Sang Yi, Azimzadeh Behrooz, Olsen Jessica, Rappaport Jessica, Maguffin Scott C, Martínez Carmen Enid, Reid Matthew C
School of Civil and Environmental Engineering, Cornell University, Ithaca, NY, 14853, USA.
Soil and Crop Sciences, School of Integrative Plant Science, College of Agriculture and Life Sciences, Cornell University, Ithaca, NY, 14853, USA.
Environ Sci Pollut Res Int. 2024 May;31(23):34144-34158. doi: 10.1007/s11356-024-33359-x. Epub 2024 May 2.
There is a need for innovative strategies to decrease the mobility of metal(loids) including arsenic (As) and cadmium (Cd) in agricultural soils, including rice paddies, so as to minimize dietary exposure to these toxic elements. Iron (Fe)-modified biochars (FBCs) are used to immobilize As and Cd in soil-water systems, but there is a lack of clarity on optimal methods for preparing FBCs because there are only limited studies that directly compare BCs impregnated with Fe under different conditions. There is also a lack of information on the long-term performance of FBCs in flooded soil environments, where reductive dissolution of Fe (oxy)hydroxide phases loaded onto biochar surfaces may decrease the effectiveness of FBCs. This study uses material characterization methods including FTIR, SEM-EDX, BET, and adsorption isotherm experiments to investigate the effects of Fe-impregnation methods (pH, pyrolysis sequence, and sonication) on the morphology and mineralogy of Fe loaded onto the biochar surface, and to FBC adsorbent properties for arsenate (As(V)), arsenite (As(III)), and Cd. Acidic impregnation conditions favored the adsorption of As(III) onto amorphous Fe phases that were evenly distributed on the biochar surface, including within the biochar pore structure. The combination of sonication with acidic Fe-impregnation conditions led to the best adsorption capacities for As(V) and As(III) (4830 and 11,166 μg As g biochar, respectively). Alkaline Fe-impregnation conditions led to the highest Cd adsorption capacity of 3054 μg Cd g biochar, but had poor effectiveness as an As adsorbent. Amending soil with 5% (w/w) of an acid-impregnated and sonicated FBC was more effective than an alkaline-impregnated FBC or ferrihydrite in decreasing porewater As concentrations. The acid-impregnated FBC also had greater longevity, decreasing As by 54% and 56% in two flooded phases, probably due to the greater stability of Fe(III) within the biochar pore structure that may have a direct chemical bond to the biochar surface. This study demonstrates that FBCs can be designed with selectivity towards different As species or Cd and that they can maintain their effectiveness under anaerobic soil conditions. This is the first study to systematically test how impregnation conditions affect the stability of FBCs in soils under multiple drying-rewetting cycles.
需要创新策略来降低包括稻田在内的农业土壤中金属(类金属)如砷(As)和镉(Cd)的迁移性,以尽量减少通过饮食接触这些有毒元素。铁(Fe)改性生物炭(FBCs)用于在土壤 - 水系统中固定As和Cd,但由于直接比较不同条件下浸渍Fe的生物炭的研究有限,因此缺乏制备FBCs的最佳方法的明确信息。关于FBCs在淹水土壤环境中的长期性能也缺乏信息,在这种环境中,负载在生物炭表面的铁(氧)氢氧化物相的还原溶解可能会降低FBCs的有效性。本研究使用傅里叶变换红外光谱(FTIR)、扫描电子显微镜 - 能谱分析(SEM - EDX)、比表面积分析(BET)和吸附等温线实验等材料表征方法,研究铁浸渍方法(pH值、热解顺序和超声处理)对负载在生物炭表面的铁的形态和矿物学的影响,以及FBC对砷酸盐(As(V))、亚砷酸盐(As(III))和Cd的吸附性能。酸性浸渍条件有利于As(III)吸附到均匀分布在生物炭表面(包括生物炭孔隙结构内)的无定形铁相上。超声处理与酸性铁浸渍条件相结合导致对As(V)和As(III)的最佳吸附容量(分别为4830和11166 μg As g生物炭)。碱性铁浸渍条件导致最高的Cd吸附容量为3054 μg Cd g生物炭,但作为As吸附剂的效果较差。用5%(w/w)酸浸渍并超声处理的FBC改良土壤在降低孔隙水As浓度方面比碱性浸渍的FBC或水铁矿更有效。酸浸渍的FBC也具有更长的使用寿命,在两个淹水阶段分别使As降低54%和56%,这可能是由于生物炭孔隙结构内Fe(III)的稳定性更高,其可能与生物炭表面有直接化学键。本研究表明,可以设计对不同As物种或Cd具有选择性的FBCs,并且它们可以在厌氧土壤条件下保持其有效性。这是第一项系统测试浸渍条件如何影响FBCs在多次干湿循环下在土壤中稳定性的研究。