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Solidification/Stabilization of Waste Incineration Fly Ash by Modified Calcium Aluminate Cement
Ordinary Portland cement (OPC) is the most common curing agent for solidification/stabilization (S/S) of fly ash (FA), however, the treatment is not efficient. This study aims to investigate the S/S of FA with the modified calcium aluminate cement (CAC) as a binder. The modified CAC was obtained...
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Published in: | Water, air, and soil pollution air, and soil pollution, 2024-03, Vol.235 (3), p.163, Article 163 |
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Ordinary Portland cement (OPC) is the most common curing agent for solidification/stabilization (S/S) of fly ash (FA), however, the treatment is not efficient. This study aims to investigate the S/S of FA with the modified calcium aluminate cement (CAC) as a binder. The modified CAC was obtained by adding sodium dihydrogen phosphate (NaH
2
PO
4
), an inorganic chemical agent, and sodium diethyl dithiocarbamate (DDTC), an organic chemical agent, into CAC. Toxicity characteristic leaching procedure and unconfined compressive strength (UCS) test were carried out to evaluate the treatment effect of the proposed binder. The sequential extraction procedure (SEP), X-ray diffraction and scanning electron microscopy (SEM) were used to study the chemical speciation
,
mineralogical characterization and microstructure of the solidified/stabilized FA. The treatment results of pure CAC and OPC showed that the immobilizing efficiency of CAC was much higher than that of OPC. When curing with 10% CAC and 1% DDTC, the leaching concentrations of Cd, Pb and Zn decreased to 0.06, 0.12 and 18.95 mg/L, respectively. With the combination of 10% CAC and 0.5% DDTC + 0.5% NaH
2
PO
4
, the leaching concentrations of Cd, Pb and Zn were 0.12, 0.16 and 10.21 mg/L, respectively. The regulated leaching limits can be met under both of the above combinations. The UCS of the solidified body was 3.02 MPa under the combination of CAC + NaH
2
PO
4
+ DDTC, which was much higher than the 1.34 MPa of the CAC + DDTC combination. SEP shows that most unstable forms of Cd, Pb and Zn in FA were converted to stable forms after the treatment by modified CAC. The immobilization mechanisms of the proposed binder included encapsulation of heavy metals and the formation of heavy metal complexes or precipitate. The CAC hydration products, the precipitate and complexes reduced the pores in FA particles and therefore reduced the leachability of heavy metals. This study demonstrated the effectiveness of the proposed modified CAC as a binder for FA treatment. As NaH
2
PO
4
is inexpensive than DDTC, the scheme of CAC + NaH
2
PO
4
+ DDTC is recommended.
Graphical Abstract |
doi_str_mv | 10.1007/s11270-024-06951-7 |
format | article |
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Ordinary Portland cement (OPC) is the most common curing agent for solidification/stabilization (S/S) of fly ash (FA), however, the treatment is not efficient. This study aims to investigate the S/S of FA with the modified calcium aluminate cement (CAC) as a binder. The modified CAC was obtained by adding sodium dihydrogen phosphate (NaH
2
PO
4
), an inorganic chemical agent, and sodium diethyl dithiocarbamate (DDTC), an organic chemical agent, into CAC. Toxicity characteristic leaching procedure and unconfined compressive strength (UCS) test were carried out to evaluate the treatment effect of the proposed binder. The sequential extraction procedure (SEP), X-ray diffraction and scanning electron microscopy (SEM) were used to study the chemical speciation
,
mineralogical characterization and microstructure of the solidified/stabilized FA. The treatment results of pure CAC and OPC showed that the immobilizing efficiency of CAC was much higher than that of OPC. When curing with 10% CAC and 1% DDTC, the leaching concentrations of Cd, Pb and Zn decreased to 0.06, 0.12 and 18.95 mg/L, respectively. With the combination of 10% CAC and 0.5% DDTC + 0.5% NaH
2
PO
4
, the leaching concentrations of Cd, Pb and Zn were 0.12, 0.16 and 10.21 mg/L, respectively. The regulated leaching limits can be met under both of the above combinations. The UCS of the solidified body was 3.02 MPa under the combination of CAC + NaH
2
PO
4
+ DDTC, which was much higher than the 1.34 MPa of the CAC + DDTC combination. SEP shows that most unstable forms of Cd, Pb and Zn in FA were converted to stable forms after the treatment by modified CAC. The immobilization mechanisms of the proposed binder included encapsulation of heavy metals and the formation of heavy metal complexes or precipitate. The CAC hydration products, the precipitate and complexes reduced the pores in FA particles and therefore reduced the leachability of heavy metals. This study demonstrated the effectiveness of the proposed modified CAC as a binder for FA treatment. As NaH
2
PO
4
is inexpensive than DDTC, the scheme of CAC + NaH
2
PO
4
+ DDTC is recommended.
Graphical Abstract</description><identifier>ISSN: 0049-6979</identifier><identifier>EISSN: 1573-2932</identifier><identifier>DOI: 10.1007/s11270-024-06951-7</identifier><language>eng</language><publisher>Cham: Springer International Publishing</publisher><subject>Aluminous cements ; Atmospheric Protection/Air Quality Control/Air Pollution ; Cadmium ; Calcium ; Calcium aluminate ; Cement ; Chemical speciation ; Climate Change/Climate Change Impacts ; Compressive strength ; Concrete ; Coordination compounds ; Curing ; Curing (processing) ; Curing agents ; Earth and Environmental Science ; Electron microscopy ; Environment ; Extraction procedures ; Fly ash ; Heavy metals ; Hydrogeology ; Immobilization ; Incineration ; Leaching ; Lead ; Metal complexes ; Microstructure ; Organic chemicals ; Organic chemistry ; Phosphates ; Portland cement ; Portland cements ; Scanning electron microscopy ; Sodium ; Sodium phosphate ; Soil Science & Conservation ; Solidification ; Speciation ; Stabilization ; Toxicity ; Waste disposal ; Water Quality/Water Pollution ; X-ray diffraction ; Zinc</subject><ispartof>Water, air, and soil pollution, 2024-03, Vol.235 (3), p.163, Article 163</ispartof><rights>The Author(s), under exclusive licence to Springer Nature Switzerland AG 2024. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><cites>FETCH-LOGICAL-c270t-e3d059371f7603f2a75579879cfe0a18fcc72304ec7f6808e1e3509490f8cf213</cites><orcidid>0000-0002-1645-562X</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids></links><search><creatorcontrib>Wang, Shifang</creatorcontrib><creatorcontrib>Zhang, Wenjie</creatorcontrib><creatorcontrib>Jia, Zhiwei</creatorcontrib><title>Solidification/Stabilization of Waste Incineration Fly Ash by Modified Calcium Aluminate Cement</title><title>Water, air, and soil pollution</title><addtitle>Water Air Soil Pollut</addtitle><description>
Ordinary Portland cement (OPC) is the most common curing agent for solidification/stabilization (S/S) of fly ash (FA), however, the treatment is not efficient. This study aims to investigate the S/S of FA with the modified calcium aluminate cement (CAC) as a binder. The modified CAC was obtained by adding sodium dihydrogen phosphate (NaH
2
PO
4
), an inorganic chemical agent, and sodium diethyl dithiocarbamate (DDTC), an organic chemical agent, into CAC. Toxicity characteristic leaching procedure and unconfined compressive strength (UCS) test were carried out to evaluate the treatment effect of the proposed binder. The sequential extraction procedure (SEP), X-ray diffraction and scanning electron microscopy (SEM) were used to study the chemical speciation
,
mineralogical characterization and microstructure of the solidified/stabilized FA. The treatment results of pure CAC and OPC showed that the immobilizing efficiency of CAC was much higher than that of OPC. When curing with 10% CAC and 1% DDTC, the leaching concentrations of Cd, Pb and Zn decreased to 0.06, 0.12 and 18.95 mg/L, respectively. With the combination of 10% CAC and 0.5% DDTC + 0.5% NaH
2
PO
4
, the leaching concentrations of Cd, Pb and Zn were 0.12, 0.16 and 10.21 mg/L, respectively. The regulated leaching limits can be met under both of the above combinations. The UCS of the solidified body was 3.02 MPa under the combination of CAC + NaH
2
PO
4
+ DDTC, which was much higher than the 1.34 MPa of the CAC + DDTC combination. SEP shows that most unstable forms of Cd, Pb and Zn in FA were converted to stable forms after the treatment by modified CAC. The immobilization mechanisms of the proposed binder included encapsulation of heavy metals and the formation of heavy metal complexes or precipitate. The CAC hydration products, the precipitate and complexes reduced the pores in FA particles and therefore reduced the leachability of heavy metals. This study demonstrated the effectiveness of the proposed modified CAC as a binder for FA treatment. As NaH
2
PO
4
is inexpensive than DDTC, the scheme of CAC + NaH
2
PO
4
+ DDTC is recommended.
Graphical Abstract</description><subject>Aluminous cements</subject><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>Cadmium</subject><subject>Calcium</subject><subject>Calcium aluminate</subject><subject>Cement</subject><subject>Chemical speciation</subject><subject>Climate Change/Climate Change Impacts</subject><subject>Compressive strength</subject><subject>Concrete</subject><subject>Coordination compounds</subject><subject>Curing</subject><subject>Curing (processing)</subject><subject>Curing agents</subject><subject>Earth and Environmental Science</subject><subject>Electron microscopy</subject><subject>Environment</subject><subject>Extraction procedures</subject><subject>Fly ash</subject><subject>Heavy metals</subject><subject>Hydrogeology</subject><subject>Immobilization</subject><subject>Incineration</subject><subject>Leaching</subject><subject>Lead</subject><subject>Metal complexes</subject><subject>Microstructure</subject><subject>Organic chemicals</subject><subject>Organic chemistry</subject><subject>Phosphates</subject><subject>Portland cement</subject><subject>Portland cements</subject><subject>Scanning electron microscopy</subject><subject>Sodium</subject><subject>Sodium phosphate</subject><subject>Soil Science & Conservation</subject><subject>Solidification</subject><subject>Speciation</subject><subject>Stabilization</subject><subject>Toxicity</subject><subject>Waste disposal</subject><subject>Water Quality/Water Pollution</subject><subject>X-ray diffraction</subject><subject>Zinc</subject><issn>0049-6979</issn><issn>1573-2932</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><recordid>eNp9kE9LAzEQxYMoWKtfwFPAc-wk2d1sjmWxWqh4qOIxpGmiKfunJruH-ulNu4I35zLM8H4zj4fQLYV7CiBmkVImgADLCBQyp0ScoQnNBSdMcnaOJgCZJIUU8hJdxbiDVLIUE6TWXe233nmje9-1s3WvN77236cJdw6_69hbvGyNb20Yt4v6gOfxE28O-Lk7snaLK10bPzR4Xg-Nb3VCKtvYtr9GF07X0d789il6Wzy8Vk9k9fK4rOYrYpLvnli-hVxyQZ0ogDumRZ6LZFAaZ0HT0hkjGIfMGuGKEkpLLc9BZhJcaRyjfIruxrv70H0NNvZq1w2hTS8Vk0yIjNNSJBUbVSZ0MQbr1D74RoeDoqCOQaoxSJWCVKcg1RHiIxSTuP2w4e_0P9QPiCh1pA</recordid><startdate>20240301</startdate><enddate>20240301</enddate><creator>Wang, Shifang</creator><creator>Zhang, Wenjie</creator><creator>Jia, Zhiwei</creator><general>Springer International Publishing</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7T7</scope><scope>7TV</scope><scope>7U7</scope><scope>7UA</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H96</scope><scope>H97</scope><scope>K9.</scope><scope>L.G</scope><scope>P64</scope><orcidid>https://orcid.org/0000-0002-1645-562X</orcidid></search><sort><creationdate>20240301</creationdate><title>Solidification/Stabilization of Waste Incineration Fly Ash by Modified Calcium Aluminate Cement</title><author>Wang, Shifang ; Zhang, Wenjie ; Jia, Zhiwei</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c270t-e3d059371f7603f2a75579879cfe0a18fcc72304ec7f6808e1e3509490f8cf213</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2024</creationdate><topic>Aluminous cements</topic><topic>Atmospheric Protection/Air Quality Control/Air Pollution</topic><topic>Cadmium</topic><topic>Calcium</topic><topic>Calcium aluminate</topic><topic>Cement</topic><topic>Chemical speciation</topic><topic>Climate Change/Climate Change Impacts</topic><topic>Compressive strength</topic><topic>Concrete</topic><topic>Coordination compounds</topic><topic>Curing</topic><topic>Curing (processing)</topic><topic>Curing agents</topic><topic>Earth and Environmental Science</topic><topic>Electron microscopy</topic><topic>Environment</topic><topic>Extraction procedures</topic><topic>Fly ash</topic><topic>Heavy metals</topic><topic>Hydrogeology</topic><topic>Immobilization</topic><topic>Incineration</topic><topic>Leaching</topic><topic>Lead</topic><topic>Metal complexes</topic><topic>Microstructure</topic><topic>Organic chemicals</topic><topic>Organic chemistry</topic><topic>Phosphates</topic><topic>Portland cement</topic><topic>Portland cements</topic><topic>Scanning electron microscopy</topic><topic>Sodium</topic><topic>Sodium phosphate</topic><topic>Soil Science & Conservation</topic><topic>Solidification</topic><topic>Speciation</topic><topic>Stabilization</topic><topic>Toxicity</topic><topic>Waste disposal</topic><topic>Water Quality/Water Pollution</topic><topic>X-ray diffraction</topic><topic>Zinc</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wang, Shifang</creatorcontrib><creatorcontrib>Zhang, Wenjie</creatorcontrib><creatorcontrib>Jia, Zhiwei</creatorcontrib><collection>CrossRef</collection><collection>Aqualine</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy & Non-Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Water, air, and soil pollution</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Wang, Shifang</au><au>Zhang, Wenjie</au><au>Jia, Zhiwei</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Solidification/Stabilization of Waste Incineration Fly Ash by Modified Calcium Aluminate Cement</atitle><jtitle>Water, air, and soil pollution</jtitle><stitle>Water Air Soil Pollut</stitle><date>2024-03-01</date><risdate>2024</risdate><volume>235</volume><issue>3</issue><spage>163</spage><pages>163-</pages><artnum>163</artnum><issn>0049-6979</issn><eissn>1573-2932</eissn><abstract>
Ordinary Portland cement (OPC) is the most common curing agent for solidification/stabilization (S/S) of fly ash (FA), however, the treatment is not efficient. This study aims to investigate the S/S of FA with the modified calcium aluminate cement (CAC) as a binder. The modified CAC was obtained by adding sodium dihydrogen phosphate (NaH
2
PO
4
), an inorganic chemical agent, and sodium diethyl dithiocarbamate (DDTC), an organic chemical agent, into CAC. Toxicity characteristic leaching procedure and unconfined compressive strength (UCS) test were carried out to evaluate the treatment effect of the proposed binder. The sequential extraction procedure (SEP), X-ray diffraction and scanning electron microscopy (SEM) were used to study the chemical speciation
,
mineralogical characterization and microstructure of the solidified/stabilized FA. The treatment results of pure CAC and OPC showed that the immobilizing efficiency of CAC was much higher than that of OPC. When curing with 10% CAC and 1% DDTC, the leaching concentrations of Cd, Pb and Zn decreased to 0.06, 0.12 and 18.95 mg/L, respectively. With the combination of 10% CAC and 0.5% DDTC + 0.5% NaH
2
PO
4
, the leaching concentrations of Cd, Pb and Zn were 0.12, 0.16 and 10.21 mg/L, respectively. The regulated leaching limits can be met under both of the above combinations. The UCS of the solidified body was 3.02 MPa under the combination of CAC + NaH
2
PO
4
+ DDTC, which was much higher than the 1.34 MPa of the CAC + DDTC combination. SEP shows that most unstable forms of Cd, Pb and Zn in FA were converted to stable forms after the treatment by modified CAC. The immobilization mechanisms of the proposed binder included encapsulation of heavy metals and the formation of heavy metal complexes or precipitate. The CAC hydration products, the precipitate and complexes reduced the pores in FA particles and therefore reduced the leachability of heavy metals. This study demonstrated the effectiveness of the proposed modified CAC as a binder for FA treatment. As NaH
2
PO
4
is inexpensive than DDTC, the scheme of CAC + NaH
2
PO
4
+ DDTC is recommended.
Graphical Abstract</abstract><cop>Cham</cop><pub>Springer International Publishing</pub><doi>10.1007/s11270-024-06951-7</doi><orcidid>https://orcid.org/0000-0002-1645-562X</orcidid></addata></record> |
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source | Springer Nature |
subjects | Aluminous cements Atmospheric Protection/Air Quality Control/Air Pollution Cadmium Calcium Calcium aluminate Cement Chemical speciation Climate Change/Climate Change Impacts Compressive strength Concrete Coordination compounds Curing Curing (processing) Curing agents Earth and Environmental Science Electron microscopy Environment Extraction procedures Fly ash Heavy metals Hydrogeology Immobilization Incineration Leaching Lead Metal complexes Microstructure Organic chemicals Organic chemistry Phosphates Portland cement Portland cements Scanning electron microscopy Sodium Sodium phosphate Soil Science & Conservation Solidification Speciation Stabilization Toxicity Waste disposal Water Quality/Water Pollution X-ray diffraction Zinc |
title | Solidification/Stabilization of Waste Incineration Fly Ash by Modified Calcium Aluminate Cement |
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