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Response of saltmarsh fungi to the presence of mercury and polychlorinated biphenyls at a Superfund site
Ascomycetous fungi are the major decomposers of standing-decaying smooth cordgrass (Spartina alterniflora), the major grass of saltmarshes of the southeastern U.S.A. In Brunswick, Georgia, smooth-cordgrass marshes have received a potentially severe chemical insult at the USEPA LCP Superfund Site [du...
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Published in: | Mycologia 1998-09, Vol.90 (5), p.777-784 |
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description | Ascomycetous fungi are the major decomposers of standing-decaying smooth cordgrass (Spartina alterniflora), the major grass of saltmarshes of the southeastern U.S.A. In Brunswick, Georgia, smooth-cordgrass marshes have received a potentially severe chemical insult at the USEPA LCP Superfund Site [dumping of mercury and polychlorinated biphenyls (PCB)]. We have examined levels of living-fungal standing crop (as ergosterol) and fungal sexual productivity (rate of ascospore expulsion) in naturally decaying leaf blades of smooth cordgrass at the LCP site, at a nearby, moderately polluted site, and at a pristine site in Georgia. Although toxicant levels in sediments at the LCP site are very high (total Hg, to 71 μg g
-1
dry sediment; methylmercury, to 190 ng g
-1
; PCB, to 156 μg g
-1
), living-fungal biomass was higher at the LCP site (about 890 μg ergosterol g
-1
organic mass of decaying-leaf system, for dead blades on wholly dead shoots) than at the nearby moderately polluted site (about 630 μg g
-1
) or the pristine site (about 590 μg g
-1
). Ascospore release was also higher at LCP than at the pristine site. Only methylmercury at tens of ng g
-1
sediment gave any evidence of negative impact upon levels of living-fungal crop. We speculate that urban/industrial nitrogen input was responsible for the higher biomass of fungi at the Brunswick sites, and that either the toxicants and/or the hypothesized N input were responsible for the major difference in cordgrass-fungal species composition found (replacement of Phaeosphaeria spartinicola by Phaeosphaeria halima). |
doi_str_mv | 10.1080/00275514.1998.12026970 |
format | article |
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-1
dry sediment; methylmercury, to 190 ng g
-1
; PCB, to 156 μg g
-1
), living-fungal biomass was higher at the LCP site (about 890 μg ergosterol g
-1
organic mass of decaying-leaf system, for dead blades on wholly dead shoots) than at the nearby moderately polluted site (about 630 μg g
-1
) or the pristine site (about 590 μg g
-1
). Ascospore release was also higher at LCP than at the pristine site. Only methylmercury at tens of ng g
-1
sediment gave any evidence of negative impact upon levels of living-fungal crop. We speculate that urban/industrial nitrogen input was responsible for the higher biomass of fungi at the Brunswick sites, and that either the toxicants and/or the hypothesized N input were responsible for the major difference in cordgrass-fungal species composition found (replacement of Phaeosphaeria spartinicola by Phaeosphaeria halima).</description><identifier>ISSN: 0027-5514</identifier><identifier>EISSN: 1557-2536</identifier><identifier>DOI: 10.1080/00275514.1998.12026970</identifier><language>eng</language><publisher>Taylor & Francis</publisher><subject>Ascomycetes ; Ascomycota ; ascospore-expulsion rate ; ASCOSPORES ; BIOSYNTHESIS ; DEGRADATION ; DOTHIDEALES ; Ecology ; ERGOSTEROL ; fungal biomass ; FUNGAL SPORES ; Fungi ; GEORGIA (USA) ; LCP Chemical ; LEAVES ; Ligules ; MEASUREMENT ; MERCURY ; methylmercury ; Nitrogen ; Phaeosphaeria ; PHAEOSPHAERIA HALIMA ; PHAEOSPHAERIA SPARTINICOLA ; POLLUTION ; POLYCHLORINATED BIPHENYLS ; Salt marshes ; SALTMARSHES ; Sediments ; SEXUAL REPRODUCTION ; SPARTINA ALTERNIFLORA ; SPORE DISPERSAL ; SPORES ; Superfund sites ; Toxicity</subject><ispartof>Mycologia, 1998-09, Vol.90 (5), p.777-784</ispartof><rights>1998 Taylor and Francis Group, LLC 1998</rights><rights>Copyright 1998 The New York Botanical Garden</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c2405-6252d36122e04690a1923c290a9513a0de3055f522795bad5cc715ea3fbbe5e3</citedby><cites>FETCH-LOGICAL-c2405-6252d36122e04690a1923c290a9513a0de3055f522795bad5cc715ea3fbbe5e3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/3761318$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/3761318$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,27924,27925,58238,58471</link.rule.ids></links><search><creatorcontrib>Newell, S.Y. (University of Georgia, Sapelo Island, GA.)</creatorcontrib><creatorcontrib>Wall, V.D</creatorcontrib><title>Response of saltmarsh fungi to the presence of mercury and polychlorinated biphenyls at a Superfund site</title><title>Mycologia</title><description>Ascomycetous fungi are the major decomposers of standing-decaying smooth cordgrass (Spartina alterniflora), the major grass of saltmarshes of the southeastern U.S.A. In Brunswick, Georgia, smooth-cordgrass marshes have received a potentially severe chemical insult at the USEPA LCP Superfund Site [dumping of mercury and polychlorinated biphenyls (PCB)]. We have examined levels of living-fungal standing crop (as ergosterol) and fungal sexual productivity (rate of ascospore expulsion) in naturally decaying leaf blades of smooth cordgrass at the LCP site, at a nearby, moderately polluted site, and at a pristine site in Georgia. Although toxicant levels in sediments at the LCP site are very high (total Hg, to 71 μg g
-1
dry sediment; methylmercury, to 190 ng g
-1
; PCB, to 156 μg g
-1
), living-fungal biomass was higher at the LCP site (about 890 μg ergosterol g
-1
organic mass of decaying-leaf system, for dead blades on wholly dead shoots) than at the nearby moderately polluted site (about 630 μg g
-1
) or the pristine site (about 590 μg g
-1
). Ascospore release was also higher at LCP than at the pristine site. Only methylmercury at tens of ng g
-1
sediment gave any evidence of negative impact upon levels of living-fungal crop. We speculate that urban/industrial nitrogen input was responsible for the higher biomass of fungi at the Brunswick sites, and that either the toxicants and/or the hypothesized N input were responsible for the major difference in cordgrass-fungal species composition found (replacement of Phaeosphaeria spartinicola by Phaeosphaeria halima).</description><subject>Ascomycetes</subject><subject>Ascomycota</subject><subject>ascospore-expulsion rate</subject><subject>ASCOSPORES</subject><subject>BIOSYNTHESIS</subject><subject>DEGRADATION</subject><subject>DOTHIDEALES</subject><subject>Ecology</subject><subject>ERGOSTEROL</subject><subject>fungal biomass</subject><subject>FUNGAL SPORES</subject><subject>Fungi</subject><subject>GEORGIA (USA)</subject><subject>LCP Chemical</subject><subject>LEAVES</subject><subject>Ligules</subject><subject>MEASUREMENT</subject><subject>MERCURY</subject><subject>methylmercury</subject><subject>Nitrogen</subject><subject>Phaeosphaeria</subject><subject>PHAEOSPHAERIA HALIMA</subject><subject>PHAEOSPHAERIA SPARTINICOLA</subject><subject>POLLUTION</subject><subject>POLYCHLORINATED BIPHENYLS</subject><subject>Salt marshes</subject><subject>SALTMARSHES</subject><subject>Sediments</subject><subject>SEXUAL REPRODUCTION</subject><subject>SPARTINA ALTERNIFLORA</subject><subject>SPORE DISPERSAL</subject><subject>SPORES</subject><subject>Superfund sites</subject><subject>Toxicity</subject><issn>0027-5514</issn><issn>1557-2536</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1998</creationdate><recordtype>article</recordtype><recordid>eNqFkMFu1DAQhi0EEkvhEUA-IG5ZxnacbI5VRQGpUiVazpbXGTepsnbwOEJ5e7yEStx68ljz_b_lj7EPAvYCDvAZQLZai3ovuu6wFxJk07Xwgu2E1m0ltWpest0Zqs7Ua_aG6LFcyxZ2bPiBNMdAyKPnZKd8sokG7pfwMPIceR6QzwkJg_uLnDC5Ja3chp7PcVrdMMU0Bpux58dxHjCsE3GbueV3y4ypFPWcxoxv2StvJ8J3_84Ldn_95f7qW3Vz-_X71eVN5WQNumqklr1qhJQIddOBFZ1UTpah00JZ6FGB1l5L2Xb6aHvtXCs0WuWPR9SoLtinrXZO8deClM1pJIfTZAPGhYwotOpAF7DZQJciUUJv5jSWz69GgDl7NU9ezdmrefJagh-34CPlmP5PSQWtUW0jlDgU7HLDxuBjOtnfMU29yXYtvnyywY1k1LNPvd86vI3GPqQS-XlXkBYOtYZa_QFaLZQw</recordid><startdate>19980901</startdate><enddate>19980901</enddate><creator>Newell, S.Y. (University of Georgia, Sapelo Island, GA.)</creator><creator>Wall, V.D</creator><general>Taylor & Francis</general><general>New York Botanical Garden</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7U7</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>M7N</scope></search><sort><creationdate>19980901</creationdate><title>Response of saltmarsh fungi to the presence of mercury and polychlorinated biphenyls at a Superfund site</title><author>Newell, S.Y. (University of Georgia, Sapelo Island, GA.) ; Wall, V.D</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c2405-6252d36122e04690a1923c290a9513a0de3055f522795bad5cc715ea3fbbe5e3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1998</creationdate><topic>Ascomycetes</topic><topic>Ascomycota</topic><topic>ascospore-expulsion rate</topic><topic>ASCOSPORES</topic><topic>BIOSYNTHESIS</topic><topic>DEGRADATION</topic><topic>DOTHIDEALES</topic><topic>Ecology</topic><topic>ERGOSTEROL</topic><topic>fungal biomass</topic><topic>FUNGAL SPORES</topic><topic>Fungi</topic><topic>GEORGIA (USA)</topic><topic>LCP Chemical</topic><topic>LEAVES</topic><topic>Ligules</topic><topic>MEASUREMENT</topic><topic>MERCURY</topic><topic>methylmercury</topic><topic>Nitrogen</topic><topic>Phaeosphaeria</topic><topic>PHAEOSPHAERIA HALIMA</topic><topic>PHAEOSPHAERIA SPARTINICOLA</topic><topic>POLLUTION</topic><topic>POLYCHLORINATED BIPHENYLS</topic><topic>Salt marshes</topic><topic>SALTMARSHES</topic><topic>Sediments</topic><topic>SEXUAL REPRODUCTION</topic><topic>SPARTINA ALTERNIFLORA</topic><topic>SPORE DISPERSAL</topic><topic>SPORES</topic><topic>Superfund sites</topic><topic>Toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Newell, S.Y. (University of Georgia, Sapelo Island, GA.)</creatorcontrib><creatorcontrib>Wall, V.D</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><jtitle>Mycologia</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Newell, S.Y. (University of Georgia, Sapelo Island, GA.)</au><au>Wall, V.D</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Response of saltmarsh fungi to the presence of mercury and polychlorinated biphenyls at a Superfund site</atitle><jtitle>Mycologia</jtitle><date>1998-09-01</date><risdate>1998</risdate><volume>90</volume><issue>5</issue><spage>777</spage><epage>784</epage><pages>777-784</pages><issn>0027-5514</issn><eissn>1557-2536</eissn><abstract>Ascomycetous fungi are the major decomposers of standing-decaying smooth cordgrass (Spartina alterniflora), the major grass of saltmarshes of the southeastern U.S.A. In Brunswick, Georgia, smooth-cordgrass marshes have received a potentially severe chemical insult at the USEPA LCP Superfund Site [dumping of mercury and polychlorinated biphenyls (PCB)]. We have examined levels of living-fungal standing crop (as ergosterol) and fungal sexual productivity (rate of ascospore expulsion) in naturally decaying leaf blades of smooth cordgrass at the LCP site, at a nearby, moderately polluted site, and at a pristine site in Georgia. Although toxicant levels in sediments at the LCP site are very high (total Hg, to 71 μg g
-1
dry sediment; methylmercury, to 190 ng g
-1
; PCB, to 156 μg g
-1
), living-fungal biomass was higher at the LCP site (about 890 μg ergosterol g
-1
organic mass of decaying-leaf system, for dead blades on wholly dead shoots) than at the nearby moderately polluted site (about 630 μg g
-1
) or the pristine site (about 590 μg g
-1
). Ascospore release was also higher at LCP than at the pristine site. Only methylmercury at tens of ng g
-1
sediment gave any evidence of negative impact upon levels of living-fungal crop. We speculate that urban/industrial nitrogen input was responsible for the higher biomass of fungi at the Brunswick sites, and that either the toxicants and/or the hypothesized N input were responsible for the major difference in cordgrass-fungal species composition found (replacement of Phaeosphaeria spartinicola by Phaeosphaeria halima).</abstract><pub>Taylor & Francis</pub><doi>10.1080/00275514.1998.12026970</doi><tpages>8</tpages></addata></record> |
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ispartof | Mycologia, 1998-09, Vol.90 (5), p.777-784 |
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language | eng |
recordid | cdi_crossref_primary_10_1080_00275514_1998_12026970 |
source | JSTOR Archival Journals and Primary Sources Collection; Taylor and Francis Science and Technology Collection |
subjects | Ascomycetes Ascomycota ascospore-expulsion rate ASCOSPORES BIOSYNTHESIS DEGRADATION DOTHIDEALES Ecology ERGOSTEROL fungal biomass FUNGAL SPORES Fungi GEORGIA (USA) LCP Chemical LEAVES Ligules MEASUREMENT MERCURY methylmercury Nitrogen Phaeosphaeria PHAEOSPHAERIA HALIMA PHAEOSPHAERIA SPARTINICOLA POLLUTION POLYCHLORINATED BIPHENYLS Salt marshes SALTMARSHES Sediments SEXUAL REPRODUCTION SPARTINA ALTERNIFLORA SPORE DISPERSAL SPORES Superfund sites Toxicity |
title | Response of saltmarsh fungi to the presence of mercury and polychlorinated biphenyls at a Superfund site |
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