College of Resources and Environment, Southwest University, Key Laboratory of Eco-environments in Three Gorges Reservoir Region, Ministry of Education, Chongqing 400715, China; Chongqing Key Laboratory of Agricultural Resources and Environment, Chongqing 400716, China.
Interdisciplinary Research Center for Agriculture Green Development in Yangtze River Basin, College of Resources and Environment, Southwest University, Chongqing 400715, China.
Sci Total Environ. 2021 Mar 25;762:143117. doi: 10.1016/j.scitotenv.2020.143117. Epub 2020 Oct 20.
Biochar, an effective and low-cost amendment for immobilizing heavy metals, has been extensively studied. However, the simultaneous inhibition effects of biochar on the plant uptake for arsenic (As) and cadmium (Cd) in co-contaminated soils are still ambiguous due to their distinct environmental behaviors. A meta-analysis was conducted to quantitatively assess the effects using 1030 individual observations from 52 articles. On average, biochar application significantly decreased the bioavailability of Cd in soils by 50.12%, while slightly increased the bioavailability of As in soils by 2.39%. The more instructive result is that biochar application could also simultaneously reduce the concentration of As and Cd in plants by 25.48% and 38.66%, respectively. The orders of the decreased percentage of As and Cd in various tissues were root < stem< leaf < grain, and root < leaf < stem < grain, respectively. According to the analysis of critical factors, manure biochar, low pyrolysis temperature (at <400 °C), low application rate (<2%), and high SOC (>30 g/kg) were more conducive to reduce the bioaccumulation of As and Cd simultaneously in co-contaminated soils. Pristine and modified biochar could inhibit As and Cd accumulation in crops, but their efficiencies need to be further improved to ensure the safety of crop productions. Overall, the meta-analysis suggests that biochar has the potential to remedy the As and Cd co-contaminated soils.
生物炭作为一种有效且廉价的重金属固定剂,已得到广泛研究。然而,由于砷(As)和镉(Cd)在环境中的行为明显不同,生物炭同时抑制其在污染土壤中植物吸收的效果仍不明确。本研究通过对 52 篇文献中的 1030 个独立观测值进行元分析,定量评估了生物炭的这种抑制效果。结果表明,生物炭的应用平均可使土壤中 Cd 的生物有效性降低 50.12%,而使 As 的生物有效性增加 2.39%。更有意义的结果是,生物炭的应用还可使植物中 As 和 Cd 的浓度分别降低 25.48%和 38.66%。不同组织中 As 和 Cd 降低比例的顺序为根<茎<叶<籽粒,以及根<叶<茎<籽粒。根据关键因素分析,有机肥生物炭、较低的热解温度(<400°C)、较低的添加率(<2%)和较高的 SOC(>30g/kg)更有利于降低同时污染土壤中 As 和 Cd 的生物累积。原始和改性生物炭可以抑制作物对 As 和 Cd 的积累,但需要进一步提高其效率,以确保作物生产的安全性。总体而言,该元分析表明生物炭具有修复 As 和 Cd 复合污染土壤的潜力。