O, N-doped porous biochar by air oxidation for enhancing heavy metal removal: The role of O, N functional groups

Oxygen- and nitrogen-doped porous oxidized biochar (O,N-doped OBC) was fabricated in this study. Biochar (BC) can be enriched in surface functional groups (O and N) and the porosity can be improved by a simple, convenient and green procedure. BC was oxidized at 200 °C in an air atmosphere with quali...

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Veröffentlicht in:Chemosphere (Oxford) 2022-04, Vol.293, p.133622-133622, Article 133622
Hauptverfasser: Dinh, Viet Cuong, Hou, Chia-Hung, Dao, Thuy Ninh
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Hou, Chia-Hung
Dao, Thuy Ninh
description Oxygen- and nitrogen-doped porous oxidized biochar (O,N-doped OBC) was fabricated in this study. Biochar (BC) can be enriched in surface functional groups (O and N) and the porosity can be improved by a simple, convenient and green procedure. BC was oxidized at 200 °C in an air atmosphere with quality control via oxidation time changes. As the oxidation time increased, the O and N contents and porosity of the materials improved. After 1.5 h of oxidation, the O and N contents of O,N-doped OBC-1.5 were 54.4% and 3.9%, higher than those of BC, which were 33.4% and 1.8%, respectively. The specific surface area and pore volume of O,N-doped OBC-1.5 were 88.5 m2 g−1 and 0.07 cm3 g−1, respectively, which were greater than those of BC. The improved surface functionality and porosity resulted in an increased heavy metal removal efficiency. As a result, the maximum adsorption capacity of Cu(II) by O,N-doped OBC was 23.32 mg L−1, which was twofold higher than that of pristine BC. Additionally, for a multiple ion solution, O,N-doped OBC-1.5 showed a greater adsorption behavior toward Cu(II) than Zn(II) and Ni(II). In a batch experiment, the concentration of Cu(II) decreased 92.3% after 90 min. In a filtration experiment, the O,N-doped OBC-based filter achieved a Cu(II) removal capacity of 12.90 mg g−1 and breakthrough time after 250 min. Importantly, the chemical mechanism was mainly governed by monolayer adsorption of Cu(II) onto a homogeneous surface of O,N-doped OBC-1.5. Surface complexation and electrostatic attraction were considered to be the chemical mechanisms governing the adsorption process. [Display omitted] •O, N-doped OBC was fabricated by a simple air oxidation process.•Air can provide natural and green O and N sources for the doping process.•Air oxidation also improved the porous structure of O, N-doped OBC.•O, N doping played an important role in improved heavy metal removal efficiency.
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Additionally, for a multiple ion solution, O,N-doped OBC-1.5 showed a greater adsorption behavior toward Cu(II) than Zn(II) and Ni(II). In a batch experiment, the concentration of Cu(II) decreased 92.3% after 90 min. In a filtration experiment, the O,N-doped OBC-based filter achieved a Cu(II) removal capacity of 12.90 mg g−1 and breakthrough time after 250 min. Importantly, the chemical mechanism was mainly governed by monolayer adsorption of Cu(II) onto a homogeneous surface of O,N-doped OBC-1.5. Surface complexation and electrostatic attraction were considered to be the chemical mechanisms governing the adsorption process. 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Biochar (BC) can be enriched in surface functional groups (O and N) and the porosity can be improved by a simple, convenient and green procedure. BC was oxidized at 200 °C in an air atmosphere with quality control via oxidation time changes. As the oxidation time increased, the O and N contents and porosity of the materials improved. After 1.5 h of oxidation, the O and N contents of O,N-doped OBC-1.5 were 54.4% and 3.9%, higher than those of BC, which were 33.4% and 1.8%, respectively. The specific surface area and pore volume of O,N-doped OBC-1.5 were 88.5 m2 g−1 and 0.07 cm3 g−1, respectively, which were greater than those of BC. The improved surface functionality and porosity resulted in an increased heavy metal removal efficiency. As a result, the maximum adsorption capacity of Cu(II) by O,N-doped OBC was 23.32 mg L−1, which was twofold higher than that of pristine BC. Additionally, for a multiple ion solution, O,N-doped OBC-1.5 showed a greater adsorption behavior toward Cu(II) than Zn(II) and Ni(II). In a batch experiment, the concentration of Cu(II) decreased 92.3% after 90 min. In a filtration experiment, the O,N-doped OBC-based filter achieved a Cu(II) removal capacity of 12.90 mg g−1 and breakthrough time after 250 min. Importantly, the chemical mechanism was mainly governed by monolayer adsorption of Cu(II) onto a homogeneous surface of O,N-doped OBC-1.5. Surface complexation and electrostatic attraction were considered to be the chemical mechanisms governing the adsorption process. [Display omitted] •O, N-doped OBC was fabricated by a simple air oxidation process.•Air can provide natural and green O and N sources for the doping process.•Air oxidation also improved the porous structure of O, N-doped OBC.•O, N doping played an important role in improved heavy metal removal efficiency.</description><subject>Adsorption</subject><subject>Adsorption mechanism</subject><subject>air</subject><subject>Air oxidation</subject><subject>biochar</subject><subject>Charcoal - chemistry</subject><subject>electrostatic interactions</subject><subject>filtration</subject><subject>Green method</subject><subject>Heavy metal removal</subject><subject>heavy metals</subject><subject>Metals, Heavy</subject><subject>oxidation</subject><subject>Oxygen and nitrogen doping</subject><subject>Porosity</subject><subject>Porous biochar</subject><subject>quality control</subject><subject>surface area</subject><subject>Water Pollutants, Chemical - analysis</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2022</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkctu2zAQRYmiQeMm_YWC3XVROXyYNNVdYTRpgSDeOGtiRI0iGpKokLIR_31o2Cm6zGpmce6dxyXkG2dzzri-2c5di31IY4sR54IJMedSaiE-kBk3y7LgojQfyYyxhSq0kuqSfE5py1gWq_ITuZSKSal4OSPj-gd9KOowYk3HEMMu0coH10Kk1YGCjzS8-BomHwbahEhxaGFwfniiLcL-QHucoKMxb7OH7ifdtEhj6JCGhh6dabMb3FGcoafsPqZrctFAl_DLuV6Rx9vfm9Wf4n5993f1675wC86mAlFAo6RZlFzxSgm-MAYcA-Mkk4DYsLpCxXNflcyAdiC01s1yiZA7IeUV-X7yHWN43mGabO-Tw66DAfOVVmiZPyOMYe9ABVsqqQ3PaHlCXQwpRWzsGH0P8WA5s8ds7Nb-l409ZmNP2WTt1_OYXdVj_U_5FkYGVicA81_2HqNNzuPgsPYR3WTr4N8x5hVep6Vc</recordid><startdate>202204</startdate><enddate>202204</enddate><creator>Dinh, Viet Cuong</creator><creator>Hou, Chia-Hung</creator><creator>Dao, Thuy Ninh</creator><general>Elsevier Ltd</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope><scope>7S9</scope><scope>L.6</scope><orcidid>https://orcid.org/0000-0002-9084-8595</orcidid></search><sort><creationdate>202204</creationdate><title>O, N-doped porous biochar by air oxidation for enhancing heavy metal removal: The role of O, N functional groups</title><author>Dinh, Viet Cuong ; Hou, Chia-Hung ; Dao, Thuy Ninh</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c410t-ee2af53849151b521488ac0a8c303aeef0dbe5103ab908a6ca2666f77eaa26233</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2022</creationdate><topic>Adsorption</topic><topic>Adsorption mechanism</topic><topic>air</topic><topic>Air oxidation</topic><topic>biochar</topic><topic>Charcoal - chemistry</topic><topic>electrostatic interactions</topic><topic>filtration</topic><topic>Green method</topic><topic>Heavy metal removal</topic><topic>heavy metals</topic><topic>Metals, Heavy</topic><topic>oxidation</topic><topic>Oxygen and nitrogen doping</topic><topic>Porosity</topic><topic>Porous biochar</topic><topic>quality control</topic><topic>surface area</topic><topic>Water Pollutants, Chemical - analysis</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Dinh, Viet Cuong</creatorcontrib><creatorcontrib>Hou, Chia-Hung</creatorcontrib><creatorcontrib>Dao, Thuy Ninh</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><collection>AGRICOLA</collection><collection>AGRICOLA - Academic</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Dinh, Viet Cuong</au><au>Hou, Chia-Hung</au><au>Dao, Thuy Ninh</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>O, N-doped porous biochar by air oxidation for enhancing heavy metal removal: The role of O, N functional groups</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2022-04</date><risdate>2022</risdate><volume>293</volume><spage>133622</spage><epage>133622</epage><pages>133622-133622</pages><artnum>133622</artnum><issn>0045-6535</issn><eissn>1879-1298</eissn><abstract>Oxygen- and nitrogen-doped porous oxidized biochar (O,N-doped OBC) was fabricated in this study. Biochar (BC) can be enriched in surface functional groups (O and N) and the porosity can be improved by a simple, convenient and green procedure. BC was oxidized at 200 °C in an air atmosphere with quality control via oxidation time changes. As the oxidation time increased, the O and N contents and porosity of the materials improved. After 1.5 h of oxidation, the O and N contents of O,N-doped OBC-1.5 were 54.4% and 3.9%, higher than those of BC, which were 33.4% and 1.8%, respectively. The specific surface area and pore volume of O,N-doped OBC-1.5 were 88.5 m2 g−1 and 0.07 cm3 g−1, respectively, which were greater than those of BC. The improved surface functionality and porosity resulted in an increased heavy metal removal efficiency. As a result, the maximum adsorption capacity of Cu(II) by O,N-doped OBC was 23.32 mg L−1, which was twofold higher than that of pristine BC. Additionally, for a multiple ion solution, O,N-doped OBC-1.5 showed a greater adsorption behavior toward Cu(II) than Zn(II) and Ni(II). In a batch experiment, the concentration of Cu(II) decreased 92.3% after 90 min. In a filtration experiment, the O,N-doped OBC-based filter achieved a Cu(II) removal capacity of 12.90 mg g−1 and breakthrough time after 250 min. Importantly, the chemical mechanism was mainly governed by monolayer adsorption of Cu(II) onto a homogeneous surface of O,N-doped OBC-1.5. Surface complexation and electrostatic attraction were considered to be the chemical mechanisms governing the adsorption process. [Display omitted] •O, N-doped OBC was fabricated by a simple air oxidation process.•Air can provide natural and green O and N sources for the doping process.•Air oxidation also improved the porous structure of O, N-doped OBC.•O, N doping played an important role in improved heavy metal removal efficiency.</abstract><cop>England</cop><pub>Elsevier Ltd</pub><pmid>35033519</pmid><doi>10.1016/j.chemosphere.2022.133622</doi><tpages>1</tpages><orcidid>https://orcid.org/0000-0002-9084-8595</orcidid></addata></record>
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subjects Adsorption
Adsorption mechanism
air
Air oxidation
biochar
Charcoal - chemistry
electrostatic interactions
filtration
Green method
Heavy metal removal
heavy metals
Metals, Heavy
oxidation
Oxygen and nitrogen doping
Porosity
Porous biochar
quality control
surface area
Water Pollutants, Chemical - analysis
title O, N-doped porous biochar by air oxidation for enhancing heavy metal removal: The role of O, N functional groups
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