加拿大油砂地区河流的污染物负荷与工业和自然资源有关。迄今为止,生物监测研究还不能明确评估与这一发展有关的潜在环境影响。作为联合艾伯塔省-加拿大油砂监测计划的一部分,我们旨在评估人为活动和自然沥青地质条件对阿萨巴斯卡河下游底栖大型无脊椎动物组合的累积影响。我们检查了大型无脊椎动物与环境相关因素之间的关联,例如营养素,离子,金属,多环芳族化合物和总悬浮固体。研究设计包括可开采沥青矿床之内和之外,活跃采矿和开采区之内和之外,市政污水流出物上方和下方的场地。我们预计观察到河流的生态状况与天然沥青和油砂活动的暴露之间存在负相关关系。但是,水和沉积物中的污染物浓度远低于已知的毒性阈值,暴露于油砂开采活动场所的底栖无脊椎动物集合似乎比来自采矿或天然沥青的污染物更受MSE养分的影响。尽管在油砂活动激烈的区域内的站点显示出轻微的环境压力迹象,但组装模式与MSE营养物质富集的关联更强,而不是扩散来自天然沥青或油砂开采的污染物。浓缩可能会增加消费者可获得的食物资源,从而有可能掩盖消费者对污染物的毒性反应。目前的法规禁止将油砂污染物直接释放到水道中,大气中的大气污染物和弥散性粉尘的扩散是主要的污染物进入淡水的途径。当达到尾矿池的储存能力时,如果河流接受提议的直接释放油砂工艺用水的提议,则这种养分污染模式可能会改变。需要进行有针对性的因果研究,以更好地评估系统中养分和污染物暴露的累积相互作用和生态效应的后果。如果河流接收到建议直接释放的油砂工艺用水,则这种营养物污染模式可能会改变。需要进行有针对性的因果研究,以更好地评估系统中养分和污染物暴露的累积相互作用和生态效应的后果。如果河流接收到建议直接释放的油砂工艺用水,则这种营养物污染模式可能会改变。需要进行有针对性的因果研究,以更好地评估系统中养分和污染物暴露的累积相互作用和生态效应的后果。
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Ecological causal assessment of benthic condition in the oil sands region, Athabasca River, Canada
Contaminant loads to rivers of the Canadian oil sands region are linked to industrial and natural sources. To date, biomonitoring studies have been unable to unequivocally assess potential environmental impacts associated with this development. As part of the Joint Alberta-Canada Oil Sands Monitoring initiative, we aimed to assess cumulative effects of anthropogenic activities and exposure to natural bitumen geology on benthic macroinvertebrate assemblages in the lower Athabasca River. We examined associations among macroinvertebrates and environmental correlates, such as nutrients, ions, metals, polycyclic aromatic compounds, and total suspended solids. The study design included sites within and outside the mineable bitumen deposits, within and outside of the active mining and extraction area, and above and below municipal sewage effluents. We predicted observing a negative association between ecological condition of the river and exposure to natural bitumen and oil sands activity. However, contaminant concentrations in water and sediment were far below known toxicity thresholds, and benthic invertebrate assemblages in sites exposed to oil sands mining activities appeared more affected by nutrient enrichment from the MSE than contaminants from mining or natural bitumen. Although sites within the area of intense oil sands activity showed signs of mild environmental stress, assemblage pattern was more strongly associated with MSE nutrient enrichment than to diffuse contamination from either natural bitumen or oil sands mining. Enrichment likely increases food resources available to consumers, thereby potentially masking toxic responses of consumers to contaminants. Current regulations prohibit the direct release of oil sands contaminants to waterways, with diffuse atmospheric deposition of aerial emissions and fugitive dust the main contaminant pathways to freshwaters. As the storage capacity of tailings ponds is reached, this nutrient-contaminant pattern could change if the river receives the proposed direct release of oil sands process water. Focused investigation-of-cause studies are required to better assess the consequences of cumulative interactions and ecological effects of nutrients and contaminant exposure in this system.