Metal Speciation and Bioavailability in Contaminated Estuary Sediments, Alameda Naval Air Station, California

Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy (XAS) to evaluate metal speciation and ecological hazard of contaminated sediments from the Seaplane Lagoon, Naval Air Station Alameda (CA)....

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Published inEnvironmental science & technology Vol. 34; no. 17; pp. 3665 - 3673
Main Authors O'Day, Peggy A, Carroll, Susan A, Randall, Simon, Martinelli, Roger E, Anderson, Susan L, Jelinski, John, Knezovich, John P
Format Journal Article
LanguageEnglish
Published Washington, DC American Chemical Society 01.09.2000
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Abstract Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy (XAS) to evaluate metal speciation and ecological hazard of contaminated sediments from the Seaplane Lagoon, Naval Air Station Alameda (CA). This site is characterized by moderate to low toxicity in surface sediments and by metal concentrations in sediments and porewaters that increase with depth. Standard 1-h ΣSEM/AVS measurements for surface sediments were compared with time-series (0.25−24 h) measurements of metal and sulfide release from sediments at 30 cm. Results show that AVS is rapidly and completely evolved after 1 h, but metal extraction continues with time and is not complete after 24 h. Sediment−water interface tests of invertebrate toxicity using sand dollar embryos (D. excentricus) and adult amphipods (E. estuarius) exposed to intact cores showed no to low toxicity in surface sediments. In sediments from 30- and 60-cm depth, high toxicity in several replicates was attributed to factors other than metal concentrations, such as high dissolved ammonia or low dissolved oxygen concentrations. Metal speciation and bonding determined from XAS show that cadmium (100%), zinc (≈80%), and manganese (≈50−70%) are associated with monosulfide phases in the sediments. The remaining fraction of zinc and manganese and all of the chromium and lead are ligated by oxygen atoms, indicating association with oxide, carbonate, or silicate minerals. Iron is present in the sediments in two fractions, as Fe(II) in the sulfide phase pyrite and as oxygen-ligated octahedral iron, probably associated with clay minerals. Bulk chemical measurements of porewaters and sediments, and speciation information from XAS, suggest that AVS could be accounted for by volatilization of porewater sulfide. Our results indicate that metals are removed from porewaters by formation of monosulfide phases only for cadmium and partially for zinc and manganese but not for lead or chromium, even though these are reduced, anoxic sediments typical of a restricted marine estuary environment. Comparison of geochemical, spectroscopic, and biological data provides new insight for the interpretation of ΣSEM/AVS measurements and points out the need for synergistic biological/geochemical tests for determining potential ecological hazard.
AbstractList Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy (XAS) to evaluate metal speciation and ecological hazard of contaminated sediments from the Seaplane Lagoon, Naval Air Station Alameda (CA). This site is characterized by moderate to low toxicity in surface sediments and by metal concentrations in sediments and porewaters that increase with depth.
Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy (XAS) to evaluate metal speciation and ecological hazard of contaminated sediments from the Seaplane Lagoon, Naval Air Station Alameda (CA). This site is characterized by moderate to low toxicity in surface sediments and by metal concentrations in sediments and porewaters that increase with depth. Standard 1-h ΣSEM/AVS measurements for surface sediments were compared with time-series (0.25−24 h) measurements of metal and sulfide release from sediments at 30 cm. Results show that AVS is rapidly and completely evolved after 1 h, but metal extraction continues with time and is not complete after 24 h. Sediment−water interface tests of invertebrate toxicity using sand dollar embryos (D. excentricus) and adult amphipods (E. estuarius) exposed to intact cores showed no to low toxicity in surface sediments. In sediments from 30- and 60-cm depth, high toxicity in several replicates was attributed to factors other than metal concentrations, such as high dissolved ammonia or low dissolved oxygen concentrations. Metal speciation and bonding determined from XAS show that cadmium (100%), zinc (≈80%), and manganese (≈50−70%) are associated with monosulfide phases in the sediments. The remaining fraction of zinc and manganese and all of the chromium and lead are ligated by oxygen atoms, indicating association with oxide, carbonate, or silicate minerals. Iron is present in the sediments in two fractions, as Fe(II) in the sulfide phase pyrite and as oxygen-ligated octahedral iron, probably associated with clay minerals. Bulk chemical measurements of porewaters and sediments, and speciation information from XAS, suggest that AVS could be accounted for by volatilization of porewater sulfide. Our results indicate that metals are removed from porewaters by formation of monosulfide phases only for cadmium and partially for zinc and manganese but not for lead or chromium, even though these are reduced, anoxic sediments typical of a restricted marine estuary environment. Comparison of geochemical, spectroscopic, and biological data provides new insight for the interpretation of ΣSEM/AVS measurements and points out the need for synergistic biological/geochemical tests for determining potential ecological hazard.
Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy (XAS) to evaluate metal speciation and ecological hazard of contaminated sediments from the Seaplane Lagoon, Naval Air Station Alameda (CA). This site is characterized by moderate to low toxicity in surface sediments and by metal concentrations in sediments and porewaters that increase with depth. Standard 1-h capital sigma SEM/AVS measurements for surface sediments were compared with time-series (0.25-24 h) measurements of metal and sulfide release from sediments at 30 cm. Results show that AVS is rapidly and completely evolved after 1 h, but metal extraction continues with time and is not complete after 24 h. Sediment-water interface tests of invertebrate toxicity using sand dollar embryos (D. excentricus) and adult amphipods (E. estuarius) exposed to intact cores showed no to low toxicity in surface sediments. In sediments from 30- and 60-cm depth, high toxicity in several replicates was attributed to factors other than metal concentrations, such as high dissolved ammonia or low dissolved oxygen concentrations. Metal speciation and bonding determined from XAS show that cadmium (100%), zinc ( approximately 80%), and manganese ( approximately 50-70%) are associated with monosulfide phases in the sediments. The remaining fraction of zinc and manganese and all of the chromium and lead are ligated by oxygen atoms, indicating association with oxide, carbonate, or silicate minerals. Iron is present in the sediments in two fractions, as Fe(II) in the sulfide phase pyrite and as oxygen-ligated octahedral iron, probably associated with clay minerals. Bulk chemical measurements of porewaters and sediments, and speciation information from XAS, suggest that AVS could be accounted for by volatilization of porewater sulfide. Our results indicate that metals are removed from porewaters by formation of monosulfide phases only for cadmium and partially for zinc and manganese but not for lead or chromium, even though these are reduced, anoxic sediments typical of a restricted marine estuary environment. Comparison of geochemical, spectroscopic, and biological data provides new insight for the interpretation of capital sigma SEM/AVS measurements and points out the need for synergistic biological/geochemical tests for determining potential ecological hazard.
Author Martinelli, Roger E
Anderson, Susan L
Carroll, Susan A
Knezovich, John P
Randall, Simon
Jelinski, John
O'Day, Peggy A
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Issue 17
Keywords Sediment water interaction
Chemical association
XANES spectrometry
Ecotoxicology
Echinodermata
Toxicity
Estuaries
Bioavailability
Sediments
EXAFS spectrometry
Amphipoda
Heavy metal
Crustacea
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Snippet Measurements of simultaneously extracted metals (SEM), acid volatile sulfide (AVS), and invertebrate toxicity were combined with X-ray absorption spectroscopy...
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SubjectTerms Airports
Animal, plant and microbial ecology
Applied ecology
Applied sciences
Biological and medical sciences
Biological and physicochemical properties of pollutants. Interaction in the soil
Contamination
Earth sciences
Earth, ocean, space
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on protozoa and invertebrates
Engineering and environment geology. Geothermics
Environmental impact
Exact sciences and technology
Fundamental and applied biological sciences. Psychology
Metals
Military base closures
Pollution
Pollution, environment geology
Sediments
Soil and sediments pollution
USA, California, Alameda Naval Air Station
Title Metal Speciation and Bioavailability in Contaminated Estuary Sediments, Alameda Naval Air Station, California
URI http://dx.doi.org/10.1021/es9913030
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Volume 34
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