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  • Effects of Combined Application of Sugar Mill Sludge and Biochar on Basic Properties and Organic Carbon Components of Black Soil in Northeast China
    ZHAO Jia, HU Xiaohang, LI Yanli
    Chinese Agricultural Science Bulletin    2024, 40 (26): 38-45.   DOI: 10.11924/j.issn.1000-6850.casb2024-0231
    Abstract   (78 HTML1 PDF(pc) (1648KB)(101)  

    The study investigated the effects of combined application of beet and sugar plant waste sludge and biochar on the fundamental properties and organic carbon components of farmland soil in Northeast China black soil region. Eight treatments were set up for comparison: no material returned to the field (CK1), 20000 kg/hm2 biochar without filter mud (CK2), 16.67 kg/hm2 filter mud without biochar (T1), 16.67 kg/hm2 filter mud with 20000 kg/hm2 biochar (T2), 33.33 kg/hm2 filter mud without biochar (T3), 33.33 kg/hm2 filter mud with 20000 kg/hm2 biochar (T4), 50 kg/hm2 filter mud without biochar (T5), and 50 kg/hm2 filter mud with 20000 kg/hm2 biochar (T6). Soil total carbon, total organic carbon, easily oxidized organic carbon, water-soluble organic carbon, particulate organic carbon, environmental factors such as alkali-hydrolyzed nitrogen, available phosphorus and available potassium, as well as soil biological activities including urease, phosphatase and sucrase were analyzed to discuss the effects of each treatment on organic carbon components and carbon pool management index. The results indicated that the combined application of filter sludge and biochar significantly increased soil total organic carbon content, easily oxidized organic carbon content and carbon pool management index. The application also affected active carbon components by enhancing available nutrients and enzyme activities which led to an increase in the soil's overall stability. In conclusion, it was found that T4 treatment, a combination of 33.33 kg/hm2 filter sludge with 20000 kg/hm2 biochar, yielded the most favorable results in terms of achieving soil carbon sequestration, increasing CPMI content, and improving the stability of soil organic carbons.


    时期 处理 CPI A AI CPMI
    块根积累期 CK1 1.00±0.09a 0.32±0.04ab 1.00±0.13ab 99.30±5.13b
    CK2 1.06±0.08a 0.18±0.04c 0.57±0.13c 59.73±9.04cd
    T1 1.03±0.07a 0.31±0.05ab 0.98±0.15ab 100.28±13.46b
    T2 1.20±0.20a 0.25±0.05bc 0.77±0.17bc 90.35±11.11b
    T3 1.03±0.06a 0.16±0.02c 0.51±0.05c 52.65±5.01d
    T4 1.22±0.26a 0.37±0.10a 1.15±0.33a 133.70±13.56a
    T5 1.05±0.03a 0.24±0.05bc 0.76±0.17bc 79.66±16.19bc
    T6 1.12±0.10a 0.37±0.10a 1.16±0.32a 127.31±22.99a
    收获期 CK1 1.00±0.05a 0.14±0.00b 1.00±0.02b 99.95±4.23b
    CK2 1.01±0.06a 0.13±0.02b 0.91±0.15b 92.15±10.51b
    T1 1.00±0.04a 0.22±0.02a 1.54±0.11a 154.06±15.94a
    T2 1.00±0.05a 0.21±0.03a 1.44±0.22a 143.09±14.03a
    T3 0.97±0.02a 0.14±0.02b 0.96±0.11b 93.23±10.41b
    T4 0.99±0.01a 0.20±0.06a 1.37±0.41a 135.14±41.76a
    T5 1.01±0.05a 0.13±0.01b 0.94±0.05b 95.30±9.32b
    T6 1.00±0.06a 0.22±0.03a 1.52±0.22a 151.53±14.18a
    表4

    施用滤泥生物炭对土壤碳库管理指数的影响

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