fluoranthene | 2.0 | 400 | 0.1 | 0.2 | 40 |
| indeno(1,2,3-cd)pyrene | 0.5 | 130 | 0.1 | 0.05 | 13 |
| anthracene | 0.81 | 300 | 0.01 | 0.0081 | 3 |
| benzo(g,h,i)perylene | 0.49 | 3.5 | 0.01 | 0.0049 | 0.035 |
| chrysene | 2.9 | 550 | 0.01 | 0.029 | 5.5 |
| acenaphthene | 1.3 | 240 | 0.001 | 0.0013 | 0.24 |
| fluoranthene | 12 | 860 | 0.001 | 0.012 | 0.86 |
| fluorene | 1.3 | 210 | 0.001 | 0.0013 | 0.21 |
| phenanthrene | 3.9 | 420 | 0.001 | 0.0039 | 0.42 |
| pyrene | 8.1 | 720 | 0.001 | 0.0081 | 0.72 |
| Benzo(a)pyrene TOXIC EQUIVALENT |
102.26 | 401.99 | |||
1mg/kg - milligrams per kilogram
Table 3. Maximum Concentrations in Off-Site Sediment on
the Unnamed Creek. (0-2 feet depth). Presented in Remedial Investigation Report,
1992 -1995. Central Wood Preserving, East Feliciana Parish, Louisiana.
| Contaminants of Concern | Max. conc. detected (mg/kg)1 | Background | Comparison Values (mg/kg) | Source |
| Inorganics | ||||
| arsenic | 126 | 14 | 20 | child EMEG3 |
| chromium | 257 | 22 | 200 | RMEG4 |
| PAHs | ||||
| benzo(a)pyrene | 9.4 | N/A2 | 0.1 | CREG5 |
| benzo(a)anthracene | 9.5 | N/A | 0.56 | LDEQ RECAP6 |
| benzo(b)fluoranthene | 16 | N/A | 0.56 | LDEQ RECAP |
| benzo(k)fluoranthene | 16 | N/A | 5.5 | LDEQ RECAP |
| dibenz(a,h)anthracene | 3 | N/A | 0.33 | LDEQ RECAP |
| indeno(1,2,3-c,d)pyrene | 7.8 | N/A | 0.56 | LDEQ RECAP |
1mg/kg = milligrams per kilogram
2N/A= Not available
3child EMEG= Environmental Media Evaluation Guide
4RMEG= Reference Dose Media Evaluation
5CREG= Cancer Risk Evaluation Guide for 1x10-6 excess cancer risk.
6LDEQ RECAP= Louisiana Department of Environmental Quality Risk Evaluation/Corrective Action Program
Table 4. Toxicity Equivalency Calculation for Polycyclic
Aromatic Hydrocarbons detected in Off-Site Sediments (0 to 2 feet depth) on
the Unnamed Creek 1992-1995. Central Wood Preserving, East Feliciana Parish,
Louisiana.
| Contaminants of Concern | Max. Conc. Detected (mg/kg)1 | Toxic Equivalency Factor | Product2 |
| Dibenzo(a,h)anthracene | 3.0 | 5 | 15 |
| Benzo(a)pyrene | 9.4 | 1 | 9.4 |
| benzo(a)anthracene | 9.5 | 0.1 | 0.95 |
| benzo(b)fluoranthene | 16 | 0.1 | 1.6 |
| benzo(k)fluoranthene | 16 | 0.1 | 1.6 |
| indeno(1,2,3-cd)pyrene | 7.8 | 0.1 | 0.78 |
| benzo(g,h,i)perylene | 6.0 | 0.01 | 0.06 |
| chrysene | 17 | 0.01 | 0.17 |
| acenaphthene | 0.5 | 0.001 | 0.0005 |
| fluoranthene | 22 | 0.001 | 0.022 |
| phenanthrene | 5.7 | 0.001 | 0.00067 |
| pyrene | 17 | 0.001 | 0.017 |
| Benzo(a)pyrene TOXIC EQUIVALENT |
29.59 |
1mg/kg - milligrams per kilogram
2product- (max. conc. detected)(toxic equ. factor)
Table 5. Maximum Concentrations in On-Site (North and South
Property) and Off-Site Soil/Sediment on the Unnamed Creek ( 0-2 feet depth).
Presented in Baseline Human Health Risk Assessment, 1993, 1994, 1995 and 1999.
Central Wood Preserving, East Feliciana Parish, Louisiana.
| Contaminants of Concern | On-site Creek Soil/Sediment | Off-site Creek Soil/Sediment | Comparison Values | |||
| Max. conc. detected (mg/kg)1 | Background | Max. conc. detected (mg/kg) | Background | mg/kg | Source | |
| Inorganics | ||||||
| arsenic | 1,100 | 11 | 590 | 11 | 20 | RMEG3 child |
| chromium, total | 2,500 | 16 | 2,800 | 16 | 200 | RMEG child |
| Polycyclic Aromatic Hydrocarbons | ||||||
| Benzo(a)pyrene | 860 | NA | 9.4 | NA | 0.1 | CREG4 |
| acenaphthene | 7,100 | NA | 0.5 | NA | 3,000 | RMEG child |
| fluoranthene | 21,000 | NA | 22 | NA | 2,000 | RMEG child |
| fluorene | 12,000 | NA | 0.69 | NA | 2,000 | RMEG |
| pyrene | 5,300 | NA | 17 | NA | 2,000 | RMEG child |
1mg/kg - milligrams per kilogram
2NA= Not available
3 RMEG= Reference Dose Media Evaluation Guide
4CREG= Cancer Risk Evaluation Guide for 1x10-6 excess cancer risk.
Table 6. Toxicity Equivalency Calculation for Polycyclic
Aromatic Hydrocarbons detected in On-Site and Off-Site Soil/Sediments (0 to
2 feet depth) on the Unnamed Creek. Presented in Baseline Human Health Risk
Assessment, 1993, 1994, 1995 and 1999. Central Wood Preserving, East Feliciana
Parish, Louisiana.
| Contaminants of Concern | Max. conc. detected (mg/kg)1 | Toxic Equivalency Factor | Products | ||
| On-Site Soil/ Sediments | Off-Site Soil/ Sediments | On-Site Soil/ Sediments | Off-Site Soil/ Sediments | ||
| Dibenzo(a,h)anthracene | ND | 3.0 | 5 | 0 | 15 |
| Benzo(a)pyrene | 860 | 9.4 | 1 | 860 | 9.4 |
| benzo(a)anthracene | 1,200 | 9.5 | 0.1 | 120 | 0.95 |
| benzo(b)fluoranthene | 1,200 | 16 | 0.1 | 120 | 1.6 |
| benzo(k)fluoranthene | 600 | 16 | 0.1 | 60 | 1.6 |
| indeno(1,2,3-cd)pyrene | 270 | 7.8 | 0.1 | 27 | 0.78 |
| anthracene | 15,000 | 29 | 0.01 | 150 | 0.29 |
| benzo(g,h,i)perylene | 150 | 6.0 | 0.01 | 1.5 | 0.06 |
| chrysene | 5,600 | 17 | 0.01 | 56 | 0.17 |
| acenaphthene | 7,100 | 0.5 | 0.001 | 7.1 | 0.0005 |
| fluoranthene | 21,000 | 22 | 0.001 | 21 | 0.022 |
| fluorene | 12,000 | 0.69 | 0.001 | 12 | 0.00069 |
| phenanthrene | 48,000 | 5.7 | 0.001 | 48 | 0.00067 |
| pyrene | 5,300 | 17 | 0.001 | 5.3 | 0.017 |
| Benzo(a)pyrene TOXIC EQUIVALENT |
1,488 | 29.89 | |||
1mg/kg - milligrams per kilogram
Table 7. Maximum Concentrations in On-site and Off-site
Surface Water. Samples collected in 1999. Central Wood Preserving, East Feliciana
Parish, Louisiana.
| Contaminant of Concern | On-site Surface Water (µg/L)1 | Off-site Surface Water (µg/L) | Comparison Values | |
| µg/L | Source | |||
| Arsenic | 220 | 29 | 50 | EPA MCL3 |
| Chromium, total | 110 | 23 | 100 | EPA MCL |
| Manganese | 6,600 | 1,000 | 50 | EPA Secondary MCL |
1 µg/l = micrograms per liter
2 NA - Not available
3 MCL= Maximum Contaminant Level
Table 8. Maximum Concentrations in Off-site Groundwater
(Residential Well). Samples collected in 1999. Central Wood Preserving. East
Feliciana Parish, Louisiana.
| Contaminants of Concern | Maximum Concentration Detected (µg/L)1 | Comparison Values | |
| (µg/L) | Source | ||
| Inorganics: | |||
| aluminum | 409 | 200 | Secondary MCL2 |
| iron | 1,070 | 300 | Secondary MCL |
| sodium | 28,500 | 20,000 | EPA DWEL3 |
| Semi-volatiles: | |||
| bis(2-ethylhexyl)phthalate | 19.6 | 3 | CREG4 |
1 µg/L - micrograms per liters
2 MCL - secondary Maximum Contaminant
3 DWEL - Drinking Water Equivalent Level
Level for aesthetic qualities of drinking water
4 CREG - Cancer Risk Evaluation Guide
TABLE 9. COMPLETED EXPOSURE PATHWAYS
| Pathway Names | Exposure Pathway Elements | Time | ||||
| Source | Environmental Media | Point of Exposure | Route of Exposure | Exposed Population | ||
| Soil (SP) | Site | Soil | On-site* | Ingestion Dermal contact |
CWP workers | Past |
| Trespassers | Present Future |
|||||
| Soil (NP) | Site | Soil | On-site | Ingestion Dermal contact |
CWP Workers | Past |
| Trespassers | Future | |||||
| Sediment | Site | Sediment | On-site | Ingestion Dermal contact |
CWP Workers | Past |
| Trespassers | Present Future |
|||||
| Air | Site | Soil Sediment | On-site | Inhalation | CWP Workers | Past |
| Residential well | Not site related | Groundwater | Tap water | Ingestion Dermal contact |
Residents | Present Past Future |
* On-site= CWP site and adjacent property (all within the fence).
TABLE 10. POTENTIAL EXPOSURE PATHWAYS
| Pathway Names | Exposure Pathway Elements | Time | ||||
| Source | Environmental Media | Point of Exposure | Route of Exposure | Exposed Population | ||
| Air | CWP Site | Airborne soil particulates | Off-site | Inhalation | Residents Trespassers |
Present Future |
| Sediment | CWP Site | Sediment | Off-site unnamed creek bottom and banks | Ingestion Dermal contact |
Residents Trespassers |
Past Present Future |
APPENDIX C: NEEDS ASSESSMENT SUMMARY AND QUESTIONAIRE
July 2000 Needs Assessment Summary
In July 2000, SEET staff administered a Needs Assessment (NA) to approximately 10 homes adjacent to the CWP site. The heads-of-household were asked about their health problems and about the health conditions of other household members. There were 30 health conditions reported by adults (over 18 years of age). No health problems were reported by 73% of the adult population. Health concerns reported for children were allergies, anemia, and chicken pox. The heads-of-household were also asked about their other environmental health concerns. Seven, both males and females, reported having no concerns. The other concern expressed was allergies. Follow-up to the community will be in the form of a mail out of the Executive Summary of the Needs Assessment to the 10 households.
Executive Summary of Responses to the Needs Assessment/Questionnaire on a Community living near the Central Wood Preserving Superfund Site, Slaughter, LA
CERCLIS NO. LAD 008187940 ![]()
February 2, 2001
On July 22, 2000, three staff members from the Office of Public Health (OPH), Section of Environmental Epidemiology and Toxicology administered a Needs Assessment (NA) in a community adjacent to the Central Wood Preserving (CWP) site in Slaughter, Louisiana (East Feliciana Parish). The community surveyed borders the east side of the site and consists of approximately 10 homes.
The heads-of-household completed a two-page survey and a shorter survey for each household member. A total of nine households (30 participants), all African American, completed a survey administered by OPH staff on a door-to-door basis. OPH staff interviewed twenty-one (70%) female participants and nine (30%) male participants. The age range of the household members was from 1 to 64 years of age. There were seven female (78%) heads-of-household and two males (22%) heads-of-household. All heads-of-household had either worked or lived in this area from 6 to 64 years. The age of the houses ranged from 10 months to more than 60 years.
The heads-of-household were asked about their health problems and about the health conditions of other household members. There were thirty health conditions reported by adults (over 18 years of age). Twenty-two heads-of-household (73%) of the adult population reported not having any health problems. Other responses include conditions such as allergies, anemia, cancer, chest pains, chicken pox, rheumatism, and sinus. Health concerns reported for children were allergies, anemia, and chicken pox.
Data were analyzed regarding whether or not the head-of-household visited a doctor or hospital and whether or not they had visited either within the last six months. Five of the heads-of-household had seen a doctor and four heads-of-household had been to a hospital within the last six months. The only hospital cited was Lane Memorial.
The heads-of-household were asked about the unnamed creek near their home that feeds into Little Sandy Creek. Three heads-of-household reported that their children played in this ditch. According to eight of the heads-of-household, flooding is not a problem in the area.
Finally, the heads-of-household were asked about their other environmental health concerns. Seven, both males and females, reported having no concerns. The only concern expressed was allergies. No health needs that OPH can offer assistance with were identified.
List of Acronyms
|
CWP |
Central Wood Preserving |
| NP | North Property |
| SP | South Property |
| ATSDR | Agency for Toxic Substances and Disease Registry |
| OPH | Office of Public Health |
| SEET | Section of Environmental Epidemiology and Toxicology |
| EPA | Environmental Protection agency |
| NPL | National Priorities List |
| CV | Comparison Values |
|
OSHA |
Occupational Health and Safety Administration |
| SI | Site Investigation |
| TRI | Toxic Release Inventory |
| RI/FS | Remedial Investigation/Feasibility Study |
| XRF | X-Ray Fluorescence |
| SIR | Standard Incidence Ratio |
| LDEQ | Louisiana Department of Environmental Quality. |
|
LDEQ RECAP |
Louisiana Department of Environmental Quality Risk Evaluation/Corrective Action Program |
| LSH | Louisiana State Highway |
| NA | Needs Assessment |
| VOCs | Volatile Organic Compounds |
| SVOCs | Semivolatile organic compounds |
| PAHs | Polycyclic Aromatic Hydrocarbon |
| RfD | Reference Dose |
| RDA | Recommended Daily Allowances |
| EMEG | Environmental Media Evaluation Guides |
| MRL | Minimal Risk Level |
| CREG | Cancer Risk Evaluation Guide |
| RMEG | Reference Dose Media Evaluation Guide |
| DWEL | Drinking Water Equivalent Level |
| LOAEL | Lowest Observed Adverse Effects Level |
| MCL | Maximum Contaminant Level |
| SMCL | Secondary Maximum Contaminant Level |
| CPT/ROST | Cone Penetration Testing/Rapid Optical Screening Tool |
| CV | Comparison Values |
| TEFs | Toxic Equivalent Factors |
| bgs | below groundwater surface |
Definitions of Selected Terms
This Central Wood Preserving Company Public Health Assessment was prepared by the Louisiana Department of Health and Hospitals/Office of Public Health under a cooperative agreement with the Agency for Toxic Substances and Disease Registry (ATSDR). It is in accordance with approved methodology and procedures existing at the time the public health assessment was begun.
Alan W. Yarbrough
Technical Project Officer, SPS, SSAB, DHAC, ATSDR
The Division of Health Assessment and Consultation, ATSDR, has reviewed this public health assessment and concurs with the findings.
Richard Gillig
for Chief, State Program Section, SSAB, DHAC, ATSDR