Made available in DSpace on 2014-06-11T19:27:24Z (GMT). No. of bitstreams: 0 Previous issue date: 2008-05-09Bitstream added on 2014-06-13T20:56:25Z : No. of bitstreams: 1 satow_mm_me_rcla.pdf: 904282 bytes, checksum: ae161851e0a9bcacaeb59223c69f2582 (MD5) / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) / Fungos do grupo das leveduras negras têm revelado grande potencial em degradar compostos aromáticos como únicas fontes de carbono, capacidade de sobreviver sob atmosferas contendo hidrocarbonetos e habitar nichos com baixa concentração de nutrientes. Apesar do potencial de aplicação destes nas áreas ambiental e industrial, sua ecologia é pouco conhecida e seu isolamento na natureza ainda é difícil. A técnica de flotação em óleo (IWATSU et al., 1981) é aplicada com sucesso para recuperação de leveduras negras provenientes da natureza. No entanto, os mecanismos envolvidos neste método são desconhecidos. Assim, neste trabalho, testaram-se três hipóteses de seleção da técnica: hidrofobicidade celular, assimilação de hidrocarbonetos e oligotrofismo. A metodologia foi aplicada em amostras de solo de “landfarming” da Refinaria do Planalto Paulista (REPLAN). Cepas isoladas e padrão foram submetidas aos testes para verificação das hipóteses formuladas. A hidrofobicidade celular das cepas foi verificada mediante quantificação da concentração celular da suspensão na fase oleosa após agitação com hidrocarboneto. Os testes de assimilação de hidrocarbonetos e oligotrofismo foram realizados mediante análises de curvas de crescimento obtidas por leituras de absorbância. Os resultados obtidos mostraram que o solo de “landfarming” é um local propício para o estudo de leveduras negras, uma vez que 107 cepas foram recuperadas e a análise molecular revelou uma espécie nova: Cladophialophora immunda. O teste de hidrofobicidade indicou que, a hidrofobicidade celular pode não ser o principal fator seletivo, pois espécies hidrofóbicas e hidrofílicas foram recuperadas pela técnica em estudo. A maioria das cepas de leveduras negras testadas apresentou crescimento em meio contendo hidrocarbonetos como fontes únicas de carbono,... / Black yeast fungi have shown great potential to degrade aromatic hydrocarbons as single carbon source, ability to survive under atmospheres with hydrocarbons and to live in niches poor in nutrient. Despite the application potential of these fungi in the environmental and industrial areas, the knowledge about their ecology is incomplete and their isolation from nature is still difficult. The oil flotation technique (IWATSU et al., 1981) has been succeed on the black yeast strains recovery from nature, however, mechanisms involved in this method are still unknown. The present study tests three hypothesis on its selective mechanisms: cell surface hydrophobicity, hydrocarbon assimilation and oligotrophism. The methodology was applied in landfarming soil samples from Planalto Paulísta Refinery (REPLAN). Six isolates and control strains were submitted to experiments to verify the hypothesis done. Hydrophobicity was studied through quantification of oil-phase cell concentration after shaking the cell suspension with hydrocarbon. Hydrocarbon assimilation and oligotrophism were verified by analyzing the growth curves obtained with absorbance data. The results showed that landfarming soil has great potential for black yeast isolation, as 107 strains were recovered and a new species – Cladophialophora immunda- was revealed by molecular analyzes. Hydrophobicity test showed that cell hydrophobicity could not be the main selective factor, since hydrophobic and hydrophillic strains were recovered. Growth in media with hydrocarbons as sole carbon source was observed in the majority of the tested black yeast strains, indicating that hydrocarbon assimilation or tolerance to these substances could be the selective factors of the method. Exophiala xenobiotica was able to grow in the poor media tested, what suggests that this substrate with the addition of hydrocarbons could be used for the isolation...(Complete abstract, click electronic access below)

Biopile and landfarming systems are ex situ technologies developed for the remediation of contaminated soils. In this study, laboratory degradation experiments and a combined full-scale landfarming and biopile system were operated for the remediation of diesel fuel-contaminated soils. The effectiveness of bulking agents (wood chips and rice hulls), inorganic nutrients (N and P), and biological agent on petroleum hydrocarbon biodegradation were also evaluated. The ratios of contaminated soils to bulking agents applied in the experiments were 1:0, 3:1, 6:1, and 10:1. The soil to bulking agent ratio of 10.7:1 was applied in the full-scale system. After 93 days of incubation, the highest reduction rate for total petroleum hydrocarbon - diesel (TPHd) removal was observed in the experiment with a soil to bulking agent ratio of 3:1. Results show that TPHd degradation trend followed a typical first-order degradation pattern. The calculated regression coefficient ranged from 0.008 ¡V 0.0129. Results also indicate that the addition of biological agent had a significant enhancement of TPHd removal. Results from the full-scale study show that the average TPHd concentrations from 5,544 mg/kg to 488 mg/kg after 231 days of operation. This implies that approximately 91.2% of TPHd removal was obtained. Field results show that temperature affected biodegradation rates, production of CO2, total hererotrophic bacterial biomass, and TPHd reduction efficiencies. Thus, temperature plays an important role for the operation of is biopile and landfarming systems.

Leaking of petroleum products from storage tanks is a commonly found cause of soil contamination. Among those petroleum products, diesel-oil contaminated soils are more difficult to treat compared to gasoline (a more volatile petroleum product). With the growing interest in environmental remediation, various approaches have been proposed for treating petroleum-hydrocarbon (PH) contaminated sites. Given that it is often not possible to remove the released oil or remediate the site completely within a short period of time, using the in situ remedial technology, soil excavation followed by more cost-effective technology should be applied to accelerate the efficiency of site cleanup. In the first-part of this study, laboratory degradation experiments were conducted to determine the optimal operational conditions to effectively and economically bioremediate diesel-fuel contaminated soils. In the second part of this study, a combined full-scale landfarming and biopile system was operated to cleanup diesel fuel-contaminated soils. In the laboratory study, except of frequent soil tilling for air replacement, different additives were added in the laboratory bioreactors to enhance the total petroleum hydrocarbon (TPH) removal efficiency. The additives included nutrients, TPH-degrading bacteria, activated sludge, fern chips, and kitchen waste composts. PH-degrading bacteria were isolated from PH-contaminated soils and activated sludge was collected from a wastewater treatment plant containing PH in the influent. PH-degrading bacteria and sludge were added to increase the microbial population and diversity. Fern chips and kitchen waste composts were added to increase the soil permeability. Results indicate that the bioreactor with kitchen waste compost addition had the highest TPH removal rate. The observed TPH-removal ratios for the compost, activated sludge, PH-degrading bacteria, fern chips, nutrients, TPH-degrading bacteria addition, and control (with HgCl2 addition) groups were 80.5%, 78.6%, 77.4%, 75.1%, 73.3%, 66.1%, and 1.6% respectively. In the field study, activated sludge was selected as the additive from the engineering point of view. With the addition of activated sludge, an increase of 20% was observed for TPH removal ratio. Results from the denaturing gradient gel electrophoresis (DGGE) tests show that the detected PH-degrading bacteria in the activated sludge included the following: Pseudomonas sp., Pseudoxanthomonas sp., Rhodocyclaceae bacterium, Variovorax sp., Acidovorax sp., Leptothrix sp., Alcaligenaceae bacterium, and Burkholderia sp. Some of these bacteria became dominant species in the field after a long-term operation, which was beneficial to the soil bioremediation. Results indicate that the in situ bioremediation has the potential to be developed into an environmentally and economically acceptable remediation technology.

North American petroleum refineries use landfarming to dispose of hydrocarbon-containing wastes for bioremediation by indigenous soil microorganisms. In this study, we isolated PAH-degrading bacteria from landfarm soil by enrichment with hydrocarbon-containing effluent. One isolate, Arthrobacter sp. UG50, was capable of using phenanthrene and anthracene as sole carbon sources. The strain degraded phenanthrene (200 mg/L) within 24 h in pure culture at high cell density (10e8 cells/mL). Anthracene (50 mg/L) was slowly degraded, with 29% degraded within 21 days. The strain could not use naphthalene, pyrene, chrysene or benzo(a)pyrene as sole carbon sources, but could degrade pyrene (50 mg/L) cometabolically when phenanthrene was provided. Anthracene degradation (50 mg/L) was enhanced by phenanthrene, with 100% degraded within 6 days. The addition of strain UG50 to petroleum sludge in baffled flasks increased total hydrocarbon degradation and degradation of low concentrations of fluorene, phenanthrene, pyrene and chrysene compared to flasks with limited aeration or containing sludge alone. / NOVA Chemicals and the Ontario Centres of Excellence

Thesis (MSc)--University of Stellenbosch, 2011. / ENGLISH ABSTRACT: Landfarming is a widely used method for the disposal of contaminants in the petrochemical industry. It involves ploughing the contaminants into the top soil layer allowing biological breakdown. A historically landfarmed site was identified at a South African petrol refinery. The refinery used to dispose so-called American Petroleum Institute (API) -sludge onto a landfarming site. API-sludge consisted of a mixture of oil and water soluble contaminants originating from a process of separating refinery waste from reusable water and oil. Landfarming on this site was discontinued after excessive quantities of sludge were ploughed into the soil over time and it became obvious that effective biodegradation could not take place. An environmental assessment had to be carried out to assess to what extent the soil has recovered from the contamination and after remediation was done over time. Bioassays together with chemical analyses were executed to determine the level of pollutants in the soil and to assess the integrated effects of their bioavailable fractions. The landfarming site of the refinery was divided into two sections namely, a more contaminated north-site and less contaminated south-site. Soil samples were collected from both sites as well as from an off-site (control site). The soils were analysed physically, chemically and used in the bioassays. Two additional control soils were also used, OECD-soil and LUFA2.2 soil. Chemical analysis of the site soils showed the presence of heavy metals and high levels of diesel range organic hydrocarbons. The north-site had higher levels of contaminants compared to the south-site. Three species of soil organisms were used in standardised tests: Eisenia andrei, Enchytraeus doerjesi and Folsomia candida were exposed to the respective soils to study their survival, growth, reproduction success and avoidance behavior. Exposures to both site-soils were not acutely toxic to any organisms. F. candida had a decrease in juvenile production in both north- and south-site soils (289.42 ± 58.62 and 253.33 ± 122.94 respectively) compared to the control soil (479.89 ± 30.42). E. doerjesi showed an increase in produced juveniles exposed to north- and south-site soil (339.75 ± 76.92 and 414.00 ± 17.78 ) compared to control soil (57 ± 34.39). E. andrei had similar cocoon production when exposed to south-site soil than in off-site soil (19.00 ± 5.3 and 18.5 ± 9.7 respectively) but significantly less in north-site soil (1.25 ± 0.7). Only E. doerjesi showed avoidance of north-site soil. To determine the sensitivity of the organisms to the API-sludge, they were exposed to concentration series of API-sludge-spiked control soils. The effect concentrations were calculated as the concentration of API-sludge that will decrease the studied endpoints by 50% of the control soil (EC50). The EC50s varied for each species exposed in the different control soils showing that the toxicity of the API-sludge is to a certain extent dependent on the physical soil properties of the substrate. The reproduction of F. candida were most sensitive to the API-sludge in off-site soil (EC50 = 90 mg/kg) and the E. doerjesi the least sensitive in LUFA2.2 soil (EC50 = 36000 mg/kg). Five plant species were exposed to API-sludge-spiked potting soil and the germination success, early growth rate and biomass were studied. The plants were not as sensitive to API-sludge as the soil animals. Lettuce and grass were affected the most by API-sludge and beans were the most resilient species. With the addition of low levels API-sludge to the substrate, the growth rate of beans was stimulated. This study showed that the south-site has been successfully remediated and most soil organisms exposed to these soils were not affected by the levels of toxicants present. However, exposures to north-site soil still had negative effects on soil organisms. It is recommended that hydrocarbon contamination should be further remediated in the north-site soil before landfarming should be allowed to continue. / AFRIKAANSE OPSOMMING: Ploegverwerking is ‘n algemene remediëringsmetode vir die verwerking van afvalmateriaal in petrochemiese industrieë. Dit behels die inploeg van toksiese afvalmateriaal in die boonstegrondlaag sodat dit biologies afgebreek kan word. ‘n Voorbeeld van ‘n histories ploegverwerkte grondstuk is geidentifiseer by ‘n Suid-Afrikaanse olieraffinadery. Die raffinadery het in die verlede van die grondstuk gebruik gemaak om sogenaamde Amerikaanse Petroleum Instituut-slik (API-slik) daarin te ploeg. Die API-slik bestaan uit ‘n mengsel van olie- en wateroplosbare kontaminante afkomstig van die proses waardeur die raffinadery se afvalprodukte van hernubare water en olie geskei word. Nadat oormatige konsentrasies slik in die grond ingewerk is en bioremediasie nie meer doeltreffend kon voortgaan nie, is die ploegverwerking gestaak. ‘n Omgewingimpakstudie moes uitgevoer word om te bepaal tot watter mate die grond herstel het nadat remediasie oor tyd uitgevoer is. Toksisiteitstoetse en chemiese analises is uitgevoer om die vlakke van besoedeling sowel as die biobeskikbare fraksie daarvan in die grond te bepaal. Die ploegverwerkte area van die raffinadery is in twee verdeel naamlik, ‘n meer gekontamineerde noordelike area en ‘n minder gekontamineerde suidelike area. Grondmonsters is van die onderskeie areas asook van ‘n ongekontamineerde veld (as kontrole) naby die ploegverwerkte area versamel Die gronde is fisies- en chemies geanaliseer en toksisiteitstoetse is uitgevoer. Twee addisionele kontolegronde is ook tydens die blootstellings gebruik naamlik, OECD- en LUFA2.2-grond. Die chemiese analises van die ploegverwerkte toetsgronde het getoon dat daar steeds swaarmetale en hoë vlakke van dieselgekoppelde organiese koolwaterstowwe in die gronde teenwoordig is. Kontaminante was in hoër konsentrasies teenwoordig in die grond van die noordelike gebied as in dié van die suidelike gebied. Drie spesies van grondorganismes is gebruik tydens standaard toksisitetitstoetse. Eisenia andrei, Enchytraeus doerjesi en Folsomia candida is blootgestel aan die onderskeie toets- en kontrolegronde waarna hul oorlewing, groei, voortplantingsukses en vermydingsreaksies bestudeer is. Blootstellings aan die ploegverwerkte toetsgronde het geen akute toksisiteit vir enige van die spesies getoon nie. F. candida se juveniele produksie was laer in beide noordelike- en suidelike toetsgronde (289.42 ± 58.62 en 253.33 ± 122.94 onderskeidelik) as in die kontolegrond (479.89 ± 30.42). E. doerjesi blootstellings het ‘n toename in juveniele getalle getoon in die noordelike- en suidelike toetsgronde (339.75 ± 76.92 en 414.00 ± 17.78) in vergelyking met die ongekontamineerde kontolegrond (57 ± 34.39). Kokonproduksie by E. andrei was soorgelyk in die suidelike toetsgrond en ongekontamineerde kontrolegronde (19.00 ± 5.3 en 18.5 ± 9.7 onderskeidelik) maar beduidend minder as in noordelike toetsgrond (1.25 ± 0.7). Slegs E. doerjesi het ‘n beduidende vermydingsreaksie vir die noordelike toetsgronde getoon. Om die sensitiwiteit van die organismes aan vars API-slik te bestudeer, is hulle blootgestel aan konsentrasiereekse van API-slik in die onderskeie kontrolegronde. Die effektiewe konsentrasie (EK50) is bereken as die konsentrasie van API-slik wat die bestudeerde eindpunte met 50% sal verminder in vergelyking met die kontrolegrond Die EK50-waardes vir al die spesies het verskil na blootstelling aan die onderskeie kontrolegronde. Dus, die toksisiteit van die API-slik is tot ‘n sekere mate ook afhanklik van die fisiese grondeienskappe van die blootsellingssubstraat. Die voortplanting van F. candida was die gevoeligste eindpunt vir die blootstelling aan API-slik in kontolegrond (EK50 = 90 mg/kg) en E. doerjesi was die minste gevoelig in LUFA2.2 grond (EK50 = 36000 mg/kg). Vyf plantspesies is ook blootgestel aan API-slikgekontamineerde potgrond en die saadontkiemingssukses, vroeë groeikoers en biomassa is bestudeer. Alhoewel plante nie so sensitief was vir die API-slik soos die gronddiere nie, was blaarslaai en gras die meeste geaffekteer tydens die blootstellings. Boontjies was die ongevoeligste en met die toevoeging van lae konsentrasies API-slik (2.5% API-slik), is hul groeikoers selfs gestimuleer. Uit die studie was dit duidelik dat die suidelike deel van die grondstuk meer suksesvol as die noordelike geremidieer is en dat meeste grondorganismes wat daaraan bloot gestel is nie geaffekteer is deur die vlakke van kontaminasie wat steeds teenwoordig is in die grond nie. Die toetsgronde uit die noordelike deel het egter steeds negatiewe effekte op die grondorganismes gehad. Dit word voorgestel dat die koolwaterstof kontaminasie verder geremidieër behoort te word in die noordelike deel van die grondstuk voordat verdere ploegverwerking van die afval daar gedoen word.