Weston Donald P, Jarman Walter M, Cabana Gilbert, Bacon Corinne E, Jacobson Lisa A
University of California, Department of Integrative Biology, Berkeley 94720-3140, USA.
Environ Toxicol Chem. 2002 Oct;21(10):2216-24.
Lauritzen Canal, a portion of San Francisco Bay near Richmond, California, USA, was heavily contaminated with dichlorodiphenyltrichloroethane (DDT) and dieldrin as a result of releases from a pesticide-formulating firm. In 1996 and 1997, 82,000 m3 of contaminated sediment was removed from the canal by dredging. This study evaluated the success of the dredging based largely on body burdens of DDT and its metabolites (sigmaDDT) in resident biota, with some data on sediment- and water-contaminant levels and sediment toxicity testing. Sediment disturbance during dredging introduced a pulse of sigmaDDT into the Lauritzen Canal ecosystem, and body burdens of fish and invertebrates increased 2- to 76-fold, depending on the species. Approximately 1 1/2 years after remediation, 11 of 14 indicators showed contamination comparable with or worse than the contamination that existed prior to dredging. Monitoring of mussels up to four years postdredging suggests some modest improvement, although the sigmaDDT body burden of canal mussels remained far above the norm for San Francisco Bay. The elevated sigmaDDT body burdens in biota that persisted for years after remediation reflect recent exposure and are not merely a result of slow metabolic elimination of the sigmaDDT pulse associated with dredging. Sediment sigmaDDT concentrations were low immediately after dredging, but within months, the canal bottom became covered with a veneer of fine sediment as contaminated as that that had been removed. The source of this material has not been conclusively established, but we suspect it came from slumping and erosion from the flanks of the canal beneath docks and around pilings where dredging was not done. In retrospect, either capping in place or more thorough dredging may have been more successful in reducing pesticide exposure of the biota, although there were difficulties associated with both alternatives.
劳里岑运河位于美国加利福尼亚州里士满附近的旧金山湾区域,因一家农药配制公司的排放而受到二氯二苯三氯乙烷(滴滴涕)和狄氏剂的严重污染。1996年和1997年,通过疏浚从运河中清除了82000立方米受污染的沉积物。本研究主要基于当地生物群中滴滴涕及其代谢物(总滴滴涕)的体内负荷来评估疏浚的成效,同时也有一些关于沉积物和水体污染物水平以及沉积物毒性测试的数据。疏浚过程中的沉积物扰动向劳里岑运河生态系统中引入了一股总滴滴涕脉冲,鱼类和无脊椎动物的体内负荷增加了2至76倍,具体倍数因物种而异。修复后大约1.5年,14项指标中有11项显示出的污染程度与疏浚前相当或更严重。对贻贝长达疏浚后四年的监测表明有一些适度的改善,尽管运河贻贝的总滴滴涕体内负荷仍远高于旧金山湾的正常水平。修复后数年生物群中持续存在的总滴滴涕体内负荷升高反映了近期的暴露情况,而不仅仅是与疏浚相关的总滴滴涕脉冲代谢消除缓慢的结果。疏浚后沉积物中的总滴滴涕浓度立即降低,但在数月内,运河底部就被一层与被清除的沉积物一样受污染的细沉积物覆盖。这种物质的来源尚未最终确定,但我们怀疑它来自未进行疏浚的码头下方和桩柱周围运河两侧的坍塌和侵蚀。回顾过去,就地覆盖或更彻底的疏浚在减少生物群接触农药方面可能会更成功,尽管这两种选择都存在困难。