State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.
State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; University of Chinese Academy of Sciences, Beijing 100049, China.
Ecotoxicol Environ Saf. 2019 Jan 15;167:376-384. doi: 10.1016/j.ecoenv.2018.10.046. Epub 2018 Oct 23.
Heavy metal (HM) pollution in agricultural soils due to the recycling of waste electrical and electronic equipment (WEEE) has become a serious concern, but most farmers cannot afford the economic losses of fallow land during remediation. Thus, it is imperative to produce low-HM crops while remediating the contaminated soils. A 17-week pot experiment was conducted to investigate the growth and HM (Cd, Cu, Pb, Cr, Zn, and Ni) acquisition of garlic chives (Allium tuberosum Rottl. ex Spreng.) intercropped with sunflower (Helianthus annuus L.) and inoculated with (I) or without (I) the arbuscular mycorrhizal (AM) fungus Funneliformis caledonium on a severely HM-contaminated soil that was collected from a WEEE-recycling site. Compared with the monoculture control, the I treatment significantly (P < 0.05) decreased Cd, Cu, Cr, Zn, and Ni concentrations in the shoots of chives through rhizosphere competition and HM (except Cr) transfer from the root to the shoot of chives, and increased the average shoot fresh weight (i.e., yield) of chives by 794% by alleviating HM toxicity. Compared with the I treatment the I treatment significantly increased soil phosphatase activity as well as root mycorrhizal colonization of both sunflower and chives. The I treatment had no effect on the tissue P concentration of sunflower but elevated the average dry biomass (shoot plus root) and P acquisition level of sunflower by 179% and 121%, respectively. In addition, the I treatment significantly increased the P concentration in the root rather than in the shoot of chives and significantly increased the level of P acquisition by chives, increasing the average yield of chives by 229%. Simultaneously, the I treatment significantly increased the level of HM (except Cd) acquisition by sunflower, enhancing the rhizosphere competition by sunflower over chives, and further reducing the transfer of all six HMs from root to shoot in the chives, and inducing significant decreases in chive shoot HM concentrations compared with the monoculture control. Furthermore, the I treatment decreased the average total concentrations and increased the average DTPA-extractable concentrations of soil HMs. The results demonstrate the multifunctional role of AM fungi in the intercropping system for both vegetable production and phytoremediation on HM-contaminated soils.
由于废旧电子电气设备(WEEE)的回收利用,农业土壤中的重金属(HM)污染已成为一个严重的问题,但大多数农民无法承受休耕地在修复过程中的经济损失。因此,在修复污染土壤的同时,生产低 HM 作物是当务之急。进行了为期 17 周的盆栽实验,以研究在严重 HM 污染土壤上种植大蒜(Allium tuberosum Rottl. ex Spreng.)与向日葵(Helianthus annuus L.)间作,并接种(I)或不接种(I)丛枝菌根(AM)真菌 Funneliformis caledonium 对植物生长和 HM(Cd、Cu、Pb、Cr、Zn 和 Ni)吸收的影响,该土壤是从 WEEE 回收现场采集的。与单作对照相比,I 处理通过根际竞争和 HM(除 Cr 外)从根向茎叶的转移,显著(P < 0.05)降低了大蒜茎叶中的 Cd、Cu、Cr、Zn 和 Ni 浓度,并通过缓解 HM 毒性,使大蒜茎叶鲜重(即产量)平均增加 794%。与 I 处理相比,I 处理显著提高了土壤磷酸酶活性以及向日葵和大蒜的根际菌根定殖。I 处理对向日葵的组织 P 浓度没有影响,但使向日葵的平均干生物量(茎叶)和 P 吸收水平分别提高了 179%和 121%。此外,I 处理显著增加了大蒜根中的 P 浓度,而不是茎叶中的 P 浓度,显著增加了大蒜对 P 的吸收水平,使大蒜的平均产量增加了 229%。同时,I 处理显著增加了向日葵对 HM(除 Cd 外)的吸收水平,增强了向日葵对大蒜的根际竞争,进一步减少了 6 种 HM 从根向茎叶的转移,与单作对照相比,显著降低了大蒜茎叶中 HM 的浓度。此外,I 处理降低了土壤中 HM 的平均总浓度,增加了土壤中 HM 的 DTPA 可提取浓度。结果表明,丛枝菌根真菌在 HM 污染土壤上的蔬菜生产和植物修复间作系统中具有多功能作用。