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Can living mulches in intercropping systems reduce the potential nitrate leaching? Studies of organic cauliflower (Brassica oleracea L. var. botrytis) and leek (Allium porrum L.) production across European conditions

Published online by Cambridge University Press:  18 July 2016

Yue Xie
Affiliation:
Department of Food Science, Aarhus University, Aarhus, Denmark.
Fabio Tittarelli
Affiliation:
Consiglio per la ricerca in agricoltura e l'analisi dell'economia agraria, Centro per lo studio delle relazioni tra pianta e suolo, Rome, Italy.
Peter von Fragstein
Affiliation:
Department of Organic Vegetable Production, University of Kassel, Kassel, Germany.
Martina Bavec
Affiliation:
Faculty of Agriculture and Life Science, University of Maribor, Maribor, Slovenia.
Stefano Canali
Affiliation:
Consiglio per la ricerca in agricoltura e l'analisi dell'economia agraria, Centro per lo studio delle relazioni tra pianta e suolo, Rome, Italy.
Hanne Lakkenborg Kristensen*
Affiliation:
Department of Food Science, Aarhus University, Aarhus, Denmark.
*
* Corresponding author: hanne.kristensen@food.au.dk
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Abstract

The effect of introduction strategy for living mulches (LMs) to reduce the potential nitrate leaching was investigated when grown with vegetables with high nitrogen (N) demand and low use efficiency in four European countries: Italy, Slovenia, Germany and Denmark over 2 yr. The plant N uptake and soil nitrate N content at harvest, in the autumn, and in the following spring were measured below open-pollinated and hybrid cultivars of cauliflower and leek crops. The cultivars performed differently over the 2 yr. In Italy and Slovenia, when LM of burr medic or white clover was broad sown (addition design ADD) at the same time as crop transplanting, the N uptake of crops was hampered without increasing the total aboveground N accumulation. Delaying LM sowing by 2.5–4 weeks maintained the N uptake of crops. In Germany, delaying white clover sowing for a month in cauliflower reduced soil nitrate at the start of leaching by 17–33 kg N ha−1 in the ADD design and 25 kg N ha−1 in the substitution design (SUB), where rows of cash crops were replaced by rows of LM. An overwintering LM of grass–clover incorporated in strips and root pruned decreased soil nitrate at the start of the leaching period by 35 kg N ha−1 in cauliflower, and in leek, an LM of dyer's woad decreased the soil nitrate by 55 kg N ha−1 at harvest and 30 kg N ha−1 at the start of leaching. The effect of delayed LM sowing depended on the LM species and system design. Overall, the SUB and ADD designs showed potential to reduce nitrate leaching, whereas the ADD design had stronger competition against either cash crop or LM. The key to reduce soil nitrate N without jeopardizing crop yields may be to identify suitable growing periods, sometimes combined with root pruning, for each LM species and system design. The LM introduction strategy can be used to control competition and reduce the potential leaching, but the performance depends on the intensity of the interspecific competition and the local conditions.

Information

Type
Themed Content: Living Mulch
Copyright
Copyright © Cambridge University Press 2016 
Figure 0

Table 1. The soil properties of the experimental fields in four countries.

Figure 1

Table 2. The cultivars of vegetables, the LM species and introduction strategies, and management of interspecific competition in four countries.

Figure 2

Table 3. Agricultural management of crops and LMs in four countries. If years are not indicated, the time point was the same in both years.

Figure 3

Table 4. The effect of living mulch (LM), year and cultivar on cauliflower and LM N uptake in the four countries.

Figure 4

Figure 1. The plant N uptake in cauliflower trials with hybrid cv. Chambord in Germany, Slovenia and Denmark. Different lower case letters indicate significant differences at P < 0.05. Different upper case letters indicate significant differences at P < 0.01. No LM: Sole crop; ADD: Addition design; SUB: Substitution design; Es LM: Early sown LM; Ls LM: Late sown LM.

Figure 5

Figure 2. The plant N uptake in cauliflower trials with cv. Snow Ball in Slovenia in 2 yr. Different lower case letters indicate the significant differences at P < 0.05. No LM: Sole crop; Es LM: Early sown LM; Ls LM: Late sown LM.

Figure 6

Figure 3. The plant N uptake in cauliflower trials with cv. Ora1, Ora2 and Emeraude in Italy in both years. Different lower case letters indicate significant differences at P < 0.05. No LM: Sole crop; Es LM: Early sown LM; Ls LM: Late sown LM; EM: cv. Emeraude.

Figure 7

Table 5. The effect of living mulch, cultivar and year on the total soil nitrate N (kg ha−1) in cauliflower trials at harvest, start of leaching and end of leaching.

Figure 8

Table 6. The effect of living mulch on soil nitrate N (kg ha−1) in trials with cauliflower cultivar Chambord and leek cultivar Hannibal at harvest, at the start of leaching and at the end of leaching in separate years.

Figure 9

Figure 4. The soil nitrate distribution in the soil layer of 0–0.9 m in cauliflower trials with cv. Chambord and cv. Belot in Germany 2012 at the start of leaching. The * indicates significant differences at P < 0.05. No LM: Sole crop; ADD: Addition design; SUB: Substitution design.

Figure 10

Table 7. The leek (including residues) and living mulch N uptake (kg N ha−1) in three countries in two years.

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Figure 5. The plant N uptake in leek trials with open pollinated cv. Hannibal in Germany, Slovenia and Denmark. Different lower case letters indicate significant differences at P < 0.05. Different upper case letters indicate significant differences at P < 0.01. No LM: Sole crop; ADD: Addition design; SUB: Substitution design; Es LM: Early sown LM; Ls LM: Late sown LM.

Figure 12

Figure 6. The plant N uptake in leek trials with cv. Striker in Slovenia and cv. Catcher in Germany. Different lower case letters indicate significant differences at P < 0.05. No LM: Sole crop; ADD: Addition design; SUB: Substitution design; Es LM: Early sown LM; Ls LM: Late sown LM.

Figure 13

Table 8. The effect of living mulch, cultivar and year on the total soil nitrate N (kg ha−1) in leek trials at the harvest, the start of leaching and the end of leaching in three countries.

Figure 14

Figure 7. The soil nitrate distribution in the soil layer of 0–1 m at harvest and at the start of leaching in leek trials with cv. Hannibal in Denmark 2013. The * indicates significant differences at P < 0.05. No LM: Sole crop; Es LM: Early sown LM; Ls LM: Late sown LM.