Int J Phytoremediation. 2014;16(7-12):790-803. doi: 10.1080/15226514.2013.856849.
Douglas fir trees grown on an artificially Cd-contaminated soil, can tolerate this trace element (up to 68 mg/kg in soil) during several months. Most of the absorbed Cd is retained in roots (25 mg/kg DM), but transfer to aerial part is also effective. Showing the highest content, up to 6 mg/kg DM, among all the aboveground parts, barks seem to be a preferred storage compartment. However, the transfer factor is quite low, about 0.3. Another objective of this study was to compare the cell wall components of trees exposed to increasing Cd amounts in soil. A decrease in lignin and an increase in pectin contents were observed in response to increasing soil cadmium concentration. A concurrent reduction in methyl-esterification of pectin suggests than the structure of this major binding site could therefore be modified as a reaction to cadmium contamination. Future prospects will focus on the modulation of pectin composition in response to Cd exposure.
在人为添加镉污染的土壤中生长的花旗松,在几个月的时间里可以耐受这种微量元素(土壤中可达 68 毫克/千克)。大部分吸收的镉保留在根部(25 毫克/千克干重),但也能有效转移到地上部分。在所有地上部分中,树皮的含量最高,可达 6 毫克/千克干重,似乎是首选的储存部位。然而,转移系数相当低,约为 0.3。本研究的另一个目的是比较暴露于土壤中不同镉含量的树木的细胞壁成分。随着土壤中镉浓度的增加,观察到木质素减少和果胶含量增加。果胶甲酯化程度的降低表明,作为对镉污染的反应,这种主要结合部位的结构可能会发生改变。未来的研究重点将放在果胶组成对镉暴露的响应上。