张宇杰, 马鹏, 王志强, 杨志远, 孙永健, 马均. 麦秆还田下水氮耦合对水稻根际环境及根系形态的影响[J]. 中国生态农业学报 (中英文), 2022, 30(6): 924−936. DOI:10.12357/cjea.20210552
引用本文: 张宇杰, 马鹏, 王志强, 杨志远, 孙永健, 马均. 麦秆还田下水氮耦合对水稻根际环境及根系形态的影响[J]. 中国生态农业学报 (中英文), 2022, 30(6): 924−936.DOI:10.12357/cjea.20210552
ZHANG Y J, MA P, WANG Z Q, YANG Z Y, SUN Y J, MA J. Water-nitrogen coupling influence on rhizosphere environment and root morphology of rice under wheat straw return[J]. Chinese Journal of Eco-Agriculture, 2022, 30(6): 924−936. DOI:10.12357/cjea.20210552
Citation: ZHANG Y J, MA P, WANG Z Q, YANG Z Y, SUN Y J, MA J. Water-nitrogen coupling influence on rhizosphere environment and root morphology of rice under wheat straw return[J]. Chinese Journal of Eco-Agriculture, 2022, 30(6): 924−936.DOI:10.12357/cjea.20210552

麦秆还田下水氮耦合对水稻根际环境及根系形态的影响

Water-nitrogen coupling influence on rhizosphere environment and root morphology of rice under wheat straw return

  • 摘要:通过大田试验, 研究不同水分管理、秸秆还田和氮素处理与水稻根系形态建成的关系, 为成都平原秸秆还田下适宜水稻生长的水氮耦合模式的建立提供理论和实践依据。以杂交稻‘F优498’为材料, 设置不同水分干湿交替灌溉(W1)、淹水灌溉(W2)、氮肥运筹总氮150 kg(N)∙hm −2, 基肥∶蘖肥∶穗肥分别为3∶3∶4 (N1)、7∶3∶0 (N2)、不施氮(N0)和秸秆还田秸秆全量翻埋还田(S1)、秸秆不还田(S0)处理, 研究在秸秆还田下不同水氮耦合对麦茬杂交籼稻根际环境及根系发育的影响。结果表明, 与W2相比, W1促进了拔节期前的秸秆腐解, 提高了拔节期后的根际土壤有机酸总量(1.38%~8.49%)和成熟期前的根际土壤微生物量碳含量(0.25%~12.93%), 提高了整个生育期根系活力(1.77%~149.91%)和除移栽后10 d与成熟期的群体根系形态指标(群体根长18.53%~75.83%、群体根数10.57%~101.33%、群体根体积2.49%~88.24%、群体根表面积8.91%~68.08%); W2提高了拔节期的有机酸总量(3.34%)和成熟期的微生物碳含量(2.69%~6.23%), 并促进了拔节期后的秸秆腐解和单茎根系发育(单茎根长12.03%~27.21%、单茎根数9.05%~51.44%)。秸秆还田(S1)与秸秆不还田(S0)相对比,S1会抑制根系形态发育并降低根系活力(2.47%~45.83%), 但能显著提高根际土壤有机酸总量(8.02%~22.74%)和微生物量碳、氮含量(1.58%~31.22%), 且在W1处理下提升效果更显著。施用氮肥能促进秸秆腐解, 并进一步增加根际土壤有机酸总量与微生物量碳、氮含量, 促进根系发育并提高根系活力。优化施氮模式(N1)与传统施氮模式(N2)相对比,N1可以促进单茎根系发育(单茎根长8.27%~38.09%、单茎根数2.96%~36.66%)与生育中后期的根系活力(2.26%~156.35%), N2则提高了群体根系指标(群体根体积12.68%~44.32%、群体根表面积4.91%~55.82%)和生育前期的根系活力(22.01%~29.31%)。干湿交替灌溉耦合优化施氮模式促进了各时期秸秆腐解, 显著加快了根系的生长发育, 并提高了根际土壤有机酸总量、微生物量碳、氮含量和根系活力, 延缓了根系衰老。综合来看, 在秸秆还田条件下, 干湿交替灌溉耦合优化施氮模式为最适水氮耦合模式。

    Abstract:To provide a theoretical and practical basis for establishing a water-nitrogen coupling model suitable for rice growth under straw return in the Chengdu Plain, the relationship between water management, straw return, N application, and rice root morphogenesis was studied through field experiments. The effects of water-nitrogen coupling on the rhizosphere environment and root development of hybrid indica rice ( Oryza sativa) ‘F You 498’ under wheat straw return conditions were investigated with the application of two water treatments, three N treatments, and two straw return treatments. The two water treatments were alternate dry-wet irrigation (W1) and submerged irrigation (W2); the straw return treatments were full-burying and return of wheat straw (S1) and no straw return (S0); and the N treatments involved the application of 150 kg∙hm −2of N applied at ratios of basal∶tillering∶panicle fertilizers of 3∶3∶4 (N1), 7∶3∶0 (N2), and 0 (N0). The results showed that compared with W2, W1 promoted straw decomposition before the jointing stage, increased the total organic acid content of rhizosphere soil after the jointing period (1.38%–8.49%) and microbial biomass C content of rhizosphere soil before maturity (0.25%–12.93%), increased root activity during the entire growth period, and increased root morphological indices of the rice population, except at 10 days after transplanting and at the mature stage (18.53%–75.83% of root length, 10.57%–101.33% of root number, 2.49%–88.24% of root volume, and 8.91%−68.08% of root surface area). Compared with W1, W2 increase the total organic acids (3.34%) and microbial biomass C content (2.69%–6.23%) at the mature stage, and the decomposition of straw and the root morphological indices of single stems (12.03%–27.21% of root length and 9.05%–51.44% of root number). Compared with S0, S1 treatment inhibited root morphology development and reduced root activity (2.47%–45.83%), but increased the total organic acid content (8.02%–22.74%) and microbial biomass C and N levels of rhizosphere soil (1.58–31.22%), and the effect of improvement was highly noticeable under W1. The application of N fertilizer promoted the decomposition of straw, increased the total organic acids and microbial biomass C and N contents of rhizosphere soil, promoted root development, and increased root activity. Compared with N0, the optimal N application mode (N1) promoted the root development of single stems (8.27%–38.09% of root length and 2.96%–36.66% of root number) and promoted and maintained the root activity (2.26%–156.35%) in the middle and late growth stages; whereas the conventional N application mode (N2) increased the population root index (12.68%–44.32% of root volume and 4.91%–55.82% of root surface area) and root activity only in the early growth stage (22.01%–29.31%). W1 irrigation coupled with optimized N application promoted straw decomposition, significantly accelerated root growth and development, increased total organic acid content, microbial biomass C and N contents, and root activity in rhizosphere soil, and delayed root senescence. Therefore, under the condition of straw return, the optimized N application mode with W1 is the most suitable agriculture model.

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