Fly ash and zero-valent iron-based in situ advanced anaerobic digestion with emphasis on the removal of antibiotics and antibiotic resistance genes from sewage sludge
This study investigated the removal of antibiotics and antibiotic resistance genes from sewage sludge by using fly ash (FA)-based in situ advanced anaerobic digestion (AAD) under mesophilic conditions. Five antibiotics (sulfadiazine, sulfamethoxazole, ofloxacin, tetracycline, and roxithromycin) and...
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| Veröffentlicht in: | Waste disposal & sustainable energy 2022-03, Vol.4 (1), p.17-28 |
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| creator | Zhang, Minquan Wangjin, Yadan Zhou, Haidong Zhao, Ziming Cao, Zhengcao Ying, Zhenxi |
| description | This study investigated the removal of antibiotics and antibiotic resistance genes from sewage sludge by using fly ash (FA)-based in situ advanced anaerobic digestion (AAD) under mesophilic conditions. Five antibiotics (sulfadiazine, sulfamethoxazole, ofloxacin, tetracycline, and roxithromycin) and 11 corresponding antibiotic resistance genes (Ib-cr,
qnr
S,
erm
F,
erm
T,
erm
X,
sul
1,
sul
2,
sul
3,
tet
A,
tet
B, and
tet
G) were selected as the targets. Adding FA to anaerobic digestion to remove antibiotics and resistance genes allows waste to be treated with waste. FA-based in situ AAD of sewage sludge effectively enhanced the process stability and methane yield, and the optimal FA-added dosage was 50 mg/L. The cumulative methane yield could be well described with the improved Gompertz model. FA addition effectively increased the overall removal of ofloxacin, by up to 85.3% at 50 mg/L FA and 10 μg/L antibiotics, and the combination of zero-valent iron and FA enhanced only the overall removal of ofloxacin to 92.4% and tetracycline to 85.6%. However, FA-based in situ AAD could not enhance the overall removal of other antibiotics from sewage sludge. Not all the same types of antibiotic resistance genes were strongly positively correlated with the concentrations of antibiotics. The removal of antibiotic resistance genes influenced by FA addition varied largely with the types of antibiotic resistance genes, FA dosage, antibiotic content, and the combination with zero-valent iron. FA addition could not be verified to enhance the removal of antibiotic resistance genes. The addition of FA or zero-valent iron and the antibiotic concentrations significantly changed the microbial community structure during in situ AAD, and the combination of zero-valent iron and FA significantly reduces the species diversity and microbial abundance. The most abundant bacteria were
Methanogarcina
,
Methanoberium
,
unidentified_Archaea
,
Terrimonas
,
Methomethoxychlorovorans
, and
Candidatus_Cloacimonas
in the ZVI-FA test. |
| doi_str_mv | 10.1007/s42768-021-00089-6 |
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qnr
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F,
erm
T,
erm
X,
sul
1,
sul
2,
sul
3,
tet
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tet
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tet
G) were selected as the targets. Adding FA to anaerobic digestion to remove antibiotics and resistance genes allows waste to be treated with waste. FA-based in situ AAD of sewage sludge effectively enhanced the process stability and methane yield, and the optimal FA-added dosage was 50 mg/L. The cumulative methane yield could be well described with the improved Gompertz model. FA addition effectively increased the overall removal of ofloxacin, by up to 85.3% at 50 mg/L FA and 10 μg/L antibiotics, and the combination of zero-valent iron and FA enhanced only the overall removal of ofloxacin to 92.4% and tetracycline to 85.6%. However, FA-based in situ AAD could not enhance the overall removal of other antibiotics from sewage sludge. Not all the same types of antibiotic resistance genes were strongly positively correlated with the concentrations of antibiotics. The removal of antibiotic resistance genes influenced by FA addition varied largely with the types of antibiotic resistance genes, FA dosage, antibiotic content, and the combination with zero-valent iron. FA addition could not be verified to enhance the removal of antibiotic resistance genes. The addition of FA or zero-valent iron and the antibiotic concentrations significantly changed the microbial community structure during in situ AAD, and the combination of zero-valent iron and FA significantly reduces the species diversity and microbial abundance. The most abundant bacteria were
Methanogarcina
,
Methanoberium
,
unidentified_Archaea
,
Terrimonas
,
Methomethoxychlorovorans
, and
Candidatus_Cloacimonas
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qnr
S,
erm
F,
erm
T,
erm
X,
sul
1,
sul
2,
sul
3,
tet
A,
tet
B, and
tet
G) were selected as the targets. Adding FA to anaerobic digestion to remove antibiotics and resistance genes allows waste to be treated with waste. FA-based in situ AAD of sewage sludge effectively enhanced the process stability and methane yield, and the optimal FA-added dosage was 50 mg/L. The cumulative methane yield could be well described with the improved Gompertz model. FA addition effectively increased the overall removal of ofloxacin, by up to 85.3% at 50 mg/L FA and 10 μg/L antibiotics, and the combination of zero-valent iron and FA enhanced only the overall removal of ofloxacin to 92.4% and tetracycline to 85.6%. However, FA-based in situ AAD could not enhance the overall removal of other antibiotics from sewage sludge. Not all the same types of antibiotic resistance genes were strongly positively correlated with the concentrations of antibiotics. The removal of antibiotic resistance genes influenced by FA addition varied largely with the types of antibiotic resistance genes, FA dosage, antibiotic content, and the combination with zero-valent iron. FA addition could not be verified to enhance the removal of antibiotic resistance genes. The addition of FA or zero-valent iron and the antibiotic concentrations significantly changed the microbial community structure during in situ AAD, and the combination of zero-valent iron and FA significantly reduces the species diversity and microbial abundance. The most abundant bacteria were
Methanogarcina
,
Methanoberium
,
unidentified_Archaea
,
Terrimonas
,
Methomethoxychlorovorans
, and
Candidatus_Cloacimonas
in the ZVI-FA test.</description><subject>Anaerobic conditions</subject><subject>Anaerobic digestion</subject><subject>Antibiotic resistance</subject><subject>Antibiotics</subject><subject>Bacteria</subject><subject>Biogas</subject><subject>Chemical oxygen demand</subject><subject>Community structure</subject><subject>Dosage</subject><subject>Drug resistance</subject><subject>Earth and Environmental Science</subject><subject>Engineering Thermodynamics</subject><subject>Environment</subject><subject>Fly ash</subject><subject>Genes</subject><subject>Heat and Mass Transfer</subject><subject>Iron</subject><subject>Methane</subject><subject>Microorganisms</subject><subject>Ofloxacin</subject><subject>Particle size</subject><subject>Power plants</subject><subject>Renewable and Green Energy</subject><subject>Roxithromycin</subject><subject>Sewage sludge</subject><subject>Sludge</subject><subject>Species diversity</subject><subject>Sulfadiazine</subject><subject>Sulfamethoxazole</subject><subject>Waste Management/Waste Technology</subject><issn>2524-7980</issn><issn>2524-7891</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2022</creationdate><recordtype>article</recordtype><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNp9kctKJDEUhgtxQFFfYFaBWUdzqVxqKaKjIMzGWYfcqjpDd9KTk1b0gXxOoz3iblZJDt_3H8I_DN8pOaeEqAsYmZIaE0YxIURPWB4Mx0ywESs90cPP-6TJ0XAGkBwZpZBUUHk8vN6sn5GFFbI5oJdYC36065gbSrVk7CzEgFJGkNoO2fBos-8Dm20nXfIopCVCSyWjp9RWKG62KwsJUB-0VUQ1bkrPQ2XuTksulZY8fOz6eneqK-09Gi0xR0BzLRsE8ckuEcF6F5Z4Onyb7Rri2b_zZPh9c_1wdYvvf_28u7q8x57TqWHHnFbSUc-15qMnVAc7T17YYJXSKijuhGUjZ5QRPvPZSTkF5bxjQnGhKT8Zfuxzt7X83fWvmT9lV3NfadjEmRB8kmOn2J7ytQDUOJttTRtbnw0l5r0Ss6_E9ErMRyVGdonvJehwXmL9iv6P9QaJSZHa</recordid><startdate>20220301</startdate><enddate>20220301</enddate><creator>Zhang, Minquan</creator><creator>Wangjin, Yadan</creator><creator>Zhou, Haidong</creator><creator>Zhao, Ziming</creator><creator>Cao, Zhengcao</creator><creator>Ying, Zhenxi</creator><general>Springer Singapore</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7X2</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>8FK</scope><scope>ABJCF</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ARAPS</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>L6V</scope><scope>M0K</scope><scope>M7S</scope><scope>P5Z</scope><scope>P62</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PTHSS</scope><scope>PYCSY</scope><orcidid>https://orcid.org/0000-0003-3821-7427</orcidid></search><sort><creationdate>20220301</creationdate><title>Fly ash and zero-valent iron-based in situ advanced anaerobic digestion with emphasis on the removal of antibiotics and antibiotic resistance genes from sewage sludge</title><author>Zhang, Minquan ; 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Sustain. Energy</stitle><date>2022-03-01</date><risdate>2022</risdate><volume>4</volume><issue>1</issue><spage>17</spage><epage>28</epage><pages>17-28</pages><issn>2524-7980</issn><eissn>2524-7891</eissn><abstract>This study investigated the removal of antibiotics and antibiotic resistance genes from sewage sludge by using fly ash (FA)-based in situ advanced anaerobic digestion (AAD) under mesophilic conditions. Five antibiotics (sulfadiazine, sulfamethoxazole, ofloxacin, tetracycline, and roxithromycin) and 11 corresponding antibiotic resistance genes (Ib-cr,
qnr
S,
erm
F,
erm
T,
erm
X,
sul
1,
sul
2,
sul
3,
tet
A,
tet
B, and
tet
G) were selected as the targets. Adding FA to anaerobic digestion to remove antibiotics and resistance genes allows waste to be treated with waste. FA-based in situ AAD of sewage sludge effectively enhanced the process stability and methane yield, and the optimal FA-added dosage was 50 mg/L. The cumulative methane yield could be well described with the improved Gompertz model. FA addition effectively increased the overall removal of ofloxacin, by up to 85.3% at 50 mg/L FA and 10 μg/L antibiotics, and the combination of zero-valent iron and FA enhanced only the overall removal of ofloxacin to 92.4% and tetracycline to 85.6%. However, FA-based in situ AAD could not enhance the overall removal of other antibiotics from sewage sludge. Not all the same types of antibiotic resistance genes were strongly positively correlated with the concentrations of antibiotics. The removal of antibiotic resistance genes influenced by FA addition varied largely with the types of antibiotic resistance genes, FA dosage, antibiotic content, and the combination with zero-valent iron. FA addition could not be verified to enhance the removal of antibiotic resistance genes. The addition of FA or zero-valent iron and the antibiotic concentrations significantly changed the microbial community structure during in situ AAD, and the combination of zero-valent iron and FA significantly reduces the species diversity and microbial abundance. The most abundant bacteria were
Methanogarcina
,
Methanoberium
,
unidentified_Archaea
,
Terrimonas
,
Methomethoxychlorovorans
, and
Candidatus_Cloacimonas
in the ZVI-FA test.</abstract><cop>Singapore</cop><pub>Springer Singapore</pub><doi>10.1007/s42768-021-00089-6</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0003-3821-7427</orcidid></addata></record> |
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| ispartof | Waste disposal & sustainable energy, 2022-03, Vol.4 (1), p.17-28 |
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| language | eng |
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| subjects | Anaerobic conditions Anaerobic digestion Antibiotic resistance Antibiotics Bacteria Biogas Chemical oxygen demand Community structure Dosage Drug resistance Earth and Environmental Science Engineering Thermodynamics Environment Fly ash Genes Heat and Mass Transfer Iron Methane Microorganisms Ofloxacin Particle size Power plants Renewable and Green Energy Roxithromycin Sewage sludge Sludge Species diversity Sulfadiazine Sulfamethoxazole Waste Management/Waste Technology |
| title | Fly ash and zero-valent iron-based in situ advanced anaerobic digestion with emphasis on the removal of antibiotics and antibiotic resistance genes from sewage sludge |
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