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美国得克萨斯州加尔维斯顿湾多环芳烃(PAHs)的循环和归宿。

Polycyclic aromatic hydrocarbons (PAHs) cycling and fates in Galveston Bay, Texas, USA.

机构信息

Department of Marine Biology, Texas A&M University at Galveston, Galveston, Texas, United States of America.

Department of Chemistry, Prairie View A&M University, Prairie View, Texas, United States of America.

出版信息

PLoS One. 2020 Dec 28;15(12):e0243734. doi: 10.1371/journal.pone.0243734. eCollection 2020.

DOI:10.1371/journal.pone.0243734
PMID:33370322
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7769252/
Abstract

The cycling and fate of polycyclic aromatic hydrocarbons (PAHs) is not well understood in estuarine systems. It is critical now more than ever given the increased ecosystem pressures on these critical coastal habitats. A budget of PAHs and cycling has been created for Galveston Bay (Texas) in the northwestern Gulf of Mexico, an estuary surrounded by 30-50% of the US capacity of oil refineries and chemical industry. We estimate that approximately 3 to 4 mt per year of pyrogenic PAHs are introduced to Galveston Bay via gaseous exchange from the atmosphere (ca. 2 mt/year) in addition to numerous spills of petrogenic PAHs from oil and gas operations (ca. 1.0 to 1.9 mt/year). PAHs are cycled through and stored in the biota, and ca. 20 to 30% of the total (0.8 to 1.5 mt per year) are estimated to be buried in the sediments. Oysters concentrate PAHs to levels above their surroundings (water and sediments) and contain substantially greater concentrations than other fish catch (shrimp, blue crabs and fin fish). Smaller organisms (infaunal invertebrates, phytoplankton and zooplankton) might also retain a significant fraction of the total, but direct evidence for this is lacking. The amount of PAHs delivered to humans in seafood, based on reported landings, is trivially small compared to the total inputs, sediment accumulation and other possible fates (metabolic remineralization, export in tides, etc.), which remain poorly known. The generally higher concentrations in biota from Galveston Bay compared to other coastal habitats can be attributed to both intermittent spills of gas and oil and the bay's close proximity to high production of pyrogenic PAHs within the urban industrial complex of the city of Houston as well as periodic flood events that transport PAHs from land surfaces to the Bay.

摘要

多环芳烃 (PAHs) 在河口系统中的迁移和归宿尚未得到充分认识。考虑到这些关键沿海生境所承受的生态系统压力不断增加,现在比以往任何时候都更加重要。本文为墨西哥湾西北部的加尔维斯顿湾(德克萨斯州)创建了一个 PAHs 预算和循环模型,该湾被 30-50%的美国炼油厂和化工业所环绕。我们估计,通过大气气体交换,每年约有 3 到 4 公吨的人为源 PAHs 被输入加尔维斯顿湾(约 2 公吨/年),此外,石油和天然气作业还会有大量的天然源 PAHs 泄漏(约 1.0 到 1.9 公吨/年)。PAHs 在生物群中循环和储存,估计有 20-30%(每年 0.8-1.5 公吨)的总 PAHs 被埋藏在沉积物中。牡蛎会将 PAHs 浓缩到比其周围环境(水和沉积物)更高的水平,并含有比其他鱼类捕捞(虾、蓝蟹和鳍鱼)更高浓度的 PAHs。较小的生物体(底栖无脊椎动物、浮游植物和浮游动物)也可能保留总 PAHs 的很大一部分,但缺乏直接证据。根据报告的上岸量,海鲜中输送给人类的 PAHs 量与总输入量、沉积物积累和其他可能的归宿(代谢再矿化、潮汐输出等)相比微不足道,这些仍然知之甚少。与其他沿海生境相比,加尔维斯顿湾生物群中 PAHs 的浓度普遍较高,这归因于间歇性的油气泄漏以及海湾与休斯顿城市工业综合体内部的人为源 PAHs 高产量以及将 PAHs 从陆地表面输送到海湾的周期性洪水事件密切相关。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/ec8d087acfba/pone.0243734.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/e27f871b7b2c/pone.0243734.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/75a087800b95/pone.0243734.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/a62bb054a8c1/pone.0243734.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/4670a33caa9c/pone.0243734.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/fee169c4d703/pone.0243734.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/b7e6356f57e8/pone.0243734.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/ec8d087acfba/pone.0243734.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/e27f871b7b2c/pone.0243734.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/75a087800b95/pone.0243734.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/a62bb054a8c1/pone.0243734.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/4670a33caa9c/pone.0243734.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/fee169c4d703/pone.0243734.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/b7e6356f57e8/pone.0243734.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2219/7769252/ec8d087acfba/pone.0243734.g007.jpg

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