A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects
Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. There...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Zhang, Haixin [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2022 |
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| Schlagwörter: |
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| Anmerkung: |
© The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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| Übergeordnetes Werk: |
Enthalten in: Water, air & soil pollution - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971, 233(2022), 9 vom: Sept. |
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| Übergeordnetes Werk: |
volume:233 ; year:2022 ; number:9 ; month:09 |
| Links: |
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| DOI / URN: |
10.1007/s11270-022-05837-w |
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| Katalog-ID: |
SPR048023248 |
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| 520 | |a Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. | ||
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| 650 | 4 | |a Transformation |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Environmental effects |7 (dpeaa)DE-He213 | |
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| 700 | 1 | |a An, Shaoshan |4 aut | |
| 700 | 1 | |a Zhu, Zhaolong |4 aut | |
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10.1007/s11270-022-05837-w doi (DE-627)SPR048023248 (SPR)s11270-022-05837-w-e DE-627 ger DE-627 rakwb eng Zhang, Haixin verfasserin aut A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. Soil microplastics (dpeaa)DE-He213 Distribution status (dpeaa)DE-He213 Migration (dpeaa)DE-He213 Transformation (dpeaa)DE-He213 Environmental effects (dpeaa)DE-He213 Huang, Yimei aut An, Shaoshan aut Zhu, Zhaolong aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 233(2022), 9 vom: Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:233 year:2022 number:9 month:09 https://dx.doi.org/10.1007/s11270-022-05837-w lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 233 2022 9 09 |
| spelling |
10.1007/s11270-022-05837-w doi (DE-627)SPR048023248 (SPR)s11270-022-05837-w-e DE-627 ger DE-627 rakwb eng Zhang, Haixin verfasserin aut A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. Soil microplastics (dpeaa)DE-He213 Distribution status (dpeaa)DE-He213 Migration (dpeaa)DE-He213 Transformation (dpeaa)DE-He213 Environmental effects (dpeaa)DE-He213 Huang, Yimei aut An, Shaoshan aut Zhu, Zhaolong aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 233(2022), 9 vom: Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:233 year:2022 number:9 month:09 https://dx.doi.org/10.1007/s11270-022-05837-w lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 233 2022 9 09 |
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10.1007/s11270-022-05837-w doi (DE-627)SPR048023248 (SPR)s11270-022-05837-w-e DE-627 ger DE-627 rakwb eng Zhang, Haixin verfasserin aut A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. Soil microplastics (dpeaa)DE-He213 Distribution status (dpeaa)DE-He213 Migration (dpeaa)DE-He213 Transformation (dpeaa)DE-He213 Environmental effects (dpeaa)DE-He213 Huang, Yimei aut An, Shaoshan aut Zhu, Zhaolong aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 233(2022), 9 vom: Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:233 year:2022 number:9 month:09 https://dx.doi.org/10.1007/s11270-022-05837-w lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 233 2022 9 09 |
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10.1007/s11270-022-05837-w doi (DE-627)SPR048023248 (SPR)s11270-022-05837-w-e DE-627 ger DE-627 rakwb eng Zhang, Haixin verfasserin aut A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. Soil microplastics (dpeaa)DE-He213 Distribution status (dpeaa)DE-He213 Migration (dpeaa)DE-He213 Transformation (dpeaa)DE-He213 Environmental effects (dpeaa)DE-He213 Huang, Yimei aut An, Shaoshan aut Zhu, Zhaolong aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 233(2022), 9 vom: Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:233 year:2022 number:9 month:09 https://dx.doi.org/10.1007/s11270-022-05837-w lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 233 2022 9 09 |
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10.1007/s11270-022-05837-w doi (DE-627)SPR048023248 (SPR)s11270-022-05837-w-e DE-627 ger DE-627 rakwb eng Zhang, Haixin verfasserin aut A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. Soil microplastics (dpeaa)DE-He213 Distribution status (dpeaa)DE-He213 Migration (dpeaa)DE-He213 Transformation (dpeaa)DE-He213 Environmental effects (dpeaa)DE-He213 Huang, Yimei aut An, Shaoshan aut Zhu, Zhaolong aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 233(2022), 9 vom: Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:233 year:2022 number:9 month:09 https://dx.doi.org/10.1007/s11270-022-05837-w lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 233 2022 9 09 |
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Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. 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Zhang, Haixin |
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review of microplastics in soil: distribution within pedosphere compartments, environmental fate, and effects |
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A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects |
| abstract |
Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
| abstractGer |
Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
| abstract_unstemmed |
Abstract Microplastics (MPs) have been detected in various environmental media and have become a global hot environmental issue. However, the current distribution of MPs in soils in different regions, the migration and transformation of MPs, and their effects on soil ecology are still unclear. Therefore, this review summarizes the recent literature on soil MPs and gains the following key insights. The abundance of soil MPs is mainly affected by the land-use type and soil layer. The particle size range observed during the experiment also causes differences in the number of MPs. The migration of MPs is influenced by soil chemical (mineralogical composition, pH, and ionic strength), physical (porosity, water holding capacity, and texture) properties, and biological factors (soil fauna activity and plant root growth). When MPs degrade, the surface cracks, the specific surface area increases, and oxygen-containing functional groups such as carboxyl, aldehyde, and hydroxyl groups are produced. MPs reduce the stability of soil aggregates and change the community structure and functional gene abundance of microorganisms, affecting the organic carbon and nitrogen cycling processes. This review will help enhance the effective control of soil MPs and provide a theoretical reference to the mechanisms of their effects on soil carbon and nitrogen cycles. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2022. Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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A Review of Microplastics in Soil: Distribution Within Pedosphere Compartments, Environmental Fate, and Effects |
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https://dx.doi.org/10.1007/s11270-022-05837-w |
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Huang, Yimei An, Shaoshan Zhu, Zhaolong |
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2024-07-03T16:30:20.047Z |
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|
| score |
7.401041 |