Hydrogen is a key energy source for subsurface microbial processes, particularly in subsurface environments with limited alternative electron donors, and environments that are not well connected to the surface. In addition to consumption of hydrogen, microbial processes such as fermentation and nitrogen fixation produce hydrogen. Hydrogen is also produced by a number of abiotic processes including radiolysis, serpentinization, graphitization, and cataclasis of silicate minerals. Both biotic and abiotically generated hydrogen may become available for consumption by microorganisms, but biotic production and consumption are usually tightly coupled. Understanding the microbiology of hydrogen cycling is relevant to subsurface engineered environments where hydrogen-cycling microorganisms are implicated in gas consumption and production and corrosion in a number of industries including carbon capture and storage, energy gas storage, and radioactive waste disposal. The same hydrogen-cycling microorganisms and processes are important in natural sites with elevated hydrogen and can provide insights into early life on Earth and life on other planets. This review draws together what is known about microbiology in natural environments with elevated hydrogen, and highlights where similar microbial populations could be of relevance to subsurface industry.
Aims: The objective of the work was to determine whether known strains of nonpathogenic vibrios can act as probiotics for the control of Vibrio infections in the Pacific white shrimp, Litopenaeus vannamei. Methods and Results: Of the ten species tested, only Vibrio alginolyticus (NCIMB 1339) and Vibrio gazogenes (NCIMB 2250) showed antagonistic activity towards a panel of shrimp pathogenic vibrios. In the case of V. alginolyticus, this activity depended on the presence of live bacteria while in V. gazogenes both live and dead bacteria showed anti‐Vibrio activity. Injection of shrimp with either V. alginolyticus or V. gazogenes at 3 × 107 or 3 × 105 total bacteria per shrimp resulted in mortality with higher levels in the case of V. alginolyticus (100% mortality 18 h postinjection of 3 × 107 bacteria). Juvenile shrimp were fed commercial diets top‐coated with either chitin (an immune stimulant) or chitin + V. gazogenes. Both chitin and V. gazogenes caused a significant decline in the number of Vibrio‐like bacteria in the fore and hind gut, and changes were also seen in the hepatosomatic index (a measure of digestive health) and the total number of blood cells in circulation. Analysis of mid/hindgut and faecal samples obtained using terminal restriction fragment length polymorphism showed that the gut microbiota of shrimp has limited bacterial diversity and that after 8 weeks exposure to the experimental diets there were significant changes in the microbial flora of the GI tract of shrimp as a result of the presence of V. gazogenes. Conclusions: Of the vibrios tested, V. gazogenes has potential as a probiotic for the control of bacterial diseases in shrimp. Significance and Impact of the Study: Overall, this study shows the promise of V. gazogenes together with chitin to improve the health and welfare of shrimp under aquaculture conditions.
A novel bacterial disease of the European shore crab, Carcinus maenas -molecular pathology and epidemiology Several rickettsia-like diseases have been reported in arthropods (insects and crustaceans), some of which result in significant losses of economically important species such as shrimp and crabs. This study reports on the molecular pathology of a recently emerged disease of the European shore crab, Carcinus maenas, termed milky disease -named as a result of the unusual milky appearance of the haemolymph (blood). This disease was more prevalent (.26 %) during summer months when the water temperature in a pilot crab farm was approximately 19 6C. The putative causative agent of the disease was a Gram-negative bacterium that could not be cultured on a range of agar-based growth media. Diseased crabs showed significant reductions in free blood cell numbers and total serum protein. Such animals also displayed raised levels of glucose and ammonium in blood. Ultrastructural and in situ hybridization studies revealed that the causative agent associated with milky disease multiplied in the fixed phagocytes of the hepatopancreas (digestive gland), ultimately to be released into the haemolymph, where the circulating blood cells showed little response to the presence of these agents. Attempts to induce the infection by short-term temperature stress failed, as did transmission experiments where healthy crabs were fed infected tissues from milky disease affected individuals. Sequence analysis of the 16S rRNA gene from the milky disease bacteria indicated that they are a previously undescribed species of a-proteobacteria with little phylogenetic similarity to members of the order Rickettsiales. INTRODUCTIONThere is increasing interest in the likely effect of global climate change on diseases in both wild and cultured organisms (Harvell et al., 1999(Harvell et al., , 2002Lafferty et al., 2004). In particular, aquatic animals are highly sensitive to temperature change and it is widely accepted that elevated temperatures can lead to reduced oxygen tension in the water, higher microbial growth and immunosuppression, resulting in higher prevalence of disease (Le Moullac & Haffner, 2000). For example, brown trout in alpine rivers and streams have been found to show increasing prevalence of proliferative kidney disease caused by the myxozoan parasite Tetracapsuloides bryosalmonae over the last 20 years (Hari et al., 2006). These increased temperatures drive the proliferation of T. bryosalmonae in its intermediate bryozoan host (Tops et al., 2006). Equally at very low water temperatures, some aquatic animals may become immunocompromised as a result of a failure of the immune system to mount an effective immune response to bacterial challenge (Chisholm & Smith, 1994).One potentially important result of climate change will be alterations in the effectiveness of aquaculture as a method of supplementing fish and shellfish for human and animal consumption taken from the wild (Alborali, 2006). Currently, it is thought that at least 15 ...
The presence and activity of microorganisms in aquifers can affect, amongst other things, nutrient cycling, contaminant degradation and water flow. The introduction of a pollutant or other changes in water chemistry can alter the microbial community composition and affect aquifer functioning. To understand the microbial response to anthropogenically induced changes, a better knowledge of baseline microbial communities in uncontaminated aquifers is needed. Here, we review the information on microorganisms in UK aquifers together with examples of research from other countries on this topic, and discuss how these communities might respond to disturbance. Research into microbial communities in UK aquifers has mostly been limited to bacteria and often reveals a community dominated by Proteobacteria. The community composition is influenced by factors such as mineralogy and water chemistry, and the natural baseline community may be altered by aquifer contamination. A UK-wide survey of aquifer microbes, similar to one recently carried out in New Zealand, would provide valuable information about the current state of UK aquifer microbiology. This would lead to a greatly improved understanding of the ecosystem services provided by the microbial communities present in aquifers, allow future monitoring and assessment of the effects of pollution, and assist in groundwater resource management.
Rare earth elements (REE) are considered to be a critical resource, because of their importance in green energy applications and the overdependence on Chinese imports. REE rich ion-adsorption deposits (IAD) result from tropical weathering of REE enriched igneous rocks. Commercial REE leaching from IAD, using salt solutions occurs via an ion-exchange mechanism. Bioleaching of IAD by Aspergillus or Bacillus, was compared to Uninoculated Control and Salt leaching (0.5 M ammonium sulfate) over 60 days. Salt leaching was most effective, followed by Aspergillus, Bacillus then Uninoculated Control. Most of the REE and major elements released by Salt leaching occurred before day 3. With bioleaching, REE and major elements release increased with time and had a greater heavy to light REE ratio. Similar total heavy REE release was observed in Salt leaching and Aspergillus (73.1% and 70.7% Lu respectively). In bioleaching experiments, pH was inversely correlated with REE release (R 2 = 0.947 for Lu) indicating leaching by microbially produced acids. These experiments show the potential for bioleaching of REE from IAD, but dissolution of undesirable elements could cause problems in downstream processing. Further understanding of the bioleaching mechanisms could lead to optimization of REE recovery.
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