The Allium cepa bioassay to evaluate landfarming soil, before and after the addition of rice hulls to accelerate organic pollutants biodegradation

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Biodegradation of oil refinery residues using mixed-culture of microorganisms isolated from a landfarming

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Clastogenicity of landfarming soil treated with sugar cane vinasse

The addition of nutrients and/or soil bulking agents is used in bioremediation to increase microbial activity in contaminated soils. For this purpose, some studies have assessed the effectiveness of vinasse in the bioremediation of soils contaminated with petroleum waste. The present study was aimed at investigating the clastogenic/aneugenic potential of landfarming soil from a petroleum refinery before and after addition of sugar cane vinasse using the Allium cepa bioassay. Our results show that the addition of sugar cane vinasse to landfarming soil potentiates the clastogenic effects of the latter probably due the release of metals that were previously adsorbed into the organic matter. These metals may have interacted synergistically with petroleum hydrocarbons present in the landfarming soil treated with sugar cane vinasse. We recommend further tests to monitor the effects of sugar cane vinasse on soils contaminated with organic wastes. © 2012 Springer Science+Business Media B.V.

Estabilização de landfarming de refinaria de petróleo, mediante metabolismo microbiano, e aplicabilidade em solos pré-desertificados

Pós-graduação em Ciências Biológicas (Microbiologia Aplicada) - IBRC

Análise da toxicidade e da mutagenicidade de um solo de landfarming, proveniente de um refinaria de petróleo, antes e depois de processos que visam estimular a biodegradação de hidrocarbonetos

Pós-graduação em Ciências Biológicas (Biologia Celular e Molecular) - IBRC

Microbial activities in boreal soils: Biodegradation of organic contaminants at low temperature and ammonia oxidation

This thesis deals with the response of biodegradation of selected anthropogenic organic contaminants and natural autochthonous organic matter to low temperature in boreal surface soils. Furthermore, the thesis describes activity, diversity and population size of autotrophic ammonia-oxidizing bacteria (AOB) in a boreal soil used for landfarming of oil-refinery wastes, and presents a new approach, in which the particular AOB were enriched and cultivated in situ from the landfarming soil onto cation exchange membranes. This thesis demonstrates that rhizosphere fraction of natural forest humus soil and agricultural clay loam soil from Helsinki Metropolitan area were capable of degrading of low to moderate concentrations (0.2 50 µg cm-3) of PCP, phenanthrene and 2,4,5-TCP at temperatures realistic to boreal climate (-2.5 to +15 °C). At the low temperatures, the biodegradation of PCP, phenanthrene and 2,4,5-TCP was more effective (Q10-values from 1.6 to 7.6) in the rhizosphere fraction of the forest soil than in the agricultural soil. Q10-values of endogenous soil respiration (carbon dioxide evolution) and selected hydrolytic enzyme activities (acetate-esterase, butyrate-esterase and β-glucosidase) in acid coniferous forest soil were 1.6 to 2.8 at temperatures from -3 to +30 °C. The results indicated that the temperature dependence of decomposition of natural autochthonous soil organic matter in the studied coniferous forest was only moderate. The numbers of AOB in the landfarming (sandy clay loam) soil were determined with quantitative polymerase chain reaction (real-time PCR) and with Most Probable Number (MPN) methods, and potential ammonium oxidation activity was measured with the chlorate inhibition technique. The results indicated presence of large and active AOB populations in the heavily oil-contaminated and urea-fertilised landfarming soil. Assessment of the populations of AOB with denaturing gradient gel electrophoresis (DGGE) profiling and sequence analysis of PCR-amplified 16S rRNA genes showed that Nitrosospira-like AOB in clusters 2 and 3 were predominant in the oily landfarming soil. This observation was supported by fluorescence in situ hybridization (FISH) analysis of the AOB grown on the soil-incubated cation-exchange membranes. The results of this thesis expand the suggested importance of Nitrosospira-like AOB in terrestrial environments to include chronically oil-contaminated soils.

Biorremediação de antraceno, fenantreno e pireno em um argissolo

O antraceno, o fenantreno e o pireno são hidrocarbonetos aromáticos policíclicos (HAPs) que podem ser carcinogênicos e que não são degradados pela maioria dos microrganismos do solo. A biorremediação é uma estratégia para eliminação dos HAPs, que pode demandar a inoculação de microrganismos degradadores e a modificação das condições químicas e físicas do solo. O objetivo do presente estudo foi isolar, identificar e caracterizar microrganismos degradadores e mineralizadores de antraceno, fenantreno e pireno em meio mineral e no solo, assim como avaliar a influência do pH e da disponibilidade de água, N, P, Fe e S na biorremediação de um solo contaminado com antraceno. Seis amostras de solo de landfarming foram inoculadas individualmente a um solo contaminado em laboratório com antraceno. Após 176 dias, o solo com maior produção de C-CO2 foi utilizado para o enriquecimento em meio mineral mais antraceno. Os microrganismos foram isolados e identificados pelo seqüenciamento do gene do RNAr. A capacidade dos microrganismos em degradar os 3 HAPs no meio mineral e no solo foi avaliada por cromatografia gasosa. A mineralização de diferentes concentrações de antraceno, fenantreno e pireno no solo foi avaliada por respirometria, assim como o efeito de diferentes doses de N, P, S e Fe, de diferentes pH e umidades do solo na mineralização do antraceno. Isolou-se do solo de landfarming um consórcio microbiano composto por 6 bactérias, identificadas como Mycobacterium fortuitum, Bacillus cereus, Microbacterium sp., Gordonia polyisoprenivorans, Microbacteriaceae bacterium e Naphthaleneutilizing bacterium, e um fungo, Fusarium oxysporum. O consórcio microbiano degradou respectivamente 48, 67 e 22% do antraceno, fenantreno e pireno do meio mineral. No solo o consórcio degradou, em média, mais de 92% e mineralizou mais de 78% das diferentes concentrações destes 3 HAPs em 70 dias. As maiores mineralizações do antraceno ocorreram nos solos com as maiores umidades gravimétricas (12,5%) e pH (7,5). A adição de 100 kg ha-1 ou mais de nitrogênio no solo e a conseqüente redução da relação C:N para valores inferiores a 67:1 diminuíram a mineralização do antraceno no solo. O aumento da disponibilidade do fósforo, do ferro e do enxofre e a presença de amplas relações C:P (1076:1 a 50:1) e C:N:P (1076:16:1 a 50:1,3:1) no solo não influenciaram a mineralização do antraceno. Conclui-se que a seleção e a inoculação ao solo de microrganismos degradadores de HAPs, associado a modificação das condições ambientais, pode conduzir a um eficiente processo de biorremediação, onde a grande maioria dos HAPs é mineralizada em curto período de tempo.

Morphological biomarkers in the Rhinocricus padbergi midgut exposed to contaminated soil

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Histological and Histochemical Analysis of the Fat Body of Rhinocricus padbergi (Diplopoda) Exposed to Contaminated Industrial Soil

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Evaluation of the use of vinasse as a biostimulation agent for the biodegradation of oily sludge in soil

Este trabalho objetivou estudar o efeito da vinhaça na biodegradação em solo da borra oleosa proveniente da refinaria de petróleo Replan-Petrobras. Foi utilizado o método respirométrico de Bartha para verificar a eficiência de tratamentos constituídos de solo, borra oleosa nas concentrações 7 e 14 % (m/m) e ajuste da umidade do solo com e sem vinhaça (0,11 mL/g solo seco) durante 121 dias. Embora a adição da vinhaça tenha proporcionado um aumento da população microbiana nos tratamentos, esta não se mostrou adequada para aumentar a eficiência de biodegradação da borra oleosa em solo, uma vez que não houve diferença entre o CO2 produzido nos tratamentos com ou sem vinhaça após o consumo total da vinhaça. Assim, o uso da vinhaça como agente estimulante em processos de biodegradação mostrou-se ineficiente nas condições estudadas.

Laboratory study on the bioremediation of diesel oil contaminated soil from a petrol station

O objetivo do presente estudo foi investigar possíveis métodos para aumentar a taxa de biodegradação aeróbia de hidrocarbonetos (tratamentos ex-situ). Neste trabalho, processos de biorremediação foram aplicados a um solo arenoso com alto nível de contaminação ocasionada por um vazamento de um tanque de armazenamento de óleo diesel subterrâneo em um posto de combustíveis. Experimentos em escala laboratorial (respirômetros de Bartha) foram utilizados para avaliar a biodegradação do óleo diesel. Estímulo da biodegradação foi realizado utilizando-se as técnicas de bioestímulo (adição de soluções de nitrogênio e fósforo ou surfactante Tween 80) e de bioaumento (consórcio bacteriano isolado de um sistema de landfarming). Para investigar as interações entre os fatores otimizadores, e encontrar a melhor combinação entre esses agentes, o estudo foi baseado em um delineamento experimental fatorial completo. A eficiência de biodegradação foi simultaneamente medida com dois métodos: respirométrico (produção de CO2 microbiano) e cromatografia gasosa. Testes de toxicidade aguda com Daphnia similis foram aplicados para examinar a eficiência dos processos em termos de geração de produtos menos tóxicos. Resultados mostraram que todas as estratégias de biorremediação aceleraram a biorremediação natural do solo contaminado e os melhores resultados foram obtidos quando os tratamentos tinham adição de nutrientes. Dados respirométricos indicaram uma máxima mineralização de hidrocarbonetos de 19,8%, obtida com a combinação dos três agentes, com uma remoção de hidrocarbonetos totais de petróleo (TPH) de 45,5% em 55 dias de tratamento. No final dos experimentos, duas espécies predominantes de bactéria foram isoladas e identificadas como Staphylococcus hominis e Kocuria palustris.

Avaliação do método de Iwatsu et al., (1981) para isolamento de leveduras negras do solo, degradadoras de hidrocarbonetos

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Biodegradação de resíduos oleosos provenientes de refinaria de petróleo através do sistema de biopilhas

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Bioremediation of PAHs - Limitations and soultions

Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.

Comparativa de métodos de descontaminación de suelos afectados por hidrocarburos. Aplicación a la obra del AVE de Málaga

El objetivo de esta tesis, va a ser la investigación y desarrollo de tratamientos de biorremediación para conseguir la recuperación de los terrenos contaminados situados en el tramo del tren de alta velocidad entre Córdoba y Málaga, reduciendo de esta forma los residuos enviados a vertederos. Para ello, se va a investigar y a desarrollar una tecnología innovadora de descontaminación in situ de suelos con altas concentraciones de hidrocarburos, basándonos en el landfarming y como principal avance la coexistencia con hidróxido de magnesio, elemento no utilizado nunca y potencialmente muy útil. Se va a pretender reducir la concentración final de hidrocarburos y el tiempo de tratamiento, sin transportar a vertedero los residuos. Se desean conseguir las condiciones ambientales óptimas que permitan potenciar la degradación microbiana de los hidrocarburos y sus productos residuales en corto tiempo Se va a investigar el empleo del hidróxido de magnesio como complemento al landfarming y a buscar las sinergias de este compuesto como gran fijador de metales pesados. ABSTRACT The aim of this thesis will be the research and development of bioremediation treatments for the recovery of contaminated land in the stretch of the high speed train between Cordoba and Malaga, thereby reducing waste sent to landfills. To do this, is to research and develop innovative technology for in situ remediation of soil with high concentrations of hydrocarbons, based on the main progress landfarming and coexistence with magnesium hydroxide, item never used and potentially very useful. It will pretend to reduce the final hydrocarbon concentration and treatment time, without transporting waste landfill. They want to get the optimum environmental conditions for enhancing microbial degradation of hydrocarbons and waste products in a short time It will investigate the use of magnesium hydroxide as a complement to landfarming and seek synergies of this compound as a great fixer of heavy metals.