Azetsu-Scott Kumiko, Yeats Phil, Wohlgeschaffen Gary, Dalziel John, Niven Sherry, Lee Kenneth
Ocean Sciences Division, Department of Fisheries and Oceans, Bedford Institute of Oceanography, P.O. Box 1006, Dartmouth, Nova Scotia, Canada B2Y 4A2.
Mar Environ Res. 2007 Mar;63(2):146-67. doi: 10.1016/j.marenvres.2006.08.001. Epub 2006 Sep 6.
Produced water undergoes changes in its physical chemistry including precipitation of heavy metals after being discharged and mixed with ambient seawater. Potential impacts of the precipitation of heavy metals on their transport and toxicity were studied using samples from offshore oil production sites on the Scotian Shelf off eastern Canada. Concentrations of aluminum, cadmium, chromium, cobalt, copper, iron, lead, manganese, nickel and zinc were measured in total, particulate and dissolved fractions together with Microtox tests for assessment of toxicity. Heavy metals in produced water were transformed from dissolved to particulate phase in a period of hours under oxygenated conditions, and aggregated to larger particles that settle rapidly (>100 m/day) over a few days. In addition, there was production of buoyant particles comprised of heavy metal precipitates sequestered onto oil droplets that were transported to the surface. The particulate fraction was generally more toxic than the dissolved fraction. This was evident at the mixing interface between produced water and seawater where elevated particulate and toxicity levels were observed. Laboratory studies suggest an increase in the toxicity of discharged produced water over time. Time-series experiments showed a sustained toxic response for more than a week following the oxidation of freshly discharged produced water that initially elicited little or no toxic response in the Microtox test. Chemical processes identified in this study, namely precipitation of heavy metals and consequent settling and rising fluxes of particles, will influence the toxicity, the fate and the transport of potential contaminants in the produced water. Therefore, these processes need to be considered in assessment of the environmental impact associated with offshore oil and gas operations.
采出水中的物理化学性质会发生变化,包括排放并与周围海水混合后重金属的沉淀。利用加拿大东部斯科舍大陆架近海石油生产场地的样本,研究了重金属沉淀对其迁移和毒性的潜在影响。测量了铝、镉、铬、钴、铜、铁、铅、锰、镍和锌在总、颗粒和溶解部分中的浓度,并进行了微毒性测试以评估毒性。在有氧条件下,采出水中的重金属在数小时内从溶解相转变为颗粒相,并在几天内聚集成更大的颗粒,这些颗粒沉降迅速(>100米/天)。此外,还产生了由重金属沉淀物附着在油滴上形成的浮力颗粒,这些颗粒被输送到海面。颗粒部分通常比溶解部分毒性更大。这在采出水与海水的混合界面处很明显,在那里观察到颗粒和毒性水平升高。实验室研究表明,排放的采出水中的毒性会随时间增加。时间序列实验表明,新鲜排放的采出水中的氧化作用最初在微毒性测试中引起很少或没有毒性反应,但在氧化后一周多的时间里仍有持续的毒性反应。本研究中确定的化学过程,即重金属沉淀以及随之而来的颗粒沉降和上升通量,将影响采出水中潜在污染物的毒性、归宿和迁移。因此,在评估与海上油气作业相关的环境影响时,需要考虑这些过程。