摘要
为探索高效利用膨润土、红壤和炉渣去除农业污水磷污染的可行性,对比分析了3种吸附剂对人工合成含磷污水的吸附去除特性,结合SEM、XDS和BET等测试结果以及等温吸附、吸附动力学及Ca2+释放量探讨了3种材料对磷的吸附机制.结果表明,炉渣对磷的吸附能力高于膨润土和红壤,吸附过程均适合Langmuir等温吸附方程(R2> 0. 96),对磷的理论饱和吸附量为:炉渣(16. 87 mg·g~(-1))>红壤(1. 21 mg·g~(-1))>膨润土(0. 92 mg·g~(-1)).炉渣对磷的吸附动力学特征符合Elovich方程(R2=0. 966),而膨润土和红壤对磷的吸附特征则更适合准二级动力学方程(R2为0. 982和0. 959).炉渣的Ca2+释放量(10. 46 mg·g~(-1))显著大于膨润土(0. 31 mg·g~(-1))和红壤(0. 03 mg·g~(-1))(P <0. 05).红壤对磷的吸附量随着p H的升高而降低;膨润土在初始p H为7. 0时,吸附量最低;但初始p H值对炉渣去除磷的影响不大.相比红壤和炉渣,膨润土解吸较快,易于进行重复利用.综上所述,吸附材料的磷吸附能力主要与其结构、化学组成、Ca2+释放能力及溶液初始p H值等有关,炉渣较膨润土和红壤对磷酸盐有着更强的去除能力,适合处理农村污水磷污染.
To screen the optimal absorbents for P removal from agricultural wastewater,the P adsorption capacity of bentonite,red soil,and slag was studied using synthetic wastewater. Combing the properties of three adsorbents measured by SEM,XDS,and BET methods,the isothermal adsorption,adsorption kinetics,and Ca2 +release capacity were analyzed to elucidate the mechanisms of P adsorption. The results showed that the P adsorption capacity of slag was higher than that of bentonite and red soil,and the Langmuir isotherm model was able to better fit the adsorption data( R2> 0. 96). The P theoretical saturation sorption capacity of slag was higher( 16. 87 mg·g~(-1)) than that of bentonite( 1. 21 mg·g~(-1)) and red soil( 0. 92 mg·g~(-1))( P < 0. 05). The results for adsorption kinetics indicated that slag rapidly removed 95. 6% of P from 10 mg·L-1 solution,and the Elovich equation fit the data well( R2= 0. 812).The adsorption kinetics of P on bentonite and red soil were better described by the pseudo-second-order kinetic equation( R2= 0. 982 and 0. 959,respectively). The Ca2 +release capacity of slag( 10. 46 mg·g~(-1)) was significantly higher compared to bentonite( 0. 31 mg·g~(-1)) and red soil( 0. 03 mg·g~(-1))( P < 0. 05). The P adsorption capacity of red soil was 0. 26 mg·g~(-1) when the p H value was 3,and it decreased as the p H values increased. At the initial p H of 7. 0,the P adsorption capacity of bentonite was about 0. 01 mg·g~(-1),lower than 0. 04 mg·g~(-1) at p H 3,and 0. 05 mg·g~(-1) at p H 11. The initial p H value had little effect on the P adsorption capacity of slag. The P-loaded bentonite,red soil,and slag were effectively regenerated by using Ca Cl2 solution,and bentonite was easier to reuse compared to red soil and slag. The key factors affecting the P adsorption capacity of the three adsorbents were physical and chemical properties,such as crystal structure and the content of metal ions,Ca2 +release capacity,and initial p H. These findings demonstrated that slag was a better choice for P removal compared to bentonite and red soil and could be used as an effective P adsorbent for agricultural wastewater treatment.
引文
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