Tharindu N. Karunaratne , Prashan M. Rodrigo , Daniel O. Oguntuyi , Todd E. Mlsna , Jilei Zhang , Xuefeng Zhang
{"title":"生物炭表面积对碳热还原纳米零价铁结构和重金属去除性能的影响","authors":"Tharindu N. Karunaratne , Prashan M. Rodrigo , Daniel O. Oguntuyi , Todd E. Mlsna , Jilei Zhang , Xuefeng Zhang","doi":"10.1016/j.jobab.2023.06.003","DOIUrl":null,"url":null,"abstract":"<div><p>Carbothermal reduction using biochar (BC) is a green and effective method of synthesizing BC-supported nanoscale zero-valent iron (nanoFe<sup>0</sup>) composites. However, the effect of BC surface area on the structure, distribution, and performance such as the heavy metal uptake capacity of nanoFe<sup>0</sup> particles remains unclear. Soybean stover-based BCs with different surface areas (1.7 − 1 472 m<sup>2</sup>/g) were prepared in this study. They have been used for in-situ synthesis BCs-supported nanoFe<sup>0</sup> particles through carbothermal reduction of ferrous chloride. The BCs-supported nanoFe<sup>0</sup> particles were found to be covered with graphene shells and dispersed onto BC surfaces, forming the BC-supported graphene-encapsulated nanoFe<sup>0</sup> (BC-G@Fe<sup>0</sup>) composite. These graphene shells covering the nanoFe<sup>0</sup> particles were formed because of gaseous carbon evolved from biomass carbonization reacting with iron oxides/iron salts. Increasing BC surface area decreased the average diameters of nanoFe<sup>0</sup> particles, indicating a higher BC surface area alleviated the aggregation of nanoFe<sup>0</sup> particles, which resulted in higher heavy metal uptake capacity. At the optimized condition, BC-G@Fe<sup>0</sup> composite exhibited uptake capacities of 124.4, 121.8, 254.5, and 48.0 mg/g for Cu<sup>2+</sup>, Pb<sup>2+</sup>, Ag<sup>+</sup>, and As<sup>3+</sup>, respectively (pH 5, 25 °C). Moreover, the BC-G@Fe<sup>0</sup> composite also demonstrated high stability for Cu<sup>2+</sup> removal from the fixed-bed continuous flow, in which 1 g of BC-G@Fe<sup>0</sup> can work for 120 h in a 4 mg/L Cu<sup>2+</sup> flow continually and clean 28.6 L Cu<sup>2+</sup> contaminated water. Furthermore, the BC-G@Fe<sup>0</sup> composite can effectively immobilize the bioavailable As<sup>3+</sup> from the contaminated soil, i.e., 5% (<em>w</em>) of BC-G@Fe<sup>0</sup> composite addition can immobilize up to 92.2% bioavailable As<sup>3+</sup> from the contaminated soil.</p></div>","PeriodicalId":52344,"journal":{"name":"Journal of Bioresources and Bioproducts","volume":"8 4","pages":"Pages 388-398"},"PeriodicalIF":20.2000,"publicationDate":"2023-07-07","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Unraveling biochar surface area on structure and heavy metal removal performances of carbothermal reduced nanoscale zero-valent iron\",\"authors\":\"Tharindu N. Karunaratne , Prashan M. Rodrigo , Daniel O. Oguntuyi , Todd E. Mlsna , Jilei Zhang , Xuefeng Zhang\",\"doi\":\"10.1016/j.jobab.2023.06.003\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><p>Carbothermal reduction using biochar (BC) is a green and effective method of synthesizing BC-supported nanoscale zero-valent iron (nanoFe<sup>0</sup>) composites. However, the effect of BC surface area on the structure, distribution, and performance such as the heavy metal uptake capacity of nanoFe<sup>0</sup> particles remains unclear. Soybean stover-based BCs with different surface areas (1.7 − 1 472 m<sup>2</sup>/g) were prepared in this study. They have been used for in-situ synthesis BCs-supported nanoFe<sup>0</sup> particles through carbothermal reduction of ferrous chloride. The BCs-supported nanoFe<sup>0</sup> particles were found to be covered with graphene shells and dispersed onto BC surfaces, forming the BC-supported graphene-encapsulated nanoFe<sup>0</sup> (BC-G@Fe<sup>0</sup>) composite. These graphene shells covering the nanoFe<sup>0</sup> particles were formed because of gaseous carbon evolved from biomass carbonization reacting with iron oxides/iron salts. Increasing BC surface area decreased the average diameters of nanoFe<sup>0</sup> particles, indicating a higher BC surface area alleviated the aggregation of nanoFe<sup>0</sup> particles, which resulted in higher heavy metal uptake capacity. At the optimized condition, BC-G@Fe<sup>0</sup> composite exhibited uptake capacities of 124.4, 121.8, 254.5, and 48.0 mg/g for Cu<sup>2+</sup>, Pb<sup>2+</sup>, Ag<sup>+</sup>, and As<sup>3+</sup>, respectively (pH 5, 25 °C). Moreover, the BC-G@Fe<sup>0</sup> composite also demonstrated high stability for Cu<sup>2+</sup> removal from the fixed-bed continuous flow, in which 1 g of BC-G@Fe<sup>0</sup> can work for 120 h in a 4 mg/L Cu<sup>2+</sup> flow continually and clean 28.6 L Cu<sup>2+</sup> contaminated water. Furthermore, the BC-G@Fe<sup>0</sup> composite can effectively immobilize the bioavailable As<sup>3+</sup> from the contaminated soil, i.e., 5% (<em>w</em>) of BC-G@Fe<sup>0</sup> composite addition can immobilize up to 92.2% bioavailable As<sup>3+</sup> from the contaminated soil.</p></div>\",\"PeriodicalId\":52344,\"journal\":{\"name\":\"Journal of Bioresources and Bioproducts\",\"volume\":\"8 4\",\"pages\":\"Pages 388-398\"},\"PeriodicalIF\":20.2000,\"publicationDate\":\"2023-07-07\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Journal of Bioresources and Bioproducts\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S2369969823000427\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"MATERIALS SCIENCE, PAPER & WOOD\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Journal of Bioresources and Bioproducts","FirstCategoryId":"1085","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S2369969823000427","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"MATERIALS SCIENCE, PAPER & WOOD","Score":null,"Total":0}
Unraveling biochar surface area on structure and heavy metal removal performances of carbothermal reduced nanoscale zero-valent iron
Carbothermal reduction using biochar (BC) is a green and effective method of synthesizing BC-supported nanoscale zero-valent iron (nanoFe0) composites. However, the effect of BC surface area on the structure, distribution, and performance such as the heavy metal uptake capacity of nanoFe0 particles remains unclear. Soybean stover-based BCs with different surface areas (1.7 − 1 472 m2/g) were prepared in this study. They have been used for in-situ synthesis BCs-supported nanoFe0 particles through carbothermal reduction of ferrous chloride. The BCs-supported nanoFe0 particles were found to be covered with graphene shells and dispersed onto BC surfaces, forming the BC-supported graphene-encapsulated nanoFe0 (BC-G@Fe0) composite. These graphene shells covering the nanoFe0 particles were formed because of gaseous carbon evolved from biomass carbonization reacting with iron oxides/iron salts. Increasing BC surface area decreased the average diameters of nanoFe0 particles, indicating a higher BC surface area alleviated the aggregation of nanoFe0 particles, which resulted in higher heavy metal uptake capacity. At the optimized condition, BC-G@Fe0 composite exhibited uptake capacities of 124.4, 121.8, 254.5, and 48.0 mg/g for Cu2+, Pb2+, Ag+, and As3+, respectively (pH 5, 25 °C). Moreover, the BC-G@Fe0 composite also demonstrated high stability for Cu2+ removal from the fixed-bed continuous flow, in which 1 g of BC-G@Fe0 can work for 120 h in a 4 mg/L Cu2+ flow continually and clean 28.6 L Cu2+ contaminated water. Furthermore, the BC-G@Fe0 composite can effectively immobilize the bioavailable As3+ from the contaminated soil, i.e., 5% (w) of BC-G@Fe0 composite addition can immobilize up to 92.2% bioavailable As3+ from the contaminated soil.