Huang Bin, Xu Ming-Gang, Hu Rong-Gui, Wu Lei
College of Resources and Environment, Shanxi Agricultural University, Taigu 030800, China.
National Key Laboratory of Efficient Utilization of Arid and Semi-arid Farmland in North China, Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081, China.
Huan Jing Ke Xue. 2025 Jun 8;46(6):3999-4010. doi: 10.13227/j.hjkx.202406182.
In recent years, the rapid socio-economic development and the improvement of people's diets have driven the conversion of paddy soil to upland crop cultivation, leading to changes in soil water content, carbon and nitrogen availability, and the intensity of greenhouse gas emission. Therefore, it is crucial to study the effects of changes in soil water content and carbon and nitrogen availability on greenhouse gas CH and CO emissions and identify the key controlling factors upon rice paddy conversion into upland field, especially during the initial stage of conversion. Soil samples used in the present study were collected from a long-term rice paddy field and an adjacent upland field previously converted from rice paddy. The paddy soil was set into submerged (water to soil ratio of 2∶1) and from submerged to a slowly draining treatment (water to soil ratio of 2∶1 slowly decreased to 70% field water capacity and then remained stable) and compared with the upland soil (soil water content remained at 70% field water capacity). Under each water gradient, the soil was supplied with labile C and N to change substrate availability: ① control (no substrate addition), ② C addition (glucose), ③ N addition (NHCl), and ④ C and N additions (glucose+NHCl). CH and CO emissions and soil biochemical properties were measured regularly during the incubation period so as to investigate the effects of soil water content, carbon and nitrogen availability, and their interaction on CH and CO emissions in paddy soil. The changes in contents of soil microbial biomass carbon (ΔMBC), dissolved organic carbon (ΔDOC), and soil mineral N (ΔMineral-N, containing ΔNH-N and ΔNO-N) over the incubation period were calculated by subtracting the initial values from the final values at the end of the incubation period. The results showed that as compared to the submerged condition, the drainage of submerged paddy soil significantly reduced CH emission by 95% on average and increased CO emission by 46% on average. The cumulative emissions of CH and CO were significantly higher in drained paddy soil (1.36 mg·kg and 584.13 mg·kg for CH and CO, respectively) relative to those in upland soil (0.01 mg·kg and 407.70 mg·kg). CH emissions from the submerged paddy soil significantly increased by 40% after carbon addition and decreased by 63% after nitrogen addition. The simultaneous additions of carbon and nitrogen had little effect on the CH emissions from submerged paddy soil. CH emissions from the drained paddy soil increased significantly by 48% after carbon addition, but there was no significant difference among other substrate addition treatments. In upland soil, the additions of carbon and nitrogen had no significant effect on CH emissions but significantly increased CO emissions by 45%-109%. The additions of carbon and nitrogen had little effect on CO emissions in submerged paddy soil. The concurrent addition of carbon and nitrogen significantly increased CO emissions by 36% in drained paddy soil. The interactions between soil water change and N addition had no significant effect on CH emissions, while the interactions between soil water change and C and CN additions significantly affected CH emissions. No significant interactions between soil water change and C and N availability were observed for CO emissions. The conversion of submerged paddy to upland soil decreased soil pH, DOC, MBC, and NH-N contents but increased NO-N content. The additions of carbon and nitrogen significantly affected soil biochemical properties. The results of correlation analysis showed that CH emissions were significantly positively correlated with soil pH, ΔMBC, and ΔNH-N and negatively correlated with ΔNO-N among treatments. Conversely, CO emissions were significantly positively correlated with ΔNO-N but negatively correlated with pH, ΔDOC, ΔMBC, and ΔNH-N. The changes of soil chemical and biological properties induced by soil water change and carbon and nitrogen availability were the main factors influencing CH and CO emissions from paddy soil. In summary, changes in soil water content and carbon and nitrogen availability affect CH and CO emissions by altering soil biochemical properties. Drainage of paddy soil is an effective measure to reduce CH emissions, but the risk of increased CO emissions during the short-term period upon drainage should be considered. Therefore, when developing strategies for rice paddy management, it is crucial to consider the combined effects of water and C and N management so as to achieve effective greenhouse gas mitigation and green and sustainable agricultural production.
近年来,社会经济的快速发展和人们饮食结构的改善推动了稻田向旱作作物种植的转变,导致土壤含水量、碳氮有效性以及温室气体排放强度发生变化。因此,研究土壤含水量和碳氮有效性变化对温室气体CH和CO排放的影响,并确定稻田转变为旱地过程中的关键控制因素至关重要,尤其是在转变初期。本研究使用的土壤样品采集自一块长期稻田和一块先前由稻田转变而来的相邻旱地。将稻田土壤设置为淹水状态(水与土壤比例为2∶1),然后从淹水状态转变为缓慢排水处理(水与土壤比例从2∶1缓慢降至70%的田间持水量,然后保持稳定),并与旱地土壤(土壤含水量保持在70%的田间持水量)进行比较。在每个水分梯度下,向土壤中添加易分解的碳和氮以改变底物有效性:①对照(不添加底物),②添加碳(葡萄糖),③添加氮(NHCl),④添加碳和氮(葡萄糖+NHCl)。在培养期间定期测量CH和CO排放以及土壤生化性质,以研究土壤含水量、碳氮有效性及其相互作用对稻田土壤CH和CO排放的影响。通过将培养期末的最终值减去初始值来计算培养期间土壤微生物生物量碳(ΔMBC)、溶解有机碳(ΔDOC)和土壤矿质氮(ΔMineral-N,包括ΔNH-N和ΔNO-N)含量的变化。结果表明,与淹水状态相比,淹水稻田土壤排水后CH排放平均显著降低了95%,CO排放平均增加了46%。排水稻田土壤中CH和CO的累积排放量(分别为1.36 mg·kg和584.13 mg·kg)相对于旱地土壤(0.01 mg·kg和407.70 mg·kg)显著更高。淹水稻田土壤添加碳后CH排放显著增加了40%,添加氮后降低了63%。同时添加碳和氮对淹水稻田土壤的CH排放影响不大。排水稻田土壤添加碳后CH排放显著增加了48%,但其他底物添加处理之间没有显著差异。在旱地土壤中,添加碳和氮对CH排放没有显著影响,但CO排放显著增加了45%-109%。添加碳和氮对淹水稻田土壤的CO排放影响不大。排水稻田土壤中同时添加碳和氮使CO排放显著增加了36%。土壤水分变化与氮添加之间的相互作用对CH排放没有显著影响,而土壤水分变化与碳和碳氮添加之间的相互作用对CH排放有显著影响。对于CO排放,未观察到土壤水分变化与碳和氮有效性之间的显著相互作用。淹水稻田转变为旱地土壤降低了土壤pH、DOC、MBC和NH-N含量,但增加了NO-N含量。添加碳和氮显著影响土壤生化性质。相关分析结果表明,处理间CH排放与土壤pH、ΔMBC和ΔNH-N显著正相关,与ΔNO-N负相关。相反,CO排放与ΔNO-N显著正相关,但与pH、ΔDOC、ΔMBC和ΔNH-N负相关。土壤水分变化和碳氮有效性引起的土壤化学和生物学性质变化是影响稻田土壤CH和CO排放的主要因素。综上所述,土壤含水量和碳氮有效性的变化通过改变土壤生化性质影响CH和CO排放。稻田排水是减少CH排放的有效措施,但应考虑排水短期内CO排放增加的风险。因此,在制定稻田管理策略时,考虑水、碳和氮管理的综合效应以实现有效的温室气体减排和绿色可持续农业生产至关重要。