生态环境学报 ›› 2026, Vol. 35 ›› Issue (7): 1136-1150.DOI: 10.16258/j.cnki.1674-5906.2026.07.013
邵佳丽1(
), 谷海红2,3,4,*(
), 张莹5, 任宇松1, 原心如1, 艾艳君1
收稿日期:2025-11-24
修回日期:2026-05-22
接受日期:2026-05-22
出版日期:2026-07-18
发布日期:2026-07-17
通讯作者:
*谷海红,haihonggu1982@hotmail.com
作者简介:邵佳丽(1996年生),女,硕士研究生,主要研究方向为土壤污染修复。E-mail: 921230274@qq.com
基金资助:
Shao Jiali1(
), Gu Haihong2,3,4,*(
), Zhang Ying5, Ren Yusong1, Yuan Xinru1, Ai Yanjun1
Received:2025-11-24
Revised:2026-05-22
Accepted:2026-05-22
Online:2026-07-18
Published:2026-07-17
摘要:
金属尾矿大多养分贫瘠、重金属污染严重,植物和微生物难以定殖,严重制约了生态修复进程。共生是生物应对胁迫的重要策略,丛枝菌根真菌(AMF)和根瘤菌(Rhizobium)均为重要的共生微生物,有利于提高植物在胁迫环境中的耐性。以钒钛磁铁尾矿为研究对象,以豆科植物紫花苜蓿(Medicago sativa L.)为修复植物,研究AMF和根瘤菌对Cu和Cr污染尾矿中植物生长、尾矿养分、重金属形态及微生物群落的影响。结果表明,高浓度重金属污染显著抑制了植物生长,降低尾矿养分质量分数。接菌显著缓解了重金属胁迫效应,其中丛枝菌根真菌和根瘤菌双接菌效果最优,使地上、地下部干质量最高分别增加150%和49.3%,根瘤数量和鲜质量亦明显提升;尾矿养分也得到了改善,双接菌使碱解氮和速效磷近乎翻倍,有机质和酶活性总体上升;显著降低了Cu和Cr的有效性,并缓解了Cr的环境毒性;此外,双接菌处理还促进了光养细菌席藻属及固氮细菌根瘤菌的增长,抑制潜在病原真菌的相对丰度,调节AMF竞争与资源分配,进一步优化微生物群落结构和功能。综上,紫花苜蓿-AMF-根瘤菌双共生系统在提高植物耐受、降低重金属有效性、改善微生物群落结构等方面具有显著优势,为尾矿生态修复提供了理论依据。
中图分类号:
邵佳丽, 谷海红, 张莹, 任宇松, 原心如, 艾艳君. 紫花苜蓿-AMF-根瘤菌双共生系统对铜和铬污染尾矿的修复作用[J]. 生态环境学报, 2026, 35(7): 1136-1150.
Shao Jiali, Gu Haihong, Zhang Ying, Ren Yusong, Yuan Xinru, Ai Yanjun. Remediation Effects of the Medicago sativa L.-AMF-Rhizobium Dual Symbiotic System on Copper- and Chromium-Contaminated Mine Tailings[J]. Ecology and Environmental Sciences, 2026, 35(7): 1136-1150.
| 种类 | pH | 速效氮质量分数/ (mg·kg−1) | 速效磷质量分数/ (mg·kg−1) | 有机质质量分数/ (g·kg−1) | 全量重金属质量分数/(mg·kg−1) | ||||
|---|---|---|---|---|---|---|---|---|---|
| Cu | Cr | Zn | Pb | Cd | |||||
| 尾矿 | 8.09 | 1.08 | 2.13 | 17.0 | 254 | 541 | 336 | 124 | 0.25 |
| 质量标准1) | >7.5 | - 2) | - | - | 100 | 250 | 300 | 170 | 0.60 |
表1 试验材料部分理化性质
Table 1 Physicochemical properties of experimental materials
| 种类 | pH | 速效氮质量分数/ (mg·kg−1) | 速效磷质量分数/ (mg·kg−1) | 有机质质量分数/ (g·kg−1) | 全量重金属质量分数/(mg·kg−1) | ||||
|---|---|---|---|---|---|---|---|---|---|
| Cu | Cr | Zn | Pb | Cd | |||||
| 尾矿 | 8.09 | 1.08 | 2.13 | 17.0 | 254 | 541 | 336 | 124 | 0.25 |
| 质量标准1) | >7.5 | - 2) | - | - | 100 | 250 | 300 | 170 | 0.60 |
图1 不同重金属胁迫与接菌方式对紫花苜蓿干质量的影响 图中不同小写字母表示同一指标相同部位所有处理间差异显著(p<0.05,n=3),下同
Figure 1 Effects of heavy metal stress and microbial inoculation on the dry biomass of Medicago sativa
图2 不同重金属胁迫与接菌方式对紫花苜蓿根瘤数量与鲜质量的影响
Figure 2 Effects of heavy metal stress and inoculation methods on the nodule number and fresh biomass of Medicago sativa
图3 不同重金属胁迫与接菌方式对尾矿碱解氮质量分数的影响
Figure 3 Effects of different heavy metal stresses and inoculation methods on alkali-hydrolyzable nitrogen content in tailings
图7 不同重金属胁迫与接菌方式对尾矿DTPA 提取态Cu质量分数的影响
Figure 7 Effects of different heavy metal stresses and inoculation methods on DTPA-extractable Cu content in tailings
图12 尾矿细菌群落的LEfSe差异分析图(LDA>4) 不同颜色的节点代表在相应组别中显著富集、并对组间差异具有显著贡献的微生物;而浅黄色节点则表示该类群在各组间无显著差异,或其对组间差异的影响不显著(下同)
Figure 12 LEfSe analysis of differential bacterial features in tailings (LDA>4)
图13 尾矿细菌群落的功能预测图 p<0.05不表示,差异不显著;*、**、***分别代表p≤0.05、p≤0.01、p≤0.001,差异显著且显著性依次提高
Figure 13 Functional prediction of bacterial communities in tailings based on PICRUSt2
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