Department of Environmental Sciences, University of Peshawar, 25120, Pakistan.
Department of Environmental Sciences, University of Peshawar, 25120, Pakistan.
Environ Pollut. 2020 Aug;263(Pt A):114446. doi: 10.1016/j.envpol.2020.114446. Epub 2020 Apr 2.
As a result of metal mining activities in Pakistan, toxic heavy metals (HMs) such as chromium (Cr) and lead (Pb) often enter the soil ecosystem, accumulate in food crops and cause serious human health and environmental issues. Therefore, this study examined the efficacy of biochar for contaminated soil remediation. Poplar wood biochar (PWB) and sugarcane bagasse biochar (SCBB) were amended to mine-contaminated agricultural soil at 3% and 7% (wt/wt) application rates. Lactuca sativa (Lettuce) was cultivated in these soils in a greenhouse, and uptake of HMs (Cr and Pb) as well as biomass produced were measured. Subsequently, health risks were estimated from uptake data. When amended at 7%, both biochars significantly (P<0.01) reduced plant uptake of Cr and Pb in amended soil with significant (P<0.01) increase in biomass of lettuce as compared to the control. Risk assessment results showed that both biochars decreased the daily intake of metals (DIM) and associated health risk due to consumption of lettuce as compared to the control. The Pb human health risk index (HRI) for adults and children significantly (P<0.01) decreased with sugarcane bagasse biochar applied at 7% rate relative to other treatments (including the control). Relative to controls, the SCBB and PWB reduced Cr and Pb uptake in lettuce by 69%, 73.7%, respectively, and Pb by 57% and 47.4%, respectively. For both amendments, HRI values for Cr were within safe limits for adults and children. HRI values for Pb were not within safe limits except for the sugarcane bagasse biochar applied at 7%. Results of the study indicated that application of SCBB at 7% rate to mine impacted agricultural soil effectively increased plant biomass and reduced bioaccumulation, DIM and associated HRI of Cr and Pb as compared to other treatments and the control.
由于巴基斯坦的金属采矿活动,有毒重金属(HMs)如铬(Cr)和铅(Pb)经常进入土壤生态系统,在粮食作物中积累,并导致严重的人类健康和环境问题。因此,本研究考察了生物炭对污染土壤修复的效果。将杨木生物炭(PWB)和甘蔗渣生物炭(SCBB)以 3%和 7%(wt/wt)的添加率添加到受矿区污染的农业土壤中。在温室中用这些土壤种植生菜(Lettuce),并测量对 HMs(Cr 和 Pb)的吸收以及产生的生物量。随后,根据吸收数据估计健康风险。当以 7%的比例添加时,与对照相比,两种生物炭都显著(P<0.01)降低了植物在添加土壤中对 Cr 和 Pb 的吸收,同时生菜的生物量显著(P<0.01)增加。风险评估结果表明,与对照相比,两种生物炭都降低了由于食用生菜而导致的金属每日摄入量(DIM)和相关健康风险。与其他处理(包括对照)相比,当以 7%的比例施用甘蔗渣生物炭时,成人和儿童的 Pb 人体健康风险指数(HRI)显著(P<0.01)降低。与对照相比,SCBB 和 PWB 分别将生菜对 Cr 和 Pb 的吸收减少了 69%和 73.7%,Pb 的吸收减少了 57%和 47.4%。对于两种生物炭,成人和儿童的 Cr 的 HRI 值都在安全范围内。除了 7%的甘蔗渣生物炭外,Pb 的 HRI 值都不在安全范围内。研究结果表明,与其他处理和对照相比,以 7%的比例向受矿区影响的农业土壤施用 SCBB 可有效增加植物生物量,并减少 Cr 和 Pb 的生物积累、DIM 和相关的 HRI。