The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics

Abstract Microplastics (MPs) have emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains li...
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Autor*in:	Dindar, Efsun [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2024

Schlagwörter:	Ammonification Rates Microplastics Nitrification N Mineralization Soil

Anmerkung:	© The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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.

Übergeordnetes Werk:	Enthalten in: Water, air & soil pollution - Springer International Publishing, 1971, 235(2024), 11 vom: 21. Sept.
Übergeordnetes Werk:	volume:235 ; year:2024 ; number:11 ; day:21 ; month:09

Links:	Volltext

DOI / URN:	10.1007/s11270-024-07500-y

Katalog-ID:	SPR05740254X

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520			\|a Abstract Microplastics (MPs) have emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts.
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allfields	10.1007/s11270-024-07500-y doi (DE-627)SPR05740254X (SPR)s11270-024-07500-y-e DE-627 ger DE-627 rakwb eng 333.7 VZ 43.50 bkl Dindar, Efsun verfasserin (orcid)0000-0002-4572-2512 aut The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics 2024 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213 Enthalten in Water, air & soil pollution Springer International Publishing, 1971 235(2024), 11 vom: 21. Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:235 year:2024 number:11 day:21 month:09 https://dx.doi.org/10.1007/s11270-024-07500-y X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OPC-GGO 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_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 43.50 VZ AR 235 2024 11 21 09
spelling	10.1007/s11270-024-07500-y doi (DE-627)SPR05740254X (SPR)s11270-024-07500-y-e DE-627 ger DE-627 rakwb eng 333.7 VZ 43.50 bkl Dindar, Efsun verfasserin (orcid)0000-0002-4572-2512 aut The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics 2024 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213 Enthalten in Water, air & soil pollution Springer International Publishing, 1971 235(2024), 11 vom: 21. Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:235 year:2024 number:11 day:21 month:09 https://dx.doi.org/10.1007/s11270-024-07500-y X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OPC-GGO 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_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 43.50 VZ AR 235 2024 11 21 09
allfields_unstemmed	10.1007/s11270-024-07500-y doi (DE-627)SPR05740254X (SPR)s11270-024-07500-y-e DE-627 ger DE-627 rakwb eng 333.7 VZ 43.50 bkl Dindar, Efsun verfasserin (orcid)0000-0002-4572-2512 aut The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics 2024 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213 Enthalten in Water, air & soil pollution Springer International Publishing, 1971 235(2024), 11 vom: 21. Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:235 year:2024 number:11 day:21 month:09 https://dx.doi.org/10.1007/s11270-024-07500-y X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OPC-GGO 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_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 43.50 VZ AR 235 2024 11 21 09
allfieldsGer	10.1007/s11270-024-07500-y doi (DE-627)SPR05740254X (SPR)s11270-024-07500-y-e DE-627 ger DE-627 rakwb eng 333.7 VZ 43.50 bkl Dindar, Efsun verfasserin (orcid)0000-0002-4572-2512 aut The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics 2024 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213 Enthalten in Water, air & soil pollution Springer International Publishing, 1971 235(2024), 11 vom: 21. Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:235 year:2024 number:11 day:21 month:09 https://dx.doi.org/10.1007/s11270-024-07500-y X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OPC-GGO 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_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 43.50 VZ AR 235 2024 11 21 09
allfieldsSound	10.1007/s11270-024-07500-y doi (DE-627)SPR05740254X (SPR)s11270-024-07500-y-e DE-627 ger DE-627 rakwb eng 333.7 VZ 43.50 bkl Dindar, Efsun verfasserin (orcid)0000-0002-4572-2512 aut The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics 2024 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213 Enthalten in Water, air & soil pollution Springer International Publishing, 1971 235(2024), 11 vom: 21. Sept. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:235 year:2024 number:11 day:21 month:09 https://dx.doi.org/10.1007/s11270-024-07500-y X:SPRINGER Resolving-System lizenzpflichtig Volltext SYSFLAG_0 GBV_SPRINGER SSG-OPC-GGO 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_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 43.50 VZ AR 235 2024 11 21 09
language	English
source	Enthalten in Water, air & soil pollution 235(2024), 11 vom: 21. Sept. volume:235 year:2024 number:11 day:21 month:09
sourceStr	Enthalten in Water, air & soil pollution 235(2024), 11 vom: 21. Sept. volume:235 year:2024 number:11 day:21 month:09
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Ammonification Rates Microplastics Nitrification N Mineralization Soil
dewey-raw	333.7
isfreeaccess_bool	false
container_title	Water, air & soil pollution
authorswithroles_txt_mv	Dindar, Efsun @@aut@@
publishDateDaySort_date	2024-09-21T00:00:00Z
hierarchy_top_id	271349417
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language_de	englisch
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author	Dindar, Efsun
spellingShingle	Dindar, Efsun ddc 333.7 bkl 43.50 misc Ammonification Rates misc Microplastics misc Nitrification misc N Mineralization misc Soil The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics
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topic_title	333.7 VZ 43.50 bkl The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics Ammonification Rates (dpeaa)DE-He213 Microplastics (dpeaa)DE-He213 Nitrification (dpeaa)DE-He213 N Mineralization (dpeaa)DE-He213 Soil (dpeaa)DE-He213
topic	ddc 333.7 bkl 43.50 misc Ammonification Rates misc Microplastics misc Nitrification misc N Mineralization misc Soil
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title	The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics
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title_full	The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics
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title_sort	the effect of n mineralization, nitrification and ammonification rates in soils contaminated with microplastics
title_auth	The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics
abstract	Abstract Microplastics (MPs) have emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. These results underscore the varying effects of different types of microplastics on soil nitrogen processes, highlighting the critical need for further investigation into their long-term environmental impacts. © The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) 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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title_short	The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics
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Springer Nature or its licensor (e.g. a society or other partner) 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 emerged as a pervasive environmental pollutant, posing significant threats to both aquatic and terrestrial ecosystems. Despite the growing concern, research on the impacts of MPs on soil ecosystems, particularly on crucial processes like nitrogen cycling, remains limited compared to aquatic environments. This study aimed to fill this knowledge gap by conducting a 60-day incubation experiment to investigate the effects of polypropylene (PP), polyethylene (PE), and polyethylene terephthalate (PET) microplastics on soil nitrogen transformation processes. The findings revealed that microplastic contamination influenced soil nitrogen dynamics, with PP having the most detrimental impact. Specifically, the ammonification rate was consistently lower than the nitrification potential, and although the nitrification potential was not negatively affected by the presence of MPs, the availability of soil nitrogen, particularly in the form of nitrate, was predominantly maintained. However, at the end of the incubation period, soils contaminated with PP showed a significant reduction in available nitrogen concentrations. Generally, it was found that PP had the most negative effect on soil nitrogen processes. 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The Effect of N Mineralization, Nitrification and Ammonification Rates in Soils Contaminated with Microplastics

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