Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids

Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g an...
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Gespeichert in:

Autor*in:	Wang, Hao [verfasserIn] Wang, Xuejiang [verfasserIn] Zhao, Jianfu [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2019

Schlagwörter:	Palygorskite Struvite MgO pH Ions Organic acids

Übergeordnetes Werk:	Enthalten in: Environmental science and pollution research - Berlin : Springer, 1994, 26(2019), 19 vom: 14. Mai, Seite 19729-19737
Übergeordnetes Werk:	volume:26 ; year:2019 ; number:19 ; day:14 ; month:05 ; pages:19729-19737

Links:	Volltext

DOI / URN:	10.1007/s11356-019-05254-3

Katalog-ID:	SPR018863884

Internformat


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245	1	0	\|a Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
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520			\|a Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products.
650		4	\|a Palygorskite \|7 (dpeaa)DE-He213
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650		4	\|a Ions \|7 (dpeaa)DE-He213
650		4	\|a Organic acids \|7 (dpeaa)DE-He213
700	1		\|a Wang, Xuejiang \|e verfasserin \|4 aut
700	1		\|a Zhao, Jianfu \|e verfasserin \|4 aut
773	0	8	\|i Enthalten in \|t Environmental science and pollution research \|d Berlin : Springer, 1994 \|g 26(2019), 19 vom: 14. Mai, Seite 19729-19737 \|w (DE-627)320517926 \|w (DE-600)2014192-0 \|x 1614-7499 \|7 nnns
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912			\|a GBV_ILN_63
912			\|a GBV_ILN_65
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
912			\|a GBV_ILN_74
912			\|a GBV_ILN_90
912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_381
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
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912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2070
912			\|a GBV_ILN_2086
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
912			\|a GBV_ILN_2110
912			\|a GBV_ILN_2111
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912			\|a GBV_ILN_2113
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912			\|a GBV_ILN_2548
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936	b	k	\|a 43.00 \|q ASE
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Indexfelder

author_variant	h w hw x w xw j z jz
matchkey_str	article:16147499:2019----::plctoomooiidayosieontinrcvrfosieatwtr
hierarchy_sort_str	2019
bklnumber	43.00 43.50 58.50
publishDate	2019
allfields	10.1007/s11356-019-05254-3 doi (DE-627)SPR018863884 (SPR)s11356-019-05254-3-e DE-627 ger DE-627 rakwb eng 333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Wang, Hao verfasserin aut Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products. Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Wang, Xuejiang verfasserin aut Zhao, Jianfu verfasserin aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 26(2019), 19 vom: 14. Mai, Seite 19729-19737 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737 https://dx.doi.org/10.1007/s11356-019-05254-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 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_381 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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 43.00 ASE 43.50 ASE 58.50 ASE AR 26 2019 19 14 05 19729-19737
spelling	10.1007/s11356-019-05254-3 doi (DE-627)SPR018863884 (SPR)s11356-019-05254-3-e DE-627 ger DE-627 rakwb eng 333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Wang, Hao verfasserin aut Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products. Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Wang, Xuejiang verfasserin aut Zhao, Jianfu verfasserin aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 26(2019), 19 vom: 14. Mai, Seite 19729-19737 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737 https://dx.doi.org/10.1007/s11356-019-05254-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 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_381 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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 43.00 ASE 43.50 ASE 58.50 ASE AR 26 2019 19 14 05 19729-19737
allfields_unstemmed	10.1007/s11356-019-05254-3 doi (DE-627)SPR018863884 (SPR)s11356-019-05254-3-e DE-627 ger DE-627 rakwb eng 333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Wang, Hao verfasserin aut Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products. Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Wang, Xuejiang verfasserin aut Zhao, Jianfu verfasserin aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 26(2019), 19 vom: 14. Mai, Seite 19729-19737 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737 https://dx.doi.org/10.1007/s11356-019-05254-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 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_381 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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 43.00 ASE 43.50 ASE 58.50 ASE AR 26 2019 19 14 05 19729-19737
allfieldsGer	10.1007/s11356-019-05254-3 doi (DE-627)SPR018863884 (SPR)s11356-019-05254-3-e DE-627 ger DE-627 rakwb eng 333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Wang, Hao verfasserin aut Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products. Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Wang, Xuejiang verfasserin aut Zhao, Jianfu verfasserin aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 26(2019), 19 vom: 14. Mai, Seite 19729-19737 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737 https://dx.doi.org/10.1007/s11356-019-05254-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 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_381 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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 43.00 ASE 43.50 ASE 58.50 ASE AR 26 2019 19 14 05 19729-19737
allfieldsSound	10.1007/s11356-019-05254-3 doi (DE-627)SPR018863884 (SPR)s11356-019-05254-3-e DE-627 ger DE-627 rakwb eng 333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Wang, Hao verfasserin aut Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids 2019 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products. Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213 Wang, Xuejiang verfasserin aut Zhao, Jianfu verfasserin aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 26(2019), 19 vom: 14. Mai, Seite 19729-19737 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737 https://dx.doi.org/10.1007/s11356-019-05254-3 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 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_381 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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 43.00 ASE 43.50 ASE 58.50 ASE AR 26 2019 19 14 05 19729-19737
language	English
source	Enthalten in Environmental science and pollution research 26(2019), 19 vom: 14. Mai, Seite 19729-19737 volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737
sourceStr	Enthalten in Environmental science and pollution research 26(2019), 19 vom: 14. Mai, Seite 19729-19737 volume:26 year:2019 number:19 day:14 month:05 pages:19729-19737
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Palygorskite Struvite MgO pH Ions Organic acids
dewey-raw	333.7
isfreeaccess_bool	false
container_title	Environmental science and pollution research
authorswithroles_txt_mv	Wang, Hao @@aut@@ Wang, Xuejiang @@aut@@ Zhao, Jianfu @@aut@@
publishDateDaySort_date	2019-05-14T00:00:00Z
hierarchy_top_id	320517926
dewey-sort	3333.7
id	SPR018863884
language_de	englisch
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The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. 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author	Wang, Hao
spellingShingle	Wang, Hao ddc 333.7 bkl 43.00 bkl 43.50 bkl 58.50 misc Palygorskite misc Struvite misc MgO misc pH misc Ions misc Organic acids Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
authorStr	Wang, Hao
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topic_title	333.7 690 ASE 43.00 bkl 43.50 bkl 58.50 bkl Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids Palygorskite (dpeaa)DE-He213 Struvite (dpeaa)DE-He213 MgO (dpeaa)DE-He213 pH (dpeaa)DE-He213 Ions (dpeaa)DE-He213 Organic acids (dpeaa)DE-He213
topic	ddc 333.7 bkl 43.00 bkl 43.50 bkl 58.50 misc Palygorskite misc Struvite misc MgO misc pH misc Ions misc Organic acids
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title	Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
ctrlnum	(DE-627)SPR018863884 (SPR)s11356-019-05254-3-e
title_full	Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
author_sort	Wang, Hao
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author_browse	Wang, Hao Wang, Xuejiang Zhao, Jianfu
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author-letter	Wang, Hao
doi_str_mv	10.1007/s11356-019-05254-3
dewey-full	333.7 690
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title_sort	application of mgo-modified palygorskite for nutrient recovery from swine wastewater: effect of ph, ions, and organic acids
title_auth	Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
abstract	Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products.
abstractGer	Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products.
abstract_unstemmed	Abstract In this study, MgO-modified palygorskite (MgO-PAL) was used for simultaneous recovery of ammonia nitrogen (AN) and phosphate, and the effects of pH, ions, and organic acids on nutrient recovery were investigated. The highest removal amount of AN and phosphate separately reached 42.6 mg/g and 69.8 mg/g at pH of 9.0, 0.6 g/L dosage of modified palygorskite, and 180 min of the reaction time. MgO-PAL provided a wide range of pH (3–9) for nutrient removal. Mg released concentration was tested to investigate the removal mechanisms. The individual presence of four cations ($ K^{+} $, $ Ca^{2+} $, $ Na^{+} $, and $ Mg^{2+} $) showed negative effect on AN removal at different mass concentrations. However, those cations, except $ Na^{+} $, exhibited positive influence on phosphate removal. Compared with $ SO_{4} $2−, $ CO_{3} $2−showed more negative effect on nutrient removal due to the reaction between $ Mg^{2+} $ and $ CO_{3} $2−. The results showed that the nutrient removal amount and the morphology and composition of collected products were not affected in the presence of acetic acid. Citric acid, humic acid, and fulvic acid displayed the inhibition effects on the morphology of the crystallized products.
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container_issue	19
title_short	Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids
url	https://dx.doi.org/10.1007/s11356-019-05254-3
remote_bool	true
author2	Wang, Xuejiang Zhao, Jianfu
author2Str	Wang, Xuejiang Zhao, Jianfu
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doi_str	10.1007/s11356-019-05254-3
up_date	2024-07-03T22:46:32.558Z
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Application of MgO-modified palygorskite for nutrient recovery from swine wastewater: effect of pH, ions, and organic acids

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