Dimitrova Tsvetelina, Repmann Frank, Raab Thomas, Freese Dirk
Central Analytical Laboratory, Brandenburg University of Technology Cottbus-Senftenberg, Konrad-Wachsmann-Allee 6, 03046, Cottbus, Germany,
Ecotoxicology. 2015 Apr;24(3):497-510. doi: 10.1007/s10646-014-1398-0. Epub 2014 Dec 5.
Phytoremediation of sites contaminated with iron cyanides can be performed using poplar and willow trees. Poplar and willow trees were grown in potting substrate spiked with ferrocyanide concentrations of up to 2,000 mg kg(-1) for 4 and 8 weeks respectively. Soil solution and leaf tissue of different age were sampled for total cyanide analysis every week. Chlorophyll content in the leaves was determined to quantify cyanide toxicity. Results showed that cyanide in the soil solution of spiked soils differed between treatments and on weekly basis and ranged from 0.5 to 1,200 mg l(-1). The maximum cyanide content in willow and poplar leaves was 518 mg kg(-1) fresh weight (FW) and 148 mg kg(-1) FW respectively. Cyanide accumulated in the leaves increased linearly with increasing cyanide concentration in the soil solution. On the long term, significantly more cyanide was accumulated in old leaf tissue than in young tissue. Chlorophyll content in poplar decreased linearly with increasing cyanide in the soil solution and in leaf tissue, and over time. The inhibitory concentration (IC50) value for poplars after 4 weeks of exposure was 173 mg l(-1) and for willow after 8 weeks of exposure-768 mg l(-1). Results show that willows tolerate much more cyanide and over a longer period than poplars, making them very appropriate for remediating sites highly contaminated with iron cyanides.
可以使用杨树和柳树对受铁氰化物污染的场地进行植物修复。分别在添加了浓度高达2000 mg kg⁻¹ 亚铁氰化物的盆栽基质中种植杨树和柳树4周和8周。每周对不同树龄的土壤溶液和叶片组织进行采样,以分析总氰化物含量。测定叶片中的叶绿素含量以量化氰化物毒性。结果表明,添加亚铁氰化物土壤的土壤溶液中的氰化物在不同处理之间以及每周都有所不同,范围为0.5至1200 mg l⁻¹。柳树和杨树叶片中的最大氰化物含量分别为518 mg kg⁻¹ 鲜重(FW)和148 mg kg⁻¹ FW。叶片中积累的氰化物随着土壤溶液中氰化物浓度的增加而线性增加。从长期来看,老叶组织中积累的氰化物明显多于幼叶组织。杨树叶片中的叶绿素含量随着土壤溶液和叶片组织中氰化物含量的增加以及时间的推移而呈线性下降。暴露4周后杨树的抑制浓度(IC50)值为173 mg l⁻¹,暴露8周后柳树的抑制浓度(IC50)值为768 mg l⁻¹。结果表明,柳树比杨树能耐受更多的氰化物,且耐受时间更长,这使得柳树非常适合用于修复受铁氰化物高度污染的场地。