Department of Chemistry "U. Schiff", University of Florence, Via Della Lastruccia 3, 50019, Florence, Sesto Fiorentino, Italy.
Laboratory of Environmental Engineering and Ecotechnology (LR16ES19), National Engineering School of Sfax, Route de La Soukra Km 4, 3038, Sfax, Tunisia.
Environ Sci Pollut Res Int. 2024 May;31(24):35249-35265. doi: 10.1007/s11356-024-33577-3. Epub 2024 May 9.
Nine biochars were produced by co-pyrolysis of sawdust and biological sludge following the "design of experiment" approach. Two kinds of sludge (both deriving from the treatment of mixed industrial-municipal wastewater) and two types of woody waste were selected as categorical predicting variables, while contact time, pyrolysis temperature, and sludge percentage were used as quantitative variables. Biochars were analysed for their product characteristics and environmental compatibility based on the European Standards (EN 12915-1:2009) for materials intended for water treatment (i.e. ash content, water leachable polycyclic aromatic hydrocarbons (PAHs) and elements), as well as for specific surface area (SSA), using them as response variables of a multivariate partial least square multiple regression, whose results provided interesting insights on the relationships between pyrolysis conditions and biochar characteristics. Biochars produced with sludge and/or providing the highest SSA values (258-370 m g) were selected to undergo a sustainable chemical treatment using a by-product of the gasification of woody biomass, complying in all cases with European Standards and achieving therefore the end-of-waste status for sewage sludge. The biochar deriving from the highest percentage of sludge (30% by weight) and with the highest SSA (390 m g) was thermally activated achieving SSA of 460 m g and then tested for the sorption of direct yellow 50 and methylene blue in ultrapure water and real wastewater, compared to a commercial activated carbon (AC). The biochar showed Langmuir sorption maxima (Q) 2-9 times lower than AC, thus highlighting promising sorption performances. Q for methylene blue in wastewater (28 mg‧g) was confirmed by column breakthrough experiments.
通过“实验设计”方法,用木屑和生物污泥共热解生产了 9 种生物炭。选择了两种污泥(均来自混合工业-市政废水的处理)和两种类型的木质废物作为分类预测变量,而接触时间、热解温度和污泥百分比则用作定量变量。根据欧洲标准(EN 12915-1:2009),对生物炭的产品特性和环境相容性进行了分析,这些标准用于水处理材料(即灰分、水可浸出的多环芳烃 (PAHs) 和元素),以及比表面积 (SSA),将其作为多元偏最小二乘多元回归的响应变量,其结果提供了关于热解条件与生物炭特性之间关系的有趣见解。选择了具有污泥和/或提供最高 SSA 值(258-370 m g)的生物炭,用木质生物质气化的副产品进行可持续的化学处理,在所有情况下都符合欧洲标准,并因此实现了污泥的废物结束状态。生物炭来自污泥的最高百分比(重量的 30%)和最高 SSA(390 m g)经过热激活,达到 460 m g 的 SSA,然后在超纯水和实际废水中测试其对直接黄 50 和亚甲蓝的吸附,与商业活性炭 (AC) 进行比较。生物炭的吸附最大值 (Q) 比 AC 低 2-9 倍,因此具有有前途的吸附性能。废水中亚甲蓝的 Q(28 mg·g)通过柱突破实验得到证实。