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image/svg+xml Jakob Voss, based on art designer at PLoS, modified by Wikipedia users Nina and Beao Closed Access logo, derived from PLoS Open Access logo. This version with transparent background. http://commons.wikimedia.org/wiki/File:Closed_Access_logo_transparent.svg Jakob Voss, based on art designer at PLoS, modified by Wikipedia users Nina and Beao European Journal of ...arrow_drop_down
image/svg+xml Jakob Voss, based on art designer at PLoS, modified by Wikipedia users Nina and Beao Closed Access logo, derived from PLoS Open Access logo. This version with transparent background. http://commons.wikimedia.org/wiki/File:Closed_Access_logo_transparent.svg Jakob Voss, based on art designer at PLoS, modified by Wikipedia users Nina and Beao
European Journal of Agronomy
Article . 2008 . Peer-reviewed
License: Elsevier TDM
Data sources: Crossref
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Fertilisation of irrigated maize with pig slurry combined with mineral nitrogen

Authors: P. Berenguer; F. Santiveri; J. Boixadera; J. Lloveras;

Fertilisation of irrigated maize with pig slurry combined with mineral nitrogen

Abstract

Maize (Zea mays L.) is a very important crop in many of the irrigated areas of the Ebro Valley (NE Spain). Intensive pig (Sus scrofa domesticus) production is also an important economic activity in these areas, and the use of pig slurry (PS) as a fertiliser for maize is a common practise. From 2002 to 2005, we conducted a field trial with maize in which we compared the application of 0, 30 and 60 m 3 ha −1 of PS combined with 0, 100 and 200 kg ha −1 of mineral N at sidedress. Yield, biomass and other related yield parameters differed from year to year and all of them were greatly influenced by soil NO3 − -N content before planting and by N (organic and/or mineral) fertilisation. All years average grain yield and biomass at maturity ranged from 9.3 and 18.9 Mg ha −1 (0 PS, 0 mineral N) to 14.4 and 29.6 Mg ha −1 (60 m 3 ha −1 of PS, 200 kg ha −1 of mineral N), respectively. Grain and total N biomass uptake average of the studied period ranged from 101 and 155 kg ha −1 (0 PS, 0 mineral N) to 180 and 308 kg ha −1 (60 m 3 ha −1 of PS, 200 kg ha −1 of mineral N), respectively. All years average soil NO3 − -N content before planting and after harvest were very high, and ranged from 138 and 75 kg ha −1 (0 PS, 0 mineral N) to 367 and 457 kg ha −1 (60 m 3 ha −1 of PS, 200 kg ha −1 of mineral N), respectively. The optimal N (organic and/or mineral) rate varied depending on the year and was influenced by the soil NO3 − -N content before planting. For this reason, soil NO3 − -N content before planting should be taken into account in order to improve N fertilisation recommendations. Moreover, the annual optimal N rates also gave the lowest soil NO3 − -N contents after harvest and the lowest N losses, as a consequence they also could be considered as the most environmentally friendly N rates. © 2008 Elsevier B.V. All rights reserved.

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selected citations
These citations are derived from selected sources.
This is an alternative to the "Influence" indicator, which also reflects the overall/total impact of an article in the research community at large, based on the underlying citation network (diachronically).
BIP!Citations provided by BIP!
popularity
This indicator reflects the "current" impact/attention (the "hype") of an article in the research community at large, based on the underlying citation network.
BIP!Popularity provided by BIP!
influence
This indicator reflects the overall/total impact of an article in the research community at large, based on the underlying citation network (diachronically).
BIP!Influence provided by BIP!
impulse
This indicator reflects the initial momentum of an article directly after its publication, based on the underlying citation network.
BIP!Impulse provided by BIP!
50
Top 10%
Top 10%
Top 10%
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