2017
DOI: 10.1016/j.agee.2016.12.020
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Synthetic fertilizer and livestock manure differently affect δ15N in the agricultural landscape: A review

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Cited by 111 publications
(78 citation statements)
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“…The δ 15 N values of synthetic N fertilizers (~0‰) are lower than that of organic N derived from the litters and microbes, due to negligible fractionation in chemical fixation of N 2 [21]. Choi et al [21] reported that various synthetic N fertilizer (mean δ 15 N: −0.3 ± 0.2‰) were significantly more 15 N-depleted than raw or composted livestock manure (mean δ 15 N: 7.8 ± 0.6‰). The synthetic N fertilizer in agroecosystem is the largest N source [47].…”
Section: Indication Of Agricultural Activity C and N Sources In Agrimentioning
confidence: 94%
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“…The δ 15 N values of synthetic N fertilizers (~0‰) are lower than that of organic N derived from the litters and microbes, due to negligible fractionation in chemical fixation of N 2 [21]. Choi et al [21] reported that various synthetic N fertilizer (mean δ 15 N: −0.3 ± 0.2‰) were significantly more 15 N-depleted than raw or composted livestock manure (mean δ 15 N: 7.8 ± 0.6‰). The synthetic N fertilizer in agroecosystem is the largest N source [47].…”
Section: Indication Of Agricultural Activity C and N Sources In Agrimentioning
confidence: 94%
“…Synthetic N fertilizer can be fixed into SON through microbial immobilization and crop uptake, transformation and returning into soil as litter [20]. Therefore, the δ 15 N SON in cropland commonly decreases with the application of 15 N-depleted inorganic N fertilizers [21]. However, overuse of N fertilizer causes many forms of N loss, such us leaching of NO 3 − derived from nitrification, releasing of N 2 and nitrogen oxides (NO X ) after denitrification, and ammonia (NH 3 ) volatilization, and these N losses generally lead to 15 N enrichment in the remaining SON [21].…”
Section: Introductionmentioning
confidence: 99%
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“…The second major DIN source is allochthonous nitrogen contributions-either in organic or mineralized form-derived from other environments, especially terrestrial soil nitrogen. The movement of nitrogen from agricultural and forest soils into aquatic ecosystems (see section Anthropogenic Nutrient Loading), for instance, can result in significant upward shifts in the stable nitrogen isotopic composition of entire aquatic food webs (McClelland et al, 1997) not only due to differences in the initial δ 15 N of transported soil nutrients (Koerner et al, 1999) but also due to bacterial and physical processing acting on soil nitrogen during transportation that causes nitrogen isotope fractionation (usually leading to 15 N enrichments) (Diebel and Vander Zanden, 2009;Botrel et al, 2014;Choi et al, 2017).…”
Section: Variation In Nitrogen Sourcesmentioning
confidence: 99%
“…In the water percolating through the soil matrix, a fraction of the DRP likely precipitated as Ca phosphates or was sorbed to amorphous and organically complexed Fe and Mn metals (Leytem and Westermann, 2003). The manure-derived DOC and NO 3 -N leached from surface soil may have been (i) utilized as nutrient or energy sources by subsoil microorganisms, resulting in increased immobilization, or (ii) lost from the system via microsite denitrification or in the subsequent reduction of deep-leached NO 3 -N (Choi et al, 2017). These processes ultimately reduced the N leaching coefficient (N leached/total N applied) for manure (158/596 = 0.3) relative to that of mineral fertilizer (430/391 = 1.1).…”
Section: Constituent Concentration and Mass Lossesmentioning
confidence: 99%