Please use this identifier to cite or link to this item: http://hdl.handle.net/10603/399053
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dc.coverage.spatial
dc.date.accessioned2022-08-17T07:21:12Z-
dc.date.available2022-08-17T07:21:12Z-
dc.identifier.urihttp://hdl.handle.net/10603/399053-
dc.description.abstractnewline Polycyclic Aromatic Hydrocarbons (PAHs) and Nitro-PAHs are ubiquitous organic pollutants. Their elevated concentration in the ambient air is a serious matter of concern as these carcinogenic, mutagenic and teratogenic for humans. Despite their environmental importance, very fewer studies have been conducted on PAHs over Indian cities, and this is the first study on the gas-particle partition of PAHs and Nitro-PAHs over the Indo-Gangetic Plain. Aerosol sample in the dual-phase (gas and particle) are collected simultaneously for the first time in Agra at a rural and traffic dominated site from October-2015 to November-2017. High Volume Sampler was used to collect gas and particulate phase samples on quartz microfiber filter papers (QFFs) and Poly Urethane Foam (PUF) plugs, respectively. Samples were extracted in a mixture of DCM and n-hexane. 16 priority PAHs and 2 Nitro-PAHs were analyzed using Gas Chromatograph-Mass Spectrometry (GC-MS). The total concentration of PAHs (gas + particulate) was 2481 and 1011 ng m-3 at traffic and rural site, respectively whereas total concertation of Nitro-PAHs was 90 and 28 ng m-3 at traffic and rural site, respectively. A higher concentration of PAHs and Nitro-PAHs was observed during winter at both the traffic and rural sites. Gas-particle partitioning of PAHs in the ambient air of Agra is governed by the dual model and shows that the PAHs concentration is influenced by the OC and EC concentration in the atmosphere. Pankow model shows that PAHs are emitted from the samples close to the sampling location and do not get enough time to get partition in between both the phases. A statistically significant correlation (plt0.0001) for Clausius Clapeyron plots was obtained which indicates the temperature dependency of gas-phase PAHs at both sites. Source analysis of PAHs and Nitro-PAHs shows that the PAHs concentration at traffic site is mainly due to traffic and combustions source whereas at rural site PAHs concentration is mainly due to biomass combustion and pyrogenic sources. ILCR values of PAHs and Nitro-PAHs shows that humans are prone to cancer risk from dermal exposure pathway, followed by ingestion and inhalation. Adults are more prone to cancer risk followed by children and infants. newlineKeywords: Polycyclic Aromatic Hydrocarbons (PAHs), Nitro-PAHs, Gas-particle partitioning, newlineSource apportionment, ILCR. newline
dc.format.extent
dc.languageEnglish
dc.relation
dc.rightsuniversity
dc.titleAtmospheric Concentrations of Polycyclic Aromatic Hydrocarbons and Nitro PAHs
dc.title.alternativeGas particle partitioning and possible sources at rural and traffic site of Agra
dc.creator.researcherVerma, Puneet Kumar
dc.subject.keywordChemistry
dc.subject.keywordPhysical Sciences
dc.subject.keywordPolymer Science
dc.description.note
dc.contributor.guideLakhani, Anita
dc.publisher.placeAgra
dc.publisher.universityDayalbagh Educational Institute
dc.publisher.institutionDepartment of Chemistry
dc.date.registered2015
dc.date.completed2021
dc.date.awarded2022
dc.format.dimensions
dc.format.accompanyingmaterialNone
dc.source.universityUniversity
dc.type.degreePh.D.
Appears in Departments:Department of Chemistry

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01_title.pdfAttached File6.94 kBAdobe PDFView/Open
02_certificate.pdf243.18 kBAdobe PDFView/Open
03_declaration.pdf237.74 kBAdobe PDFView/Open
04_abstract.pdf283.04 kBAdobe PDFView/Open
05_acknowledgement.pdf112.23 kBAdobe PDFView/Open
06_contents.pdf225.28 kBAdobe PDFView/Open
07_list_of_tables.pdf23.99 kBAdobe PDFView/Open
09_abbreviations.pdf192.84 kBAdobe PDFView/Open
10_chapter1.pdf1.54 MBAdobe PDFView/Open
11_chapter2.pdf540.69 kBAdobe PDFView/Open
12_chapter3.pdf1.19 MBAdobe PDFView/Open
14_chapter5.pdf1.42 MBAdobe PDFView/Open
15_chapter6.pdf2.08 MBAdobe PDFView/Open
16_chapter7.pdf1.75 MBAdobe PDFView/Open
17_chapter8.pdf1.33 MBAdobe PDFView/Open
18_conclusion.pdf317.17 kBAdobe PDFView/Open
19_references.pdf496.3 kBAdobe PDFView/Open
20_appendix.pdf317.96 kBAdobe PDFView/Open
21_summary.pdf622.38 kBAdobe PDFView/Open
80_recommendation.pdf308.97 kBAdobe PDFView/Open


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