Beijing Key Laboratory of Farmland Soil Pollution Prevention-control and Remediation, College of Resources and Environmental Sciences, China Agricultural University, No. 2 Yuanmingyuan Xilu, Haidian, Beijing 100193, PR China; Key Laboratory of Arable Land Quality Monitoring and Evaluation, State Key Laboratory of Efficient Utilization of Arid and Semi-arid Arable Land in Northern China, Ministry of Agriculture and Rural Affairs, Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences (CAAS), Beijing 100081, PR China.
Beijing Key Laboratory of Farmland Soil Pollution Prevention-control and Remediation, College of Resources and Environmental Sciences, China Agricultural University, No. 2 Yuanmingyuan Xilu, Haidian, Beijing 100193, PR China.
Sci Total Environ. 2024 Jan 1;906:167418. doi: 10.1016/j.scitotenv.2023.167418. Epub 2023 Sep 27.
Carbonized organic materials are widely used to achieve soil improvement and alleviate soil pollution. The carbonization process significantly changes the total phosphorus (P) content and the P form in the solid phase derived from organic materials, which in turn has a significant impact on the P fertilizer effect in soils. In the present study, a meta-analysis with 278 observational data was conducted to detect the impact of the carbonization process (including pyrolytic carbonization and hydrothermal carbonization) on the transformation of P fractions in biochar or hydrochar derived from different organic materials. The results showed that the carbonization process significantly increased the total P content of the solid phase by 67.9%, and that the rate of P recovery from raw materials stayed high with a mean value of 86.8%. Among them, the impact of sludge-derived char was smaller when compared to the manure-derived char and biomass-derived char. The increase of total P in the biochar (or hydrochar) produced at >500 °C (or >200 °C) was more notable than that at <500 °C (or <200 °C). Simultaneously, the carbonization process significantly decreased the proportion of available P pool in the solid phase by 51.7% on average and increased the proportion of stable P pool in the solid phase by 204%. Appropriate production temperature helps to adjust the proportion of stable P pool in the solid phase. This meta-analysis pointed out that the carbonized solid phase recovers most of the P in the feedstock and that it promotes a significant transformation of available P pool in the feedstock to stable P in the carbonized solid phase. These findings provide useful information for the rational use of carbonization technology, the development of corresponding field management strategies, and the potential value of carbonized solid phase utilization.
碳化有机材料被广泛应用于土壤改良和缓解土壤污染。碳化过程显著改变了有机材料衍生固相中的总磷(P)含量和 P 形态,进而对土壤中 P 肥效产生重大影响。本研究通过 278 个观测数据的元分析,检测了碳化过程(包括热解碳化和水热碳化)对不同有机材料来源的生物炭或水炭中 P 形态转化的影响。结果表明,碳化过程使固相总 P 含量显著增加了 67.9%,且原料中 P 的回收率保持较高,平均值为 86.8%。其中,与粪肥衍生炭和生物质衍生炭相比,污泥衍生炭的影响较小。在 >500°C(或 >200°C)条件下生产的生物炭(或水炭)中总 P 的增加量比在 <500°C(或 <200°C)条件下更为显著。同时,碳化过程使固相中有效磷库的比例平均降低了 51.7%,而稳定磷库的比例增加了 204%。适当的生产温度有助于调整固相中稳定磷库的比例。本元分析指出,碳化固相回收了原料中大部分 P,并促使原料中的有效磷库向碳化固相中的稳定磷库发生显著转化。这些发现为碳化技术的合理应用、相应田间管理策略的制定以及碳化固相利用的潜在价值提供了有用信息。