Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar
Autor(a) principal: | |
---|---|
Data de Publicação: | 2021 |
Tipo de documento: | Trabalho de conclusão de curso |
Idioma: | por |
Título da fonte: | Repositório Institucional da UNESP |
Texto Completo: | http://hdl.handle.net/11449/214095 |
Resumo: | H2S is a toxic, corrosive gas and an unpleasant odor. According to Security US Occupational and Healthy Administration (OSHA), the exposure limit allowable (for 8 hours) is 10 ppm. Concentrations of 20 ppm are the limit for basic health problems. In work environments, human exposure to H2S can occur during oil extraction and by workers inside underground galleries of cities. The prior determination of H2S is important from the point of view of hygiene occupational. An interesting procedure, to do this simply, using portable, low-cost and easy-to-handle equipment is the use of passive samplers and assets. First, a passive sampler was mounted with the collecting surface (filter of cellulose) impregnated with basic suspension of zinc hydroxide. H2S is collected in the form of zinc sulfide on the cellulose filter. The filter surface is further treated with acidic solution of N,N-dimethyl-p-phenyldiamine (N-N) and ferric chloride. The product of this reaction is a blue colored compound and is known by the trade name of methylene blue. The intensity of color formed is proportional to the average concentration of analyte (H2S) present during the sampling period. The determination of H2S can be done directly by visual comparison or even by digitizing the image obtained. In this case you can use a simple camera built in mobile phone and use of Digital Image-Based software (DIB). As an advantage of the method, it does not require the energy source and the chemical reaction carried out in the filter Sampled can be done at the sampling site. The concentration of H2S can be known immediately, in situ, at the end of the sampling period. Subsequently, the construction of an active-sampler for the determination of H2S was carried out with direct reading of the analytical signal on a reagent-impregnated cellulose filter fluorescent and through the contact between the gas and the compound the fluorescence of the internal filter and thus it is possible to quantify the amount of hydrogen sulphide in the environment. Both techniques are transparent but the collecting surface is impregnated with the reagent it must be highly homogeneous and difficulties are encountered to obtain such in a period small sampling time. |
id |
UNSP_2b6a6b82f38d3b132fc4528bfc040dd8 |
---|---|
oai_identifier_str |
oai:repositorio.unesp.br:11449/214095 |
network_acronym_str |
UNSP |
network_name_str |
Repositório Institucional da UNESP |
repository_id_str |
2946 |
spelling |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em arDevelopment of reaction and calibration of passive and asset sample for identification of H2S in airIndoorH2SAmostrador passivoAmostrador ativoH2S is a toxic, corrosive gas and an unpleasant odor. According to Security US Occupational and Healthy Administration (OSHA), the exposure limit allowable (for 8 hours) is 10 ppm. Concentrations of 20 ppm are the limit for basic health problems. In work environments, human exposure to H2S can occur during oil extraction and by workers inside underground galleries of cities. The prior determination of H2S is important from the point of view of hygiene occupational. An interesting procedure, to do this simply, using portable, low-cost and easy-to-handle equipment is the use of passive samplers and assets. First, a passive sampler was mounted with the collecting surface (filter of cellulose) impregnated with basic suspension of zinc hydroxide. H2S is collected in the form of zinc sulfide on the cellulose filter. The filter surface is further treated with acidic solution of N,N-dimethyl-p-phenyldiamine (N-N) and ferric chloride. The product of this reaction is a blue colored compound and is known by the trade name of methylene blue. The intensity of color formed is proportional to the average concentration of analyte (H2S) present during the sampling period. The determination of H2S can be done directly by visual comparison or even by digitizing the image obtained. In this case you can use a simple camera built in mobile phone and use of Digital Image-Based software (DIB). As an advantage of the method, it does not require the energy source and the chemical reaction carried out in the filter Sampled can be done at the sampling site. The concentration of H2S can be known immediately, in situ, at the end of the sampling period. Subsequently, the construction of an active-sampler for the determination of H2S was carried out with direct reading of the analytical signal on a reagent-impregnated cellulose filter fluorescent and through the contact between the gas and the compound the fluorescence of the internal filter and thus it is possible to quantify the amount of hydrogen sulphide in the environment. Both techniques are transparent but the collecting surface is impregnated with the reagent it must be highly homogeneous and difficulties are encountered to obtain such in a period small sampling time.O H2S é um gás, tóxico e corrosivo e odor desagradável. De acordo com a Segurança Ocupacional e Administração Saudável dos EUA (do inglês OSHA), o limite de exposição permissível (durante 8 horas) é de 10 ppm. Concentrações de 20 ppm são o limite para problemas críticos de saúde. Em ambientes de trabalho a exposição humana ao H2S, pode ocorrer durante a extração de petróleo e por trabalhadores no interior de galerias subterrâneas de cidades. A determinação previa de H2S é importante sob o ponto de vista da higiene ocupacional. Um procedimento interessante, para fazer isso de maneira simples, utilizando equipamento portátil, de baixo custo e de fácil manuseio é a utilização de amostradores passivos e ativos. Primeiramente foi montado um amostrador passivo com a a superfície coletora (filtro de celulose) impregnada com suspensão básica de hidróxido de zinco. O H2S é coletado na forma de sulfeto de zinco sobre o filtro de celulose. A superficie do filtro é tratada posteriormente com solução ácida de N,N-dimetil-p-fenildiamina (N,N) e cloreto férrico. O produto dessa reação é um composto de cor azul e é conhecido com nome comercial de azul de metileno. A intensidade de cor formada é proporcional à concentração média do analito (H2S) presente durante o período de amostragem. A determinação do H2S pode ser feita diretamente por comparação visual ou mesmo por digitalização da imagem obtida. Neste caso pode-se usar uma câmara fotográfica simples embutida em celular e utilização de software Digital Image-Based (DIB). Como vantagem o método não requer fonte de energia e a reação química feita no filtro amostrado pode ser feita no local da amostragem. A concentração de H2S pode ser conhecida imediatamente, in situ, no final do período de amostragem. Posteriormente foi realizada a construção de um amostrador-ativo para determinação de H2S com leitura direta do sinal analítico sobre um filtro de celulose impregnado com reagente fluorescente e através do contato entre o gás e o composto a fluorescência do filtro diminui e assim é possível quantificar a quantidade de ácido sulfídrico no ambiente. Ambas as técnicas se mostram eficazes porém a superfície coletora impregnada com o reagente deve ser altamente homogênea e dificuldades são encontradas para se obter tal em um período de amostragem pequeno.Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)109167/2017-1Universidade Estadual Paulista (Unesp)Cardoso, Arnaldo Alves [UNESP]Universidade Estadual Paulista (Unesp)Catai, Marcus Augusto dos Santos2021-08-19T17:32:16Z2021-08-19T17:32:16Z2021-03-03info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/bachelorThesisapplication/pdfhttp://hdl.handle.net/11449/214095porinfo:eu-repo/semantics/openAccessreponame:Repositório Institucional da UNESPinstname:Universidade Estadual Paulista (UNESP)instacron:UNESP2023-10-07T06:02:07Zoai:repositorio.unesp.br:11449/214095Repositório InstitucionalPUBhttp://repositorio.unesp.br/oai/requestopendoar:29462024-08-05T14:12:09.427550Repositório Institucional da UNESP - Universidade Estadual Paulista (UNESP)false |
dc.title.none.fl_str_mv |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar Development of reaction and calibration of passive and asset sample for identification of H2S in air |
title |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
spellingShingle |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar Catai, Marcus Augusto dos Santos Indoor H2S Amostrador passivo Amostrador ativo |
title_short |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
title_full |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
title_fullStr |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
title_full_unstemmed |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
title_sort |
Desenvolvimento de reação e calibração de amostradores passivos e ativos para identificação de H2S em ar |
author |
Catai, Marcus Augusto dos Santos |
author_facet |
Catai, Marcus Augusto dos Santos |
author_role |
author |
dc.contributor.none.fl_str_mv |
Cardoso, Arnaldo Alves [UNESP] Universidade Estadual Paulista (Unesp) |
dc.contributor.author.fl_str_mv |
Catai, Marcus Augusto dos Santos |
dc.subject.por.fl_str_mv |
Indoor H2S Amostrador passivo Amostrador ativo |
topic |
Indoor H2S Amostrador passivo Amostrador ativo |
description |
H2S is a toxic, corrosive gas and an unpleasant odor. According to Security US Occupational and Healthy Administration (OSHA), the exposure limit allowable (for 8 hours) is 10 ppm. Concentrations of 20 ppm are the limit for basic health problems. In work environments, human exposure to H2S can occur during oil extraction and by workers inside underground galleries of cities. The prior determination of H2S is important from the point of view of hygiene occupational. An interesting procedure, to do this simply, using portable, low-cost and easy-to-handle equipment is the use of passive samplers and assets. First, a passive sampler was mounted with the collecting surface (filter of cellulose) impregnated with basic suspension of zinc hydroxide. H2S is collected in the form of zinc sulfide on the cellulose filter. The filter surface is further treated with acidic solution of N,N-dimethyl-p-phenyldiamine (N-N) and ferric chloride. The product of this reaction is a blue colored compound and is known by the trade name of methylene blue. The intensity of color formed is proportional to the average concentration of analyte (H2S) present during the sampling period. The determination of H2S can be done directly by visual comparison or even by digitizing the image obtained. In this case you can use a simple camera built in mobile phone and use of Digital Image-Based software (DIB). As an advantage of the method, it does not require the energy source and the chemical reaction carried out in the filter Sampled can be done at the sampling site. The concentration of H2S can be known immediately, in situ, at the end of the sampling period. Subsequently, the construction of an active-sampler for the determination of H2S was carried out with direct reading of the analytical signal on a reagent-impregnated cellulose filter fluorescent and through the contact between the gas and the compound the fluorescence of the internal filter and thus it is possible to quantify the amount of hydrogen sulphide in the environment. Both techniques are transparent but the collecting surface is impregnated with the reagent it must be highly homogeneous and difficulties are encountered to obtain such in a period small sampling time. |
publishDate |
2021 |
dc.date.none.fl_str_mv |
2021-08-19T17:32:16Z 2021-08-19T17:32:16Z 2021-03-03 |
dc.type.status.fl_str_mv |
info:eu-repo/semantics/publishedVersion |
dc.type.driver.fl_str_mv |
info:eu-repo/semantics/bachelorThesis |
format |
bachelorThesis |
status_str |
publishedVersion |
dc.identifier.uri.fl_str_mv |
http://hdl.handle.net/11449/214095 |
url |
http://hdl.handle.net/11449/214095 |
dc.language.iso.fl_str_mv |
por |
language |
por |
dc.rights.driver.fl_str_mv |
info:eu-repo/semantics/openAccess |
eu_rights_str_mv |
openAccess |
dc.format.none.fl_str_mv |
application/pdf |
dc.publisher.none.fl_str_mv |
Universidade Estadual Paulista (Unesp) |
publisher.none.fl_str_mv |
Universidade Estadual Paulista (Unesp) |
dc.source.none.fl_str_mv |
reponame:Repositório Institucional da UNESP instname:Universidade Estadual Paulista (UNESP) instacron:UNESP |
instname_str |
Universidade Estadual Paulista (UNESP) |
instacron_str |
UNESP |
institution |
UNESP |
reponame_str |
Repositório Institucional da UNESP |
collection |
Repositório Institucional da UNESP |
repository.name.fl_str_mv |
Repositório Institucional da UNESP - Universidade Estadual Paulista (UNESP) |
repository.mail.fl_str_mv |
|
_version_ |
1808128331138203648 |