Lagauzère S, Boyer P, Stora G, Bonzom J-M
Laboratoire de Radioécologie et d'Ecotoxicologie, Institut de Radioprotection et de Sûreté Nucléaire (IRSN), DEI/SECRE, Cadarache bât. 186, BP 3, 13115 Saint-Paul-lez-Durance Cedex, France.
Chemosphere. 2009 Jul;76(3):324-34. doi: 10.1016/j.chemosphere.2009.03.062. Epub 2009 Apr 28.
Freshwater sediments represent a compartment for accumulation of toxic substances, notably of metallic pollutants such as uranium. However, they also constitute a privileged habitat for many benthic macro-invertebrate species with important roles in the functioning of these ecosystems, particularly through their bioturbation activities. Uranium accumulation in sediments can thus have harmful effects on these organisms (e.g., developmental delay, malformations, mortality). The present study aimed to evaluate the consequences of these effects on the bioturbation activity of Chironomus riparius larvae and Tubifex tubifex worms. These two species, which are widespread in freshwater ecosystems, are characteristic of two different modes of bioturbation: bioirrigation and upward bioconveying, respectively. By quantifying the burial and redistribution of fluorescent particulate tracers (microspheres), sediment reworking induced by these macro-invertebrates was measured after 12d of exposure. Biodiffusion D(b) and bioadvection W rates, as well as several other parameters, were estimated to assess and compare the bioturbation activity of the two species, separately and in combination, between uncontaminated and uranium-spiked sediments. The results reveal that C. riparius larvae were more sensitive to uranium, but their bioturbation activity, even under uncontaminated conditions, had little effect on sediment reworking. Particle mixing was mainly induced by T. tubifex worms, which were only affected by uranium at high concentrations in the sediment. Finally, bioturbation by T. tubifex led to a high degree of uranium release from sediment to the overlying water, which highlights the crucial role of this mostly dominant species on uranium biogeochemical cycles at concentrations existing in naturally contaminated sites.
淡水沉积物是有毒物质的蓄积场所,尤其是铀等金属污染物。然而,它们也是许多底栖大型无脊椎动物物种的优先栖息地,这些物种在这些生态系统的功能中发挥着重要作用,特别是通过它们的生物扰动活动。沉积物中的铀积累因此可能对这些生物产生有害影响(例如发育延迟、畸形、死亡)。本研究旨在评估这些影响对摇蚊幼虫和颤蚓的生物扰动活动的后果。这两个物种在淡水生态系统中广泛分布,分别代表两种不同的生物扰动模式:生物灌溉和向上生物输送。通过量化荧光颗粒示踪剂(微球)的埋藏和再分布,在暴露12天后测量了这些大型无脊椎动物引起的沉积物重塑。估计了生物扩散系数D(b)和生物平流速率W以及其他几个参数,以评估和比较这两个物种在未受污染和添加铀的沉积物中单独和组合时的生物扰动活动。结果表明,摇蚊幼虫对铀更敏感,但其生物扰动活动即使在未受污染的条件下对沉积物重塑的影响也很小。颗粒混合主要由颤蚓引起,颤蚓仅在沉积物中高浓度铀的情况下受到影响。最后,颤蚓的生物扰动导致沉积物中大量的铀释放到上覆水中,这突出了这种最主要的物种在自然污染场地中现有浓度下对铀生物地球化学循环的关键作用。