Effects of soil water content on Cd immobilization and uptake by leek with the combined application of biochar and organic fertilizer.

This study investigated the effects of soil water content on Cd immobilization and uptake by leek with the combined application of biochar and organic fertilizer using mechanism experiment and pot experiment. Mechanism experiment was conducted with the three-layer mesh method, which can reveal the individual mechanisms and contributions of biochar and soil to Cd immobilization. The results of mechanism experiment showed that the Cd adsorption amount by biochar was very little at low soil water content (θw = 20%, w/w), and both of Cd adsorption amount and rate significantly increased at higher θw (40% and 60%). The Cd immobilization by biochar at higher θw (40% and 60%) was significantly better than that at low θw (20%) in soils because F1 (percentages of exchangeable Cd) decreased with increasing moisture. For example, the F1 percentages were 58.27%, 40.67%, and 38.46% in the soil at 4.40 mg·kg-1 under M20, M40, and M60 (θw = 20%, 40%, 60%) at day 120, respectively. The results of pot experiment showed that the Cd in leek leaves and roots continuously accumulated with planting time in each batch, and biochar and organic fertilizer treatments significantly reduced the Cd enrichment in leek. Combined treatment of biochar and organic fertilizer (BO) is superior to biochar treatments (BC) and CK for Cd immobilization in soil. For example, the percentages of F1 under the treatments of CK, BC, and BO were 64.43%, 49.13%, and 43.67% at 75% field water capacity treatment, respectively. For the same treatment, with increasing water contents, the better the Cd was immobilized in the soil and the greater the leek biomass. However, the total uptake of Cd by leek were increased by promoting crop growth under water content conditions.

Cadmium long-term immobilization by biochar and potential risks in soils with different pH under combined aging.

Cd long-term immobilization by biochar and potential risk in soils with different pH were quantified under a combined artificial aging, which simulated five years of aging in the field based on local climate. Two biochars (original and KMnO4-modified) and five soils with different pH were tested, and an improved three-layer mesh method was employed in this study. Five aging cycles were carried out (Cycle 1-Cycle 5), and each aging cycle quantitatively simulated 1 year of natural aging. As the aging time increased, Cd leaching loss in all soils gradually increased from Cycle 1 to Cycle 5; for relatively stable Cd fraction, it decreased firstly and then stabilized in acidic and neutral soils (S1-S4), while it decreased firstly and then increased in alkaline soil (S5). Biochars significantly promoted Cd immobilization in strongly acidic soil (S1) by increasing relatively stable fractions and decreasing leaching loss. For weakly acidic and neutral soils (S2-S4), although biochars still had positive effects, the immobilization effects were weakened to certain extents compared with S1. The percentage of Cd leaching loss decreased by 19.12% in strongly acidic soil (S1) and by 1.12-11.35% in weakly acidic and neutral soils (S2-S4) after modified biochar treatment. For alkaline soil (S5), the application of biochars had negative effects on Cd immobilization by decreasing relatively stable fractions and increasing leaching loss, and posed risks to the environment. For strongly acidic soil (S1) and weakly acidic and neutral soils (S2-S4), the percentages of relatively stable fractions increased from 6.09-19.93% to 24.98-36.70% after modified biochar treatment. However, for alkaline soil, the percentage of relatively stable fractions decreased from 55.27% to 53.93% after biochar treatment. The more acidic the soil, the more effective the Cd immobilization by biochar. Biochars with high pH level are not suitable for the remediation of alkaline Cd contaminated soil.

Effects of competitive adsorption with Ni(II) and Cu(II) on the adsorption of Cd(II) by modified biochar co-aged with acidic soil.

To investigate the effects of competitive adsorption with Ni(II) and Cu(II) on the adsorption of Cd(II) by modified biochar co-aged with acidic soil, four biochars were employed in this study, namely original biochar, KMnO4-modified biochar and two aged biochars which co-aged with an acidic soil using above biochars under freeze-thaw cycling and dry-wet cycling for 54 days simulating 6 years of natural aging. The results showed that biochar adsorption capacities of three heavy metal ions were in the order of Cd(II) > Cu(II) > Ni(II) in the single system while Cu(II) > Cd(II) > Ni(II) in binary and ternary systems. Modification improved biochar adsorption capacity of Cd(II), but competitive adsorption with Ni(II) and Cu(II) weakened the improvement of modification on adsorption performance of modified biochar in binary and ternary systems. The QMBC/QBC of Cd(II) (QMBC and QBC are the adsorption capacities of heavy metals by modified and original biochars) decreased from 231.57% (single system) to 216.67%∼219.41% (binary system) and further decreased to 207.74% (ternary system). Co-aging with soil weakened the adsorption capacities of biochars for Cd(II), even worse, competition aggravated this negative effect of co-aging. The QAMBC/QMBC of Cd(II) (QAMBC is the adsorption capacities of heavy metals by aged modified biochar) decreased from 65.41% (single system) to 14.43%∼19.46% (binary and ternary systems). Therefore, the impact of competition should be fully considered when evaluating Cd long-term remediation effects of modified biochar in Cd polluted soils accompanied with other heavy metals.