El Khalil Hicham, El Hamiani Ouafae, Bitton Gabriel, Ouazzani Naaila, Boularbah Ali
Faculté des Sciences et Techniques Guéliz, Département de Biologie, Laboratoire Aliments, Environnement et Santé, Université Cadi Ayyad, Boulevard Abdelkrim Khattabi, BP 549, 40 000 Marrakech, Morocco.
Environ Monit Assess. 2008 Jan;136(1-3):147-60. doi: 10.1007/s10661-007-9671-9. Epub 2007 Mar 21.
The aim of the present work is the assessment of metal toxicity in runoff, in their contaminated soils and in the groundwater sampled from two mining areas in the region of Marrakech using a microbial bioassay MetPLATE. This bioassay is based on the specific inhibition of the beta-galactosidase enzyme of a mutant strain of Escherichia coli, by the metallic pollutants. The stream waters from all sampling stations in the two mines were all very toxic and displayed percent enzyme inhibition exceeding 87% except SWA4 and SWB1 stations in mine C. Their high concentrations of copper (Cu) and zinc (Zn) confirm the acute toxicity shown by MetPLATE. The pH of stream waters from mine B and C varied between 2.1 and 6.2 and was probably responsible for metal mobilization, suggesting a problem of acid mine drainage in these mining areas. The bioassay MetPLATE was also applied to mine tailings and to soils contaminated by the acidic waters. The results show that the high toxicity of these soils and tailings was mainly due to the relatively concentration of soluble Zn and Cu. The use of MetPLATE in groundwater toxicity testing shows that, most of the samples exhibited low metal toxicity (2.7-45.5% inhibition) except GW3 of the mine B (95.3% inhibition during the wet season and 82.9% inhibition during the dry season). This high toxicity is attributed to the higher than usual concentrations of Cu (189 microg Cu l(-1)) and Zn (1505 microg Zn l(-1)). These results show the potential risk of the contamination of different ecosystems situated to the vicinity of these two metalliferous sites. The general trend observed was an increase in metal toxicity measured by the MetPLATE with increasing total and mobile metal concentrations in the studied matrices. Therefore, the MetPLATE bioassay is a reliable and fast bioassay to estimate the metals toxicity in the aquatic and solids samples.
本研究的目的是使用微生物生物测定法MetPLATE评估马拉喀什地区两个矿区径流、受污染土壤及地下水中的金属毒性。该生物测定法基于金属污染物对大肠杆菌突变株β-半乳糖苷酶的特异性抑制作用。两个矿区所有采样点的溪流水均具有很高的毒性,酶抑制率超过87%,但矿区C的SWA4和SWB1站点除外。其高浓度的铜(Cu)和锌(Zn)证实了MetPLATE所显示的急性毒性。矿区B和C的溪流水pH值在2.1至6.2之间变化,这可能是金属迁移的原因,表明这些矿区存在酸性矿山排水问题。MetPLATE生物测定法也应用于尾矿和受酸性水污染的土壤。结果表明,这些土壤和尾矿的高毒性主要归因于可溶性锌和铜的相对浓度。在地下水毒性测试中使用MetPLATE表明,除矿区B的GW3(雨季抑制率为95.3%,旱季抑制率为82.9%)外,大多数样品表现出较低的金属毒性(抑制率为2.7 - 45.5%)。这种高毒性归因于高于正常浓度的铜(189微克/升铜)和锌(1505微克/升锌)。这些结果表明这两个含金属矿区附近不同生态系统存在污染的潜在风险。观察到的总体趋势是,通过MetPLATE测定的金属毒性随着研究基质中总金属和可移动金属浓度的增加而增加。因此,MetPLATE生物测定法是一种可靠且快速的生物测定法,可用于评估水生和固体样品中的金属毒性。