Nitrogen fertilization enhances soil quality in the short-term in irrigated intensified maize systems

Introduction

Soil quality is a primary indicator of sustainable agricultural management (Doran, 2002Doran JW, 2002. Soil health and global sustainability: translating science into practice. Agric Ecosyst Environ. 88:119–127. https://doi.org/10.1016/s0167-8809(01)00246-8
) since it encompasses the ability of a soil to support crop growth without harming environmental quality (Karlen et al., 1997Karlen DL, Mausbach MJ, Doran JW, Cline RG, Harris RF, Schuman GE, 1997. Soil Quality: A Concept, Definition, and Framework for Evaluation (A Guest Editorial). Soil Sci Soc Am J. 61:4–10. https://doi.org/10.2136/sssaj1997.03615995006100010001x
). A number of soil quality and health indicators are easy to find in the literature (Andrews & Carroll, 2001Andrews SS, Carroll CR, 2001. Designing a soil quality assessment tool for sustainable agroecosystem management. Ecol Appl. 11:1573–1585. https://doi.org/10.2307/3061079
; Bünemann et al., 2018Bünemann EK, Bongiorno G, Bai Z, Creamer RE, Deyn GD, Goede R, de Fleskens L, Geissen V, Kuyper TW, Mäder P, Pulleman M, Sukkel W, van Groenigen JW, Brussaard L, 2018. Soil quality – A critical review. Soil Biol Biochem. 120:105–125. https://doi.org/10.1016/j.soilbio.2018.01.030
) and the ideal indicator should be informative, sensitive, effective, and relevant (Lehmann et al., 2020Lehmann J, Bossio DA, Kögel-Knabner I, Rillig MC, 2020. The concept and future prospects of soil health. Nat Rev Earth Environ. 1:544–553. https://doi.org/10.1038/s43017-020-0080-8
). One of the main indicators is soil organic carbon (SOC), due to its importance and the role it plays in many soil functions and ecosystems services (Nuneset al., 2021Nunes MR, Veum KS, Parker PA, Holan SH, Karlen DL, Amsili JP, Es HM, Wills SA, Seybold CA, Moorman TB, 2021. The soil health assessment protocol and evaluation applied to soil organic carbon. Soil Sci Soc Am J. 85:1196–1213. https://doi.org/10.1002/saj2.20244
). However, SOC changes usually take time to occur and, thereby, increases and/or decreases are observed several years after any management change (Smith, 2004Smith P, 2004. How long before a change in soil organic carbon can be detected? Global Change Biol. 10:1878–1883. https://doi.org/10.1111/j.1365-2486.2004.00854.x
). Accordingly, it is interesting to evaluate and test other more rapid indicators that provide insight into soil carbon (C) changes in the short-term (Plaza-Bonilla et al., 2014Plaza-Bonilla D, Álvaro-Fuentes J, Cantero-Martínez C, 2014. Identifying soil organic carbon fractions sensitive to agricultural management practices. Soil Tillage Res. 139: 19–22. https://doi.org/10.1016/j.still.2014.01.006
), such as soil C fractions or soil biological properties (e.g., microbial biomass or enzyme activities) (Lehmannet al., 2020Lehmann J, Bossio DA, Kögel-Knabner I, Rillig MC, 2020. The concept and future prospects of soil health. Nat Rev Earth Environ. 1:544–553. https://doi.org/10.1038/s43017-020-0080-8
). Identifying selected soil quality indicators would allow optimal management practices to be adopted, especially in semiarid irrigated maize production areas in which rapid changes in certain soil properties have been observed after a shift in management practices (Álvaro-Fuentes et al., 2021Álvaro-Fuentes J, Franco-Luesma S, Lafuente V, Sen P, Usón A, Cantero-Martínez C, Arrúe JL, 2021. Stover management modifies soil organic carbon dynamics in the short-term under semiarid continuous maize. Soil Tillage Res. 213:105143. https://doi.org/10.1016/j.still.2021.105143
).

In Mediterranean areas, irrigated maize is intensively managed with the associated elevated use of agriculture inputs (pesticides, fertilisers, tillage) and the continuous growth of maize as the main cropping system, with no crop diversification. Increased fertiliser use, particularly of nitrogen (N) fertilisers, is linked to high production costs and severe environmental problems, including greenhouse gas emissions (Franco-Luesma et al., 2020Franco-Luesma S, Cavero J, Plaza-Bonilla D, Cantero-Martínez C, Tortosa G, Bedmar EJ, Álvaro-Fuentes J, 2020. Irrigation and tillage effects on soil nitrous oxide emissions in maize monoculture. Agron J. 112:56–71. https://doi.org/10.1002/agj2.20057
) and nitrate pollution (Berenguer et al., 2008Berenguer P, Santiveri F, Boixadera J, Lloveras J, 2008. Fertilisation of irrigated maize with pig slurry combined with mineral nitrogen. Eur J Agron. 28:635–645. https://doi.org/10.1016/j.eja.2008.01.010
). However, the effect of N fertilisation on SOC and associated C pools is not clear since it has been associated to both positive and negative effects on soil organic matter mineralisation (Mahal et al., 2019Mahal NK, Osterholz WR, Miguez FE, Poffenbarger HJ, Sawyer JE, Olk DC, Archontoulis SV, Castellano MJ, 2019. Nitrogen Fertilizer Suppresses Mineralization of Soil Organic Matter in Maize Agroecosystems. Frontiers Ecol Evol. 7:59. https://doi.org/10.3389/fevo.2019.00059
). Likewise, the expected positive effect of N fertilisation on soil C inputs and, thus, on SOC storage is dependent on attaining the agronomic optimum N fertilisation rate (Poffenbarger et al., 2017Poffenbarger HJ, Barker DW, Helmers MJ, Miguez FE, Olk DC, Sawyer JE, Six J, Castellano MJ, 2017. Maximum soil organic carbon storage in Midwest U.S. cropping systems when crops are optimally nitrogen-fertilized. Plos One. 12:e0172293. https://doi.org/10.1371/journal.pone.0172293
). According to Poffenbarger et al. (2017)Poffenbarger HJ, Barker DW, Helmers MJ, Miguez FE, Olk DC, Sawyer JE, Six J, Castellano MJ, 2017. Maximum soil organic carbon storage in Midwest U.S. cropping systems when crops are optimally nitrogen-fertilized. Plos One. 12:e0172293. https://doi.org/10.1371/journal.pone.0172293
, N rates above the agronomic optimum N fertilisation rate do not increase crop residue inputs, but may favour soil organic matter mineralisation due to the increase in soil mineral N.

One option which is gaining ground as a method for reducing the use of N fertilisers in irrigated maize systems in Mediterranean Spain is crop diversification, introducing N-fixing crops (Gabriel & Quemada, 2011Gabriel JL, Quemada M, 2011. Replacing bare fallow with cover crops in a maize cropping system: yield, N uptake and fertiliser fate. Eur J Agron. 34:133-143. https://doi.org/10.1016/j.eja.2010.11.006
). In this area, the majority of studies have been oriented at evaluating what agronomic impact the introduction of legumes as cover crops has, as a substitute for the typical bare fallow between maize seasons (Salmerón et al., 2010Salmerón M, Cavero J, Quílez D, Isla R, 2010. Winter Cover Crops Affect Monoculture Maize Yield and Nitrogen Leaching under Irrigated Mediterranean Conditions. Agron J. 102:1700. https://doi.org/10.2134/agronj2010.0180
; Gabriel et al., 2012Gabriel JL, Muñoz-Carpena R, Quemada M, 2012. The role of cover crops in irrigated systems: Water balance, nitrate leaching and soil mineral nitrogen accumulation. Agric Ecosyst Environ. 155:50–61. https://doi.org/10.1016/j.agee.2012.03.021.
). However, less attention has been paid to evaluating the performance of double-annual cropping systems in which the system is intensified through the growth of two crops within the same year, involving the associated increased production and profitability per land unit (Maresma et al., 2019Maresma A, Martínez-Casasnovas JA, Santiveri F, Lloveras J, 2019. Nitrogen management in double-annual cropping system (barley-maize) under irrigated Mediterranean enviroments. Eur J Agron. 103:98-107. https://doi.org/10.1016/j.eja.2018.12.002
). Besides the agronomic performance, the impact of cropping system changes on soil quality parameters has also been evaluated but only in terms of cover crops for which positive impacts on SOC and C fractions (García-González et al., 2018García-González I, Hontoria C, Gabriel JL, Alonso-Ayuso M, Quemada M, 2018. Cover crops to mitigate soil degradation and enhance soil functionality in irrigated land. Geoderma. 322:81–88. https://doi.org/10.1016/j.geoderma.2018.02.024
), arbuscular mycorrhizal fungi (Hontoria et al., 2019Hontoria C, García-González I, Quemada M, Roldán A, Alguacil MM, 2019. The cover crop determines the AMF community composition in soil and in roots of maize after a ten-year continuous crop rotation. Sci Total Environ. 660:913–922. https://doi.org/10.1016/j.scitotenv.2019.01.095
) and soil microorganisms (Muñoz et al., 2007Muñoz A, López-Piñeiro A, Ramírez M, 2007. Soil quality attributes of conservation management regimes in a semi-arid region of south western Spain. Soil Tillage Res. 95:255–265. https://doi.org/10.1016/j.still.2007.01.009
) have been reported. However, the impact of cropping intensification on other soil properties related to soil quality, such as soil enzyme activities, and in other systems besides cover crops (e.g., cropping intensification through double-annual cropping systems) is less studied in these irrigated maize systems (Maresma et al., 2019Maresma A, Martínez-Casasnovas JA, Santiveri F, Lloveras J, 2019. Nitrogen management in double-annual cropping system (barley-maize) under irrigated Mediterranean enviroments. Eur J Agron. 103:98-107. https://doi.org/10.1016/j.eja.2018.12.002
; Zugasti-López et al., 2024Zugasti-López I, Cavero J, Clavería I, Álvaro-Fuentes J, Isla R, 2024. Alternatives to maize monocropping in Mediterranean irrigated conditions to reduce greenhouse gas emissions. Sci Total Environ. 912:169030. https://doi.org/10.1016/j.scitotenv.2023.169030
). Accordingly, this study had a double objective that consisted of: (i) assessing the effects of N fertilisation on soil quality under different cropping systems (monocropping vs. double-annual cropping systems) under irrigated maize conditions; and (ii) identifying soil parameters related to soil quality that respond quickly to short-term management changes in Mediterranean irrigated maize systems. Our main hypothesis was that the expected positive effect of N fertilisation on crop residue production would promote a short-term increase in soil parameter values related to soil quality.

Material and methods

Results

The N fertilisation rate impacted the aboveground crop residue biomass but only in the two diversified cropping systems (Table 2). In the MM systems, the total crop residue biomass produced in the two growing seasons (2018-2019 and 2019-2020) was similar among the different N fertilisation rates. However, in the PM rotation the two fertilised treatments showed greater crop residue biomass than the unfertilised treatment (Table 2). In the BM rotation, residue production decreased in the order HN>MN>0N. Additionally, in the two intensified systems (PM and BM), the proportions of maize residue biomass in the two double cropping systems were 62 and 66% for the maize-barley and maize-pea systems, respectively (Table 2).

The analysis of variance of soil properties showed significant differences for the two main factors considered, soil depth and fertilisation N rate (Table 3). The soil depth affected all the soil properties studied, except for WSM. In all cases, the greatest values were always observed in the first 10 cm soil depth. The maximum difference between the two soil depths (0-10 and 10-30) was observed for the macroaggregate C in which the C content of the topsoil was 40% greater than at 10-30 cm depth. In the other soil properties, the difference between the two soil depths ranged between 10 and 24% (Table 3).

The N fertilisation rate affected macroaggregate C, SOC, POM-C, MBC, and the ß-glucosidase enzyme activity. These five soil properties were also affected by the soil depth, as were POxC and the dehydrogenase enzyme activity (Table 3). The unfertilised treatment (0N) showed the lowest SOC, POM-C, MBC and ß-glucosidase activity. However, in the case of macroaggregate C, the 0N and MN levels presented lower contents than with HN (Table 3). The WSM, POxC and dehydrogenase activity did not differ between N fertilisation levels. When the effect of the N fertilisation rate was analysed across cropping systems and for each soil layer, different trends were observed depending on the soil variable considered (Figs. 1 and 2). At the 0-10 cm soil depth, WSM, POxC and MBC were affected by the N fertilisation rate but only in the BM system, where the 0N rate always presented the lowest values (together with MBC in the case of BM) (Fig. 1). The POM-C and ß-glucosidase activity was affected by the N fertilisation rate in the two diversified systems (PM and BM). As before, in these two cropping systems the lowest POM-C and ß-glucosidase activity values were observed for the 0N rate (Fig. 1). The exception was the PM system, where both soil properties presented similar values for the 0N and the MN rates. The total SOC content showed differences in the MM monoculture and the BM rotation. In MM, the HN rate led to a 10% greater SOC content compared to 0N (Fig. 1). However, in the BM rotation, the SOC content in 0N was 17 and 22% lower than the MN and HN, respectively (Fig. 1). In the MM and PM systems, the C concentration of soil macroaggregates was significantly greater under HN than under 0N, this difference being almost two-fold in the case of PM (Fig. 1). The dehydrogenase activity was the only soil variable studied which did not present significant differences among N rates for any cropping system (Fig. 1). At the 10-30 cm soil depth, ß-glucosidase activity was the only soil variable to show significant differences between N fertilisation rates (Fig. 2). In particular, the differences in ß-glucosidase activity were only observed in the BM system, where the 0N rate showed the lowest enzyme activity with values close to 0.8 μmol pNP g^-1 dry soil h^-1 (Fig. 1).

The WSM was affected by the interaction between the cropping system and soil depth (Table 3). Compared to the PM and BM systems, in the MM system the WSM at 10-30 cm soil depth was greater than at 0-10 cm (data not shown). Likewise, the POM-C was affected by the interaction between the N fertilisation rate and soil depth. The POM-C in the 0N treatment was similar between the two soil depths, unlike MN and HN in which greater POM-C was observed at 0-10 cm depth compared to 10-30 cm (data not shown) (Table 3).

The eight soil parameters studied together with the aboveground crop residue biomass showed significant positive Pearson correlation coefficients except for the relationship between aboveground crop residues and the macroaggregate C concentration (Table 4). There was no correlation between macroaggregate C and the following parameters: WSM, MBC, POM-C and the two enzyme activities (dehydrogenase and ß-glucosidase), nor in any of the relationships of the aboveground crop residue biomass with soil parameters, except for the relationship between crop residues and ß-glucosidase (Table 4). The highest coefficients were found in the relationship between SOC and POM-C (0.88) and between SOC and the ß-glucosidase enzyme activity (0.88). In contrast, the lowest significant coefficients were found in the relationships between aboveground crop residue biomass and ß-glucosidase, and between SOC and macroaggregate C, where the coefficients only reached 0.28 and 0.36, respectively (Table 4).

Discussion

This study, performed under irrigated Mediterranean conditions, demonstrates the short-term effect of N fertilisation in different cropping systems on soil properties related to soil quality. In general, it was observed that unfertilised treatments always tended to show lower soil property values compared to the two fertilised treatments (MN and HN). According to Geisseler and Scow (2014)Geisseler D, Scow KM, 2014. Long-term effects of mineral fertilizers on soil microorganisms – A review. Soil Biol Biochem. 75:54–63. https://doi.org/10.1016/j.soilbio.2014.03.023
, mineral N fertilisation increases SOC levels and, concomitantly, soil microbial biomass, with SOC being a major factor controlling microbial growth and activity. In our experiment, the significant increase between the unfertilised and fertilised plots was not only observed for SOC and microbial biomass but also for other soil properties related to the C cycle (POM-C, Macro-C) and microbial activity (ß-glucosidase). Interestingly, in our study, the positive effect of N fertilisation on SOC, C fractions and related microbial activity properties relied on the cropping system established. Hence, the BM cropping system showed the greatest impact of N fertilisation on soil properties, followed by PM and, lastly, the monoculture (MM). In other words, cropping intensification, by reducing the fallow period, boosted the positive effect of N fertilisation on SOC, C fractions and microbial activity. It has been reported that reduced fallow duration improves the overall soil condition (Álvaro-Fuentes et al., 2008Álvaro-Fuentes J, Arrúe JL, Gracia R, López MV, 2008. Tillage and cropping intensification effects on soil aggregation: Temporal dynamics and controlling factors under semiarid conditions. Geoderma. 145:390–396. https://doi.org/10.1016/j.geoderma.2008.04.005
; Rosenweig et al., 2018Rosenzweig ST, Fonte SJ, Schipanski ME, 2018. Intensifying rotations increases soil carbon, fungi, and aggregation in semi-arid agroecosystems. Agric Ecosyst Environ. 258:14–22. https://doi.org/10.1016/j.agee.2018.01.016.
; Gabriel et al., 2021Gabriel JL, García-González I, Quemada M, Martin-Lammerding D, Alonso-Ayuso M, Hontoria C, 2021. Cover crops reduce soil resistance to penetration by preserving soil surface water content. Geoderma. 386:114911. https://doi.org/10.1016/j.geoderma.2020.114911
). Therefore, in our experiment, the reduction of the bare fallow period in the PM and BM systems should have improved the overall soil performance. In an irrigated experiment in central Spain, after 10 years, the reduction of the fallow period through the introduction of barley and vetch cover crops between summer maize and sunflower crops improved several soil properties such as reduced penetration resistance and increased SOC and water-stable aggregates (García-González et al., 2018García-González I, Hontoria C, Gabriel JL, Alonso-Ayuso M, Quemada M, 2018. Cover crops to mitigate soil degradation and enhance soil functionality in irrigated land. Geoderma. 322:81–88. https://doi.org/10.1016/j.geoderma.2018.02.024
; Gabriel et al., 2021Gabriel JL, García-González I, Quemada M, Martin-Lammerding D, Alonso-Ayuso M, Hontoria C, 2021. Cover crops reduce soil resistance to penetration by preserving soil surface water content. Geoderma. 386:114911. https://doi.org/10.1016/j.geoderma.2020.114911
). In that experiment, after two years, SOC and water-stable aggregates in the barley-maize system increased about 29 and 41% compared to the maize monoculture (García-González et al. 2018García-González I, Hontoria C, Gabriel JL, Alonso-Ayuso M, Quemada M, 2018. Cover crops to mitigate soil degradation and enhance soil functionality in irrigated land. Geoderma. 322:81–88. https://doi.org/10.1016/j.geoderma.2018.02.024
). In our experiment, the difference between the monoculture and the two intensified cropping systems was lower for SOC (15%) but greater for the water-stable macroaggregates (74%).

It is well established that crop residues and carbon inputs control SOC accrual in agroecosystems (Virto et al., 2012Virto I, Barré P, Burlot A, Chenu C, 2011. Carbon input differences as the main factor explaining the variability in soil organic C storage in no-tilled compared to inversion tilled agrosystems. Biogeochemistry. 108:17–26. https://doi.org/10.1007/s10533-011-9600-4
; Fujisaki et al., 2018Fujisaki K, Chevallier T, Chapuis-Lardy L, Albrecht A, Razafimbelo T, Masse D, Ndour YB, Chotte JL, 2018. Soil carbon stock changes in tropical croplands are mainly driven by carbon inputs: A synthesis. Agric Ecosyst Environ. 259:147–158. https://doi.org/10.1016/j.agee.2017.12.008
). In our study, the PM and BM rotations implied two crops per year (pea/barley and maize) whereas in the MM only one crop (maize) was grown per year followed by a 6-month fallow period between the two consecutive maize seasons. Replacing this fallow period with a crop (pea or barley) in the two rotations (PM and BM, respectively) resulted in 15% greater aboveground crop residues which returned to the soil surface. However, according to the results of the correlation analysis, the differences in aboveground crop residues between cropping systems was not enough to explain the variability observed in the soil parameters studied. Therefore, in this irrigated Mediterranean system, other variables such as belowground crop residues or root exudates could be more important drivers of the changes found in the soil parameters studied. It has been observed that root C presents greater mean residence times and, consequently, greater stabilisation in the soil than aboveground crop C (Rasse et al., 2005Rasse DP, Rumpel C, Dignac M-F, 2005. Is soil carbon mostly root carbon? Mechanisms for a specific stabilisation. Plant Soil. 269: 341-356 https://doi.org/10.1007/s11104-004-0907-y
).

Besides the intensification of the cropping systems, N fertilisation also favours crop residue production and SOC increase (Halvorson et al., 2011Halvorson AD, Jantalia CP, 2011. Nitrogen Fertilization Effects on Irrigated No-Till Corn Production and Soil Carbon and Nitrogen. Agron J. 103:1423. https://doi.org/10.2134/agronj2011.0102
; Poffenbarger et al., 2017Poffenbarger HJ, Barker DW, Helmers MJ, Miguez FE, Olk DC, Sawyer JE, Six J, Castellano MJ, 2017. Maximum soil organic carbon storage in Midwest U.S. cropping systems when crops are optimally nitrogen-fertilized. Plos One. 12:e0172293. https://doi.org/10.1371/journal.pone.0172293
). However, in an irrigated maize monoculture experiment, also in NE Spain, it was observed that under conventional tillage, N fertilisation did not affect SOC and the related C fractions, but this was positively affected under no-tillage (Pareja-Sánchez et al., 2020Pareja-Sánchez E, Cantero-Martínez C, Álvaro-Fuentes J, Plaza-Bonilla D, 2020. Soil organic carbon sequestration when converting a rainfed cropping system to irrigated corn under different tillage systems and N fertilizer rates. Soil Sci Soc Am J. 84: 1219–1232. https://doi.org/10.1002/saj2.20116
). These latter authors concluded that intensive tillage limited crop growth and, in turn, residue production with the concomitant constraint in SOC build-up (Pareja-Sánchez et al., 2020Pareja-Sánchez E, Cantero-Martínez C, Álvaro-Fuentes J, Plaza-Bonilla D, 2020. Soil organic carbon sequestration when converting a rainfed cropping system to irrigated corn under different tillage systems and N fertilizer rates. Soil Sci Soc Am J. 84: 1219–1232. https://doi.org/10.1002/saj2.20116
). Furthermore, in our study, also under conventional tillage conditions, in the MM system the crop residues did not respond to N fertilisation. This would explain the lack of response to N fertilisation found in the majority of soil properties in the MM system. However, in the two diversified systems (PM and BM) aboveground crop residues did respond to N fertilisation and, concomitantly, different soil properties were affected by N fertilisation.

Active SOC pool measurements are an effective way of detecting early changes in SOC trends in response to land use and management changes (Cotrufo et al., 2019Cotrufo MF, Ranalli MG, Haddix ML, Six J, Lugato E, 2019. Soil carbon storage informed by particulate and mineral-associated organic matter. Nat Geosci. 12:989–994. https://doi.org/10.1038/s41561-019-0484-6
). In our study, two active C pools were measured, POM-C and POxC. In the two diversified systems, the differences in POM-C between the fertilised and the unfertilised treatments were higher than for POxC and, indeed, significant differences in POM-C were even obtained in PM where no differences were found in POxC. Also, in NE Spain, but under rainfed conditions, it was concluded that POM-C was a better predictor of total SOC changes than POxC for a number of management practices and soil depths (Plaza-Bonilla et al., 2014Plaza-Bonilla D, Álvaro-Fuentes J, Cantero-Martínez C, 2014. Identifying soil organic carbon fractions sensitive to agricultural management practices. Soil Tillage Res. 139: 19–22. https://doi.org/10.1016/j.still.2014.01.006
). This is related to the nature of each active C fraction since the POxC pool is associated with smaller and heavier POM-C and therefore with a higher degree of stabilisation (Culman et al., 2012Culman SW, Snapp SS, Freeman MA, Schipanski ME, Beniston J, Lal R, Drinkwater LE, Franzluebbers AJ, Glover JD, Grandy AS, Lee J, Six J, Maul JE, Mirksy SB, Spargo JT, Wander MM, 2012. Permanganate Oxidizable Carbon Reflects a Processed Soil Fraction that is Sensitive to Management. Soil Sci Soc Am J. 76:494–504. https://doi.org/10.2136/sssaj2011.0286
).

ß-glucosidase has been recognised as an interesting indicator of short-term soil quality changes (Ndiaye et al., 2009Ndiaye EL, Sandeno JM, McGrath D, Dick RP, 2000. Integrative biological indicators for detecting change in soil quality. Am J Altern Agric. 15:26–36. https://doi.org/10.1017/S0889189300008432
) and the stability of this enzyme activity between seasons is also an advantage as a soil quality indicator (Knight & Dick 2004Knight TR, Dick RP, 2004. Differentiating microbial and stabilized β-glucosidase activity relative to soil quality. Soil Biol. Biochem. 36:2089–2096. https://doi.org/10.1016/j.soilbio.2004.06.007
). In our experiment, the ß-glucosidase activity was the only soil parameter which showed differences at both soil depths and it was also the only parameter that positively correlated with aboveground crop residues, showing its ability as a fast-response parameter to reflect changes in soil and crop management.

Conclusions

Our results demonstrate that under Mediterranean irrigated maize conditions, N fertilisation has a positive effect on a number of soil parameters related to soil quality in the short-term. Furthermore, this positive effect of N fertilisation on soil quality may vary depending on the cropping system considered. Indeed, when intensified cropping systems are implemented, N fertilisation increases its positive effect on soil properties related to soil quality. In this sense, in Mediterranean irrigated maize systems the combination of N fertilisation and cropping intensification is a promising strategy for attaining beneficial soil quality effects only two years after the start of the experiment.

Competing interests

The authors have declared that no competing interests exist.

Authors’ contributions

Victoria Lafuente: Data acquisition, formal analysis, Writing—review. Ana Bielsa: Data acquisition, formal analysis. María Alonso-Ayuso: Writing—review; editing. Samuel Franco-Luesma: Conceptualization, data acquisition, writing—original draft, data curation, methodology, formal analysis, investigation. Carmen Castañeda: Conceptualization, methodology, investigation; Laura B. Martínez-García: Data curation, formal analysis, investigation. José L. Arrúe: Writing—review; editing. Jorge Álvaro-Fuentes: Conceptualization, methodology, investigation, writing—review; editing, supervision, project administration, resources, funding acquisition.

References