Occurrence of plant and fecal steroid and their evolution during co-composting of sewage sludge and lignocellulosic waste
•Changes in steroid components during co-composting of sewage sludge/lignocellulosic waste.•Py-GC/MS as a performant tool for rapid monitoring of steroids for co-compost maturity.•Occurrence of sulfurization process during composting leading to definite S-steroids. Steroid composition change during...
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creator | El Fels, Loubna El Ouaqoudi, Fatima-Zahra Lemee, Laurent Geffroy, Claude Ambles, André Hafidi, Mohamed |
description | •Changes in steroid components during co-composting of sewage sludge/lignocellulosic waste.•Py-GC/MS as a performant tool for rapid monitoring of steroids for co-compost maturity.•Occurrence of sulfurization process during composting leading to definite S-steroids.
Steroid composition change during six months of co-composting of sewage sludge and palm waste was studied using Py-GC/MS. The main steroids identified were C27–C29 sterenes and stanols, 5β-cholesta-3-one, cholesta-3,5-diene and 2 thiosteranes. Except for thiosteranes and some of the C27–C29 cholestenes, the relative concentrations decreased during co-composting due to microbial degradation. Plant 5α-cholestanol, 24-methyl- and ethyl-5α-cholestanols were accompanied by fecal 5β-cholestanol and 5β-cholestanone. Some of the sterenes and cholesta-3,5-diene were formed by pyrolysis of bound forms of stanols and cholesterol, respectively. Sulfurization occurred during co-composting and increased with time. The process affects cholestanol and campestanol of plant origin leading as pyrolysis products to thiocholestane and thiocampestane (with the 5α (H) configuration), respectively, and to the corresponding sterenes. The change in steroids during co-composting is positively correlated with the physico-chemical parameters of mature compost, especially C/N and NH4+ / NO3− ratios. |
doi_str_mv | 10.1016/j.bej.2015.10.025 |
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Steroid composition change during six months of co-composting of sewage sludge and palm waste was studied using Py-GC/MS. The main steroids identified were C27–C29 sterenes and stanols, 5β-cholesta-3-one, cholesta-3,5-diene and 2 thiosteranes. Except for thiosteranes and some of the C27–C29 cholestenes, the relative concentrations decreased during co-composting due to microbial degradation. Plant 5α-cholestanol, 24-methyl- and ethyl-5α-cholestanols were accompanied by fecal 5β-cholestanol and 5β-cholestanone. Some of the sterenes and cholesta-3,5-diene were formed by pyrolysis of bound forms of stanols and cholesterol, respectively. Sulfurization occurred during co-composting and increased with time. The process affects cholestanol and campestanol of plant origin leading as pyrolysis products to thiocholestane and thiocampestane (with the 5α (H) configuration), respectively, and to the corresponding sterenes. The change in steroids during co-composting is positively correlated with the physico-chemical parameters of mature compost, especially C/N and NH4+ / NO3− ratios.</description><identifier>ISSN: 1369-703X</identifier><identifier>EISSN: 1873-295X</identifier><identifier>DOI: 10.1016/j.bej.2015.10.025</identifier><language>eng</language><publisher>Elsevier B.V</publisher><subject>Analytical pyrolysis (Py-GC/MS) ; Biodesulfurization ; Biotransformations ; Earth Sciences ; Fecal and plant steroids ; Geochemistry ; Lignin ; Sciences of the Universe ; Waste treatment</subject><ispartof>Biochemical engineering journal, 2016-01, Vol.105, p.497-504</ispartof><rights>2015</rights><rights>Distributed under a Creative Commons Attribution 4.0 International License</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c368t-2c299245629cac3912b9988785a074512d234c468e0116153bf5e7316e89f3c53</citedby><cites>FETCH-LOGICAL-c368t-2c299245629cac3912b9988785a074512d234c468e0116153bf5e7316e89f3c53</cites><orcidid>0000-0001-9520-3289 ; 0000-0002-2731-9658</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.bej.2015.10.025$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>230,314,780,784,885,3548,27923,27924,45994</link.rule.ids><backlink>$$Uhttps://hal.science/hal-01247794$$DView record in HAL$$Hfree_for_read</backlink></links><search><creatorcontrib>El Fels, Loubna</creatorcontrib><creatorcontrib>El Ouaqoudi, Fatima-Zahra</creatorcontrib><creatorcontrib>Lemee, Laurent</creatorcontrib><creatorcontrib>Geffroy, Claude</creatorcontrib><creatorcontrib>Ambles, André</creatorcontrib><creatorcontrib>Hafidi, Mohamed</creatorcontrib><title>Occurrence of plant and fecal steroid and their evolution during co-composting of sewage sludge and lignocellulosic waste</title><title>Biochemical engineering journal</title><description>•Changes in steroid components during co-composting of sewage sludge/lignocellulosic waste.•Py-GC/MS as a performant tool for rapid monitoring of steroids for co-compost maturity.•Occurrence of sulfurization process during composting leading to definite S-steroids.
Steroid composition change during six months of co-composting of sewage sludge and palm waste was studied using Py-GC/MS. The main steroids identified were C27–C29 sterenes and stanols, 5β-cholesta-3-one, cholesta-3,5-diene and 2 thiosteranes. Except for thiosteranes and some of the C27–C29 cholestenes, the relative concentrations decreased during co-composting due to microbial degradation. Plant 5α-cholestanol, 24-methyl- and ethyl-5α-cholestanols were accompanied by fecal 5β-cholestanol and 5β-cholestanone. Some of the sterenes and cholesta-3,5-diene were formed by pyrolysis of bound forms of stanols and cholesterol, respectively. Sulfurization occurred during co-composting and increased with time. The process affects cholestanol and campestanol of plant origin leading as pyrolysis products to thiocholestane and thiocampestane (with the 5α (H) configuration), respectively, and to the corresponding sterenes. The change in steroids during co-composting is positively correlated with the physico-chemical parameters of mature compost, especially C/N and NH4+ / NO3− ratios.</description><subject>Analytical pyrolysis (Py-GC/MS)</subject><subject>Biodesulfurization</subject><subject>Biotransformations</subject><subject>Earth Sciences</subject><subject>Fecal and plant steroids</subject><subject>Geochemistry</subject><subject>Lignin</subject><subject>Sciences of the Universe</subject><subject>Waste treatment</subject><issn>1369-703X</issn><issn>1873-295X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><recordid>eNp9kMtKxDAUhosoeH0Ad9m66JhL0zS4EvEGA7NRcBcyp6czGTLNkLQjvr2pIy5dnZyf8_2QryiuGZ0xyurbzWyJmxmnTOZ9Rrk8Ks5Yo0TJtfw4zm9R61JR8XFanKe0oZTWQqmz4msBMMaIPSAJHdl52w_E9i3pEKwnacAYXPuTDGt0keA--HFwoSftGF2_IhBKCNtdSMO05Y6En3aFJPmxzWMivVv1AdD70YfkgHza3HtZnHTWJ7z6nRfF-9Pj28NLOV88vz7cz0sQdTOUHLjWvJI112BBaMaXWjeNaqSlqpKMt1xUUNUNUsZqJsWyk6gEq7HRnQApLoqbQ-_aerOLbmvjlwnWmZf7uZkyynillK72LN-ywy3EkFLE7g9g1EyezcZkz2byPEXZc2buDgzmT-wdRpPATT5bFxEG0wb3D_0NYJaGFw</recordid><startdate>20160115</startdate><enddate>20160115</enddate><creator>El Fels, Loubna</creator><creator>El Ouaqoudi, Fatima-Zahra</creator><creator>Lemee, Laurent</creator><creator>Geffroy, Claude</creator><creator>Ambles, André</creator><creator>Hafidi, Mohamed</creator><general>Elsevier B.V</general><general>Elsevier</general><scope>AAYXX</scope><scope>CITATION</scope><scope>1XC</scope><orcidid>https://orcid.org/0000-0001-9520-3289</orcidid><orcidid>https://orcid.org/0000-0002-2731-9658</orcidid></search><sort><creationdate>20160115</creationdate><title>Occurrence of plant and fecal steroid and their evolution during co-composting of sewage sludge and lignocellulosic waste</title><author>El Fels, Loubna ; El Ouaqoudi, Fatima-Zahra ; Lemee, Laurent ; Geffroy, Claude ; Ambles, André ; Hafidi, Mohamed</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c368t-2c299245629cac3912b9988785a074512d234c468e0116153bf5e7316e89f3c53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2016</creationdate><topic>Analytical pyrolysis (Py-GC/MS)</topic><topic>Biodesulfurization</topic><topic>Biotransformations</topic><topic>Earth Sciences</topic><topic>Fecal and plant steroids</topic><topic>Geochemistry</topic><topic>Lignin</topic><topic>Sciences of the Universe</topic><topic>Waste treatment</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>El Fels, Loubna</creatorcontrib><creatorcontrib>El Ouaqoudi, Fatima-Zahra</creatorcontrib><creatorcontrib>Lemee, Laurent</creatorcontrib><creatorcontrib>Geffroy, Claude</creatorcontrib><creatorcontrib>Ambles, André</creatorcontrib><creatorcontrib>Hafidi, Mohamed</creatorcontrib><collection>CrossRef</collection><collection>Hyper Article en Ligne (HAL)</collection><jtitle>Biochemical engineering journal</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>El Fels, Loubna</au><au>El Ouaqoudi, Fatima-Zahra</au><au>Lemee, Laurent</au><au>Geffroy, Claude</au><au>Ambles, André</au><au>Hafidi, Mohamed</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Occurrence of plant and fecal steroid and their evolution during co-composting of sewage sludge and lignocellulosic waste</atitle><jtitle>Biochemical engineering journal</jtitle><date>2016-01-15</date><risdate>2016</risdate><volume>105</volume><spage>497</spage><epage>504</epage><pages>497-504</pages><issn>1369-703X</issn><eissn>1873-295X</eissn><abstract>•Changes in steroid components during co-composting of sewage sludge/lignocellulosic waste.•Py-GC/MS as a performant tool for rapid monitoring of steroids for co-compost maturity.•Occurrence of sulfurization process during composting leading to definite S-steroids.
Steroid composition change during six months of co-composting of sewage sludge and palm waste was studied using Py-GC/MS. The main steroids identified were C27–C29 sterenes and stanols, 5β-cholesta-3-one, cholesta-3,5-diene and 2 thiosteranes. Except for thiosteranes and some of the C27–C29 cholestenes, the relative concentrations decreased during co-composting due to microbial degradation. Plant 5α-cholestanol, 24-methyl- and ethyl-5α-cholestanols were accompanied by fecal 5β-cholestanol and 5β-cholestanone. Some of the sterenes and cholesta-3,5-diene were formed by pyrolysis of bound forms of stanols and cholesterol, respectively. Sulfurization occurred during co-composting and increased with time. The process affects cholestanol and campestanol of plant origin leading as pyrolysis products to thiocholestane and thiocampestane (with the 5α (H) configuration), respectively, and to the corresponding sterenes. The change in steroids during co-composting is positively correlated with the physico-chemical parameters of mature compost, especially C/N and NH4+ / NO3− ratios.</abstract><pub>Elsevier B.V</pub><doi>10.1016/j.bej.2015.10.025</doi><tpages>8</tpages><orcidid>https://orcid.org/0000-0001-9520-3289</orcidid><orcidid>https://orcid.org/0000-0002-2731-9658</orcidid></addata></record> |
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subjects | Analytical pyrolysis (Py-GC/MS) Biodesulfurization Biotransformations Earth Sciences Fecal and plant steroids Geochemistry Lignin Sciences of the Universe Waste treatment |
title | Occurrence of plant and fecal steroid and their evolution during co-composting of sewage sludge and lignocellulosic waste |
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