Demuynck Sylvain, Succiu Iuliana Rosalia, Grumiaux Fabien, Douay Francis, Leprêtre Alain
Université Lille Nord de France, Lille, France; Equipe Ecologie Numérique et Ecotoxicologie, Laboratoire Génie Civil et géo-Environnement (LGCgE), Lille Nord de France EA 4515, bâtiment SN3, Cité Scientifique, F-59655 Villeneuve d'Ascq, Cedex, France.
Université Lille Nord de France, Lille, France; Equipe Ecologie Numérique et Ecotoxicologie, Laboratoire Génie Civil et géo-Environnement (LGCgE), Lille Nord de France EA 4515, bâtiment SN3, Cité Scientifique, F-59655 Villeneuve d'Ascq, Cedex, France.
Ecotoxicol Environ Saf. 2014 Sep;107:170-7. doi: 10.1016/j.ecoenv.2014.05.011. Epub 2014 Jun 18.
The earthworm Eisenia fetida avoidance behaviour test was used to assess the quality recovery of metal-contaminated soils from lands submitted for 10 years to remediation. Soils were from plots located in the surroundings of a former lead smelter plant of Northern France. Metal concentrations in the soils ranged from 93 to 1231, 56 to 1424, 0.3 to 20 and 15 to 45.5mg metal/kg dry soil for Pb, Zn, Cd and Cu, respectively. Several former agricultural plots were treated either by a single phytostabilisation process involving the plantation of a tree mix or by fly ash aided-phytostabilisation. Silico-aluminous or sulfo-calcic ashes used were ploughed up to a 25- to 30-cm soil depth at a rate of 23.3kg/m(2) (i.e., 6 percent W/W). E. fetida was shown to avoid significantly the 10 years ash-treated soils whose habitat function has to be considered as limited. This avoidance would relate to a change of the texture of soils induced by the addition of ashes and consisting in an increased level of fine silts together with a decreased level of clays. By contrast, afforested metal-contaminated soils appeared for E. fetida as more attractive than unplanted ones. Regarding the influence of the metal contamination of the soils on E. fetida, none of the soils tested even the highest contaminated one was significantly avoided by worms. This lack of reaction would result from the low bioavailability of the metals in the soils tested. At the lights of our results and those previously published on both these ashes and these ash-treated soils, the usefulness of these soil treatments is discussed.
采用赤子爱胜蚓回避行为试验来评估经过10年修复的金属污染土壤的质量恢复情况。土壤取自法国北部一家 former铅冶炼厂周边的地块。土壤中铅、锌、镉和铜的金属浓度分别为93至1231、56至1424、0.3至20以及15至45.5毫克金属/千克干土。几个 former 农业地块采用了单一的植物稳定化处理方法,即种植混合树木,或者采用粉煤灰辅助植物稳定化处理。所用的硅铝质或硫钙质粉煤灰以23.3千克/平方米(即6%重量/重量)的比例翻耕至25至30厘米的土壤深度。结果表明,赤子爱胜蚓会显著回避经过10年粉煤灰处理的土壤,其栖息地功能应被视为有限。这种回避可能与添加粉煤灰导致的土壤质地变化有关,具体表现为细粉砂含量增加,黏土含量降低。相比之下,对于赤子爱胜蚓来说,植树造林的金属污染土壤比未种植的土壤更具吸引力。关于土壤金属污染对赤子爱胜蚓的影响,即使是污染最严重的土壤,受试蚯蚓也没有显著回避。这种缺乏反应可能是由于受试土壤中金属的生物有效性较低。根据我们的研究结果以及之前发表的关于这些粉煤灰和这些经粉煤灰处理土壤的研究结果,讨论了这些土壤处理方法的实用性。