生物炭和草酸活化磷矿粉对镉镍复合污染土壤的应用效果

采用室内培养实验,利用生物炭和草酸活化磷矿粉对镉镍复合污染土壤进行修复,比较两者不同配比对土壤重金属镉镍的修复效果及对土壤无机氮和微生物量氮(MBN)转化的影响.结果表明,随着草酸活化磷矿粉和生物炭施用量的增加,土壤p H逐渐增加,镉和镍均由弱酸提取态逐渐向可还原态、可氧化态和残渣态转化,生物有效性降低.其中,C50P3(50 g·kg~(-1)生物炭与3 g·kg~(-1)草酸活化磷矿粉)配施的修复效果最好,弱酸提取态Ni占全量的质量分数降低了37.0%,残渣态Ni增加了14.8%,弱酸提取态Cd含量占全量的质量分数降低了40.2%,残渣态增加了35.2%.施用修复剂40 d后,相较于C0P0(空白对照)处理,C50P0(单施50 g·kg~(-1)生物炭)处理与C0P3(单施3 g·kg~(-1)草酸活化磷矿粉)处理微生物量氮含量均分别增加了1.5倍和1倍;铵态氮含量分别减少了12.5%和6.4%,硝态氮含量分别降低了11.6%和10.2%.综合比较可知,生物炭和草酸活化磷矿粉配施对土壤重金属镉镍复合污染的修复效果要优于单施,且50 g·kg~(-1)生物炭与3 g·kg~(-1)草酸活化磷矿粉(C50P3)配施的修复效果最好,修复剂的加入促进了土壤无机氮向有机氮的转化.

Remediation of Cd/Ni Contaminated Soil by Biochar and Oxalic Acid Activated Phosphate Rock

Taking soil contaminated with a combination of Cd and Ni as the research objective, biochar, and oxalic acid activated phosphate rock (APR) were applied both together and separately for the remediation of this contaminated soil. The effects of different ratios of amendments on the remediation of Cd and Ni heavy metals in the soil and on inorganic nitrogen and microbial biomass nitrogen (MBN) in the soil were compared. The results show that an increasing amount of biochar and APR, increases the soil pH gradually and acid-extractable Cd and Ni are gradually transformed into reducible, oxidable and residual Cd and Ni, resulting in a reduction in Cd and Ni bioavailability. After 40 days incubation, the acid extractable Ni decreased by 37.04% with a 14.8% increase in residual Ni, and acid extractable Cd decreased 40.28% with a 35.20% increase in residual Cd with the amendment of C50P3 (Applying 50 g·kg^-1 biochar and 3 g·kg^-1 APR) when compared to C0P0 treatment (Applying nothing). Furthermore, the MBN content for C50P0 (Applying 50 g·kg^-1 biochar only) and C0P3 (Applying 3 g·kg^-1 APR only) increased by 1.5 and 1 times, respectively, while the content of ammonium nitrogen decreased by 12.5% and 6.4%, respectively and the content of nitrate nitrogen decreased by 11.6% and 10.2%, respectively. This comparison shows that the combined effect of the application of biochar and APR is superior to each respective separate treatment. A mixture of 50 g·kg^-1 of biochar and 3g·kg^-1 of APR (C50P3) demonstrates the best effect on the remediation of the Cd and Ni in soil. Furthermore, the application of amendments promoted the transformation of inorganic nitrogen into organic nitrogen.