模拟海洋条件下分散的Forties原油和阿拉斯加北坡原油在微观环境中的生物降解

Sarah J Macnaughton , Richard Swannell , Fabien Daniel , Louise Bristow
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引用次数: 55

摘要

对于公海的石油泄漏,操作经验表明,传统的应对技术,如机械回收,往往只能在重大泄漏中去除一小部分石油,最近路易斯安那州密西西比河泄漏事件是一个例外。抛光工艺。牛。7(2002)155]。相比之下,使用分散剂可以通过将石油分散到水柱中,从而使相当一部分石油从海面上去除。人们认为,石油一旦分散,就可以在水柱中生物降解,尽管关于生物降解的机制和速度的信息很少。在模拟海洋条件下,对Forties原油和阿拉斯加北坡(ANS)原油的分散、微生物定植和生物降解进行了两项研究。使用Forties原油的研究持续了27天,并在模拟英国周围水域河口和海岸条件(15°C,营养物为1 mg N-NO3/l)的条件下进行,而ANS研究模拟了威廉王子湾典型的低温条件(8°C),进行了35天。两项研究的结果都表明,微生物在4天后会在油滴中定植,并形成由油、细菌、原生动物和线虫组成的中性浮力簇。到第16天,这些簇的大小增加了,它们沉入了微观世界的底部,可能是由于油的生物降解导致浮力下降,然而,正烷烃的生物降解仅在Forties研究中得到证实。在生物作用被抑制的对照组中,没有发现油的定植或生物降解。油降解菌在所有生物活性微生物中均有增殖。在没有分散剂的情况下,尽管微生物的生长速度和种群规模比用Forties观察到的要大,但ANS的定殖开始被推迟。这一差异反映了ANS在8°C时比Forties原油在15°C时看到的液滴数量更多。尽管这些研究存在不止一个变量的差异,使比较变得复杂,但研究结果表明,扩散(自然或化学)改变了石油对海洋环境的影响,可能对石油泄漏事件中与分散剂使用政策相关的石油泄漏管理产生重要影响。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Biodegradation of Dispersed Forties Crude and Alaskan North Slope Oils in Microcosms Under Simulated Marine Conditions

For oil spills in the open sea, operational experience has found that conventional response techniques, such as mechanical recovery, tend to remove only a small fraction of oil during major spills, a recent exception being the Mississippi River spill in Louisiana [Spill Sci. Technol. Bull. 7 (2002) 155]. By contrast, the use of dispersants can enable significant fractions of oil to be removed from the sea surface by dispersing the oil into the water column. It is thought that once dispersed the oil can biodegrade in the water column, although there is little information on the mechanism and rate of biodegradation. Two studies were undertaken on dispersion, microbial colonisation and biodegradation of Forties crude and Alaskan North Slope (ANS) oils under simulated marine conditions. The study using the Forties crude lasted 27 days and was carried out in conditions simulating estuarine and coastal conditions in waters around the UK (15 °C and in the presence of nutrients, 1 mg N-NO3/l), while the ANS study simulated low temperature conditions typical of Prince William Sound (8 °C) and took place over 35 days. The results of both studies demonstrated microbial colonisation of oil droplets after 4 days, and the formation of neutrally buoyant clusters consisting of oil, bacteria, protozoa and nematodes. By day 16, the size of the clusters increased and they sank to the bottom of the microcosms, presumably because of a decrease in buoyancy due to oil biodegradation, however biodegradation of n-alkanes was confirmed only in the Forties study. No colonisation or biodegradation of oil was noted in the controls in which biological action was inhibited. Oil degrading bacteria proliferated in all biologically active microcosms. Without dispersant, the onset of colonisation was delayed, although microbial growth rates and population size in ANS were greater than observed with the Forties. This difference reflected the greater droplet number seen with ANS at 8 °C than with Forties crude at 15 °C. Although these studies differed by more than one variable, complicating comparison, the findings suggest that dispersion (natural or chemical) changes the impact of the oil on the marine environment, potentially having important implications for management of oil spills in relation to the policy of dispersant use in an oil spill event.

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