Cu fractions, mobility and bioavailability in soil-wheat system after Cu-enriched livestock manure applications

Fertilization of crops with livestock manure (LM) is a common waste disposal option, but repeated application of LM containing high concentrations of heavy metals such as Cu could lead to crop toxicity and environmental risk. To examine the Cu availability and uptake by wheat in a Mollisol affected...

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Veröffentlicht in:Chemosphere (Oxford) 2011, Vol.82 (2), p.215-222
Hauptverfasser: Guan, T.X., He, H.B., Zhang, X.D., Bai, Z.
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He, H.B.
Zhang, X.D.
Bai, Z.
description Fertilization of crops with livestock manure (LM) is a common waste disposal option, but repeated application of LM containing high concentrations of heavy metals such as Cu could lead to crop toxicity and environmental risk. To examine the Cu availability and uptake by wheat in a Mollisol affected by Cu-enriched LM, pot experiments were conducted. LM (376 mg kg −1 Cu originally) was spiked with different concentrations of Cu (0, 100, 200, 400, 600 and 800 mg kg −1 soil, added as CuSO 4) to simulate soil Cu contamination by LM application. The results indicated that Cu was predominately distributed in organic bound fraction, while the most drastic increase was found in reducible fraction. Acid-extractable fraction played a more important role than other fractions in controlling the mobility and bioavailability of Cu. DTPA-extractable Cu may overestimate the Cu bioavailability since DTPA solution could extract soluble and part of stable forms. The application of LM at 1% level significantly decline the Cu mobility, but that at 3% level exhibited the opposite effect. Although the quantities of Cu in wheat was very low compared with the accumulation in soil, Cu concentrations in roots increased evidently from 12 to 533 mg kg −1 and that in aerial parts were in a narrow range from 12.1 to 32.7 mg kg −1, indicating the more sensitivity of roots to the Cu toxicity. The Cu concentrations in grains after 3% manure application did not approach the threshold for Cu toxicity (
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To examine the Cu availability and uptake by wheat in a Mollisol affected by Cu-enriched LM, pot experiments were conducted. LM (376 mg kg −1 Cu originally) was spiked with different concentrations of Cu (0, 100, 200, 400, 600 and 800 mg kg −1 soil, added as CuSO 4) to simulate soil Cu contamination by LM application. The results indicated that Cu was predominately distributed in organic bound fraction, while the most drastic increase was found in reducible fraction. Acid-extractable fraction played a more important role than other fractions in controlling the mobility and bioavailability of Cu. DTPA-extractable Cu may overestimate the Cu bioavailability since DTPA solution could extract soluble and part of stable forms. The application of LM at 1% level significantly decline the Cu mobility, but that at 3% level exhibited the opposite effect. Although the quantities of Cu in wheat was very low compared with the accumulation in soil, Cu concentrations in roots increased evidently from 12 to 533 mg kg −1 and that in aerial parts were in a narrow range from 12.1 to 32.7 mg kg −1, indicating the more sensitivity of roots to the Cu toxicity. 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Although the quantities of Cu in wheat was very low compared with the accumulation in soil, Cu concentrations in roots increased evidently from 12 to 533 mg kg −1 and that in aerial parts were in a narrow range from 12.1 to 32.7 mg kg −1, indicating the more sensitivity of roots to the Cu toxicity. The Cu concentrations in grains after 3% manure application did not approach the threshold for Cu toxicity (&lt;20 mg kg −1) even at higher Cu addition rates.</description><subject>aerial parts</subject><subject>animal manures</subject><subject>Applied sciences</subject><subject>bioaccumulation</subject><subject>Bioavailability</subject><subject>copper</subject><subject>Copper - analysis</subject><subject>Copper - chemistry</subject><subject>Copper - metabolism</subject><subject>crops</subject><subject>ecotoxicology</subject><subject>Exact sciences and technology</subject><subject>fertilizer rates</subject><subject>Fertilizers - analysis</subject><subject>Fractions</subject><subject>heavy metals</subject><subject>Livestock manure</subject><subject>Manure - analysis</subject><subject>Mobility</subject><subject>Pentetic Acid - chemistry</subject><subject>Pentetic Acid - metabolism</subject><subject>Plant Roots - metabolism</subject><subject>Pollution</subject><subject>Refuse Disposal</subject><subject>risk</subject><subject>roots</subject><subject>soil</subject><subject>Soil - chemistry</subject><subject>Soil Pollutants - analysis</subject><subject>Soil Pollutants - chemistry</subject><subject>Soil Pollutants - metabolism</subject><subject>soil pollution</subject><subject>Soil-wheat system</subject><subject>spatial distribution</subject><subject>toxicity</subject><subject>Triticum - metabolism</subject><subject>Triticum aestivum</subject><subject>waste disposal</subject><subject>wheat</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2011</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkE2P0zAQhi0EYsvCXwBzQFxIGSd2Gh9XEV_SShxgz9bYmVCXJC52UtR_j7stH0dOlsbP63n9MPZSwFqAqN_u1m5LY0j7LUVal3A_X4NoHrCVaDa6EKVuHrIVgFRFrSp1xZ6ktAPIYaUfs6tSgAQtyxUL7cL7iG72YUpv-BisH_x85Dh13PqAB_QDXmZ-4in4ofi5JZx5OqaZRo79TJG3S0FT9LlWxwd_oDQH952POC2ROO73g3d4v-Ipe9TjkOjZ5bxmd-_ffW0_FrefP3xqb24LJ-tyLmRXy76qFWIla2uVRKUBBVgroIMeVNmQ1ShrXVmB2lVl31cVCGykLZ1W1TV7fX53H8OPJfcxo0-OhgEnCksyjarkRoE6kfpMuhhSitSbffQjxqMRYE66zc78o9ucdJ-usu6cfX7ZstiRuj_J334z8OoCYHI4ZNOT8-kvVymQUmwy9-LM9RgMfouZufuSN-Uv6RqU1plozwRlawdP0STnaXLU-UhuNl3w_1H4F_wkrtU</recordid><startdate>2011</startdate><enddate>2011</enddate><creator>Guan, T.X.</creator><creator>He, H.B.</creator><creator>Zhang, X.D.</creator><creator>Bai, Z.</creator><general>Elsevier Ltd</general><general>Elsevier</general><scope>FBQ</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>7TV</scope><scope>C1K</scope><scope>SOI</scope></search><sort><creationdate>2011</creationdate><title>Cu fractions, mobility and bioavailability in soil-wheat system after Cu-enriched livestock manure applications</title><author>Guan, T.X. ; He, H.B. ; Zhang, X.D. ; Bai, Z.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c462t-4d64f365aa346bb54a590a10bb10d0f0528eb9a4693b1a9c32ff3301a84b2c953</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2011</creationdate><topic>aerial parts</topic><topic>animal manures</topic><topic>Applied sciences</topic><topic>bioaccumulation</topic><topic>Bioavailability</topic><topic>copper</topic><topic>Copper - analysis</topic><topic>Copper - chemistry</topic><topic>Copper - metabolism</topic><topic>crops</topic><topic>ecotoxicology</topic><topic>Exact sciences and technology</topic><topic>fertilizer rates</topic><topic>Fertilizers - analysis</topic><topic>Fractions</topic><topic>heavy metals</topic><topic>Livestock manure</topic><topic>Manure - analysis</topic><topic>Mobility</topic><topic>Pentetic Acid - chemistry</topic><topic>Pentetic Acid - metabolism</topic><topic>Plant Roots - metabolism</topic><topic>Pollution</topic><topic>Refuse Disposal</topic><topic>risk</topic><topic>roots</topic><topic>soil</topic><topic>Soil - chemistry</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - chemistry</topic><topic>Soil Pollutants - metabolism</topic><topic>soil pollution</topic><topic>Soil-wheat system</topic><topic>spatial distribution</topic><topic>toxicity</topic><topic>Triticum - metabolism</topic><topic>Triticum aestivum</topic><topic>waste disposal</topic><topic>wheat</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Guan, T.X.</creatorcontrib><creatorcontrib>He, H.B.</creatorcontrib><creatorcontrib>Zhang, X.D.</creatorcontrib><creatorcontrib>Bai, Z.</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Guan, T.X.</au><au>He, H.B.</au><au>Zhang, X.D.</au><au>Bai, Z.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Cu fractions, mobility and bioavailability in soil-wheat system after Cu-enriched livestock manure applications</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2011</date><risdate>2011</risdate><volume>82</volume><issue>2</issue><spage>215</spage><epage>222</epage><pages>215-222</pages><issn>0045-6535</issn><eissn>1879-1298</eissn><coden>CMSHAF</coden><abstract>Fertilization of crops with livestock manure (LM) is a common waste disposal option, but repeated application of LM containing high concentrations of heavy metals such as Cu could lead to crop toxicity and environmental risk. To examine the Cu availability and uptake by wheat in a Mollisol affected by Cu-enriched LM, pot experiments were conducted. LM (376 mg kg −1 Cu originally) was spiked with different concentrations of Cu (0, 100, 200, 400, 600 and 800 mg kg −1 soil, added as CuSO 4) to simulate soil Cu contamination by LM application. The results indicated that Cu was predominately distributed in organic bound fraction, while the most drastic increase was found in reducible fraction. Acid-extractable fraction played a more important role than other fractions in controlling the mobility and bioavailability of Cu. DTPA-extractable Cu may overestimate the Cu bioavailability since DTPA solution could extract soluble and part of stable forms. The application of LM at 1% level significantly decline the Cu mobility, but that at 3% level exhibited the opposite effect. Although the quantities of Cu in wheat was very low compared with the accumulation in soil, Cu concentrations in roots increased evidently from 12 to 533 mg kg −1 and that in aerial parts were in a narrow range from 12.1 to 32.7 mg kg −1, indicating the more sensitivity of roots to the Cu toxicity. The Cu concentrations in grains after 3% manure application did not approach the threshold for Cu toxicity (&lt;20 mg kg −1) even at higher Cu addition rates.</abstract><cop>Kidlington</cop><pub>Elsevier Ltd</pub><pmid>21040942</pmid><doi>10.1016/j.chemosphere.2010.10.018</doi><tpages>8</tpages></addata></record>
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subjects aerial parts
animal manures
Applied sciences
bioaccumulation
Bioavailability
copper
Copper - analysis
Copper - chemistry
Copper - metabolism
crops
ecotoxicology
Exact sciences and technology
fertilizer rates
Fertilizers - analysis
Fractions
heavy metals
Livestock manure
Manure - analysis
Mobility
Pentetic Acid - chemistry
Pentetic Acid - metabolism
Plant Roots - metabolism
Pollution
Refuse Disposal
risk
roots
soil
Soil - chemistry
Soil Pollutants - analysis
Soil Pollutants - chemistry
Soil Pollutants - metabolism
soil pollution
Soil-wheat system
spatial distribution
toxicity
Triticum - metabolism
Triticum aestivum
waste disposal
wheat
title Cu fractions, mobility and bioavailability in soil-wheat system after Cu-enriched livestock manure applications
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