Department of Chemistry, University of Cyprus, P.O. Box 20537, Nicosia 1678, Cyprus.
Laboratory of Environmental Technologies and Applications, Department of Electronic Engineering, Hellenic Mediterranean University, 73100 Chania, Greece.
Molecules. 2023 Mar 10;28(6):2552. doi: 10.3390/molecules28062552.
biomass was converted to biochar and the removal of Am by pristine and oxidized biochar fibers was investigated in laboratory and environmental water samples. This species has the added advantage of a unique microsponge structure that is beneficial for the production of porous adsorbents. The main purpose of this study was to valorize this biomass to produce an efficient adsorbent and investigate its performance in radionuclide-contaminated waters. Following the preparation of Am solutions at a concentration of 10 mol/L, the adsorption efficiency () was determined as a function of pH, adsorbent mass, ionic strength, temperature, and type of aqueous solution by batch experiments. At the optimum adsorbent dose of 0.1 g and pH value of 4, a log value of 4.2 was achieved by the oxidized biochar sample. The effect of temperature and ionic strength indicated that adsorption is an endothermic and entropy-driven process (Δ° = -512 kJ mol and Δ° = -1.2 J K mol) leading to the formation of inner-sphere complexes. The adsorption kinetics were relatively slow (24 h equilibrium time) due to the slow diffusion of the radionuclide to the biochar surface and fitted well to the pseudo-first-order kinetic model. Oxidized biochar performed better compared to the unmodified sample and overall appears to be an efficient adsorbent for the treatment of Am-contaminated waters, even at ultra-trace concentrations.
生物质被转化为生物炭,并用原始和氧化的生物炭纤维去除环境水样和实验室水样中的 Am。这种物质具有独特的微海绵结构,有利于生产多孔吸附剂,这是其额外的优点。本研究的主要目的是利用这种生物质来生产一种高效的吸附剂,并研究其在放射性核素污染水中的性能。在制备浓度为 10mol/L 的 Am 溶液后,通过批量实验确定了 pH 值、吸附剂质量、离子强度、温度和水溶液类型对吸附效率()的影响。在最佳吸附剂剂量为 0.1g 和 pH 值为 4 的条件下,氧化生物炭样品的吸附效率达到了 4.2 的对数。温度和离子强度的影响表明,吸附是一个吸热和熵驱动的过程(Δ°=-512kJ/mol,Δ°=-1.2J/K/mol),导致形成内球络合物。由于放射性核素向生物炭表面的缓慢扩散,吸附动力学相对较慢(24 小时达到平衡),并且很好地符合准一级动力学模型。与未改性样品相比,氧化生物炭的性能更好,总体上似乎是一种处理 Am 污染水的高效吸附剂,即使在痕量浓度下也是如此。