School of Environmental Science and Engineering, Huazhong University of Science and Technology, Luoyu Road 1037, Wuhan, Hubei, 430074, China.
School of Environmental Science and Engineering, Huazhong University of Science and Technology, Luoyu Road 1037, Wuhan, Hubei, 430074, China; Hubei Provincial Engineering Laboratory of Solid Waste Treatment, Disposal and Recycling, Luoyu Road 1037, Wuhan, Hubei, 430074, China; State Key Laboratory of Coal Combustion, Huazhong University of Science and Technology, Luoyu Road 1037, Wuhan, Hubei, 430074, China.
Water Res. 2020 May 1;174:115629. doi: 10.1016/j.watres.2020.115629. Epub 2020 Feb 23.
A novel technique for phosphorus recovery from the liquid phase of anaerobic digestate was developed using biochar derived from iron-rich sludge (dewatered sludge conditioned with Fenton's reagent). The biochar pyrolyzed from iron-rich sludge at a low temperature of 300 °C (referred to as Fe-300 biochar) showed a better phosphorus (P) adsorption capacity (most of orthophosphate and pyrophosphate) than biochars pyrolyzed at other higher temperatures of 500-900 °C, with the maximum P adsorption capacity of up to 1.843 mg g for the liquid phase of anaerobic digestate. Adsorption isotherms study indicated that 70% P was precipitated through chemical reaction with Fe elements, i.e., Fe(II) and Fe(III) existed on the surface of the Fe-300 biochar, and other 30% was through surface physical adsorption as simulated by a dual Langmuir-Langmuir model using the potassium dihydrogen orthophosphate (KHPO) as a model solution. The seed germination rate was increased up to 92% with the addition of Fe-300 biochar after adsorbing most of P, compared with 66% without the addition of biochar. Moreover, P adsorbed by the chemical reaction in form of iron hydrogen phosphate can be solubilized by a phosphate-solubilizing microorganism of Pseudomonas aeruginosa, with the total solubilized P amount of 3.045 mg g at the end of an incubation of 20 days. This study indicated that the iron-rich sludge-derived biochar could be used as a novel and beneficial functional material for P recovery from the liquid phase of anaerobic digestate. The recovered P with biochar can be re-utilized in garden soil as an efficient P-fertilizer, thus increasing the added values of both the liquid phase of anaerobic digestate and the iron-rich sludge.
从厌氧消化液的液相中回收磷的新技术是利用富铁污泥(用过氧化氢铁调理的脱水污泥)制成的生物炭开发的。在 300°C 的低温下从富铁污泥中热解得到的生物炭(称为 Fe-300 生物炭)比在 500-900°C 的其他较高温度下热解得到的生物炭具有更好的磷(P)吸附能力(大部分正磷酸盐和焦磷酸盐),对于厌氧消化液的液相,最大的 P 吸附能力高达 1.843mg/g。吸附等温线研究表明,70%的 P 通过与 Fe 元素的化学反应沉淀,即 Fe(II)和 Fe(III)存在于 Fe-300 生物炭的表面,其余 30%通过表面物理吸附模拟,使用磷酸二氢钾(KHPO)作为模型溶液。与不添加生物炭相比,在用 Fe-300 生物炭吸附大部分 P 后,种子发芽率提高了 92%。此外,以磷酸氢铁形式通过化学反应吸附的 P 可以被铜绿假单胞菌等磷酸盐溶解微生物溶解,在 20 天的孵育结束时,总溶解 P 量为 3.045mg/g。本研究表明,富铁污泥衍生的生物炭可用作从厌氧消化液液相中回收 P 的新型有益功能材料。用生物炭回收的 P 可以作为高效 P 肥料重新用于花园土壤,从而提高厌氧消化液和富铁污泥的附加值。