Effect of crop residue quality, nitrogen rate and CNPS stoichiometry on microbial respiration and C pools in a dispersive subsoil

IF 6.8 1区 农林科学 Q1 SOIL SCIENCE
Andrew T. Regan , John A. Kirkegaard , Alan E. Richardson , Brian R. Wilson , Chris N. Guppy
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引用次数: 0

Abstract

Soil organic matter (SOM) is crucial for nutrient cycling, biological health, and aggregate stability. Integrated residue and nutrient management (IRNM) is an innovative method of retaining SOM in cropping systems and involves the incorporation of crop residues with exogenous nutrients at a targeted ratio of 10,000 C:833 N:200 P:143S. The practicalities of IRNM for adoption by farmers remain uncertain as limited data exists on soil C response to residues of varying quality and specific impacts of each nutrient. Furthermore, little is known about the effectiveness of IRNM to build SOM on degraded soils such as dispersive subsoils, and recent studies have found stable SOM can occur in both the mineral-associated organic carbon (MAOC) and particulate organic carbon (POC) fractions. An incubation experiment was conducted to determine the microbial respiration response and changes to mid-infrared spectroscopy derived soil C pools under three residue treatments (no residue (Nil-res), a sorghum residue with low nutrient content (R1) and a sorghum residue with higher nutrient content (R2)), three N rates (Nil N, Half N, Full N), and three nutrient treatments (N, N(+S), and N(+S+P)). The application of residue compared to Nil-res caused an increase in total organic carbon (TOC) from 0.57 % to 0.69 %, MAOC from 0.44 % to 0.51 % and POC from 0.09 % to 0.13 %. Within residue treatment groups, the application of N at the Full N rate was the major determinant of C increase followed by application of N(+S+P) compared to N and N(+S). There was an increase in CO2 respiration following application of both residues versus Nil-res, and Full N versus Half N and Nil-N. Microbial respiration was significantly higher in the N and N(+S+P) treatments compared to the N(+S) and nutrient control. When residue was applied, the correlation between respiration and C was negative in the nutrient control and positive when applied with N(+S+P). The concomitant increase in CO2 respiration and MAOC following residue incorporation indicated microbial cycling of C occurred leading to stabilisation. Overall, the study provided initial evidence that microbial cycling of C is mediated by the adequate supply of nutrients and this occurred on a soil that contains abiotic stressors that limit plant growth (therefore C inputs) and microbial health.
作物残茬品质、施氮量和CNPS化学计量对分散底土微生物呼吸和碳库的影响
土壤有机质(SOM)对养分循环、生物健康和团聚体稳定性至关重要。残留物和养分综合管理(IRNM)是一种在种植系统中保留SOM的创新方法,涉及作物残留物与外源养分的结合,目标比例为10,000 C:833 N:200 P:143S。由于关于土壤C对不同质量残留物的反应和每种养分的具体影响的数据有限,农民采用IRNM的实用性仍不确定。此外,人们对IRNM在退化土壤(如分散性底土)上构建SOM的有效性知之甚少,最近的研究发现,稳定的SOM可以发生在矿物相关有机碳(MAOC)和颗粒有机碳(POC)组分中。通过培养试验,研究了3种秸秆处理(无秸秆(Nil-res)、低营养含量高粱秸秆(R1)和高营养含量高粱秸秆(R2))、3种施氮率(无氮、半氮、全氮)和3种养分处理(N、N(+S)和N(+S+P))下微生物呼吸响应和中红外光谱土壤碳库的变化。施用残渣使总有机碳(TOC)从0.57 %增加到0.69 %,MAOC从0.44 %增加到0.51 %,POC从0.09 %增加到0.13 %。在残茬处理组中,与N + N +S相比,全氮施氮是碳增加的主要决定因素,其次是N(+S+P)。在施用两种残留物与硝态氮、全氮与半氮和硝态氮之后,CO2呼吸增加。氮(+S)和氮(+S) +磷处理的微生物呼吸显著高于氮(+S)和营养对照。施残渣处理下,养分对照下呼吸与碳呈负相关,施N(+S+P)处理下呼吸与碳呈正相关。残渣掺入后CO2呼吸和MAOC的增加表明C的微生物循环导致稳定。总体而言,该研究提供了初步证据,表明微生物的碳循环是由充足的养分供应介导的,这种循环发生在含有限制植物生长(因此是碳输入)和微生物健康的非生物胁迫源的土壤上。
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来源期刊
Soil & Tillage Research
Soil & Tillage Research 农林科学-土壤科学
CiteScore
13.00
自引率
6.20%
发文量
266
审稿时长
5 months
期刊介绍: Soil & Tillage Research examines the physical, chemical and biological changes in the soil caused by tillage and field traffic. Manuscripts will be considered on aspects of soil science, physics, technology, mechanization and applied engineering for a sustainable balance among productivity, environmental quality and profitability. The following are examples of suitable topics within the scope of the journal of Soil and Tillage Research: The agricultural and biosystems engineering associated with tillage (including no-tillage, reduced-tillage and direct drilling), irrigation and drainage, crops and crop rotations, fertilization, rehabilitation of mine spoils and processes used to modify soils. Soil change effects on establishment and yield of crops, growth of plants and roots, structure and erosion of soil, cycling of carbon and nutrients, greenhouse gas emissions, leaching, runoff and other processes that affect environmental quality. Characterization or modeling of tillage and field traffic responses, soil, climate, or topographic effects, soil deformation processes, tillage tools, traction devices, energy requirements, economics, surface and subsurface water quality effects, tillage effects on weed, pest and disease control, and their interactions.
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