铁改性生物炭抑制土壤中As的迁移

    Inhibition effect of iron modified biochar on migration of As in soil

    • 摘要: 砷 (As) 的毒性极强,为了治理含 As土壤,该研究通过室内土柱模拟试验,研究铁改性生物炭对土壤中 As迁移能力和形态的影响。结果表明:添加 1%~8% 生物炭和铁改性生物炭后,能显著降低土柱灌水后渗滤液中 As的含量,增加土壤表层 (0~20 cm) As的含量,降低土壤深层 (>20~50 cm) As的含量,促进土壤中有效态 As向稳定态 As转化,生物炭的添加量越大,土壤中 R-As的含量就越高。对比铁改性生物炭和生物炭发现,生物炭负载 Fe3+后,其吸附和固持能力更强,更能促进有效态As向R-As转化,进而降低As污染的风险。因此,在治理含As土壤时,可在表层土壤施加2%的铁改性生物炭,达到吸附和固化As的目的,进而提高土壤的安全性。

       

      Abstract: Abstract:The objective of this study was to investigate the effect of iron (FeCl3 · 6H2O) modified biochar on the migrationcapacity and morphology of As in soil. The biochar was made from cotton straw. The modified biochar was prepared by 20:1biochar and FeCl3·6H2O. The pH value of biochar was 11.4 and that of the modified biochar was 8.5. Soil at 0-20 cm layer offarmland was collected for column experiments. The column was 50 cm in height. The 0-20 cm of soil column was themixture of biochar or modified biochar and soil at the ratio of 0, 1%, 2%, 4% and 8%, respectively. The bulk density of soilcolumn was consistent with that in the field. The column was irrigated for 20 times. The irrigation amount was 200 mL foreach time. The filtrates and soil samples were collected to determine the As content and forms. The results showed that thetotal As content values in filtrates from soil columns with 1% - 8% biochar were gradually decreased with irrigation times.After two times of irrigation, the As content was lower than 10 µg/L (national security drinking water standard in China).However, the values of As content in all the filtrates from soil columns with 1%-8% iron modified biochar were lower than5 µg/L, which was much lower than the standard. The content of As in the soil decreased with the increase of addition amountof biochar and iron modified biochar. It also decreased with increasing soil depth. The content of As in the first layer of soilwere the highest. In the biochar treatments, the proportion of As in the first layer accounted for 45.46% (soil with 1% biocharaddition), 48.41% (soil with 2% biochar addition), 48.88% (soil with 4% biochar addition) and 51.92% (soil with 8% biocharaddition) of the total, respectively. In the iron modified biochar treatments, the proportion of As in the first layer accounted for51.71% (soil with 1% modified biochar addition), 51.99% (soil with 2% modified biochar addition), 54.46% (soil with 4%modified biochar addition) and 60.26% (soil with 8% modified biochar addition) of the total, respectively. The content ofmodified biochar in the first layer was 1.42-1.66 times of that in soils without modified biochar addition. Thus, the Asmigration in soil could be prevented by adding biochar in 0-20 cm layer, and the inhibition role of the iron modified biocharwas stronger than that of biochar. In the soil without biochar, the As was present in six forms including residue arsenic (R-As),calcium arsenic (Ca-As), water arsenic (W-As), exchange arsenic (E-As), aluminum arsenic (Al-As) and iron arsenic (Fe-As).After adding biochar, the As still occurred in the six forms but the content of W-As decreased while the content of R-Asincreased in the layer less than four, and the R-As and Al-As were the two main forms in the fifth and sixth layers. The soilwith iron modified biochar had a small amount of W-As and E-As, and R-As, Ca-As and Al-As were mainly present in thefirst and second layers. Therefore, adding iron modified biochar into soil greatly decreased the content of W-As and increasedthe content of R-As. The iron modified biochar can promote transformation of As forms into R-As, which will reduce the riskof As to pollute soil.

       

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