K. Delong, Kylie Palmer, A. Wagner, Mudith M Weerabaddana, N. Slowey, A. Herrmann, N. Duprey, A. Martínez-García, Jonathan Jung, I. Hajdas, N. Rose, S. Roberts, L. Roberts, A. Cundy, P. Gaca, J. Andrew Milton, Handong Yang, S. Turner, Chun‐Yuan Huang, Chuan‐Chou Shen, J. Zinke
{"title":"花园岸边的Siderastrea siderea珊瑚是人类世系列的候选全球边界层型剖面和点","authors":"K. Delong, Kylie Palmer, A. Wagner, Mudith M Weerabaddana, N. Slowey, A. Herrmann, N. Duprey, A. Martínez-García, Jonathan Jung, I. Hajdas, N. Rose, S. Roberts, L. Roberts, A. Cundy, P. Gaca, J. Andrew Milton, Handong Yang, S. Turner, Chun‐Yuan Huang, Chuan‐Chou Shen, J. Zinke","doi":"10.1177/20530196221147616","DOIUrl":null,"url":null,"abstract":"The proposed Anthropocene Global Boundary Stratotype Section and Point (GSSP) candidate site of West Flower Garden Bank (27.8762°N, 93.8147°W) is an open ocean location in the Gulf of Mexico with a submerged coral reef and few direct human impacts. Corals contain highly accurate and precise (<±1 year) internal chronologies, similar to tree rings, and their exoskeletons are formed of aragonite and can be preserved in the rock record. Here we present results from a large Siderastrea siderea coral (core 05WFGB3; 1755–2005 CE) sampled with annual and monthly resolutions that show clear markers of global and regional human impacts. Atmospheric nuclear bomb testing by-products (14C, 239+240Pu) have clear increases in this coral starting in 1957 for 14C and the first increase in 1956 for 239+240Pu (potential bases for the Anthropocene GSSP). Coral δ13C declined especially after 1956 consistent with the Suess effect resulting from the burning of fossil fuels. Coral skeletal δ15N starts to increase in 1963 corresponding with the increase in agricultural fertilizers. Coral Hg concentrations (1933–1980) loosely track fluctuations in industrial pollution and coral Ba/Ca increases from 1965–1983 when offshore oil operations expand after 1947. Coral temperature proxies contain the 20th-century global warming trend whereas coral growth declines during this interval.","PeriodicalId":74943,"journal":{"name":"The anthropocene review","volume":"10 1","pages":"225 - 250"},"PeriodicalIF":0.0000,"publicationDate":"2023-02-21","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"3","resultStr":"{\"title\":\"The Flower Garden Banks Siderastrea siderea coral as a candidate Global boundary Stratotype Section and Point for the Anthropocene series\",\"authors\":\"K. Delong, Kylie Palmer, A. Wagner, Mudith M Weerabaddana, N. Slowey, A. Herrmann, N. Duprey, A. Martínez-García, Jonathan Jung, I. Hajdas, N. Rose, S. Roberts, L. Roberts, A. Cundy, P. Gaca, J. Andrew Milton, Handong Yang, S. Turner, Chun‐Yuan Huang, Chuan‐Chou Shen, J. 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引用次数: 3
摘要
West Flower Garden Bank(27.8762°N,93.8147°W)拟建的人类世全球边界层型剖面和点(GSSP)候选地点是墨西哥湾的一个公海位置,珊瑚礁被淹没,几乎没有直接的人类影响。珊瑚礁含有高度准确和精确的(<±1 年)内部年代,类似于树木年轮,它们的外骨骼由霰石形成,可以保存在岩石记录中。在这里,我们展示了一个大型Siderastrea siderea珊瑚(核心05WFGB3;1755–2005 CE)以年度和月度分辨率采样,显示出全球和区域人类影响的明确标志。大气核弹试验副产物(14C,239+240Pu)在该珊瑚中的14C含量从1957年开始明显增加,239+240 Pu含量在1956年首次增加(人类世GSSP的潜在基础)。珊瑚δ13C下降,尤其是在1956年之后,这与化石燃料燃烧产生的苏伊士效应一致。1963年,随着农业肥料的增加,珊瑚骨骼δ15N开始增加。珊瑚汞浓度(1933年至1980年)大致跟踪工业污染的波动,珊瑚Ba/Ca在1965年至1983年期间增加,1947年后海上石油作业扩大。珊瑚温度指标包含了20世纪的全球变暖趋势,而珊瑚生长在这段时间内下降。
The Flower Garden Banks Siderastrea siderea coral as a candidate Global boundary Stratotype Section and Point for the Anthropocene series
The proposed Anthropocene Global Boundary Stratotype Section and Point (GSSP) candidate site of West Flower Garden Bank (27.8762°N, 93.8147°W) is an open ocean location in the Gulf of Mexico with a submerged coral reef and few direct human impacts. Corals contain highly accurate and precise (<±1 year) internal chronologies, similar to tree rings, and their exoskeletons are formed of aragonite and can be preserved in the rock record. Here we present results from a large Siderastrea siderea coral (core 05WFGB3; 1755–2005 CE) sampled with annual and monthly resolutions that show clear markers of global and regional human impacts. Atmospheric nuclear bomb testing by-products (14C, 239+240Pu) have clear increases in this coral starting in 1957 for 14C and the first increase in 1956 for 239+240Pu (potential bases for the Anthropocene GSSP). Coral δ13C declined especially after 1956 consistent with the Suess effect resulting from the burning of fossil fuels. Coral skeletal δ15N starts to increase in 1963 corresponding with the increase in agricultural fertilizers. Coral Hg concentrations (1933–1980) loosely track fluctuations in industrial pollution and coral Ba/Ca increases from 1965–1983 when offshore oil operations expand after 1947. Coral temperature proxies contain the 20th-century global warming trend whereas coral growth declines during this interval.