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a Dep. of Soil Management and Soil Care, Ghent Univ. Coupure Links 653, 9000 Gent, Belgium
b Lab. of Applied Physical Chemistry (ISOFYS), Ghent Univ., Coupure Links 653, 9000 Gent, Belgium
* Corresponding author (Barbara.Chaves{at}ilvo.vlaanderen.be).
Following mineralization of N-rich crop residues, large amounts of mineral N can be released into the soil. Manipulating N mineralization of crop residues may be an option to reduce NO3 in soil. The potential to manipulate the N release from vegetable crop residues by using organic wastes was tested under field conditions. At the start of the experiment, cauliflower (Brassica oleracea L. var. botrytis L.) residues (
73 Mg fresh matter ha1) together with an immobilizer waste (
5 Mg C ha1 of straw, green waste compost, sawdust, or paper sludge) were incorporated into a silt loam soil. After 154 d, a remineralizing waste (
1 Mg C ha1 of vinasse or dairy sludge) was incorporated. During the field experiment, the mineral N content in the soil was measured at regular time intervals, and net N release, NO3 leaching, and denitrification were simulated using a N mineralizationimmobilization model coupled to a NO3 leaching model. Straw, green waste compost, and sawdust were able to immobilize between 54 and 68% of the N released by the cauliflower residues and reduced NO3 leaching by 56 to 68%. Paper sludge released an extra amount of N due to its low C/N ratio. No consistent remineralization of N could be found in any of the treatments, probably due to an unsuitable composition of the remineralizer wastes. Manipulating N release of N-rich crop residues by using organic wastes may be a suitable method to reduce NO3 leaching; however, stimulating remineralization of immobilized N by the start of the following spring may not be easy to achieve.
Abbreviations: CD, coefficient of determination CRM, coefficient of residual mass
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