An understanding of crop availability of livestock slurry nitrogen (N) is necessary to maximise crop N use efficiency and to minimise environmental losses. Results from field and laboratory incubation experiments suggest that first-year crop availability of slurry N comes mainly from its ammonium fraction because net mineralisation of organic N is often negligible in the short term. A two-year field experiment during 2011 and 2012 in northern Italy was undertaken with several aims: to estimate the N fertiliser value of raw dairy cow slurry, digested dairy cow slurry, and the liquid and solid fractions of the digested slurry, and to verify if applied ammonium recovery was similar both among slurries and between slurries and inorganic N fertiliser (ammonium sulphate).Different fertilisers were applied before silage maize cultivation followed by an unfertilised Italian ryegrass crop. The results showed that ammonium recovery was significantly higher in mineral-fertilised (75%) versus slurry-fertilised (30%) treatments, except in digested slurry (65%). This indicates that ammonium applied with organic materials is less efficient than when applied with mineral fertiliser. For the digested slurry and its liquid fraction, most of the applied ammonium was available to the maize during its application year (55%) due to a low carbon (C)/organic N ratio. The apparent N recovery of the raw slurry and digested slurry solid fraction increased substantially between the first (-1.4%) and second (20%) years, as these materials had high C/organic N ratios; they likely immobilised N for several months post application, producing residual effects during the Italian ryegrass and next maize crops.
IntroductionRaw and anaerobically digested livestock slurries can be valuable fertilisers because they supply nutrients and organic matter to the soil.Anaerobic digestion of organic biomasses has seen considerable growth in Europe (Eurobserv'er, 2013) and in northern Italy (Fabbri et al., 2013) over the last decade.Many biogas plants co-digest livestock and biomasses to increase methane production, and in northern Italy, energy crops are often dedicated for co-digestion (Fabbri et al., 2013). To facilitate the use of digested slurries as fertilisers, liquid and solid fractions are separated to ease their transport (Möller and Müller, 2012).A deep understanding of applied slurry nitrogen (N) turnover in soil, and identification of practices to reduce N losses are required to maximise crop N use efficiency and to minimise environmental losses. Nutrient management plans (NMPs) maximise crop N use efficiency through calculation of the slurry amount needed for optimal crop production, and determination of application dates that match crop nutrient requirements according to soil type, local climate, and crop characteristics (Grignani et al., 2003). The slurry N fertiliser value is normally accounted for in a NMP by apparent nitrogen recovery (ANR), an expression of the fraction of applied total N that on average can be taken up by the cro...