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Persistent Toxic Chemicals of Human Health Concern in Fish from San Francisco Bay and the Sacramento River, CA

J.A. Davis, M.D. May, and S.E. Wainwright, San Francisco Estuary Institute
R. Fairey, C. Roberts, G. Ichikawa, Moss Landing Marine Laboratories, Moss Landing, CA
R. Tjeerdema, M. Stoelting, J. Becker, Institute of Marine Sciences, University of California, Santa Cruz, CA
M. Petreas, M. Mok, M. McKinney, Hazardous Materials Laboratory, Cal/EPA, Berkeley, CA
K. Taberski, San Francisco Bay Regional Water Board, Cal/EPA, Oakland, CA

ABSTRACT

As a result of a 1994 San Francisco Bay Regional Water Board study, the Office of Environmental Health Hazard Assessment issued an interim health advisory for people consuming fish from San Francisco Bay. This interim advisory remains in effect. In 1997 the Regional Monitoring Program for Trace Substances in the San Francisco Estuary (RMP) and the Sacramento River Watershed Program (SRWP) began monitoring fish contamination in the Bay and on the Sacramento River (River).

RMP sampling in 1997 targeted seven species that are frequently caught and eaten by Bay fishers and seven popular fishing areas in the Bay (Figure 1). Persistent toxic chemicals in Bay fish remained at concentrations of potential human health concern. Mercury exceeded a human health screening value in 44 of 84 Bay samples (Figure 2). All collected samples of leopard shark and striped bass exceeded the mercury screening value. White catfish from the Sacramento River also had relatively high mercury concentrations. Rainbow trout from the northern Sacramento River had the lowest mercury concentrations among the species sampled.

Concentrations of PCBs and other trace organics were highest in white croaker and shiner surfperch, the two species with the highest fat content in their muscle tissue. PCBs exceeded the screening value in 51 of 72 Bay samples (Figure 3). All of the white croaker and shiner surfperch samples exceeded the screening value for PCBs. Dieldrin, DDT (Figure 4), and chlordane had lower numbers of Bay samples above screening values: 27 of 72 for dieldrin, 16 of 72 for DDTs, and 11 of 72 for chlordanes. Rainbow trout from the northern Sacramento River watershed had relatively low concentrations of organic contaminants. White catfish from the Sacramento River had relatively low lipid content but moderately high wet weight concentrations.

Dioxins and dibenzofuran TEQs in all seven Bay samples analyzed exceeded the screening value of 0.15 ng/g wet weight. Dioxin-like PCBs accounted for 83% of the overall dioxin-like potency in these fish samples.

Significant variation in contaminant concentrations among Bay locations was observed. Oakland Harbor had significantly elevated wet weight concentrations of mercury, PCBs, DDTs, and chlordanes. Length-adjusted mercury concentrations were relatively high at Oakland Harbor and S.F. Waterfront. Lipid normalized concentrations of PCBs, DDTs, and chlordanes, and dieldrin were elevated at Oakland Harbor.

Mercury concentrations in the Bay in 1997 were not significantly different from concentrations in 1994. Statistically significant declines in concentrations from 1994 to 1997 were observed for PCBs, DDTs, chlordanes, and dieldrin. Dioxin ITEQs also showed a statistically significant decline from 1994 to 1997. Continued monitoring will be required to establish whether the declines observed are real indications of declining masses of contaminants in the Bay or due to variation in other factors.

Removal of skin from white croaker fillets reduced concentrations of PCBs, dieldrin, DDT, chlordane, and dioxins by 33 to 49%.

Inroduction

As a result of a 1994 San Francisco Bay Regional Water Board study, the Office of Environmental Health Hazard Assessment issued an interim health advisory for people consuming fish from San Francisco Bay. This interim advisory remains in effect. In 1997 the Regional Monitoring Program for Trace Substances in the San Francisco Estuary (RMP) and the Sacramento River Watershed Program (SRWP) began monitoring fish contamination in the Bay and on the Sacramento River (River). In 1998 sampling was performed for a one-time study of fish tissue contamination in the Delta, funded primarily through the Deltakeeper. Data from these three efforts can be pieced together to provide a broad overview of fish tissue contamination in much of the watershed of the San Francisco Estuary.

The primary objectives of all three of these efforts have been:

1) to determine whether persistent toxic chemicals occur in fish that are being used as human food at concentrations of potential human health concern, and

2) to provide data that are useful in tracking long-term trends and evaluating the effectiveness of management efforts to improve water quality.

Species examined in the studies
 
California Halibut
image source: PCF
Jacksmelt
image source: PCF
Leopard Shark
image source: PCF
Shiner Surfperch
image source: TNF
Striped Bass
image source: FWF
White Croaker
image source: PCF
White Sturgeon
image source: PCF
White Catfish
image source: FWF
Rainbow Trout
image source: FWF

Sampling Design: San Francisco Bay

  • Regional Monitoring Program
  • Most recent sampling in 1997
  • Seven popular species:
    • striped bass,
    • California halibut,
    • leopard shark,
    • white sturgeon,
    • white croaker,
    • shiner surfperch, and
    • jacksmelt
  • Seven popular fishing locations throughout the Bay (Figure 1)
  • Sampling every three years
  • Mercury, PCBs, dioxins, and organochlorine pesticides
  • Includes replication and special studies
  • Data available from 1994 and 1997

Conclusion: San Francisco Bay

  • Concentrations of mercury, PCBs, DDT, chlordane, dieldrin, and dioxins exceeded screening values, indicating potential health concerns for Bay fishers
  • Fish from Oakland Harbor had elevated concentrations of mercury, PCBs, DDT, chlordane, and dieldrin
  • Mercury concentrations in 1997 were not significantly different from concentrations in 1994. Lipid-weight concentrations of PCBs, DDT, chlordane, dieldrin, and dioxins were lower in 1997 than in 1994. Continued monitoring will be required to establish whether the apparent decreases observed are indicative of long-term trends or short-term fluctuations due to other processes
  • No change in consumption advice for halibut, leopard shark, shiner surfperch, striped bass, white croaker, and white sturgeon
  • Jacksmelt findings are being evaluated: PCB concentrations may be of concern
  • Substantially lower concentrations of trace organics were measured in white croaker fillets with the skin removed. Concentrations of PCBs, DDTs, chlordanes, dieldrin, and dioxin ITEQs were reduced by 30- 50%

Sampling Design: Sacramento River

  • Sacramento River Watershed Program Agreement X 999610-01-0 with U.S. EPA
  • Sampling began in 1997
  • Main focus on two popular species: white catfish and largemouth bass
  • 13 fishing locations from Shasta Lake to northern Delta (Figure 5)
  • Mercury, PCBs, and organochlorine pesticides - Minimal replication - Data from 1997

Sampling Design: Delta

  • Delta Fish Study
  • Funds from Deltakeeper and Central Valley Regional Water Quality Control Board
  • One time study in 1998
  • Two popular species: white catfish and largemouth bass
  • 18 fishing locations, including locations on the San Joaquin River south of the Delta (Figure 6)
  • Mercury, selenium, arsenic, PCBs, and organochlorine pesticides
  • Minimal replication
  • PRELIMINARY data from 1998, mercury only

Conclusions: Delta and River

  • Mercury concentrations in white catfish are similar to those for which advice was issued in the Bay
  • PCB concentrations in rainbow trout and white catfish are at the low end of the range observed for Bay fish
  • Need more samples for evaluating need for consumption advice

Figures and Tables

Figure 1. RMP Fish Sampling Sites
 
Figure 2. Mercury Concentration in Fish Tissue (ug/g wet)
 
Figure 3. PCB Concentration in Fish Tissue (ug/g wet)
 
Figure 4. DDT Concentration in Fish Tissue (ug/g wet)
 
Figure 5. Sacramento River Watershed Program Sampling Sites
Figure 6. Delta Fish Study Sampling Sites


For further information please contact:
Jay Davis
San Francisco Estuary Institute
2nd Floor

7770 Pardee Lane

Oakland, California 94621
phone (510) 430-0801
fax (510) 430-0885
e-mail jay@sfei.org

Related Document: (file size = 770k)
Contaminant Concentrations in Fish from San Francisco Bay 1997, May 1999

 

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