Articles
ASSESSING RISK OF NITRATE LEACHING FROM THE HORTICULTURAL INDUSTRY OF ALMERIA, SPAIN
Article number
571_29
Pages
243 – 248
Language
English
Abstract
Approximately 24,000 ha of plastic greenhouses are used for intensive horticultural production in the coastal region of Almeria, in south-eastern Spain.
Underlying aquifers have appreciable concentrations of NO3–, suggesting contamination from the horticultural industry.
Ninety-two percent of cropping occurs on soils, the other 8% with “open” hydroponic systems.
As part of a survey conducted to identify nutrient and irrigation management practices that risk causing nitrate contamination of groundwater, 52 greenhouses were sampled to determine mineral N in the soil profile at the end of a crop. 28 greenhouses were sampled to 40 cm depth, and 17 to 60 cm (also 7 greenhouses to <40 cm). Total amounts of NH4+-N, NO3–-N and mineral N (combined NH4+-N and NO3–-N) to these depths were determined.
In 28 greenhouses sampled to 40 cm, mineral N at sampling was 153776 kg N ha-1, with mean and median values of, respectively, 317 and 279 kg N ha-1. In 17 greenhouses sampled to 60 cm, mineral N at sampling was 2821,654 kg N ha-1, with mean and median values of, respectively, 527 and 360 kg N ha-1. On average, NH4+-N was 58% of mineral N. Soil NO3–-N showed a large and skewed distribution between greenhouses, with many having relatively small amounts, and a small number having very large amounts.
The variation in soil NO3–-N data may have resulted from considerable denitrification loss occurring in some greenhouses.
The soil mineral N data suggested that large amounts of mineral N entered the soil and were potential sources of contamination of underlying aquifers.
Management practices to reduce this risk are proposed.
Underlying aquifers have appreciable concentrations of NO3–, suggesting contamination from the horticultural industry.
Ninety-two percent of cropping occurs on soils, the other 8% with “open” hydroponic systems.
As part of a survey conducted to identify nutrient and irrigation management practices that risk causing nitrate contamination of groundwater, 52 greenhouses were sampled to determine mineral N in the soil profile at the end of a crop. 28 greenhouses were sampled to 40 cm depth, and 17 to 60 cm (also 7 greenhouses to <40 cm). Total amounts of NH4+-N, NO3–-N and mineral N (combined NH4+-N and NO3–-N) to these depths were determined.
In 28 greenhouses sampled to 40 cm, mineral N at sampling was 153776 kg N ha-1, with mean and median values of, respectively, 317 and 279 kg N ha-1. In 17 greenhouses sampled to 60 cm, mineral N at sampling was 2821,654 kg N ha-1, with mean and median values of, respectively, 527 and 360 kg N ha-1. On average, NH4+-N was 58% of mineral N. Soil NO3–-N showed a large and skewed distribution between greenhouses, with many having relatively small amounts, and a small number having very large amounts.
The variation in soil NO3–-N data may have resulted from considerable denitrification loss occurring in some greenhouses.
The soil mineral N data suggested that large amounts of mineral N entered the soil and were potential sources of contamination of underlying aquifers.
Management practices to reduce this risk are proposed.
Authors
R.B. Thompson, M. Gallardo, C. Giménez
Keywords
greenhouse, horticultural management, fertigation, nitrogen, horticulture
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