欢迎访问《生态学杂志》官方网站,今天是 分享到:

生态学杂志 ›› 2021, Vol. 40 ›› Issue (1): 115-122.doi: : 10.13292/j.1000-4890.202101.034

• 研究报告 • 上一篇    下一篇

生物炭对玉米/大豆、玉米/花生间作系统土壤水肥热及产量的影响

苏旭1,栾策1,2,吴奇1,姜展博1,祝晓妍1,王丽学1*   

  1. 1沈阳农业大学水利学院, 沈阳 110161;2辽宁生态工程职业学院, 沈阳 110122)
  • 出版日期:2021-01-10 发布日期:2021-06-10

Effects of biochar on soil water, nutrient, heat and yield of maize/soybean and maize/peanut intercropping systems.

SU Xu1, LUAN Ce1,2, WU Qi1, JIANG Zhan-bo1, ZHU Xiao-yan1, WANG Li-xue1*   

  1. (1College of Water Conservancy, Shenyang Agricultural University, Shenyang 110161, China; 2Liaoning Vocational College of Ecological Engineering, Shenyang 110122, China).
  • Online:2021-01-10 Published:2021-06-10

摘要: 于2019年5—9月在沈阳农业大学水利学院科研试验基地进行田间试验,设置2种种植模式MS、MP(玉米/大豆间作、玉米/花生间作)和3个生物炭施用量T0T1T2(0、15和30 t·hm-2)的田间小区试验,研究施入生物炭对玉米/大豆、玉米/花生间作系统土壤水热、养分吸收和产量的影响。结果表明:施入生物炭对作物生育初期0~30 cm土壤储水量影响不显著,随着生育期的推进,由于受降雨等因素的影响,生物炭处理显著提高了0~30 cm土壤储水量,其中在抽雄期MPT2处理的增幅最大,达15.49%;在苗期与拔节期,由于降雨少,生物炭对30~60 cm土壤储水量的影响并不显著,从抽雄期开始至生育末期表现出显著性差异,但提升效果不如0~30 cm土层。生物炭可以显著提高苗期与拔节期土壤有效积温,在苗期MPT2处理下提升效果最为显著,增幅达20.97%,而在作物生育中后期,生物炭对土壤有效积温的影响减弱,在抽雄期和灌浆期的影响最小。生物炭施入土壤后虽然显著降低了作物生育前期土壤的矿质氮含量,但显著提高了作物生长发育中后期的矿质氮含量(25.19%~48.82%),因而增加了MS总产量(12.79%~13.71%)和MP总产量(15.86%~18.01%)。因此,生物炭有效调控了作物生长发育关键期土壤的水肥热状况,改善了间作系统的作物生长环境,使得间作这一本来就有着产量优势的种植模式产生了更大的增产效应。

关键词: 生物炭, 间作, 储水量, 有效积温, 矿质氮

Abstract: A field experiment was carried out in the experimental field of Water Conservancy Institute of Shenyang Agricultural University in May-September 2019. There were two planting modes (maize/soybean intercropping, MS; maize/peanut intercropping, MP) crossed with three biochar application doses (0, T0; 15 t·hm-2, T1; 30 t·hm-2, T2). We investigated the effects of biochar application on hydrothermal, nutrient absorption and yield in the maize/soybean and maize/peanut intercropping systems. Results showed that biochar application did not affect soil water storage of 0-30 cm in the early stage of crop growth. Influenced by the rainfall, the biochar application significantly increased soil water storage at 0-30 cm soil layer with crop growth. The maximum increment (15.49%) was observed under the MPT2 treatment during the tassel stage. Biochar application did not affect water storage at 30-60 cm soil layer at the seedling stage and jointing stage due to the low rainfall. While biochar application increased water storage at 30-60 cm soil layer at the tassel stage, the magnitude of such effect was less than that at the 0-30 cm soil layer. Biochar application significantly increased the effective accumulated soil temperature at the seedling stage and jointing stage. The greatest increment occurred in the MPT2 treatment at the seedling stage, reaching up to 20.97%. The effects of biochar application on the effective accumulated temperature were weakened at the middle and late stages, while such effect was least at the tasseling stage and filling stage. After biochar application, soil mineral nitrogen content was significantly reduced at the early stage of crop growth, but significantly increased by 25.19%-48.82% at the middle and late stages of crop growth. The total yield of MS increased by 12.79%-13.71% and the total yield of MP by 15.86%-18.01%. Therefore, biochar application effectively regulated soil water, nutrient and heat conditions during the critical stage of crop growth, improved the water and heat environment of soil and crop growth in the intercropping systems, which together facilitated the positive effects of intercropping on crop yield.

Key words: biochar, intercropping, water storage, effective accumulated temperature, mineral nitrogen.