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作 者:何娴 徐仁扣[1,2] HE Xian;XU Renkou(State Key Laboratory of Soil and Sustainable Agriculture,Institute of Soil Science,Chinese Academy of Sciences,Nanjing 210008,China;University of Chinese Academy of Sciences,Beijing 100049,China)
机构地区:[1]土壤与农业可持续发展国家重点实验室(中国科学院南京土壤研究所),南京210008 [2]中国科学院大学,北京100049
出 处:《土壤》2022年第5期1016-1023,共8页Soils
基 金:国家自然科学基金项目(41877036)资助。
摘 要:选择稻草、玉米秸秆和油菜秸秆作为制备生物质炭的原料,分别用H_(2)O_(2)和HNO_(3)/H_(2)SO_(4)对生物质炭进行改性处理,以未改性的生物质炭和HCl处理的生物质炭作为对照。按土重3%的比例向采自安徽郎溪的酸性水稻土中添加上述生物质炭,在经历一个干湿交替周期后,进行Cd(Ⅱ)吸附/解吸试验,研究添加生物质炭对水稻土吸附Cd(Ⅱ)的影响及其机制。结果表明,两种改性方法均有效增加了生物质炭表面的质子结合位点数,且HNO_(3)/H_(2)SO_(4)改性对生物质炭表面羧基官能团的扩增效果更显著。官能团的增加使得添加了HNO_(3)/H_(2)SO_(4)改性生物质炭的水稻土对Cd(Ⅱ)的专性吸附能力显著增强。因此,添加HNO_(3)/H_(2)SO_(4)改性生物质炭可作为酸性水稻土吸附固定重金属Cd的一种新型方法。The straws of rice,maize and rape were selected as raw materials for preparing biochars.The biochars were modified with H_(2)O_(2)and HNO_(3)/H_(2)SO_(4),respectively,and the unmodified biochar and HCl treated biochar were used as control.The above biochars were added to an acidic paddy soil from Langxi,Anhui Province at the rate of 3%.The mixed soil samples were submerged for one month at 25℃,and then dried naturally.After a wet/dry cycle,Cd(Ⅱ)adsorption/desorption experiments were carried out.Results indicate that the modifications of H_(2)O_(2)and HNO_(3)/H_(2)SO_(4)increase the number of proton binding sites on biochars and HNO_(3)/H_(2)SO_(4)modification leads to greater increase in the number of proton binding sites due to the greater increase of carboxyl functional groups than H_(2)O_(2)modification.The addition of modified biochars improve the adsorption capacity of the acidic paddy soil for Cd(Ⅱ),especially the addition of HNO_(3)/H_(2)SO_(4)modified biochar.Therefore,adding HNO_(3)/H_(2)SO_(4)modified biochar could be used as a new method for adsorption and immobilization of Cd in acidic paddy soils.
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