Manure fertilization increases soil respiration and creates a negative carbon budget in a Mediterranean maize (Zea mays L.)-based cropping system
Graphical abstract
Introduction
Soil carbon (C) sequestration is considered to be as cost-effective and a win–win option to offset anthropogenic CO2 emissions to the atmosphere (Lal et al., 2015). Croplands are considered as crucial sinks or sources of C, and the agronomy influences soil C dynamics and balance (Lal et al., 2015). Thus, ‘on-farm’ research of soil management, particularly fertilization, is important to identify suitable options for improving soil C sequestration and reducing soil CO2 emission (Paustian et al., 2016).
Soil CO2 efflux or soil respiration (SR) is principally the sum of root metabolic activity and soil heterotrophic respiration (Rh), which is the result of mesofaunal and microbial metabolism and is strongly correlated with total soil C losses (Hanson et al., 2000). Factors influencing soil CO2 efflux are the soil organic mass concentration and quality (Ferréa et al., 2012), root biomass composition (Ryan et al., 1996), soil chemical and physical properties and site productivity (Subke et al., 2011), soil temperature (T) and soil water content (SWC). T and SWC are the primary environmental factors that regulate the seasonal variation of SR (Davidson et al., 1998). Large seasonal variations in SR are evident in a Mediterranean climate due to the marked dynamics of both soil T and SWC (Rey et al., 2002). Furthermore from winter to early spring, the primary factor that affects SR is T, while during the dry period, SWC plays the most important role in controlling the process (Almagro et al., 2009).
Management practices such as irrigation (de Dato et al., 2010), tillage, crop residue management and fertilization regulate the microbial activity, which mediates the processes of organic mass turnover and nutrient cycling and, consequently, the soil C balance (Lal et al., 2015). Nitrogen (N) fertilization affects SR dynamics in agroecosystems and its relationship with abiotic factors (Ding et al., 2007). Different N fertilization sources affect soil metabolic activity as well as the soil C balance (Mancinelli et al., 2010, López-López et al., 2012, Wang et al., 2015).
Although organic fertilization is considered the most effective approach to create a positive soil C budget in croplands (Lal et al., 2015), recent studies have shown that a negative soil C budget can also occur under this fertilization system (Wang et al., 2015, Mori and Hojito, 2015). Therefore, the effect of fertilization on soil organic C dynamics is still unclear and requires further study. Maize-based cropping systems in the Mediterranean region are irrigated and supplied with high inputs of N fertilization compared to North European countries (e.g. Kayser et al., 2011) or arid climate areas (e.g. Gheysari et al., 2009). The agricultural practices employed are therefore important drivers of the economic and environmental benefits of these systems (Casa et al., 2011). Such cropping systems are suitable for studying the relationships between SR and its driving factors at a non-limiting SWC and nutrient availability (Shrestha et al., 2013) and for assessing soil C balance dynamics (Grignani et al., 2007). Therefore, the objectives of this study were i) to analyse the effects of different fertilization sources on SR and Rh, ii) to explore the effect of the fertilization regime on the sensitivity of SR and Rh to T and iii) to assess the effect of the different fertilization regimes on the soil C balance.
We hypothesized that i) soil CO2 emission dynamics in a Mediterranean irrigated cropping system were primarily influenced by fertilization management and T, and ii) fertilization affected the soil C budget via different C inputs and CO2 efflux.
Section snippets
Study site
The study was conducted on a private farm located in a Nitrate Vulnerable Zone (NVZ) in the dairy district of Arborea (39°47′ N 8°33′ E, 3 m a.s.l.) in the Central-western coast of Sardinia, Italy. The district was identified as NVZ according to the European Nitrate Directive (ND) (91/676/EC) because the groundwater nitrate concentration was found over the threshold of 50 mg L− 1. The ND implementation imposed a restriction on the N supplied from organic effluents (slurry and manure) to a maximum of
SWC, soil T, SR and Rh
SWC varied markedly (P < 0.001) with the season, consistently with the water provided (Fig. 1a), and was not significantly affected by treatment. The maximum SWC (approximately 0.30 m3 m− 3) was observed in December (Fig. 1a). Over the entire monitoring period, SWC was always higher than 0.085 m3 m− 3, and the lowest SWC was observed in the spring (Fig. 1a). The soil T (10 cm depth) ranged from 8 to 25 °C, with minimum values in January and February and a maximum in July (Fig. 1b). During the maize crop
SWC, soil T, SR and Rh
During the observation period, SWC never fell below 0.085 m3 m− 3, which corresponds to a matric potential of approximately − 33 kPa (Saxton and Rawls, 2006). Lado-Monserrat et al. (2014) reported significant effects of the SWC on soil CO2 efflux below a threshold of − 100 kPa. Therefore, the observed SWC is consistent with the assumption that the SWC was never a constraint to the SR or Rh at our research site.
In a Mediterranean climate in a rainfed cropping system, T was shown to display inverse
Conclusions
Our findings clearly show that the fertilization with just organic fertilizer did not increase the soil C budget in maize-based irrigated cropping systems, in sandy soils under Mediterranean climate. Organic fertilization increased the soil CO2 efflux response to T at a non-limiting SWC. MI showed lower sensitivity of SR or Rh to T than MA and SL.
In the autumn-spring hay crop, the top dressing of mineral N fertilizer in late winter improved the soil C balance, also because of an increase in
Acknowledgments
This research was carried out as part of the research project “Fattori gestionali sulle perdite di C dal suolo per emissioni di CO2 in atmosfera in agroecosistemi mediterranei”, in the Cooperativa Produttori Arborea within “P.O.R. SARDEGNA F.S.E. 2007-2013 - Obiettivo competitività regionale e occupazione, Asse IV Capitale umano, Linee di Attività l.1.1. e l.3.1”. The field database was built for the research project “Strumenti innovativi per la valutazione quantitativa in campo della dinamica
References (57)
- et al.
Changes in CO2 emissions after crop conversion from continuous maize to alfalfa
Agric. Ecosyst. Environ.
(2010) - et al.
Temperature dependence of soil CO2 efflux is strongly modulated by seasonal patterns of moisture availability in a Mediterranean ecosystem
Soil Biol. Biochem.
(2009) - et al.
An approach for estimating net primary productivity and annual carbon inputs to soil for common agricultural crops in Canada
Agric. Ecosyst. Environ.
(2007) - et al.
Fifty years of contrasted residue management of an agricultural crop: impacts on the soil carbon budget and on soil heterotrophic respiration
Agric. Ecosyst. Environ.
(2013) - et al.
Replacing organic with mineral N fertilization does not reduce nitrate leaching in double crop forage systems under Mediterranean conditions
Agric. Ecosyst. Environ.
(2016) - et al.
Estimating heterotrophic and autotrophic soil respiration in a semi natural forest of Lombardy, Italy
Pedobiologia
(2012) - et al.
Changes in soil aggregation and microbial community structure control carbon sequestration after afforestation of semiarid shrublands
Soil Biol. Biochem.
(2015) - et al.
Nitrate leaching in a silage maize field under different irrigation and nitrogen fertilizer rates
Agric. Water Manag.
(2009) - et al.
Production, nitrogen and carbon balance of maize-based forage systems
Eur. J. Agron.
(2007) - et al.
Review of mechanisms and quantification of priming effects
Soil Biol. Biochem.
(2000)
Carbon sequestration in soil
Curr. Opin. Environ. Sustain.
Impact of fertilisation practices on soil respiration, as measured by the metabolic index of short-term nitrogen input behavior
J. Environ. Manag.
Soil carbon dioxide emission and carbon content as affected by conventional and organic cropping systems in Mediterranean environment
Appl. Soil Ecol.
Winter wheat cultivars and nitrogen (N) fertilization— effects on root growth, N uptake efficiency and N use efficiency
Eur. J. Agron.
The effect of manure application on carbon dynamics and budgets in a managed grassland of Southern Hokkaido, Japan
Agric. Ecosyst. Environ.
Soil carbon fluxes and balances and soil properties of organically amended no-till corn production systems
Geoderma
A history of research on the link between (micro)aggregates, soil biota, and soil organic matter dynamics
Soil Tillage Res.
Carbon budget of a winter-wheat and summer-maize rotation cropland in the North China Plain
Agric. Ecosyst. Environ.
Changes in soil organic carbon stocks under agriculture in Brazil
Soil Tillage Res.
Role of maize stover incorporation on nitrogen oxide emissions in a non-irrigated Mediterranean barley field
Plant Soil
Emission of carbon dioxide influenced by nitrogen and water levels from soil incubated straw
Plant Soil Environ.
Fieni
Effect of cropping systems on soil chemical characteristics, with emphasis on soil acidification
Plant Soil
Soil Organic Matter Quality Under Different Levels of Cropping Systems Intensification
Microbial enzyme shifts explain litter decay responses to simulated nitrogen deposition
Ecology
Nitrogen fertilization management in precision agriculture: a preliminary application example on maize
Ital. J. Agron.
Soil water content and temperature as independent or confounded factors controlling soil respiration in a temperate mixed hardwood forest
Glob. Chang. Biol.
Impact of drought and increasing temperatures on soil CO2 emissions in a Mediterranean shrubland (gariga)
Plant Soil
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2021, Agricultural SystemsCitation Excerpt :Our results also suggest that manure can be used to increase soil C stock (cf. Matson et al., 1997; Smith, 1997; Buyanovsky and Wagner, 1998). However, the net effect of the manure application on GHG emissions was positive, because manure was a driving factor of soil respiration (cf. Rochette and Gregorich, 1998; Lai et al., 2017; Yang et al., 2018), which is a primary source of CO2 emissions from agricultural soils (Paustian et al., 2000; Schlesinger and Andrews, 2000; Lai et al., 2012). Thus, our results are in agreement with the conclusion of Schlesinger (1999) that manure is not a solution to agriculture's GHG emissions problem.