Abstract:Background
Labile carbon input could stimulate soil organic carbon (SOC) mineralization through priming effect, resulting in soil carbon (C) loss. Meanwhile, labile C could also be transformed by microorganisms in soil as the processes of new C sequestration and stabilization. Previous studies showed the magnitude of priming effect could be affected by soil depth and nitrogen (N). However, it remains unknown how the soil depth and N availability affect the amount and stability of the new sequest… Show more
“…4 and 5 ), (ii) relatively sufficient nutrients in top and middle soils, and (iii) suitable pH and favorable soil structure and properties in top and middle soils ( Wang et al, 2014 ; Tian et al, 2016b ), which provided advantageous conditions for the decomposition of deciduous residues by microbes. Conversely, PI was higher in deep soils than in top and middle soils in our study, concurrent with the result of a prior study ( Liao et al, 2020 ). The proportion of residual organic carbon was calculated based on the input amount of organic carbon and emission amount of CO 2 in soils at different depths, which exhibited that the proportion of residual organic carbon was 88.88%, 88.05%, and 80.60% in top, middle, and deep soils, respectively.…”
Section: Discussionsupporting
confidence: 92%
“…Soil depth is frequently associated with new increases in CO 2 emissions ( Meyer et al, 2018 ; Liao et al, 2020 ). Throughout the incubation period, the CO 2 efflux rates and cumulative CO 2 emissions were higher in top and middle soils than in deep soils, which might be explained by the following factors: (i) high MBC and activities of soil catalase, alkaline phosphatase, and cellulase in top and middle soils ( Figs.…”
Section: Discussionmentioning
confidence: 99%
“…Responses of soil CO 2 emissions to different environments are variable because of different soil environments and physicochemical characteristics in soils at varying depths ( De Graaff et al, 2014 ; Tian et al, 2016b ; Liao et al, 2020 ). In top soils (≤10 cm), large amounts of SOC are produced and CO 2 emissions are increased because of litter, fertilization, soil fungi, bacteria, and animals ( Blanco-Canqui & Lal, 2008 ; Tian et al, 2016b ; Banfield et al, 2018 ).…”
Background
In farmland, microbes in soils are affected by exogenous carbon, nitrogen, and soil depth and are responsible for soil organic carbon (SOC) mineralization. The cherry industry has been evolving rapidly in northwest China and emerged as a new source of income for local farmers to overcome poverty. Accordingly, it is highly imperative to probe the effect of defoliation and nitrogen addition on carbon dioxide (CO2) emissions and microbial communities in soils of dryland cherry orchards.
Methods
CO2 emissions and microbial communities were determined in soil samples at three depths, including 0–10 cm, 10–30 cm, and 30–60 cm, from a 15-year-old rain-fed cherry orchard. The samples were respectively incubated with or without 1% defoliation under three input levels of nitrogen (0 mg kg−1, 90 mg kg−1, and 135 mg kg−1) at 25°C in the dark for 80 days.
Results
Defoliation and nitrogen addition affected CO2 emissions and microbial communities and increased microbial biomass carbon (MBC), the activity of soil catalase, alkaline phosphatase, and cellulase in soils of the dryland cherry orchard. The culture with defoliation significantly promoted CO2 emissions in soils at the three depths mainly by increasing the MBC, catalase, alkaline phosphatase, and cellulase activities, resulted in positive priming index. Nitrogen addition elevated the MBC and changed soil enzymes and reduced CO2 emissions in soils at the three depths. Moreover, the priming index was higher in deep soils than in top and middle soils under the condition of defoliation and nitrogen addition. No significant differences were observed in the soil bacterial diversity (Chao1, Shannon, and Simpson) among all treatments. Meanwhile, the relative abundance of Proteobacteria was markedly increased and that of Acidobacteria was substantially diminished in soils at the three depths by defoliation and nitrogen addition. The results sustained that defoliation and nitrogen can regulate SOC dynamics by directly and indirectly affecting soil microbial activities and communities. As a result, the combination of defoliation return and nitrogen fertilization management is a promising strategy to increase SOC and promote soil quality in dryland cherry orchards.
“…4 and 5 ), (ii) relatively sufficient nutrients in top and middle soils, and (iii) suitable pH and favorable soil structure and properties in top and middle soils ( Wang et al, 2014 ; Tian et al, 2016b ), which provided advantageous conditions for the decomposition of deciduous residues by microbes. Conversely, PI was higher in deep soils than in top and middle soils in our study, concurrent with the result of a prior study ( Liao et al, 2020 ). The proportion of residual organic carbon was calculated based on the input amount of organic carbon and emission amount of CO 2 in soils at different depths, which exhibited that the proportion of residual organic carbon was 88.88%, 88.05%, and 80.60% in top, middle, and deep soils, respectively.…”
Section: Discussionsupporting
confidence: 92%
“…Soil depth is frequently associated with new increases in CO 2 emissions ( Meyer et al, 2018 ; Liao et al, 2020 ). Throughout the incubation period, the CO 2 efflux rates and cumulative CO 2 emissions were higher in top and middle soils than in deep soils, which might be explained by the following factors: (i) high MBC and activities of soil catalase, alkaline phosphatase, and cellulase in top and middle soils ( Figs.…”
Section: Discussionmentioning
confidence: 99%
“…Responses of soil CO 2 emissions to different environments are variable because of different soil environments and physicochemical characteristics in soils at varying depths ( De Graaff et al, 2014 ; Tian et al, 2016b ; Liao et al, 2020 ). In top soils (≤10 cm), large amounts of SOC are produced and CO 2 emissions are increased because of litter, fertilization, soil fungi, bacteria, and animals ( Blanco-Canqui & Lal, 2008 ; Tian et al, 2016b ; Banfield et al, 2018 ).…”
Background
In farmland, microbes in soils are affected by exogenous carbon, nitrogen, and soil depth and are responsible for soil organic carbon (SOC) mineralization. The cherry industry has been evolving rapidly in northwest China and emerged as a new source of income for local farmers to overcome poverty. Accordingly, it is highly imperative to probe the effect of defoliation and nitrogen addition on carbon dioxide (CO2) emissions and microbial communities in soils of dryland cherry orchards.
Methods
CO2 emissions and microbial communities were determined in soil samples at three depths, including 0–10 cm, 10–30 cm, and 30–60 cm, from a 15-year-old rain-fed cherry orchard. The samples were respectively incubated with or without 1% defoliation under three input levels of nitrogen (0 mg kg−1, 90 mg kg−1, and 135 mg kg−1) at 25°C in the dark for 80 days.
Results
Defoliation and nitrogen addition affected CO2 emissions and microbial communities and increased microbial biomass carbon (MBC), the activity of soil catalase, alkaline phosphatase, and cellulase in soils of the dryland cherry orchard. The culture with defoliation significantly promoted CO2 emissions in soils at the three depths mainly by increasing the MBC, catalase, alkaline phosphatase, and cellulase activities, resulted in positive priming index. Nitrogen addition elevated the MBC and changed soil enzymes and reduced CO2 emissions in soils at the three depths. Moreover, the priming index was higher in deep soils than in top and middle soils under the condition of defoliation and nitrogen addition. No significant differences were observed in the soil bacterial diversity (Chao1, Shannon, and Simpson) among all treatments. Meanwhile, the relative abundance of Proteobacteria was markedly increased and that of Acidobacteria was substantially diminished in soils at the three depths by defoliation and nitrogen addition. The results sustained that defoliation and nitrogen can regulate SOC dynamics by directly and indirectly affecting soil microbial activities and communities. As a result, the combination of defoliation return and nitrogen fertilization management is a promising strategy to increase SOC and promote soil quality in dryland cherry orchards.
“…The arid regions of Southwest China, such as the transition zone between Sichuan Basin and the eastern edge of the Qinghai-Tibet Plateau, the hotspots of land degradation, have experienced a massive landuse conversion of marginal farmlands (FL) to forest plantations under grain for green program of China (GGP) (Cheng et al, 2015;Liao et al, 2020). However, previous research on FL conversion in this region has mostly emphasized soil C accumulation; apart from total N (TN), other N cycling variables are rarely reported.…”
Section: Introductionmentioning
confidence: 99%
“…Gregory et al (2016) also reported higher C and N sequestration potential of deep soil Liao et al (2020). reported that C and N pools in the subsoil (below 0-30 cm) are assumed to be more stable than the topsoil due to differences in the composition of SOM and environmental conditions.…”
Aims
Plant-soil interactions, and regulatory roles of soil nitrogen (N) fractions in availability and the magnitudes of N sequestration, therein the interplay of soil C-N in cold arid regions is poorly characterized.
Methods
Post-afforestation and land-abandonment dynamics of C and N sequestration, and total inorganic N (TIN) availability were identified by quantifying changes in diverse N fraction, and their distributions patterns in 0–100 cm soil profile across a chronosequence of Zanthoxylum bungeanum (28-year (H28), 20-year (H20), 15-year (H15), and 8-year (H8) old) plantations, and abandoned-land (GL), originally converted from former farmland (FL) in cold-arid valley in Southwest China.
Results
Afforestation and GL favored gains in labile and non-labile (LON and NLON) N fractions and total N stocks. Concentrations of LON fractions and TIN was comparatively higher at 0–40 cm. Gains in NLON fractions and total organic N (TON) was significantly higher in the deep soil, as confirmed by correlation and redundancy analysis. N and C sequestration was synchronous (r = 0.948), with cumulative (0–100 cm) increase of 1.149–1.277 folds in H28 compared to H8, at an average sequestration rate of 1.336 − 0.121 Mg ha − 1 yr − 1, respectively. N pool management index (NPMI) correlated positively with soil TON, TIN, available phosphorus, potassium, and organic N fractions. NPMI improved significantly (P < 0.05) with the plantations age.
Conclusion
Plantations age and soil depths significantly influence ecosystems N dynamics. Furthermore, TON, NPMI, N fractions, and TIN can be useful indicators to gain comprehensive insights on ecosystems N restoration patterns.
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