Jose L. Sericano

NOAA gulf of Mexico status and trends program: Trace organic contaminant distribution in sediments and oysters

Polynuclear aromatic hydrocarbons (PAH), chlorinated pesticides, and polychlorinated biphenyls (PCB) concentrations were determined in sediment and oysters to provide information on the current status of the concentration of these contaminants in Gulf of Mexico coastal areas removed from point sources of input. Coprostanol analyses of sediments showed that anthropogenic materials are associated with the sediments at all 153 stations sampled. The levels of contaminants encountered are low compared with areas of known contamination. Average PAH concentrations are nearly the same in oysters and sediments, although the molecular weight distribution is different. Average DDT and PCB concentrations are higher by a factor of 10 to 130 in oysters as compared to sediments. Continued sampling and analyses will allow for long-term trends in the concentrations of these contaminants to be determined.

Polybrominated diphenyl ether flame retardants in the U.S. marine environment: a review.

Polybrominated diphenyl ethers (PBDEs) are used as flame retardants in polymeric materials such as furnishing foam, rigid plastics and textiles. The U.S. has historically led the world production of these man-made chemicals and was responsible for about 50% of the total global demand in 2001. Paradoxically, scientific studies addressing sources, behavior and fate of PBDEs in the U.S. environment are limited when compared to those in Europe. This paper reviews the distribution of PBDEs in marine and estuarine matrices of the three U.S. coasts (Atlantic, Pacific and Gulf of Mexico) and Alaska. PBDEs are ubiquitous in all compartments including water, sediment and biota. Contamination is higher in urbanized regions such as the coast of California. In numerous cases, concentrations of PBDEs in U.S. marine matrices are among the highest in the world. Higher PBDE levels in the U.S. marine environment reflect that over 90% of the Penta-BDE global production has been utilized in the United States. BDEs 47, 99 and 100 typically dominate the composition of PBDEs in most samples and exhibit high concentrations in several matrices. BDEs 17, 28, 33, 49, 153, 154 and 155 are also of concern since they are known to be present in a minor proportion in the Penta-BDE products. BDEs 206, 207, 208 and 209 which occur in Deca-BDE products do not appear to accumulate in most marine organisms although they may be debrominated into more toxic congeners. There is still no regulation addressing PBDEs contamination in the U.S. aquatic environments. Thus, efforts to understand the cycling of PBDEs in the environment as well as toxic effects in organisms are needed to support the development of quality criteria. Some PBDE congeners fulfill the criteria to be recognized as persistent organic pollutants (POPs). The addition of PBDEs to the list of POPs established by the United Nations Stockholm Convention will be important in elevating environmental concerns regarding these chemicals to an appropriate level of awareness.

Long-term Bioaccumulation Monitoring with Transplanted Bivalves in the San Francisco Estuary

Abstract The California State Mussel Watch and the Regional Monitoring Program for Trace Substances have conducted biomonitoring for trace elements and organic contaminants in the San Francisco Estuary using transplanted bivalves (Mytilus californianus, Crassostrea gigas, and Corbicula fluminea). Significant declines (p

Human Contamination of the Marine Environment-Arthur Harbor and McMurdo Sound, Antarctica.

Polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCBs), pesticides, and trace metal concentrations in McMurdo Sound and Arthur Harbor, Antarctica, sediments and marine biota are reported. Biomarkers of contaminant exposure, biliary metabolites and EROD assays, were also measured. Hydrocarbon and trace metal contamination are generally limited to within hundreds of meters of human settlements. Local releases of fossil fuels, disposal of waste materials, and aging of ship and station structures contribute to contamination. High concentrations of PCBs were detected in sediments (250-4200 ng g{sup -1}) and organisms (up to 420 ng g{sup -1}) from Winter Quarters Bay (WQB). Trace metal and PAH sediment concentrations rarely exceed levels known to cause toxic effects in marine organisms, whereas PCBs in WQB often do. Biological responses to exposure include the formation of PAH metabolites and the inducement of the P4501A detoxification system in fish. Induction of EROD activity in in vitro rat hepatoma H4IIE cell bioassays by tissue extracts correlated with known levels of PCB contamination in invertebrate tissues. Local sources of contaminants greatly exceed those attributable to long-distance atmospheric transport. 31 refs., 4 figs.

Trace contaminant concentrations in the Kara Sea and its adjacent rivers, Russia.

Trace organic (chlorinated pesticides, PCBs, PAHs and dioxins/furans) and trace metal concentrations were measured in surficial sediment and biological tissues (i.e., worms, crustaceans, bivalve molluscs, and fish livers) collected from the Russian Arctic. Total DDT, chlordane, PCB and PAH concentrations ranged from ND to 1.2, ND to <0.1, ND to 1.5 and <20-810 ng g(-1), respectively, in a suite of 40 surficial sediment samples from the Kara Sea and the adjacent Ob and Yenisey Rivers. High sedimentary concentrations of contaminants were found in the lower part of the Yenisey River below the salt wedge. Total dioxins/furans were analysed in a subset of 20 sediment samples and ranged from 1.4 to 410 pg g(-1). The highest trace organic contaminant concentrations were found in organisms, particularly fish livers. Concentrations as high as 89 ng g(-1) chlordane; 1010 ng g(-1) total DDTs; 460 ng g(-1) total PCBs; and 1110 ng g(-1) total PAH, were detected. A subset of 11 tissue samples was analysed for dioxins and furans with total concentrations ranging from 12 to 61 pg g(-1). Concentrations of many trace organic and metal contaminants in the Kara Sea appear to originate from riverine sources and atmospheric transport from more temperate areas. Most organic contaminant concentrations in sediments were low; however, contaminants are being concentrated in organisms and may pose a health hazard for inhabitants of coastal villages.

Polynuclear Aromatic Hydrocarbons in American Oysters Crassostrea virginica from the Terminos Lagoon, Campeche, Mexico

Abstract The concentrations of polynuclear aromatic hydrocarbons in oyster tissues from one of the most productive shrimp-fishing and oyster-farming areas in the coastal Gulf of Mexico, the Terminos Lagoon, were measured to assess the impact that offshore crude oil production on the continental shelf of Campeche might have on local resources. Total PAH concentrations in oyster tissues ranged from 2470 to 42,500 ng/g during this six-month study. The predominance of low and medium molecular weight alkylated compounds over their parent compounds indicates the petrogenic source of these PAHs. The apparent correlation between the geographical distributions of the measured PAH concentrations and the distinctive circulation pattern into and inside the lagoon suggests that offshore oil activities are the source of these PAHs to local oysters. Although comparable, the concentrations reported in this study are on the high side of those reported earlier in samples from the same general area and from the northern coast of the Gulf of Mexico. This should be a cause for concern in a protected area where oysters are farmed for human consumption and should result in the implementation of monitoring programs.

Temporal and spatial patterns of anthropogenic disturbance at McMurdo Station, Antarctica

Human visitations to Antarctica have increased in recent decades, raising concerns about preserving the continents environmental quality. To understand the spatial and temporal patterns of anthropogenic disturbances at the largest scientific station in Antarctica, McMurdo Station, a long-term monitoring program has been implemented. Results from the first nine years (1999?2007) of monitoring are reported. Most physical disturbance of land surfaces occurred prior to 1970 during initial establishment of the station. Hydrocarbons from fuel and anthropogenic metals occur in patches of tens to hundreds of square meters in areas of fuel usage and storage. Most soil contaminant concentrations are not expected to elicit biological responses. Past disposal practices have contaminated marine sediments with polychlorinated biphenyls (PCBs), petroleum hydrocarbons, and metals in close proximity to the station that often exceed concentrations expected to elicit biological responses. Chemical contamination and organic enrichment reduced marine benthic ecological integrity within a few hundred meters offshore of the station. Contaminants were detected in marine benthic organisms confirming bioavailability and uptake. PCBs in sediments are similar to suspected source materials, indicating minimal microbial degradation decades after release. Anthropogenic disturbance of the marine environment is likely to persist for decades. A number of monitoring design elements, indicators and methodologies used in temperate climates were effective and provide guidance for monitoring programs elsewhere in Antarctica.

Chlorinated pesticides, polychlorinated biphenyls and polycyclic aromatic hydrocarbons in the fat tissue of seabirds from King George Island, Antarctica.

Persistent organic pollutants (POPs), such as chlorinated pesticides, polychlorinated biphenyls (PCBs) and polycyclic aromatic hydrocarbons (PAHs), have been detected worldwide, including in the Antarctic region. The Antarctic continent can no longer be considered pristine, as there has been a localized but considerable human impact on the region (UNEP, 2002). Local pollution caused by research stations, tourism and long-range transport account for the presence of these compounds in the biota (Risebrough and Carmignani, 1972; Lukowski,1983a,b; Montone et al., 2001b; Corsolini et al., 2002), atmosphere (Bidleman et al., 1993; Montone et al., 2005), water (Gupta et al., 1996; Bicego et al., 1996; Bicego et al., 2002) and sediment (Montone et al., 2001a; Martins et al., 2004; Curtosi et al., 2007) in Antarctica. Several organisms may be used to investigate local pollution. Birds have a number of advantages in this respect. The ecology and behavior of birds are particularly well understood and the background knowledge of their biology enhances their usefulness as biomonitors (Furness and Greenwood, 1993). Antarctica has over 40 species of nesting birds. Many are natives to this remote region of Earth (e.g., Adelie penguin, Antarctic petrel, Snow petrel) and others come to the Antarctic continent and sub Antarctic islands to breed and then migrate to lower latitudes the rest of the year (e.g., Southern fulmar, Cape petrel, South Polar skua). As long-range migratory and top predators, skuas can accumulate high concentrations of anthropogenic contaminants as they forage over large areas. In contrast, penguins show greater fidelity to the Antarctic and sub Antarctic region. This baseline report presents the concentration of selected chlorinated pesticides, polychlorinated biphenyls and polycyclic aromatic hydrocarbons (PAHs) measured in archived fat samples from Brown skuas (Catharacta antarctica, n = 6) and three species of penguins [Adelie (Pygoscelis adeliae; n = 2), Chinstrap (Pygoscelis antarctica; n = 2) and Gentoo (Pygoscelis papua; n = 3)] captured in the vicinity of a Brazilian and a Polish Antarctic Station on King George Island. Opportunistic samples of Antarctic tern (Sterna vittata; n = 2), Snowy sheathbill (Chionis alba; n = 1) and Blue-eyed shag (Phalacrocorax atriceps; n = 1) were also analyzed. Subcutaneous fat samples from these birds were collected near the Comandante Ferraz (62 050S–58 230W; Brazil) andH. Arctowski (62 090S–58 280W; Poland) Antarctic Stations, located in Admiralty Bay during the summer of 1997–1998 (Fig. 1), wrapped in aluminium foil and immediately frozen at 15 C. The analytical procedure followed that described by MacLeod et al. (1985). Briefly, after the addition of anhydrous Na2SO4, approximately 0.5 g of wet tissue was extracted withmethylene chloride using a tissumizer. Prior to extraction, 4,40-dibromooctafluorbiphenyl (DBOFB), 2,20,4,50,6-pentachlorobiphenyl (PCB 103); 2,20,3,30,4, 5,50,6-octachlorobiphenyl (PCB 198); d8-naphthalene, d10-acenaphthene, d10-phenanthrene, d12-chrysene and d12-perylene were added to samples, blanks and reference material (SRM 1945 from the National Institute of Standards and Technology) as surrogates for chlorinated pesticides, PCBs and PAHs, respectively. Extracts were initially cleaned by using partially deactivated silica:alumina column chromatography eluted with a 1:1 mixture of pentane and methylene chloride. The fraction was further purified by high-performance liquid chromatography (HPLC) to remove excess lipids and finally concentrated to a volume of 0.5 mL in hexane. Internal standards (2,4,5,6-tetrachlorometaxylene (TCMX) for chlorinated pesticides and PCBs; and d10-fluorene and d10-benzo[a]pyrene) for PAHs) were added prior to gas chromatographic analysis. Chlorinated pesticides and PCBs were analyzed through gas chromatography using an electron capture detector (ECD). PAHs were quantitatively analyzed through a gas chromatograph coupled to a mass spectrometer (GC–MS) in a selected ion mode (SIM). Table 1 displays mean concentrations (±standard deviation) on a lipid weight (lw) basis for HCHs, HCB, DDTs, chlordanes, dieldrin, mirex, total PCBs and total PAHs in the seabirds studied. Except for HCHs and HCB, the concentrations of most chlorinated pesticides were significantly higher in skuas than in the other species of birds (Fig. 2). In contrast, no significant differences in the concentrations of these compounds were found among the three species of penguins studied (Fig. 3). Lukowski (1983a) found a similar profile of DDTs in adipose tissue of the same three species of penguins collected in the proximity of the Arctowski Station in Admiralty Bay, but at significantly lower concentrations (0.548 ± 0.314, 0.340 ± 0.238, 0364 ± 0.155 ng g 1 w for P. adeliae, P. antarctica and P. papua, respectively). Average concentrations of oxychlordane, dieldrin, mirex and p,p0-DDE in skuas (408 ± 169, 254 ± 158, 2210 ± 1590 and 5840 ± 4020 ng g 1 lw, respectively) were approximately 15, 10, 25 and 30 times higher than in penguins. Lukowski (1983b) also found DDT contents approximately 15 times higher in skua than in penguins. This difference demon-

Accumulation and depuration of organic contaminants by the American oyster (Crassostrea virginica)

Abstract Oysters and other bivalves are widely used to assess the levels of environmental contamination; however, very little actual field calibration of bivalves has been done. The purpose of this research, therefore, has been to evaluate the uptake and depuration of selected PCBs and PAHs in transplanted American oysters, Crassostrea virginica , under field conditions in Galveston Bay, Texas. Transplanted oyster were found to bioaccumulate contaminants and reach concentrations nearly equal to those of indigenous oysters for PAHs and low molecular weight PCBs within 30–48 days. In contrast, high molecular weight PCBs did not reach equivalent concentrations. When returned to a clean environment, oysters significantly depurated PAHs and low molecular weight PCBs. There were, however, differences in depuration rates when newly contaminated oysters were compared to chronically contaminated oysters. Oysters are useful tools in biomonitoring studies but have their limitations. Transplant studies help to establish these limitations on the use of oysters as sentinel organisms to avoid misleading interpretation of the oyster contaminant concentrations.

Parasites of sentinel bivalves in the NOAA status and trends program: distribution and relationship to contaminant body burden

The National Status and Trends Mussel Watch data for 1997 were used to compare the distribution of parasites between sentinel bivalves of the East, West, Gulf and Great Lakes coasts of the USA and to assess the relationship of parasitism to contaminant body burden. Overall, five patterns dominated the geographic distribution of the parasite fauna. (1) Certain parasites, such as Nematopsis, were principally associated with oysters from the southeast and Gulf coasts. (2) Discounting Nematopsis, oysters and mussels did not differ significantly in total parasite infection intensity. (3) West coast mussel populations were always lower in infection intensity than East coast mussels and rarely showed anything but a sporadic pattern of infection. (4) East coast mussels typically had a focus of infection in the Boston Harbor region. (5) With the exception of Nematopsis, mussels on the West coast, Mytilus edulis and Mytilus californianus, did not differ significantly in their parasite fauna. The geographic distributions of most parasites and disease-causing organisms varied independently. Any two parasites rarely co-occurred predictably over wide areas and never on more than one coast. Certain contaminants were correlated with certain parasites on one coast but not the other or in one bivalve type but not another. Statistics that emphasized infection intensity found significant relationships between parasitism and contaminant body burden most often in East and Gulf coast oysters and West coast mussels and, in most cases, higher body burdens were associated with lower infection intensities. Statistics that emphasized prevalence also identified significant relationships most often in East and Gulf coast oysters and West coast mussels. In contrast to infection intensity, most significant results occurred because parasites were observed more often in locales characterized by higher contaminant body burdens. In no case was a parasite/ contaminant pair significant for both infection intensity and prevalence.