dc.creator | Lins, Josiane Maria de Santana Melo | |
dc.date.accessioned | 2018-02-15T18:24:07Z | |
dc.date.accessioned | 2023-03-22T17:30:07Z | |
dc.date.available | 2023-03-22T17:30:07Z | |
dc.date.issued | 2017-03-23 | |
dc.identifier.citation | LINS, Josiane Maria de Santana Melo. Otimização do tratamento de águas oleosas com alto grau de emulsificação utilizando biossurfactante e flotação por ar dissolvido (fad). 2017, 77 f. Dissertação (Mestrado) - Universidade Católica de Pernambuco. Pró-Reitoria Acadêmica. Coordenação Geral de Pós-Graduação. Mestrado em Desenvolvimento de Processos Ambientais, 2017. | por |
dc.identifier.uri | https://hdl.handle.net/20.500.12032/76487 | |
dc.description.abstract | Residual Frying Oil (RFO) is part of one of the waste generated daily in households,
industries and voluntary delivery points (public and mixed-economy companies). The
uncontrolled disposal of residues of frying oils, in sinks or dumped directly into
bodies of water, entails a series of environmental damages, such as obstruction of
pipes in sewage systems and increased costs of treatment processes, in addition to
Increased pollution. The collection and reuse of these waste oils prevents them from
being disposed of inappropriately and benefits the environment. The percentage
recovery of residual oil from fried foods depends to a large extent on the washing
operations. These operations are also responsible for the effective separation of the
organic and aqueous phases from the emulsions generated so as to obtain a lower
possible oil content in the aqueous phase, while the oil can still be used for reuse in
the soap and detergent production processes. In this work, actions were taken to
improve the operational conditions to improve the process of chemical washing of
the ORF by cleaning products industries, in order to generate an adequate effluent
for subsequent physical-chemical treatment by Dissolved Air Flotation (DAF). After
conditioning, the OFR collection vessel was rinsed with steam and received addition
of chemical reagents (HCLO3, NaOH and NaCl). The material was then treated
through DAF, with a biosurfactant acting as a biodegradable manifold, in a
laboratory scale prototype operating in continuous mode. The experiments were
performed according to a Central Composite Designs (CCD) of type 22. As factors,
the ratio between the effluent flow to be treated and the biosurfactant flow rate (X1)
was used, and the ratio of the air flow to the effluent flow recirculated to produce the
microbubbles (X2). As a response variable the water-oil separation efficiency was
used. A maximum separation efficiency of 98.0% for X1 and X2 values equal to
1.0.103 and 1.05.104, respectively. | eng |
dc.format | application/pdf | * |
dc.language | por | por |
dc.publisher | Universidade Católica de Pernambuco | por |
dc.rights | Acesso Aberto | por |
dc.subject | Biosurfactants | eng |
dc.subject | Water - Purification - Biological treatment | eng |
dc.subject | Wastewater - Purification | eng |
dc.subject | Flotation | eng |
dc.subject | Dissertations | eng |
dc.subject | Biossurfactantes | por |
dc.subject | Água - Purificação - Tratamento biológico | por |
dc.subject | Águas residuais - Purificação | por |
dc.subject | Flotação | por |
dc.subject | Dissertações | por |
dc.title | Otimização do tratamento de águas oleosas com alto grau de emulsificação utilizando biossurfactante e flotação por ar dissolvido (fad). | por |
dc.type | Dissertação | por |