30年后潮间带沉积物中残余燃油C的组成和毒性

K Lee , R.C Prince , C.W Greer , K.G Doe , J.E.H Wilson , S.E Cobanli , G.D Wohlgeschaffen , D Alroumi , T King , G.H Tremblay
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引用次数: 28

摘要

1970年,在Arrow油轮搁浅后,大约2000立方米的Bunker C原油影响了新斯科舍省300公里的海岸线。只有10%的受污染海岸进行了清理,其余的都留给自然净化。为了确定这次溢油事件对环境的长期影响,我们分别于1993年、1997年和2000年在黑鸭湾的一个隐蔽泻湖回收了沉积物和间水样本。这个被严重污染的地点被故意留下,让它自己恢复。目视观察和化学分析证实,大量的风化货油仍然存在于该地点的沉积物中。然而,对底栖无脊椎动物丰度的直接观察表明,自然过程减少了剩余油的影响。为了证实这一假设,我们对黑鸭湾的沉积物和间隙水样进行了全面的生物试验和化学分析。沉积物中残油对冬比目鱼肝脏CYP1A蛋白水平和混合功能加氧酶(MFO)诱导的影响有限。Microtox固相试验(费氏弧菌)未检测出毒性。在8种受污染的沉积物中,有4种经片足类生存试验检测出显著的沉积物毒性。微生物毒素100%试验(费氏弧菌)和类针鼹受精试验(彩色Lytechinus pictus)均认为间质水样无毒。沉积物洗脱液在草虾胚胎-幼虫毒性(GSELTOX)试验(Palaemonetes pugio)中也被发现是无毒的。这一污染地点的恢复是由于自然过程介导的生物降解和沉积物中石油的物理去除。矿化实验表明,所有测试沉积物都具有十六烷、八烷和萘的降解能力,而化学分析证实,阿罗组的Bunker C油经历了大量的生物降解。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Composition and Toxicity of Residual Bunker C Fuel Oil in Intertidal Sediments After 30 Years

In 1970, approximately 2000 m3 of Bunker C crude oil impacted 300 km of Nova Scotia’s coastline following the grounding of the tanker Arrow. Only 10% of the contaminated coast was subjected to cleanup, the remainder was left to cleanse naturally. To determine the long-term environmental impact of residual oil from this spill event, samples of sediment and interstitial water were recovered in 1993, 1997 and 2000 from a sheltered lagoon in Black Duck Cove. This heavily oiled site was intentionally left to recover on its own. Visual observations and chemical analysis confirmed that substantial quantities of the weathered cargo oil were still present within the sediments at this site. However, direct observations of benthic invertebrate abundance suggest that natural processes have reduced the impacts of the residual oil. To confirm this hypothesis, sediment and interstitial water samples from Black Duck Cove were assessed with a comprehensive set of biotests and chemical assays.

Residual oil in the sediments had limited effect on hepatic CYP1A protein levels and mixed function oxygenase (MFO) induction in winter flounder (Pleuronectes americanus). No toxicity was detected with the Microtox solid phase test (Vibrio fischeri). Significant sediment toxicity was detected by the amphipod survival test (Eohaustorius estuarius) in four out of the eight contaminated sediments. Interstitial water samples were deemed non-toxic by the Microtox 100% test (Vibrio fischeri) and the echinoid fertilization test (Lytechinus pictus). Sediment elutriates were also found to be non-toxic in the grass shrimp embryo-larval toxicity (GSELTOX) test (Palaemonetes pugio).

Recovery at this contaminated site is attributed to natural processes that mediated biodegradation and physical removal of oil from the sediments. In support of the latter mechanism, mineralization experiments showed that all test sediments had the capacity for hexadecane, octacosane and naphthalene degradation, while chemical analysis confirmed that the Bunker C oil from the Arrow had undergone substantial biodegradation.

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