Song Shijie, Cheng Xing, Niu Ruilin, Ruan Hao, Zhang Jiajie, Liu Lu
College of Geology and Environment, Xi'an University of Science and Technology, Xi'an 710054, China; Research Institute of Coal Green Mining Geology, Xi'an University of Science and Technology, Xi'an 710054, China; Key Laboratory of Geological Guarantee for Coal Green Development of Shaanxi Province, Xi'an 710054, China.
Ecotoxicol Environ Saf. 2025 Jul 1;299:118404. doi: 10.1016/j.ecoenv.2025.118404. Epub 2025 May 27.
Based on the ecological restoration needs of coal gangue accumulation areas, this study focuses on the potential application of in situ remediation techniques using forage plants. Taking the heavy metal pollution characteristics of the shallow soil (0-20 cm) in a typical coal gangue accumulation area in the Fengfeng mining district of Hebei as a prototype, pot experiments were conducted to investigate the heavy metal content in soil and plants under different heavy metal concentration gradients of Cu (14, 64, 100 mg/kg), Cd (1, 4, 8 mg/kg), and Pb (15, 38, 170 mg/kg) for both single and composite pollution types, revealing the heavy metal accumulation coefficients and translocation capabilities of alfalfa Medicago sativa L.(alfalfa) and Lolium perenne L.(ryegrass). The results indicated that:(1) When the soil was polluted by a single heavy metal, compared with ryegrass, alfalfa had better enrichment ability for Pb, and ryegrass had better enrich ability for Cu. When the concentration of Cd in soil was less than 1 mg/kg, the ability of alfalfa to enrich and transport Cd was better than that of ryegrass. (2) When heavy metal Cu-Pb-Cd combined pollution occurred in soil, the ability of alfalfa to enrich Cu and Pb was significantly better than that of ryegrass. The Cu BCF and Pb BCF of alfalfa were 1.14-2.29 and 1.53-3.96 times that of ryegrass, respectively. The ability of alfalfa to enrich high concentrations of Cd was also significantly better than that of ryegrass. The Cd BCF of alfalfa was greater than 1. (3) If the soil contaminated by heavy metal Cu-Pb-Cd is remedied in situ by planting forage plants, the technical strategy of ' selecting alfalfa + selecting or cultivating varieties with developed roots and stems + applying plant roots and stems targeted protective agent ' is adopted.
基于煤矸石堆积区生态修复需求,本研究聚焦于利用饲用植物进行原位修复技术的潜在应用。以河北峰峰矿区典型煤矸石堆积区浅层土壤(0 - 20厘米)的重金属污染特征为原型,开展盆栽试验,研究单一和复合污染类型下,不同重金属浓度梯度(铜14、64、100毫克/千克,镉1、4、8毫克/千克,铅15、38、170毫克/千克)的土壤和植物中的重金属含量,揭示紫花苜蓿(Medicago sativa L.)和黑麦草(Lolium perenne L.)的重金属积累系数和转运能力。结果表明:(1)土壤受单一重金属污染时,与黑麦草相比,紫花苜蓿对铅的富集能力更强,黑麦草对铜的富集能力更强。当土壤镉浓度小于1毫克/千克时,紫花苜蓿对镉的富集和转运能力优于黑麦草。(2)土壤发生重金属铜 - 铅 - 镉复合污染时,紫花苜蓿对铜和铅的富集能力显著优于黑麦草。紫花苜蓿的铜生物富集系数(BCF)和铅生物富集系数分别是黑麦草的1.14 - 2.29倍和1.53 - 3.96倍。紫花苜蓿对高浓度镉的富集能力也显著优于黑麦草,其镉生物富集系数大于1。(3)若对重金属铜 - 铅 - 镉污染土壤采用种植饲用植物进行原位修复,采用“选用紫花苜蓿 + 选用或培育根茎发达品种 + 施用植物根茎靶向保护剂”的技术策略。