Microbial community analysis of biopiles in Antarctica provides evidence of successful hydrocarbon biodegradation and initial soil ecosystem recovery.

Microorganisms comprise the bulk of biodiversity and biomass in Antarctic terrestrial ecosystems. To effectively protect and manage the Antarctic environment from anthropogenic impacts including contamination, the response and recovery of microbial communities should be included in soil remediation efficacy and environmental risk assessments. This is the first investigation into the microbial dynamics associated with large scale bioremediation of hydrocarbon contaminated soil in Antarctica. Over five years of active management, two significant shifts in the microbial community were observed. The initial shift at 12-24 months was significantly correlated with the highest hydrocarbon degradation rates, increased microbial loads, and significant increases in alkB gene abundances. ANCOM analysis identified bacterial genera most likely responsible for the bulk of degradation including Alkanindiges, Arthrobacter, Dietzia and Rhodococcus. The second microbial community shift occurring from 36 to 60 months was associated with further reductions in hydrocarbons and a recovery of amoA nitrification genes, but also increasing pH, accumulation of nitrite and a reduction of oligotrophic bacterial species. Over time, the addition of inorganic fertilisers altered the soil chemistry and led to a disruption of the nitrogen cycle, most likely decoupling ammonia oxidisers from nitrite oxidisers, resulting in nitrite accumulation. The results from this study provide key insights to the long-term management of hydrocarbon bioremediation in Antarctic soils.

A comparison between biostimulation and bioaugmentation in a solid treatment of anaerobic sludge: Drug content and microbial evaluation.

Emerging pollutants can reach the environment through the sludge of Wastewater Treatment Plants. In this work, the use of Trametes versicolor in biopiles at lab-scale was studied, evaluating its capacity to remove the most hydrophobic Pharmaceuticals and assessing the evolution of the biopiles microbial communities. The total removal of drugs at real concentrations from sewage sludge was assessed for non-inoculated and fungal inoculated biopiles, testing if the re-inoculation of the biopiles after 22 days of treatment would improve the removal yields. It was found that 2 out of the 15 initially detected pharmaceuticals were totally degraded after 22 days, and re-inoculated fungal biopiles achieved higher removal rates than non-re-inoculated fungal biopiles for single compounds and for all the drugs simultaneously: 66.45% and 49.18% re-inoculated and non-re-inoculated biopiles, respectively. Finally, the study of the bacterial and fungal communities revealed that fungal inoculated and non-inoculated biopiles evolved to similar communities adapted to the presence of those drugs.

Evaluation of remediation techniques in soils affected by residual contamination with heavy metals and arsenic.

Residual soil pollution from the Aznalcóllar mine spill is still a problem in some parts of the affected area, today converted in the Guadiamar Green Corridor. Dispersed spots of polluted soils, identified by the absence of vegetation, are characterized by soil acid pH and high concentrations of As, Pb, Cu and Zn. Ex situ remediation techniques were performed with unrecovered soil samples. Landfarming, Composting and Biopiles techniques were tested in order to immobilize pollutants, to improve soil properties and to promote vegetation recovery. The effectiveness of these techniques was assessed by toxicity bioassays: Lactuca sativa L. root elongation test, Vibrio fischeri bioluminescence reduction test, soil induced respiration test, and Eisenia andrei survival and metal bioaccumulation tests. Landfarming and Composting were not effective techniques, mainly due to the poor improvement of soil properties which maintained high soluble concentrations of Zn and Cu after treatments. Biopile technique, using adjacent recovered soils in the area, was the most effective action in the reduction of soil toxicity; the improvement of soil properties and the reduction in pollutants solubility were key to improve the response of the tested organisms. Therefore, the mixture of recovered soils with polluted soils in the areas affected by residual contamination is considered a more suitable technique to reduce the residual pollution and to promote the complete soil recovery in the Guadiamar Green Corridor.

On site remediation of a fuel spill and soil reuse in Antarctica.

The first large-scale remediation of fuel contamination in Antarctica treated 10000L of diesel dispersed in 1700t of soil, and demonstrated the efficacy of on-site bioremediation. The project progressed through initial site assessment and natural attenuation, passive groundwater management, then active remediation and the managed reuse of soil. Monitoring natural attenuation for the first 12years showed contaminant levels in surface soil remained elevated, averaging 5000mg/kg. By contrast, in five years of active remediation (excavation and biopile treatment) contaminant levels decreased by a factor of four. Chemical indicators showed hydrocarbon loss was apportioned to both biodegradation and evaporative processes. Hydrocarbon degradation rates were assessed against biopile soil temperatures, showing a phase of rapid degradation (first 100days above soil temperature threshold of 0°C) followed by slower degradation (beyond 100days above threshold). The biopiles operated successfully within constraints typical of harsh climates and remote sites, including limitations on resources, no external energy inputs and short field seasons. Non-native microorganisms (e.g. inoculations) and other organic materials (e.g. bulking agents) are prohibited in Antarctica making this cold region more challenging for remediation than the Arctic. Biopile operations included an initial fertiliser application, biannual mechanical turning of the soil and minimal leachate recirculation. The biopiles are a practical approach to remediate large quantities of contaminated soil in the Antarctic and already 370t have been reused in a building foundation. The findings presented demonstrate that bioremediation is a viable strategy for Antarctica and other cold regions. Operators can potentially use the modelled relationship between days above 0°C (threshold temperature) and the change in degradation rates to estimate how long it would take to remediate other sites using the biopile technology with similar soil and contaminant types.

Biorremediación de lodos contaminados con aceites lubricantes usados / Bioremediation of sludge contaminated with used lubricants

Los lodos contaminados con residuos de aceites lubricantes usados generan gran impacto ambiental negativo al no ser manejados adecuadamente. Se propuso la biorremediación para disminuir la concentración de dichos contaminantes. Los ensayos fueron realizados en las instalaciones de la planta de tratamiento de aguas residuales (PTAR) de Río Frío (Girón, Santander, Colombia), donde se evaluaron consorcios microbianos nativos, que posteriormente se adicionaron a las biopilas conformadas por lodos deshidratados provenientes del tratamiento primario de aguas residuales domésticas (usados como fuente de materia orgánica), lodos provenientes de lavaderos de carros y lodos de alcantarillado de la zona industrial de la ciudad de Bucaramanga (Colombia). Se aislaron, identificaron y conservaron cepas microbianas con capacidad degradadora de hidrocarburos totales de petróleo (TPH) como Pseudomonas spp., Acinetobacter spp, Enterobacter cloacae, Citrobacter spp., Bacillus brevis, Micrococcus spp y Nocardia spp. Se hizo una serie de pruebas piloto donde se inoculó cada montaje con un consorcio bacteriano a una concentración de 3x108 UFC/ml de bacterias y microorganismos fúngicos como Aspergillus spp., Fusarium spp., Trichoderma spp., a una concentración de 1x106 esporas/ml; se monitorearon parámetros de temperatura, pH, humedad y oxigenación. Se realizaron dos ensayos para verificar el comportamiento de dichos tratamientos; se analizó la variable continua TPH en ppm mediante el método de modelos mixtos lineares en bloques aleatorios completos, que revelaron diferencias significativas entre la biopila control y las biopilas bajo prueba; se obtuvieron porcentajes de remoción hasta de 94% de TPH en 120 días y 84% en 40 días, lo que reflejó un efecto positivo en la utilización de los consorcios de microorganismos bajo prueba en la descontaminación de lodos de alcantarillado industrial y lodos de lavaderos de carros.

The sludge contaminated with residues of used lubricating oils produce large negative environmental impact by not being handled properly. We proposed Biorremediation to decreasethe concentration of these polltants. The trials were conducted on the waste water treatment plant (WWTP) Río Frío (Girón, Santander, Colombia) ,we evaluate native microbial associations, and subsequently they were added to biopiles, made up of dried sludge the waste water treatment (source of organic mater) sludge from washing cars and sewage sludge from the industrial area of the city Bucaramanga (Colombia). Several pilot test were completed and we isolated, identified and retained microbial atrains with ability to degrading total petroleum hydrocarbons (TPH) such as Pseudomonas spp., Escherichia coli, Citrobacter spp., Bacillus brevis, Micrococcus spp., among others. We inoculated each pilot assembly with a bacterial concentration of 3x108 UFC/ml and fungal microorganisms like Aspergillus spp., Fusarium spp., Trichoderma spp. in a concentration of 1x106 Spores/ml. Parameters such as temperature, pH, humidity, oxygenation were monitoring frequently. Two trials were completed to verify the behabior and results of treatment, we analized continuously the concentration of TPH using linear mixed models approach in a randomized complete blocks, which revealed significant differences between control biopile (without microorganism consortia) and biopiles under test, obtaining removal percentages to 94% of TPH in 120 days, and 84% in 40 days, reflecting a positive effect on the use of consortia of microorganisms under test in the decontamination of domestic sewage sludge and industrial sludge and sludge the car wash.