Returning crop residues is a possible practice for balancing soil carbon (c) loss. the turnover rate of organic c from crop residues to soil c is dependent on soil microbial community dynamics. However, the relationship between any temporal changes in the soil microbial community after crop straw inputs and the dynamics of straw-c distribution in the soil organic carbon (Soc) pool remains unclear. the present study investigated the allocation of straw-c into soil dissolved organic carbon (Doc), microbial biomass carbon (MBc), particulate organic carbon (poc) and mineral-associated organic carbon (Maoc) using stable isotope probing, as well as the temporal changes in the soil bacterial and fungal communities using high-throughput sequencing. After the first 180 days of straw decomposition, approximately 3.93% and 19.82% of straw-C was transformed into soil MaOC and POC, respectively, while 0.02% and 2.25% of straw-C was transformed into soil DOC and MBC, respectively. The temporal change of the soil microbial community was positively correlated with the dynamics of straw-c distribution to Soc (R > 0.5, P < 0.05). The copiotrophic bacteria (e.g., Streptomyces, Massilia and Sphingobacterium), cellulolytic bacteria and fungi (e.g., Dyella and Fusarium, Talaromyces), acidophilic bacteria (e.g., Edaphobacter and unclassified Acidobacteriaceae), denitrifying and N-fixing microbes (e.g., Burkholderia-Paraburkholderia, Paraphaeosphaeria and Bradyrhizobium), and fungi unclassified Sordariomycetes were significantly correlated with straw-C distribution to specific SOC fractions (P < 0.05), which explained more than 90% of the variation of straw-C allocation into soils. copiotrophic, certain cellulolytic and denitrifying microbes had positively correlated with Doc-and Maoc-derived from straw, and other cellulolytic fungi (e.g., Talaromyces) and specific bacteria (e.g. Bradyrhizobium) were positively correlated with poc-derived from straw. our results highlight that the temporal change of soil microbial community structure well reflects the conversion and distribution process of straw-c to Soc fractions. Soil organic matter, the largest terrestrial carbon (C) pool, plays an important role in improving soil fertility and sustaining soil productivity 1,2. Many agricultural management practices, such as fertilizer application, straw return, and tillage, could affect the soil organic carbon (SOC) pool 3-6 , especially the labile organic carbon fractions, such as dissolved organic carbon (DOC), microbial biomass carbon (MBC) and particulate organic carbon (POC). DOC and MBC, considered to be soil active organic C, have been reported as important factors in impacting soil fertility 7,8. Moreover, the formation, migration and transformation of DOC can affect soil microbial community structure and activity 9-11 , and the formation of mineral-associated organic carbon (MaOC) 12,13 , which usually represents the largest fraction of SOC pool 14. POC has been considered as a transition state of stable organic C, which is predominantly of...