2g; 3). The largest MWD of aggregate for each

treated soil occurred at 21 d, while maximum MBC contents were also found at that time. Consistently significantly higher MBC content for 5% biochar-amended soil throughout the incubation duration obviously facilitated the aggregation of soil particles at the high throughput screening compounds end of the incubation. Furthermore, the porosity seemed to present an opposite trend to soil aggregation during the incubation especially for the 5% biochar-amended soil. Obvious increase of MWD of aggregate led to decrease of porosity of the 5% biochar-amended soil from the beginning to the end of the incubation. This might indicate that a high application rate (5%) of the biochar might more facilitate to connect with microaggregates to form macroaggregates in the soils (Fig. 4; b) with time, followed by decreasing porosity. With respect to the mechanism of macroaggregate formation in the amended soils in this study, we inferred that the mucilage produced by microbial activity (Fig. 3) and hyphae in the interface between soil particles and biochar (Fig. 4d) caused soil particles to bind and microaggregates to form macroaggregates. The increasing MWD of the soil aggregates of the biochar-amended

Target Selective Inhibitor Library soils after 105 d incubation can be attributed to an increase in the amount of oxidized functional groups after mineralization of the biochar (Cheng et al., 2006), which facilitated flocculation of both the soil particles and the biochar. Six et al. (2004) demonstrated Rolziracetam that organic amendments can connect soil particles through electrostatic attraction, leading to the formation

of microaggregates. Liu et al. (2012) provided that soil aggregate sizes and stability could be significantly increased through the addition of biochar to the soil, especially for the silt loam soil in the Loess Plateau in China. In this study, the soil loss rate decreased significantly as more biochar was added, indicating that the biochar incorporation reduced the potential for soil erosion in the highly weathered soil. The results of the ANOVA and the correlation analysis (Table 2 and Table 3, respectively) showed that the rate of soil loss was affected by several physical properties of the soil, including Bd, porosity, Ksat and soil aggregate sizes. Several studies have demonstrated that the addition of organic matter to soil reduces soil erosion by increasing the sizes of the soil aggregates, as well as by stabilizing the aggregates (Moutier et al., 2000, Tejada and Gonzalez, 2007 and Wuddivira et al., 2009). Based on our results, we deduced that the major reason for reduction of soil loss after the addition of biochar was the redistribution of the relative proportions of soil aggregate sizes. Cantón et al. (2009) indicated that aggregate stability and macroaggregate formation were important factors in maintaining soil porosity and in decreasing soil erosion.