• ISSN 1008-505X
  • CN 11-3996/S

连作土壤上施用改良剂和微生物制剂促进土壤有机氮活化和氮素供应的效应

Amendment and microbial agent activate soil organic nitrogen and improve nitrogen supply to peanut in continuous cropping soil

  • 摘要:
    目的 土壤改良剂可通过改善土壤微环境、调节微生物活动来影响土壤易矿化有机氮组分和矿化速率,为作物提供更充足的有效氮源,进而促进作物的健康生长。我们比较了长期施用改良剂和微生物制剂对连作土壤氮素有效性及作物生长的影响,以提出适宜于连作经济作物种植的土壤管理措施。
    方法 于 2011 在沈阳农业大学国家花生产业技术体系土壤肥料基地开展长期定位试验,供试作物为花生,以花生连作为对照 (PC),设置玉米—花生轮作 (MPR)、花生连作配合施用改良剂 (PCCA) 和微生物制剂 (PCBA),共四个处理,均基施 N 60 kg/hm2、P2O5 82.5 kg/hm2、K2O 112.5 kg/hm2。2023 年花生苗期、开花下针期、结荚期及成熟期采集土壤样品,进行氮矿化培养试验,同时测定土壤无机氮、有机氮组分、微生物量氮、固定态铵含量。成熟期取植物样本,调查养分含量、生物量及花生产量。
    结果 与 PC 相比,PCCA 处理提高了花生各生育时期土壤铵态氮、硝态氮含量,铵态氮增幅为 25.54%~198.57%,硝态氮增幅为 12.47%~94.82%;PCCA 和 PCBA 处理显著提高了培养 21天后土壤的净氮矿化速率,较 PC 增幅为 37.5%~43.75%,且 PCCA 的增幅显著高于 PCBA。PCCA 和 MPR 处理对各生育期土壤有机氮组分含量的影响不尽相同,与 PC 相比,PCCA 处理各生育期土壤酸解铵态氮和酸解氨基酸态氮含量显著提升了 7.79%~29.32%、13.87%~19.02%,MPR 处理显著提高了 9.15~32.16%、12.17%~22.00%;PCCA和 MPR 处理分别显著提升了成熟期酸解氨基糖态氮含量 26.16%、 30.77%,成熟期酸解未知态氮含量 30.65%、37.84%,显著降低了非酸解氮含量 15.50%、13.38%,MPR 处理各有机氮组分含量与 PCCA 处理相当。PCCA、PCBA 和 MPR 均显著提高了土壤微生物量氮及固定态铵含量,培养后 (21天) 微生物量氮较 PC 的增幅为 18.43%~22.28%;固定态铵的增幅为 11.58%~22.49%,PCCA 对固定态铵的提升效果要优于 MPR。
    结论 在花生连作土壤上,施用生物炭和硅粉制备的改良剂或者轮作提升了土壤酸解铵态氮、酸解氨基酸态氮含量,提高了土壤氮矿化速率和矿化量,改良剂处理矿化形成的部分无机氮以固定态铵的形式在土壤中保存下来,提高了土壤氮素供应的稳定性,因而在提升花生荚果和茎叶的氮磷钾积累量方面获得了优于轮作的效果。微生物菌剂对土壤有机氮组分,特别是酸解有机氮组分无显著影响,但提升了花生苗期和开花下针期土壤中的铵态氮和硝态氮含量,因而促进了花生早期的养分供给,也获得了显著的增产效果。因此,施用改良剂和微生物制剂均是替代轮作的有效措施。

     

    Abstract:
    Objectives Soil amendments are frequently employed to enhance the micro - environmental conditions and accelerate the mineralization rates of organic matter. By doing so, they furnish crops with an efficient nutrient supply and foster a conducive environment for healthy growth. In this study, we conducted a comparative analysis to assess the impact of the long - term application of soil amendments and microbial agents on soil nitrogen availability and crop growth within a continuously cropped system. The ultimate aim is to formulate appropriate soil management strategies tailored for economically significant continuous cropping systems.
    Methods A positioning experiment was carried out in the Base for Soil Fertilizer of National Peanut Industry Technology System of Shenyang Agricultural University since 2011. The four treatments were: maize-peanut rotation (MPR), peanut continuous cropping (PC), peanut continuous cropping applied with amendments (PCCA) and microbial agent (PCBA). All the treatments were basal applied with N 60 kg/hm2, P2O5 82.5 kg/hm2 and K2O 112.5 kg/hm2. Soil samples were collected during the seedling, flowering and needing, podding, and maturity stages of peanut in 2023 for nitrogen mineralization incubation tests, and the determination of soil inorganic N, organic nitrogen fractions, microbial biomass nitrogen (MBN), and fixed ammonium (FN). At maturity, plant samples were collected to determine nutrient content, biomass, and peanut yield.
    Results Compared with PC, PCCA treatments increased soil NH4+-N by 25.54%−198.57% and NO3-N by 12.47%−94.82% across all growth stages, increased net nitrogen mineralization rate after 21 days of incubation by 37.5%–43.75%, and the increase by PCCA was significantly higher than that by PCBA. The effects of PCCA and MPR on organic nitrogen fractions depended on the growth stages. Compared to PC, PCCA significantly increased soil acidolysed ammonium nitrogen and acidolysed amino acid nitrogen contents by 7.79%–29.32% and 13.87%–19.02%, respectively, and MPR increased these fractions by 9.15%–32.16% and 12.17%–22.00%, respectively. At maturity, PCCA and MPR significantly increased acidolysed amino sugar nitrogen by 26.16% and 30.77%, and acidolysed unknown nitrogen by 30.65% and 37.84%, respectively, but significantly reduced non-acidolysed nitrogen by 15.50% and 13.38%. The organic nitrogen fractions in MPR were comparable to those in PCCA. PCCA, PCBA, and MPR significantly increased soil MBN and FN by 18.43%–22.28% and 11.58%–22.49% after 21 days of incubation, respectively. PCCA had a more pronounced effect on fixed ammonium relative to MPR.
    Conclusions On peanut continuous cropping soil, the application of amendments prepared from biochar and silica powder or crop rotation increased the contents of soil acidolysed ammonium nitrogen and acidolysed amino acid nitrogen, as well as the rate and amount of soil nitrogen mineralization. In the amendment-treated soil, a portion of the inorganic nitrogen formed through mineralization was preserved in the soil in the form of fixed ammonium, enhancing the stability of soil nitrogen supply. As a result, the amendment treatment achieved better effects than crop rotation in increasing the accumulation of N, P, and K in peanut pods and shoots. Microbial agents had no significant impact on soil organic nitrogen fractions, especially acidolysed organic nitrogen fractions. However, they elevated the contents of ammonium nitrogen and nitrate nitrogen in the soil during the peanut seedling stage and the pegging-flowering stage, thereby promoting nutrient supply in the early growth stages of peanuts and also resulting in a significant yield increase. Therefore, the application of both amendments and microbial agents are effective measures to replace crop rotation.

     

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