Fertilisation of irrigated maize with pig slurry combined with mineral nitrogen
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 200...
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Published in: | European journal of agronomy Vol. 28; no. 4; pp. 635 - 645 |
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Main Authors: | , , , |
Format: | Journal Article |
Language: | English |
Published: |
Amsterdam
Elsevier B.V
01-05-2008
Amsterdam, the Netherlands: Elsevier Science Pub. Co Elsevier Science |
Subjects: | |
Online Access: | Get full text |
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Summary: | 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 NO
3
−-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
−1of 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
−1of mineral N), respectively. All years average soil NO
3
−-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
−1of mineral N), respectively. The optimal N (organic and/or mineral) rate varied depending on the year and was influenced by the soil NO
3
−-N content before planting. For this reason, soil NO
3
−-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 NO
3
−-N contents after harvest and the lowest N losses, as a consequence they also could be considered as the most environmentally friendly N rates. |
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Bibliography: | http://dx.doi.org/10.1016/j.eja.2008.01.010 |
ISSN: | 1161-0301 1873-7331 |
DOI: | 10.1016/j.eja.2008.01.010 |