HEALTH CONSULTATION
STATE MARINE OF PORT ARTHUR
PORT ARTHUR, JEFFERSON COUNTY, TEXAS
BACKGROUND AND STATEMENT OF ISSUES
The State Marine of Port Arthur National Priorities List site, is a 17-acre former barge cleaningfacility on a small peninsula adjacent to Sabine Lake in the northeastern part of Port Arthur,Jefferson County, Texas. It shares a common fence line with the Palmer Barge NationalPriorities List site. Barge cleaning operations at State Marine, from 1974 until 1988, resulted incontamination of surface soil and Sabine Lake sediment with polycyclic aromatic hydrocarbons(PAHs) and metals [1].
Sabine Lake is heavily fished, both commercially and recreationally (for sport as well as forconsumption). Among the types of fish caught are black drum, flounder, red drum, andsheepshead [2]. Crustaceans such as blue crabs and brown, pink, and white shrimp are alsotaken from the lake[3].
When the State Marine site was proposed to the National Priorities List in 1998, the TexasDepartment of Health Environmental Epidemiology and Toxicology Division (TDH), through acooperative agreement with the Agency for Toxic Substances and Disease Registry (ATSDR),completed a public health assessment for the site. Because only limited fish sampling data wereavailable for review at the time, the site was characterized as an indeterminate public healthhazard [1]. Fish and crab sampling data have since become available and are evaluated in thishealth consultation [2].
In 1994, the TDH Seafood Safety Division collected seafood, including fish and crabs normallycaught and eaten by area fishermen, from Sabine Lake, which is less than one mile from theState Marine site. Samples of edible portions were analyzed for volatile organic compounds(VOCs), semi-VOCs (including PAHs), metals, pesticides, polychlorinated biphenyls (PCBs),and dioxins [2, 3]. Pesticides and PCBs were below detection levels. VOCs and SVOCs wereeither below detection levels, or if detected, were concluded to be due to laboratorycontamination. Concentrations of dioxins were below concentrations which would warrant aconsumption advisory. Metals concentrations, including mercury, were below levels of healthconcern.
Public Health Implications
Fishing along the shoreline of the site has been documented by the TNRCC (May 1996) andobserved by TDH (August 1998). The sample results indicated that ingestion of finfish andcrabs from Sabine Lake is not a public health concern. Therefore, TDH concluded thatconsumption of seafood from Sabine Lake poses no public health hazard due to contaminantsfrom the State Marine site.
ATSDR's Child Health Initiative
We recognize that the unique vulnerabilities of children demand special attention. Windows ofvulnerability (critical periods) exist during development, particularly during early gestation, butalso throughout pregnancy, infancy, childhood and adolescence ---- periods when toxicants maypermanently impair or alter structure and function [4]. Unique childhood vulnerabilities may bepresent because, at birth, many organs and body systems (including the lungs and the immune,endocrine, reproductive, and nervous systems) have not achieved structural or functionalmaturity. These organ systems continue to develop throughout childhood and adolescence. Children may exhibit differences in absorption, metabolism, storage, and excretion of toxicants,resulting in higher biologically-effective doses to target tissues. Depending on the affectedmedia, they also may be more exposed than adults because of behavior patterns specific tochildren. In an effort to account for children's unique vulnerabilities, and in accordance withATSDR's Child Health Initiative [5] and EPA's National Agenda to Protect Children's Healthfrom Environmental Threats [6], we used the potential exposure of children as a guide inassessing the potential public health implications of the contaminants.
- Results of sampling data indicate that contaminants from the State Marine site have notaccumulated in the fish and shellfish; therefore, ingestion of seafood caught from SabineLake, in the area of the State Marine site, does not pose a public health hazard.
Action Recommended
- None at this time.
- Agency for Toxic Substances and Disease Registry. Public Health Assessment StateMarine of Port Arthur. July 30, 1999.
- Texas Department of Health (TDH) Seafood Safety Division. Fish Tissue Sampling Data1970-1997.
- Agency for Toxic Substances and Disease Registry. Public Health Assessment PalmerBarge Line Co. Draft for Public Comment. November 1-30, 2001.
- US Environmental Protection Agency. 2000. Strategy for research on environmentalrisks to children. Washington, DC: US Environmental Protection Agency, Office ofResearch and Development. EPA/600/R-00/068, Section 1.2.
- Agency for Toxic Substances and Disease Registry (ATSDR). Child health initiative. Atlanta: US Department of Health and Human Services; 1995.
- US Environmental Protection Agency. The children's environmental health yearbook;1998.
Susan L. Prosperie, M.S., R.S.
Health Assessor
Environmental Epidemiology and Toxicology Division
John F. Villanacci, Ph.D.
Co-Director
Environmental Epidemiology and Toxicology Division
ATSDR REGIONAL REPRESENTATIVE
George Pettigrew, P.E.
Senior Regional representative
ATSDR - Region 6
ATSDR TECHNICAL PROJECT OFFICER
Alan W. Yarbrough
Environmental Health Scientist
Division of Health Assessment and Consultation
Superfund Site Assessment Branch
State Programs Section
This health consultation was prepared by the Texas Department of Health under a cooperativeagreement with the Agency for Toxic Substances and Disease Registry (ATSDR). It is inaccordance with approved methodology and procedures existing at the time the healthconsultation was initiated.
Alan W. Yarbrough
Technical Project Officer, SPS, SSAB, DHAC, ATSDR
The Division of Health Assessment and Consultation, ATSDR, has reviewed this healthconsultation and concurs with its findings.
Richard Gillig
Chief, Superfund Site Assessment Branch, DHAC, ATSDR
| Fin Fish Collected from Sabine Lake by TDH Seafood Safety Division January 1994 | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Constituent Analyzed | SAB 1-1 Southern Flounder | SAB 1-2 Black Drum | SA 1-3 Black Drum | SAB 1-4 Red Drum | SAB 1-5 Red Drum | SAB 1-6 Southern Flounder | SAB 1-7 Red Drum | SAB 1-8 Red Drum | SAB 1-9 Black Drum | SAB 1-10 Black Drum |
| Pesticide | nd | nd | nd | nd | nd | nd | nd | nd | nd | nd |
| PCBs | nd | nd | nd | nd | nd | nd | nd | nd | nd | nd |
| SVOCs (mg/kg) Bis 2(eh)p | nd | nd | nd | nd | nd | nd 1.2 | nd | nd | nd | nd |
| VOCs (µg/kg) acetone CS2 MC MEK | all nd except 2440 nd nd nd | all nd except 330 72 nd 135 | all nd except 99100 47 nd nd | all nd except 34900 23 nd nd | nd | all nd except 122 nd nd nd | all nd except 933 nd 38 nd | all nd except 780 nd 24 nd | all nd except 98 nd 38 nd | all nd except nd nd 78 nd |
| Metals (mg/kg) Arsenic Cadmium Copper Lead Mercury Zinc | <0.04 ---- <0.4 <0.4 0.114 2.90 | <0.04 ---- <0.4 <0.4 0.244 3.87 | <0.5 ---- <0.4 <0.4 0.107 3.42 | <0.04 ---- <0.39 <0.39 0.163 3.60 | 0.08 ---- <0.4 <0.4 0.137 3.60 | 0.023 0.513 <0.40 0.047 <0.070 3.1 | 0.038 <0.034 <0.40 <0.034 0.0742 3.5 | <0.014 0.177 <0.50 0.063 0.188 3.9 | 0.031 <0.039 <0.40 <0.039 0.186 2.9 | 0.038 0.162 <0.40 0.049 0.156 3.6 |
CS2-carbon disulfide; MC-methylene chloride; MEK-methylene choride
| Constituent Analyzed | SAB 1-1 Blue Crab | SAB 1-2 Blue Crab | SAB 1-3 Sheepshead | SAB 1-4 Blue Crab |
|---|---|---|---|---|
| Dioxin (ng/kg) 2378 TCDF 12378 PeCDF 23478 PeCDF 123478 HxCDF 123678 HxCDF 234678 HxCDF 123789 HxCDF 1234678 HpCDF 1234789 HpCDF 12346789 OCDF 2378 TCDD 12378 PeCDD 123478HxCDD 123678 HxCDD 123789 HxCDD 1234678 HpCDD 12346789 OCDD | 1 nd 0.19 nd nd nd nd nd nd nd 0.25 | |||
| Pesticide | nd | nd | nd | |
| PCBs | nd | nd | nd | |
| SVOCs (mg/kg) benzoic acid | nd -- | all nd except 0.4 | nd -- | |
| VOCs (µg/kg) acetone methylene chloride | all nd except 225 -- | all nd except 134 43 | all nd except 251 -- | |
| Metals (mg/kg) Arsenic Cadmium Copper Lead Mercury Zinc | 0.088 0.497 8.6 0.163 <0.049 35.3 | 0.017 0.430 <0.40 0.055 <0.074 2.9 | 0.048 0.355 8.8 <0.075 <0.072 31.6 |


