Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill

Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrifica...
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Autor*in:	Ye, Rong [verfasserIn] Huo, Weizhong [verfasserIn] Zheng, Xiangyu [verfasserIn] Shao, Yuchao [verfasserIn] Wang, Hongtao [verfasserIn] Lu, Wenjing [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2023

Schlagwörter:	Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures

Übergeordnetes Werk:	Enthalten in: Chemosphere - Amsterdam [u.a.] : Elsevier Science, 1972, 344
Übergeordnetes Werk:	volume:344

DOI / URN:	10.1016/j.chemosphere.2023.140286

Katalog-ID:	ELV065276434

Internformat


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520			\|a Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures.
650		4	\|a Simulated aerated landfill
650		4	\|a Fungal nitrification
650		4	\|a Ammonia nitrogen removal
650		4	\|a Elevated temperatures
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700	1		\|a Wang, Hongtao \|e verfasserin \|4 aut
700	1		\|a Lu, Wenjing \|e verfasserin \|4 aut
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allfields	10.1016/j.chemosphere.2023.140286 doi (DE-627)ELV065276434 (ELSEVIER)S0045-6535(23)02556-0 DE-627 ger DE-627 rda eng 333.7 VZ 43.00 bkl Ye, Rong verfasserin aut Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill 2023 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures. Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures Huo, Weizhong verfasserin aut Zheng, Xiangyu verfasserin aut Shao, Yuchao verfasserin aut Wang, Hongtao verfasserin aut Lu, Wenjing verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 344 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:344 GBV_USEFLAG_U GBV_ELV SYSFLAG_U SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 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_2034 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 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_4333 GBV_ILN_4334 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.00 Umweltforschung Umweltschutz: Allgemeines VZ AR 344
spelling	10.1016/j.chemosphere.2023.140286 doi (DE-627)ELV065276434 (ELSEVIER)S0045-6535(23)02556-0 DE-627 ger DE-627 rda eng 333.7 VZ 43.00 bkl Ye, Rong verfasserin aut Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill 2023 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures. Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures Huo, Weizhong verfasserin aut Zheng, Xiangyu verfasserin aut Shao, Yuchao verfasserin aut Wang, Hongtao verfasserin aut Lu, Wenjing verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 344 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:344 GBV_USEFLAG_U GBV_ELV SYSFLAG_U SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 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_2034 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 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_4333 GBV_ILN_4334 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.00 Umweltforschung Umweltschutz: Allgemeines VZ AR 344
allfields_unstemmed	10.1016/j.chemosphere.2023.140286 doi (DE-627)ELV065276434 (ELSEVIER)S0045-6535(23)02556-0 DE-627 ger DE-627 rda eng 333.7 VZ 43.00 bkl Ye, Rong verfasserin aut Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill 2023 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures. Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures Huo, Weizhong verfasserin aut Zheng, Xiangyu verfasserin aut Shao, Yuchao verfasserin aut Wang, Hongtao verfasserin aut Lu, Wenjing verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 344 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:344 GBV_USEFLAG_U GBV_ELV SYSFLAG_U SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 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_2034 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 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_4333 GBV_ILN_4334 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.00 Umweltforschung Umweltschutz: Allgemeines VZ AR 344
allfieldsGer	10.1016/j.chemosphere.2023.140286 doi (DE-627)ELV065276434 (ELSEVIER)S0045-6535(23)02556-0 DE-627 ger DE-627 rda eng 333.7 VZ 43.00 bkl Ye, Rong verfasserin aut Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill 2023 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures. Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures Huo, Weizhong verfasserin aut Zheng, Xiangyu verfasserin aut Shao, Yuchao verfasserin aut Wang, Hongtao verfasserin aut Lu, Wenjing verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 344 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:344 GBV_USEFLAG_U GBV_ELV SYSFLAG_U SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 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_2034 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 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_4333 GBV_ILN_4334 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.00 Umweltforschung Umweltschutz: Allgemeines VZ AR 344
allfieldsSound	10.1016/j.chemosphere.2023.140286 doi (DE-627)ELV065276434 (ELSEVIER)S0045-6535(23)02556-0 DE-627 ger DE-627 rda eng 333.7 VZ 43.00 bkl Ye, Rong verfasserin aut Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill 2023 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures. Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures Huo, Weizhong verfasserin aut Zheng, Xiangyu verfasserin aut Shao, Yuchao verfasserin aut Wang, Hongtao verfasserin aut Lu, Wenjing verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 344 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:344 GBV_USEFLAG_U GBV_ELV SYSFLAG_U SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 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_2034 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 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_4333 GBV_ILN_4334 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.00 Umweltforschung Umweltschutz: Allgemeines VZ AR 344
language	English
source	Enthalten in Chemosphere 344 volume:344
sourceStr	Enthalten in Chemosphere 344 volume:344
format_phy_str_mv	Article
bklname	Umweltforschung Umweltschutz: Allgemeines
institution	findex.gbv.de
topic_facet	Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures
dewey-raw	333.7
isfreeaccess_bool	false
container_title	Chemosphere
authorswithroles_txt_mv	Ye, Rong @@aut@@ Huo, Weizhong @@aut@@ Zheng, Xiangyu @@aut@@ Shao, Yuchao @@aut@@ Wang, Hongtao @@aut@@ Lu, Wenjing @@aut@@
publishDateDaySort_date	2023-01-01T00:00:00Z
hierarchy_top_id	306354217
dewey-sort	3333.7
id	ELV065276434
language_de	englisch
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author	Ye, Rong
spellingShingle	Ye, Rong ddc 333.7 bkl 43.00 misc Simulated aerated landfill misc Fungal nitrification misc Ammonia nitrogen removal misc Elevated temperatures Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill
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topic_title	333.7 VZ 43.00 bkl Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill Simulated aerated landfill Fungal nitrification Ammonia nitrogen removal Elevated temperatures
topic	ddc 333.7 bkl 43.00 misc Simulated aerated landfill misc Fungal nitrification misc Ammonia nitrogen removal misc Elevated temperatures
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title	Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill
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title_full	Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill
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title_sort	effect of temperature on fungal nitrification in simulated in-situ aeration of aged msw landfill
title_auth	Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill
abstract	Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures.
abstractGer	Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures.
abstract_unstemmed	Fungal nitrification is one kind of heterotrophic nitrification that involves certain species of fungi promoting the transformation of organic nitrogen and ammonia nitrogen to nitrite/nitrate. In this study, simulated aerated landfill reactors (SALRs) were constructed to investigate fungal nitrification in aged municipal solid refuse, with a focus on understanding the effect of temperature on the performance of fungal nitrification as well as fungal contribution to ammonia nitrogen transformation. Different nitrogen metabolism patterns have been observed in the system with fungi only (SALRF) and complete microbial consortium, i.e., bacteria + fungi (SALRC). At a temperature of 35 °C, autotrophic nitrification dominated the ammonia nitrogen transformation, while fungal nitrification did not significantly contribute to ammonia removal. However, at elevated temperatures (i.e., 45 °C and 55 °C), fungi played a crucial role in ammonia transformation through fungal assimilation and fungal nitrification, with bacterial function suppressed. Furthermore, 45 °C was found to be the optimal temperature for fungal nitrification, exhibiting the highest nitrification rate (13.98 mg L−1 d−1) which accounted for 49.80% of total nitrification rate in the aerated landfill. High throughput sequencing revealed reshaping of fungal community in response to temperature variation. The abundance of Aspergillus fumigatus, with a relative abundance ranging from 67.13% to 92.71% at elevated temperatures, suggested its significant potential for fungal nitrification. These findings have implications for the promotion of nitrogen cycle through strengthening fungal nitrification in aerated landfill sites which often operate at high temperatures.
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title_short	Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill
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author2	Huo, Weizhong Zheng, Xiangyu Shao, Yuchao Wang, Hongtao Lu, Wenjing
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doi_str	10.1016/j.chemosphere.2023.140286
up_date	2024-07-06T22:27:46.185Z
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Effect of temperature on fungal nitrification in simulated in-situ aeration of aged MSW landfill

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Vorhandene Bände

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