董双快, 徐万里, 吴福飞, 闫翠侠, 李典鹏, 贾宏涛. 铁改性生物炭促进土壤砷形态转化抑制植物砷吸收[J]. 农业工程学报, 2016, 32(15): 204-212. DOI: 10.11975/j.issn.1002-6819.2016.15.028
    引用本文: 董双快, 徐万里, 吴福飞, 闫翠侠, 李典鹏, 贾宏涛. 铁改性生物炭促进土壤砷形态转化抑制植物砷吸收[J]. 农业工程学报, 2016, 32(15): 204-212. DOI: 10.11975/j.issn.1002-6819.2016.15.028
    Dong Shuangkuai, Xu Wanli, Wu Fufei, Yan Cuixia, Li Dianpeng, Jia Hongtao. Fe-modified biochar improving transformation of arsenic form in soil and inhibiting its absorption of plant[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2016, 32(15): 204-212. DOI: 10.11975/j.issn.1002-6819.2016.15.028
    Citation: Dong Shuangkuai, Xu Wanli, Wu Fufei, Yan Cuixia, Li Dianpeng, Jia Hongtao. Fe-modified biochar improving transformation of arsenic form in soil and inhibiting its absorption of plant[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2016, 32(15): 204-212. DOI: 10.11975/j.issn.1002-6819.2016.15.028

    铁改性生物炭促进土壤砷形态转化抑制植物砷吸收

    Fe-modified biochar improving transformation of arsenic form in soil and inhibiting its absorption of plant

    • 摘要: 通过盆栽试验研究了不同砷污染水平(10、20、40和80 mg/kg)下,添加不同量(10、20和40 g/kg)改性前后的生物炭对土壤砷形态及植物吸收砷规律的影响。该文以棉花秸秆生物炭及改性生物炭(棉花秸秆生物炭与FeCl3?6H2O按质量比为20∶1)为试材,小白菜为供试植物。结果表明:生物炭(10~40 g/kg)和改性生物炭(10 g/kg)能促进小白菜的生长,在添加量分别为20和10 g/kg时生物量最大,其最大值分别为8.26和6.68 g/盆,改性生物炭在添加量为10 g/kg时高于对照组和等量未改性生物炭处理组。在砷质量分数为10和20 mg/kg的基础上,添加生物炭(10~40 g/kg)后,土壤中砷主要以残渣态形式存在;水溶态砷分别增加了0.22%~3.36%和0.96%~3.70%;改性生物炭添加对土壤砷质量分数为10 mg/kg时水溶态砷无明显影响,土壤砷质量分数为20 mg/kg时,添加改性生物炭(10~40 g/kg)后水溶态砷减少了0.12%~0.58%。在高浓度(40和80 mg/kg)砷土壤中,水溶态砷含量随着土壤中砷含量的增加而增大;添加生物炭(10~40 g/kg)后,土壤中水溶态砷分别增加了0.21%~1.56%和2.11%~8.94%,但砷主要以铝形砷形式存在,残渣态砷次之。各处理组小白菜可食部分和根部砷质量分数在添加10~40 g/kg生物炭后的变化规律不尽相同,等量的改性生物炭添加后,可食部分由18.28 mg/kg显著降低至2.66 mg/kg(P<0.05),根部从133.99 mg/kg显著降低至20.21 mg/kg(P<0.05)。改性生物炭与未改性生物炭相比,改性生物炭能降低土壤中水溶态砷的含量及对小白菜吸收砷有显著的抑制作用。因此,该研究可为改性生物炭在含砷土壤的修复应用中提供数据支撑与理论基础。

       

      Abstract: Arsenic has the chemical nature and toxicity to environment like heavy metals, and its toxicity will have a serious impact on human health, animal or plant.Only 0.1 g arsenic trioxide can cause human death, and long-term excessively drinking water or eating other foods containing arsenic will cause cancer in human organs.To reduce the effect of arsenic on human body, animal and plant, this paper uses unmodified biochar and biochar modified by FeCl3?6H2O as test material; the former was prepared using cotton stalks whose carbonization temperature and time were 500 ℃ and 4 h, respectively, and the latter was prepared with the 20∶1 mass ratio of cotton stalk biochar to FeCl3?6H2O.A total of 35 groups of soil containing unmodified biochar or modified biochar or arsenic were designed, and the arsenic content of cabbage that was planted in pot was tested by atomic fluorescence spectrometer (PF6-1) to explore the influence of unmodified biochar and modified biochar on soil and plants absorbing arsenic.The results showed that: Unmodified biochar (10-40 g/kg) or modified biochar (10 g/kg) could promote the growth of cabbage, and the biomass of cabbage was the largest when the unmodified biochar was 20 g/kg and the modified biochar as 10 g/kg, which was 8.26 and 6.68 g per pot respectively.When the content of modified biochar was 10 g/kg, the biomass of cabbage was bigger than the control group and the treatment group with equivalent amount of unmodified biochar.The arsenic in soil was mainly residual form, and soluble arsenic increased by 0.22%-3.36% and 0.96%-3.70% respectively when the arsenic content was 10 and 20 mg/kg and the addition content of biochar was 10-40 g/kg.The soluble arsenic had no effect when the arsenic content was 10 mg/kg and the addition content of modified biochar was 10-40 g/kg, but the soluble arsenic decreased by 0.12%-0.58% when the arsenic content was 20 mg/kg.The content of soluble arsenic was increasing with soil arsenic content increasing when the content of arsenic in soil was 40 and 80 mg/kg; after adding biochar (10-40 g/kg), soluble arsenic increased by 0.21%-1.56% and 2.11%-8.94%, respectively, but the form of arsenic was mainly aluminum arsenic, and arsenic residues followed.The variation of arsenic mass fraction in edible parts and roots of cabbage in each treatment group was different after adding biochar (10-40 g/kg), but the mass fraction of arsenic in edible parts of cabbage significantly reduced from 18.28 to 2.66 mg/kg (P<0.05), and the mass fraction of arsenic in roots of cabbage significantly reduced from 133.99 to 20.21 mg/kg (P<0.05) after adding same amount of modified biochar.Comparing the modified biochar and unmodified biochar, it was found that modified biochar could reduce the content of soluble arsenic in soil and inhibit cabbage from absorbing arsenic.Therefore, this study may provide data support and theoretical basis for the application of modified biochar and unmodified biochar in soil restoration.

       

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