Nitrogen absorption and mineralization change with cover crop types and greenhouse vegetable planting years in fluvo-aquic soil

Purpose Cover cropping during the summer fallow is a feasible practice for soil residual nitrogen (N) absorption and subsequent N supply in greenhouse vegetables. However, the change in these effects with a progression in the cultivation years of greenhouse vegetables remains unknown. This study aim...

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Veröffentlicht in:Journal of soils and sediments 2024-02, Vol.24 (2), p.744-759
Hauptverfasser: Pan, Feifei, Ni, Congmin, Tang, Jiao, Zhang, Huaixia
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creator Pan, Feifei
Ni, Congmin
Tang, Jiao
Zhang, Huaixia
description Purpose Cover cropping during the summer fallow is a feasible practice for soil residual nitrogen (N) absorption and subsequent N supply in greenhouse vegetables. However, the change in these effects with a progression in the cultivation years of greenhouse vegetables remains unknown. This study aimed to evaluate the effects of different cover crops on the uptake of residual N in soil and N mineralization as affected by the planting years of greenhouse vegetables. Methods Five soil samples were collected from fields that had been cultivated with greenhouse vegetables for different number of years (0, 5, 10, 15, and 20 years); upper layers (0–30 cm) of the soil were sampled from a major vegetable production area in Xinxiang City, Henan Province, China. Three cover crop treatments were included for each soil sample: no cover crop planted during summer fallow with no straw return (CK), summer maize ( Zea mays L.) planted and straw return (SM), and alfalfa ( Medicago sativa L.) planted and straw return (A). Pot and incubation experiments were conducted to determine the amounts of N absorbed by cover crops during the fallow and soil N mineralization after cover crop straw return. Results The effects of cover crops on soil residual N absorption and subsequent N mineralization changed with cover crop types and greenhouse vegetable planting years. SM performed better as a cover crop than A in crop biomass development (on average 6.67 times larger), soil residual N absorption (4.46 times larger), and loss (3.61 times smaller) control, regardless of the greenhouse vegetable planting years. In terms of soil net N mineralization and straw-induced N mineralization, SM was inferior to A (1.15 and 2.12 times smaller). With the increase of planting years, total biomass yield and N uptake by the SM increased, whereas these parameters decreased for treatment A due to the plants’ different tolerance to soil available N and pH (pondus hydrogenii). For all cover crop treatments, with the increase of greenhouse vegetable planting years, net N mineralization of the soil increased due to the positive contribution of soil organic matter, whereas straw-induced N mineralization decreased due to the negative regulation of accumulated soil nitrate nitrogen. Conclusions Non-legumes, as represented by SM, were a good choice for cover cropping regardless of the greenhouse vegetable cultivation years. However, attention should be paid to N supplementation at an early stage of subsequent c
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However, the change in these effects with a progression in the cultivation years of greenhouse vegetables remains unknown. This study aimed to evaluate the effects of different cover crops on the uptake of residual N in soil and N mineralization as affected by the planting years of greenhouse vegetables. Methods Five soil samples were collected from fields that had been cultivated with greenhouse vegetables for different number of years (0, 5, 10, 15, and 20 years); upper layers (0–30 cm) of the soil were sampled from a major vegetable production area in Xinxiang City, Henan Province, China. Three cover crop treatments were included for each soil sample: no cover crop planted during summer fallow with no straw return (CK), summer maize ( Zea mays L.) planted and straw return (SM), and alfalfa ( Medicago sativa L.) planted and straw return (A). Pot and incubation experiments were conducted to determine the amounts of N absorbed by cover crops during the fallow and soil N mineralization after cover crop straw return. Results The effects of cover crops on soil residual N absorption and subsequent N mineralization changed with cover crop types and greenhouse vegetable planting years. SM performed better as a cover crop than A in crop biomass development (on average 6.67 times larger), soil residual N absorption (4.46 times larger), and loss (3.61 times smaller) control, regardless of the greenhouse vegetable planting years. In terms of soil net N mineralization and straw-induced N mineralization, SM was inferior to A (1.15 and 2.12 times smaller). With the increase of planting years, total biomass yield and N uptake by the SM increased, whereas these parameters decreased for treatment A due to the plants’ different tolerance to soil available N and pH (pondus hydrogenii). For all cover crop treatments, with the increase of greenhouse vegetable planting years, net N mineralization of the soil increased due to the positive contribution of soil organic matter, whereas straw-induced N mineralization decreased due to the negative regulation of accumulated soil nitrate nitrogen. Conclusions Non-legumes, as represented by SM, were a good choice for cover cropping regardless of the greenhouse vegetable cultivation years. However, attention should be paid to N supplementation at an early stage of subsequent crop cultivation, especially in newly built greenhouse vegetables.</description><identifier>ISSN: 1439-0108</identifier><identifier>EISSN: 1614-7480</identifier><identifier>DOI: 10.1007/s11368-023-03677-7</identifier><language>eng</language><publisher>Berlin/Heidelberg: Springer Berlin Heidelberg</publisher><subject>Absorption ; Agricultural practices ; Alfalfa ; Biomass ; biomass production ; China ; Cover crops ; Crop production ; Crops ; Cultivation ; Earth and Environmental Science ; Environment ; Environmental Physics ; fallow ; Greenhouses ; Legumes ; Medicago sativa ; Mineralization ; nitrate nitrogen ; Nitrogen ; Organic matter ; Organic soils ; Planting ; Sec 3 • Remediation and Management of Contaminated or Degraded Lands • Research Article ; Soil ; Soil organic matter ; Soil Science &amp; Conservation ; Soils ; Straw ; Summer ; vegetable growing ; Vegetables ; Zea mays</subject><ispartof>Journal of soils and sediments, 2024-02, Vol.24 (2), p.744-759</ispartof><rights>The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2023. 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However, the change in these effects with a progression in the cultivation years of greenhouse vegetables remains unknown. This study aimed to evaluate the effects of different cover crops on the uptake of residual N in soil and N mineralization as affected by the planting years of greenhouse vegetables. Methods Five soil samples were collected from fields that had been cultivated with greenhouse vegetables for different number of years (0, 5, 10, 15, and 20 years); upper layers (0–30 cm) of the soil were sampled from a major vegetable production area in Xinxiang City, Henan Province, China. Three cover crop treatments were included for each soil sample: no cover crop planted during summer fallow with no straw return (CK), summer maize ( Zea mays L.) planted and straw return (SM), and alfalfa ( Medicago sativa L.) planted and straw return (A). Pot and incubation experiments were conducted to determine the amounts of N absorbed by cover crops during the fallow and soil N mineralization after cover crop straw return. Results The effects of cover crops on soil residual N absorption and subsequent N mineralization changed with cover crop types and greenhouse vegetable planting years. SM performed better as a cover crop than A in crop biomass development (on average 6.67 times larger), soil residual N absorption (4.46 times larger), and loss (3.61 times smaller) control, regardless of the greenhouse vegetable planting years. In terms of soil net N mineralization and straw-induced N mineralization, SM was inferior to A (1.15 and 2.12 times smaller). With the increase of planting years, total biomass yield and N uptake by the SM increased, whereas these parameters decreased for treatment A due to the plants’ different tolerance to soil available N and pH (pondus hydrogenii). For all cover crop treatments, with the increase of greenhouse vegetable planting years, net N mineralization of the soil increased due to the positive contribution of soil organic matter, whereas straw-induced N mineralization decreased due to the negative regulation of accumulated soil nitrate nitrogen. Conclusions Non-legumes, as represented by SM, were a good choice for cover cropping regardless of the greenhouse vegetable cultivation years. However, attention should be paid to N supplementation at an early stage of subsequent crop cultivation, especially in newly built greenhouse vegetables.</description><subject>Absorption</subject><subject>Agricultural practices</subject><subject>Alfalfa</subject><subject>Biomass</subject><subject>biomass production</subject><subject>China</subject><subject>Cover crops</subject><subject>Crop production</subject><subject>Crops</subject><subject>Cultivation</subject><subject>Earth and Environmental Science</subject><subject>Environment</subject><subject>Environmental Physics</subject><subject>fallow</subject><subject>Greenhouses</subject><subject>Legumes</subject><subject>Medicago sativa</subject><subject>Mineralization</subject><subject>nitrate nitrogen</subject><subject>Nitrogen</subject><subject>Organic matter</subject><subject>Organic soils</subject><subject>Planting</subject><subject>Sec 3 • Remediation and Management of Contaminated or Degraded Lands • Research Article</subject><subject>Soil</subject><subject>Soil organic matter</subject><subject>Soil Science &amp; Conservation</subject><subject>Soils</subject><subject>Straw</subject><subject>Summer</subject><subject>vegetable growing</subject><subject>Vegetables</subject><subject>Zea mays</subject><issn>1439-0108</issn><issn>1614-7480</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><recordid>eNp9kU9v1DAQxSMEEqXwBXqyxKUX07Ena8dHVJU_UlUucLYmxsm6ytqpnSxaLnx13N1KSBx6mtHM742e5jXNhYAPAkBfFSFQdRwkckClNdcvmjOhRMt128HL2rdoOAjoXjdvSrkHQF3XZ82fu7DkNPrIqC8pz0tItY0_2S5En2kKv-k4cluKo2e_wrJlLu19Zi6nmS2H2ZcjP2bv4zatxbO9H_1C_eTZPFFcQhzZwVMuLEQ2TOs-cXpYg2Mlhelt82qgqfh3T_W8-fHp5vv1F3777fPX64-33CHgwp1R1IOWwkkAMsPGoW5x0LLbtD0qMp0ZCEj3wgmF0nS9oU6YwQlCoRXgeXN5ujvn9LD6sthdKM5P1aCvpi2KDW461UpZ0ff_ofdpzbG6s9JI0SoBiJWSJ6r-oZTsBzvnsKN8sALsYyb2lImtmdhjJlZXEZ5EpcL1n_nf6WdUfwEF4JBv</recordid><startdate>20240201</startdate><enddate>20240201</enddate><creator>Pan, Feifei</creator><creator>Ni, Congmin</creator><creator>Tang, Jiao</creator><creator>Zhang, Huaixia</creator><general>Springer Berlin Heidelberg</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H96</scope><scope>H97</scope><scope>L.G</scope><scope>SOI</scope><scope>7S9</scope><scope>L.6</scope><orcidid>https://orcid.org/0000-0001-9789-3287</orcidid></search><sort><creationdate>20240201</creationdate><title>Nitrogen absorption and mineralization change with cover crop types and greenhouse vegetable planting years in fluvo-aquic soil</title><author>Pan, Feifei ; Ni, Congmin ; Tang, Jiao ; Zhang, Huaixia</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c303t-c96ab0721c200a9f5c3743f72854b36a989fa0a7b1c163298b9a819fc1a317603</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2024</creationdate><topic>Absorption</topic><topic>Agricultural practices</topic><topic>Alfalfa</topic><topic>Biomass</topic><topic>biomass production</topic><topic>China</topic><topic>Cover crops</topic><topic>Crop production</topic><topic>Crops</topic><topic>Cultivation</topic><topic>Earth and Environmental Science</topic><topic>Environment</topic><topic>Environmental Physics</topic><topic>fallow</topic><topic>Greenhouses</topic><topic>Legumes</topic><topic>Medicago sativa</topic><topic>Mineralization</topic><topic>nitrate nitrogen</topic><topic>Nitrogen</topic><topic>Organic matter</topic><topic>Organic soils</topic><topic>Planting</topic><topic>Sec 3 • Remediation and Management of Contaminated or Degraded Lands • Research Article</topic><topic>Soil</topic><topic>Soil organic matter</topic><topic>Soil Science &amp; Conservation</topic><topic>Soils</topic><topic>Straw</topic><topic>Summer</topic><topic>vegetable growing</topic><topic>Vegetables</topic><topic>Zea mays</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Pan, Feifei</creatorcontrib><creatorcontrib>Ni, Congmin</creatorcontrib><creatorcontrib>Tang, Jiao</creatorcontrib><creatorcontrib>Zhang, Huaixia</creatorcontrib><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy &amp; Non-Living Resources</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) 3: Aquatic Pollution &amp; Environmental Quality</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><collection>AGRICOLA</collection><collection>AGRICOLA - Academic</collection><jtitle>Journal of soils and sediments</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Pan, Feifei</au><au>Ni, Congmin</au><au>Tang, Jiao</au><au>Zhang, Huaixia</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Nitrogen absorption and mineralization change with cover crop types and greenhouse vegetable planting years in fluvo-aquic soil</atitle><jtitle>Journal of soils and sediments</jtitle><stitle>J Soils Sediments</stitle><date>2024-02-01</date><risdate>2024</risdate><volume>24</volume><issue>2</issue><spage>744</spage><epage>759</epage><pages>744-759</pages><issn>1439-0108</issn><eissn>1614-7480</eissn><abstract>Purpose Cover cropping during the summer fallow is a feasible practice for soil residual nitrogen (N) absorption and subsequent N supply in greenhouse vegetables. However, the change in these effects with a progression in the cultivation years of greenhouse vegetables remains unknown. This study aimed to evaluate the effects of different cover crops on the uptake of residual N in soil and N mineralization as affected by the planting years of greenhouse vegetables. Methods Five soil samples were collected from fields that had been cultivated with greenhouse vegetables for different number of years (0, 5, 10, 15, and 20 years); upper layers (0–30 cm) of the soil were sampled from a major vegetable production area in Xinxiang City, Henan Province, China. Three cover crop treatments were included for each soil sample: no cover crop planted during summer fallow with no straw return (CK), summer maize ( Zea mays L.) planted and straw return (SM), and alfalfa ( Medicago sativa L.) planted and straw return (A). Pot and incubation experiments were conducted to determine the amounts of N absorbed by cover crops during the fallow and soil N mineralization after cover crop straw return. Results The effects of cover crops on soil residual N absorption and subsequent N mineralization changed with cover crop types and greenhouse vegetable planting years. SM performed better as a cover crop than A in crop biomass development (on average 6.67 times larger), soil residual N absorption (4.46 times larger), and loss (3.61 times smaller) control, regardless of the greenhouse vegetable planting years. In terms of soil net N mineralization and straw-induced N mineralization, SM was inferior to A (1.15 and 2.12 times smaller). With the increase of planting years, total biomass yield and N uptake by the SM increased, whereas these parameters decreased for treatment A due to the plants’ different tolerance to soil available N and pH (pondus hydrogenii). For all cover crop treatments, with the increase of greenhouse vegetable planting years, net N mineralization of the soil increased due to the positive contribution of soil organic matter, whereas straw-induced N mineralization decreased due to the negative regulation of accumulated soil nitrate nitrogen. Conclusions Non-legumes, as represented by SM, were a good choice for cover cropping regardless of the greenhouse vegetable cultivation years. However, attention should be paid to N supplementation at an early stage of subsequent crop cultivation, especially in newly built greenhouse vegetables.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><doi>10.1007/s11368-023-03677-7</doi><tpages>16</tpages><orcidid>https://orcid.org/0000-0001-9789-3287</orcidid></addata></record>
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subjects Absorption
Agricultural practices
Alfalfa
Biomass
biomass production
China
Cover crops
Crop production
Crops
Cultivation
Earth and Environmental Science
Environment
Environmental Physics
fallow
Greenhouses
Legumes
Medicago sativa
Mineralization
nitrate nitrogen
Nitrogen
Organic matter
Organic soils
Planting
Sec 3 • Remediation and Management of Contaminated or Degraded Lands • Research Article
Soil
Soil organic matter
Soil Science & Conservation
Soils
Straw
Summer
vegetable growing
Vegetables
Zea mays
title Nitrogen absorption and mineralization change with cover crop types and greenhouse vegetable planting years in fluvo-aquic soil
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