Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile

Microbiological bioassays of nitrification and nitrogen mineralization have been used for evaluation of soil quality on metal-contaminated soils. We evaluated the effectiveness of nitrification and nitrogen mineralization bioassays as quality indicators of soil degradation caused by metal contaminat...

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Autores principales: Moya,Héctor, Verdejo,José, Yáñez,Carolina, Álvaro,Juan E., Sauvé,Sébastien, Neaman,Alexander
Lenguaje:English
Publicado: Chilean Society of Soil Science / Sociedad Chilena de la Ciencia del Suelo 2017
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Acceso en línea:http://www.scielo.cl/scielo.php?script=sci_arttext&pid=S0718-95162017000100017
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spelling oai:scielo:S0718-951620170001000172017-09-27Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central ChileMoya,HéctorVerdejo,JoséYáñez,CarolinaÁlvaro,Juan E.Sauvé,SébastienNeaman,Alexander Copper toxicity nitrification potential nitrogen mineralization soil quality Microbiological bioassays of nitrification and nitrogen mineralization have been used for evaluation of soil quality on metal-contaminated soils. We evaluated the effectiveness of nitrification and nitrogen mineralization bioassays as quality indicators of soil degradation caused by metal contamination. We performed standard tests based on protocols of ISO 14238 (2012) and ISO 15685 (2012) on 90 soil samples collected from agricultural areas in central Chile that were historically contaminated by mining activities. Potential nitrification rate (PNR) was best explained by pH and organic matter content (OM) (R²=0.32), while nitrogen mineralization (Nmin) was best explained by OM and clay content (R²=0.44). Following normalization of the bioassays responses with respect to OM yielded significant correlations between PNR and pH and total Cu content (R²=0.22), and between Nmin and clay and total Cu contents (R²=0.19). However, inasmuch as total Cu content improved the regression model showing the inhibitory effect of Cu in both bioassays, it accounted for a mere small proportion of the variance. This was despite the wide range of Cu contents in the soils studied (51-2878 mg kg-1). Hence, due to the known sensitivity of the nitrification and nitrogen mineralization process to physicochemical characteristics of soils, these bioassays seem to have limited applicability for metal toxicity assessment in metal-contaminated soils.info:eu-repo/semantics/openAccessChilean Society of Soil Science / Sociedad Chilena de la Ciencia del SueloJournal of soil science and plant nutrition v.17 n.1 20172017-03-01text/htmlhttp://www.scielo.cl/scielo.php?script=sci_arttext&pid=S0718-95162017000100017en10.4067/S0718-95162017005000016
institution Scielo Chile
collection Scielo Chile
language English
topic Copper toxicity
nitrification potential
nitrogen mineralization
soil quality
spellingShingle Copper toxicity
nitrification potential
nitrogen mineralization
soil quality
Moya,Héctor
Verdejo,José
Yáñez,Carolina
Álvaro,Juan E.
Sauvé,Sébastien
Neaman,Alexander
Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
description Microbiological bioassays of nitrification and nitrogen mineralization have been used for evaluation of soil quality on metal-contaminated soils. We evaluated the effectiveness of nitrification and nitrogen mineralization bioassays as quality indicators of soil degradation caused by metal contamination. We performed standard tests based on protocols of ISO 14238 (2012) and ISO 15685 (2012) on 90 soil samples collected from agricultural areas in central Chile that were historically contaminated by mining activities. Potential nitrification rate (PNR) was best explained by pH and organic matter content (OM) (R²=0.32), while nitrogen mineralization (Nmin) was best explained by OM and clay content (R²=0.44). Following normalization of the bioassays responses with respect to OM yielded significant correlations between PNR and pH and total Cu content (R²=0.22), and between Nmin and clay and total Cu contents (R²=0.19). However, inasmuch as total Cu content improved the regression model showing the inhibitory effect of Cu in both bioassays, it accounted for a mere small proportion of the variance. This was despite the wide range of Cu contents in the soils studied (51-2878 mg kg-1). Hence, due to the known sensitivity of the nitrification and nitrogen mineralization process to physicochemical characteristics of soils, these bioassays seem to have limited applicability for metal toxicity assessment in metal-contaminated soils.
author Moya,Héctor
Verdejo,José
Yáñez,Carolina
Álvaro,Juan E.
Sauvé,Sébastien
Neaman,Alexander
author_facet Moya,Héctor
Verdejo,José
Yáñez,Carolina
Álvaro,Juan E.
Sauvé,Sébastien
Neaman,Alexander
author_sort Moya,Héctor
title Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
title_short Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
title_full Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
title_fullStr Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
title_full_unstemmed Nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in Central Chile
title_sort nitrification and nitrogen mineralization in agricultural soils contaminated by copper mining activities in central chile
publisher Chilean Society of Soil Science / Sociedad Chilena de la Ciencia del Suelo
publishDate 2017
url http://www.scielo.cl/scielo.php?script=sci_arttext&pid=S0718-95162017000100017
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