Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate
In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption b...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Xu, Nan [verfasserIn] |
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| Format: |
Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2016 |
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| Rechteinformationen: |
Nutzungsrecht: © Springer International Publishing Switzerland 2016 |
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| Schlagwörter: |
Climate Change/Climate Change Impacts |
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| Systematik: |
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| Übergeordnetes Werk: |
Enthalten in: Water, air & soil pollution - Dordrecht : Springer, 1971, 227(2016), 2, Seite 1-11 |
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| Übergeordnetes Werk: |
volume:227 ; year:2016 ; number:2 ; pages:1-11 |
| Links: |
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| DOI / URN: |
10.1007/s11270-016-2757-7 |
|---|
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OLC1971828424 |
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| 520 | |a In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. | ||
| 540 | |a Nutzungsrecht: © Springer International Publishing Switzerland 2016 | ||
| 650 | 4 | |a Environment | |
| 650 | 4 | |a Sorption | |
| 650 | 4 | |a Environment, general | |
| 650 | 4 | |a Phosphate | |
| 650 | 4 | |a Removal | |
| 650 | 4 | |a Fusiform aragonite | |
| 650 | 4 | |a Hydrogeology | |
| 650 | 4 | |a Water Quality/Water Pollution | |
| 650 | 4 | |a Climate Change/Climate Change Impacts | |
| 650 | 4 | |a Atmospheric Protection/Air Quality Control/Air Pollution | |
| 650 | 4 | |a Soil Science & Conservation | |
| 700 | 1 | |a Wang, Yunlong |4 oth | |
| 700 | 1 | |a Xu, Xiaoting |4 oth | |
| 700 | 1 | |a Liu, Cheng |4 oth | |
| 700 | 1 | |a Qian, Junchao |4 oth | |
| 700 | 1 | |a Feng, Gang |4 oth | |
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10.1007/s11270-016-2757-7 doi PQ20160430 (DE-627)OLC1971828424 (DE-599)GBVOLC1971828424 (PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0 (KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma DE-627 ger DE-627 rakwb eng 570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Xu, Nan verfasserin aut Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate 2016 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. Nutzungsrecht: © Springer International Publishing Switzerland 2016 Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation Wang, Yunlong oth Xu, Xiaoting oth Liu, Cheng oth Qian, Junchao oth Feng, Gang oth Enthalten in Water, air & soil pollution Dordrecht : Springer, 1971 227(2016), 2, Seite 1-11 (DE-627)12929134X (DE-600)120499-3 (DE-576)014472643 0049-6979 nnns volume:227 year:2016 number:2 pages:1-11 http://dx.doi.org/10.1007/s11270-016-2757-7 Volltext http://search.proquest.com/docview/1762876739 GBV_USEFLAG_A SYSFLAG_A GBV_OLC FID-BIODIV SSG-OLC-UMW SSG-OLC-TEC SSG-OLC-FOR SSG-OLC-IBL SSG-OLC-DE-84 SSG-OPC-GGO GBV_ILN_70 GBV_ILN_4012 GBV_ILN_4219 GBV_ILN_4313 ZC 7520 AR 227 2016 2 1-11 |
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10.1007/s11270-016-2757-7 doi PQ20160430 (DE-627)OLC1971828424 (DE-599)GBVOLC1971828424 (PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0 (KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma DE-627 ger DE-627 rakwb eng 570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Xu, Nan verfasserin aut Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate 2016 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. Nutzungsrecht: © Springer International Publishing Switzerland 2016 Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation Wang, Yunlong oth Xu, Xiaoting oth Liu, Cheng oth Qian, Junchao oth Feng, Gang oth Enthalten in Water, air & soil pollution Dordrecht : Springer, 1971 227(2016), 2, Seite 1-11 (DE-627)12929134X (DE-600)120499-3 (DE-576)014472643 0049-6979 nnns volume:227 year:2016 number:2 pages:1-11 http://dx.doi.org/10.1007/s11270-016-2757-7 Volltext http://search.proquest.com/docview/1762876739 GBV_USEFLAG_A SYSFLAG_A GBV_OLC FID-BIODIV SSG-OLC-UMW SSG-OLC-TEC SSG-OLC-FOR SSG-OLC-IBL SSG-OLC-DE-84 SSG-OPC-GGO GBV_ILN_70 GBV_ILN_4012 GBV_ILN_4219 GBV_ILN_4313 ZC 7520 AR 227 2016 2 1-11 |
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10.1007/s11270-016-2757-7 doi PQ20160430 (DE-627)OLC1971828424 (DE-599)GBVOLC1971828424 (PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0 (KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma DE-627 ger DE-627 rakwb eng 570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Xu, Nan verfasserin aut Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate 2016 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. Nutzungsrecht: © Springer International Publishing Switzerland 2016 Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation Wang, Yunlong oth Xu, Xiaoting oth Liu, Cheng oth Qian, Junchao oth Feng, Gang oth Enthalten in Water, air & soil pollution Dordrecht : Springer, 1971 227(2016), 2, Seite 1-11 (DE-627)12929134X (DE-600)120499-3 (DE-576)014472643 0049-6979 nnns volume:227 year:2016 number:2 pages:1-11 http://dx.doi.org/10.1007/s11270-016-2757-7 Volltext http://search.proquest.com/docview/1762876739 GBV_USEFLAG_A SYSFLAG_A GBV_OLC FID-BIODIV SSG-OLC-UMW SSG-OLC-TEC SSG-OLC-FOR SSG-OLC-IBL SSG-OLC-DE-84 SSG-OPC-GGO GBV_ILN_70 GBV_ILN_4012 GBV_ILN_4219 GBV_ILN_4313 ZC 7520 AR 227 2016 2 1-11 |
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10.1007/s11270-016-2757-7 doi PQ20160430 (DE-627)OLC1971828424 (DE-599)GBVOLC1971828424 (PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0 (KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma DE-627 ger DE-627 rakwb eng 570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Xu, Nan verfasserin aut Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate 2016 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. Nutzungsrecht: © Springer International Publishing Switzerland 2016 Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation Wang, Yunlong oth Xu, Xiaoting oth Liu, Cheng oth Qian, Junchao oth Feng, Gang oth Enthalten in Water, air & soil pollution Dordrecht : Springer, 1971 227(2016), 2, Seite 1-11 (DE-627)12929134X (DE-600)120499-3 (DE-576)014472643 0049-6979 nnns volume:227 year:2016 number:2 pages:1-11 http://dx.doi.org/10.1007/s11270-016-2757-7 Volltext http://search.proquest.com/docview/1762876739 GBV_USEFLAG_A SYSFLAG_A GBV_OLC FID-BIODIV SSG-OLC-UMW SSG-OLC-TEC SSG-OLC-FOR SSG-OLC-IBL SSG-OLC-DE-84 SSG-OPC-GGO GBV_ILN_70 GBV_ILN_4012 GBV_ILN_4219 GBV_ILN_4313 ZC 7520 AR 227 2016 2 1-11 |
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10.1007/s11270-016-2757-7 doi PQ20160430 (DE-627)OLC1971828424 (DE-599)GBVOLC1971828424 (PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0 (KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma DE-627 ger DE-627 rakwb eng 570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Xu, Nan verfasserin aut Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate 2016 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. Nutzungsrecht: © Springer International Publishing Switzerland 2016 Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation Wang, Yunlong oth Xu, Xiaoting oth Liu, Cheng oth Qian, Junchao oth Feng, Gang oth Enthalten in Water, air & soil pollution Dordrecht : Springer, 1971 227(2016), 2, Seite 1-11 (DE-627)12929134X (DE-600)120499-3 (DE-576)014472643 0049-6979 nnns volume:227 year:2016 number:2 pages:1-11 http://dx.doi.org/10.1007/s11270-016-2757-7 Volltext http://search.proquest.com/docview/1762876739 GBV_USEFLAG_A SYSFLAG_A GBV_OLC FID-BIODIV SSG-OLC-UMW SSG-OLC-TEC SSG-OLC-FOR SSG-OLC-IBL SSG-OLC-DE-84 SSG-OPC-GGO GBV_ILN_70 GBV_ILN_4012 GBV_ILN_4219 GBV_ILN_4313 ZC 7520 AR 227 2016 2 1-11 |
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570 333.7 DE-600 BIODIV fid ZC 7520 AVZ rvk Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate Environment Sorption Environment, general Phosphate Removal Fusiform aragonite Hydrogeology Water Quality/Water Pollution Climate Change/Climate Change Impacts Atmospheric Protection/Air Quality Control/Air Pollution Soil Science & Conservation |
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mechanisms and applications of the synthesized fusiform aragonite for the removal of high concentration of phosphate |
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Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate |
| abstract |
In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. |
| abstractGer |
In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. |
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In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH. |
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Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a2200265 4500</leader><controlfield tag="001">OLC1971828424</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230714182230.0</controlfield><controlfield tag="007">tu</controlfield><controlfield tag="008">160308s2016 xx ||||| 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s11270-016-2757-7</subfield><subfield code="2">doi</subfield></datafield><datafield tag="028" ind1="5" ind2="2"><subfield code="a">PQ20160430</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)OLC1971828424</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-599)GBVOLC1971828424</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(PRQ)c1327-9f9abcc5b0a7b0370da89e0ccf5323aa1def6eed85d3f6e11b1344453c4bb8c0</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(KEY)0054442620160000227000200001mechanismsandapplicationsofthesynthesizedfusiforma</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">570</subfield><subfield code="a">333.7</subfield><subfield code="q">DE-600</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">BIODIV</subfield><subfield code="2">fid</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">ZC 7520</subfield><subfield code="q">AVZ</subfield><subfield code="2">rvk</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Xu, Nan</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Mechanisms and Applications of the Synthesized Fusiform Aragonite for the Removal of High Concentration of Phosphate</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2016</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">ohne Hilfsmittel zu benutzen</subfield><subfield code="b">n</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Band</subfield><subfield code="b">nc</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">In the present work, the synthesized calcium carbonate (CaCO3) identified as fusiform aragonite was obtained through the biomimetic mineralization process for possible recovery of high concentration of phosphorus (P) within the wide range of pH. It was characterized before/after phosphate sorption by the combination of X-ray diffraction analysis (XRD), scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FTIR), and X-ray absorption near-edge structure (XANES) at molecular level. By batch experiments, the sorption isotherms and envelopes of the fusiform aragonite to phosphate were explored. The experimental data showed that the fusiform aragonite at pH ≥6.0 has a steep raising sorption capacity with increasing initial P (>9.0 mM) due to its unique crystalline structure and morphology. The likely mechanism is that the occurrence of fast nucleation growth of Ca-P phases (including amorphous calcium phosphate (ACP), dibasic calcium phosphate (DCP), and hydroxyapatite (HAP)) is triggered upon attainment of the stabilized crystal morphology of aragonite in solution due to phosphate sorption. These features may contribute to the fusiform aragonite as an idea adsorbent for high phosphate removal from wastewater even independent of pH.</subfield></datafield><datafield tag="540" ind1=" " ind2=" "><subfield code="a">Nutzungsrecht: © Springer International Publishing Switzerland 2016</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Environment</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Sorption</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Environment, general</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Phosphate</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Removal</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Fusiform aragonite</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Hydrogeology</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Water Quality/Water Pollution</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Climate Change/Climate Change Impacts</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Atmospheric Protection/Air Quality Control/Air Pollution</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Soil Science & Conservation</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Wang, Yunlong</subfield><subfield code="4">oth</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Xu, Xiaoting</subfield><subfield code="4">oth</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Liu, Cheng</subfield><subfield code="4">oth</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Qian, Junchao</subfield><subfield code="4">oth</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Feng, Gang</subfield><subfield code="4">oth</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Water, air & soil pollution</subfield><subfield code="d">Dordrecht : Springer, 1971</subfield><subfield code="g">227(2016), 2, Seite 1-11</subfield><subfield code="w">(DE-627)12929134X</subfield><subfield code="w">(DE-600)120499-3</subfield><subfield code="w">(DE-576)014472643</subfield><subfield code="x">0049-6979</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:227</subfield><subfield code="g">year:2016</subfield><subfield code="g">number:2</subfield><subfield code="g">pages:1-11</subfield></datafield><datafield tag="856" ind1="4" ind2="1"><subfield code="u">http://dx.doi.org/10.1007/s11270-016-2757-7</subfield><subfield code="3">Volltext</subfield></datafield><datafield tag="856" ind1="4" ind2="2"><subfield code="u">http://search.proquest.com/docview/1762876739</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_OLC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">FID-BIODIV</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-UMW</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-TEC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-FOR</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-IBL</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-DE-84</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OPC-GGO</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4012</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4219</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="936" ind1="r" ind2="v"><subfield code="a">ZC 7520</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">227</subfield><subfield code="j">2016</subfield><subfield code="e">2</subfield><subfield code="h">1-11</subfield></datafield></record></collection>
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