• ISSN 1008-505X
  • CN 11-3996/S

膜下滴灌西瓜栽培体系化肥氮的去向及土壤氮素平衡

The fate of chemical fertilizer nitrogen and soil nitrogen balance in water mellon cultivation system under drip irrigation and plasticfim mulching

  • 摘要:
    目的 我们采用通过高丰度15N同位素微区试验,定量研究了西北旱区膜下滴灌西瓜生产体系下,不同施氮水平化肥氮的作物吸收、土壤残留与损失去向,计算了土壤氮素表观平衡,为该区域西瓜生产氮肥优化管理与环境减排提供科学依据。
    方法 西瓜田间试验在甘肃省农业科学院张掖节水试验站进行,设置四个氮肥水平:N0 (0 kg/hm2)、N100 (100 kg/hm2)、N200 (200 kg/hm2)、N300 (300 kg/hm2),每个处理小区内预留0.8 m×2 m=1.6 m2的微区,施用为丰度为10%的15N尿素(N 46%)。西瓜生育期内,采集每次降雨和灌溉水样,测定氮素含量。西瓜收获后,采集微区内全部8株西瓜植株,分为茎、叶、果实,测定干物质量、氮素含量、15N丰度和果实固形物含量。同时,在微区内采集0—100 cm 土壤样本,每20 cm一个样品,测定土壤样品15N丰度,计算化肥氮在各层土壤中的残留量。以施肥量减去西瓜吸收量和土壤残留量,作为氮素损失量。
    结果 氮肥施入量显著影响西瓜产量、品质及氮素利用效率,西瓜产量与可溶性固形物含量均随施氮量增加呈先增后降趋势,在N200处理达到最优,且边缘糖分响应尤为明显。植株干物质与氮积累量随施氮量持续上升,但氮肥利用率、氮收获指数随施氮量的增加而降低,表明过量施氮不利于氮素向果实转运。西瓜吸收的氮素60.64%~74.30%来自土壤。施入土壤中的肥料氮的11.63%~22.79%被作物当季吸收,41.99%~59.06%残留在土壤中,28.84%~35.22%损失掉。残留氮素主要分布于0—40 cm土层,且残留量与损失量随施氮量增加而上升。土壤氮素平衡分析表明,施氮量超过103 kg/hm2后,氮素由亏缺转为盈余,增加了环境污染风险。
    结论 西瓜吸收的氮素超过60%源于土壤,随着施氮量由100 kg/hm2增加到300 kg/hm2,西瓜吸收的土壤氮素量基本稳定,吸收的肥料氮量仅增加了不到10%,且主要用于提高植株生物量与茎叶氮积累量,因而显著降低氮收获指数。施入土壤中的氮素去向为:西瓜当季吸收量占11.63%~22.79%,土壤残留41.99%~59.06%,损失量占28.84%~35.22%,土壤残留主要在0—40 cm土层,仍可能为后茬作物利用。土壤当季氮素平衡的施肥量为N103 kg/hm2,但综合考虑氮肥的增产增收效果以及对土壤氮库的补充功能,河西走廊旱区膜下滴灌栽培西瓜的适宜氮肥用量应不超过200 kg/hm2。

     

    Abstract:
    Objectives We conducted a high-abundance 15N isotope microplot experiment to quantitatively investigate the fate of fertilizer N through crop uptake, soil residue, and losses under varying N application rates in a plastic-mulched and drip-irrigated watermelon production system in the arid region of Northwest China. Soil apparent N balance was calculated to provide a scientific basis for optimizing N management and reducing environmental emissions in regional watermelon production.
    Methods A field experiment was carried out at the Zhangye Water-Saving Experiment Station of the Gansu Academy of Agricultural Sciences. Four N application rate treatments were established: N0 (0 kg/hm2), N100 (100 kg/hm2), N200 (200 kg/hm2), and N300 (300 kg/hm2). Within each plot, a 0.8 m×2 m=1.6 m2 microplot was designated and applied with urea enriched to 10% 15N abundance (46% N). During the watermelon growing season, water samples from rainfall and irrigation events were collected to determine N content. At harvest, all eight watermelon plants within each microplot were sampled, separated into stem, leaf, and fruit samples for analysis of dry biomass, N content, 15N abundance, and fruit soluble solids content. Concurrently, soil samples were collected from the 0–100 cm profile at 20 cm intervals to measure 15N abundance and calculate residual fertilizer-N in each layer. N loss was estimated as the difference between the applied N rate and the sum of plant N uptake and soil N residue.
    Results N application rate significantly affected watermelon yield, quality, and N use efficiency (NUE). Both yield and soluble solids content initially increased and then decreased with rising N rates, peaking at the N200 treatment; this response was particularly pronounced in marginal fruit sweetness. Plant dry matter and N accumulation increased continuously with higher N inputs. However, NUE and the N harvest index declined with increasing N rates, indicating that excessive N application hindered N translocation to the fruits. Of the total N absorbed by watermelon, 60.64%–74.30% originated from the soil. Regarding the applied fertilizer-N, 11.63%–22.79% was taken up by the crop in the current season, 41.99%–59.06% remained in the soil, and 28.84%–35.22% was lost. Residual N was primarily concentrated in the 0–40 cm soil layer, and both residual and loss amounts increased with higher N application rates. Soil N balance analysis revealed that the system shifted from N deficit to surplus when the application rate exceeded 103 kg·hm2, thereby elevating the risk of environmental pollution.
    Conclusion Over 60% of the N absorbed by watermelon is derived from soil reserves. As N rates increased from 100 to 300 kg/hm2, soil-derived N uptake remained relatively stable, while fertilizer-N uptake increased by less than 10%. The additional fertilizer N was primarily allocated to increasing plant biomass and vegetative N accumulation, consequently lowering the NHI. The fate of applied N is distributed as follows: 11.63%–22.79% is taken up by watermelon in the current season, 41.99%–59.06% reside in the soil, and 28.84%–35.22% is lost. Soil-residual N was mainly retained in the 0–40 cm layer and remains potentially available for subsequent crops. While the soil N balance threshold for the current season was 103 kg/hm2, considering both the agronomic benefits and the role of fertilization in replenishing soil N pools, the recommended optimal N rate for mulched drip-irrigated watermelon in the Hexi Corridor arid region should not exceed 200 kg/hm2.

     

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