Groundwater: Difference between revisions

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==References==
==References==
<b>Groundwater treatment<b>
1. W.W.J.M de Vet et al characterized the microbial populations in groundwater sources and sand filters for drinking water production. They found that both bacteria and archaea, especially Nitrospira, are important in ammonia nitrification. No nitrifying organisms were detected in subsurface aerated groundwater; therefore, the nitrifying capacity is low. Iron-oxidizing bacteria Gallionella ferruginea was detected in subsurface aerated groundwater. It indicted the iron oxidation could be existed and thereby could improve nitrification in groundwater.
2. Sven Jechalke et al developed a novel aerated treatment pond for enhanced biodegradation of groundwater contaminants.  They use coconut fibre and polypropylene textiles to grow contaminant-degrading biofilms. The results showed that the efficiencies for benzene, MTBE and COD were 99.9%, 38% and 61% respectively. Ammonium degradation rates were low.


[Sample reference] [http://ijs.sgmjournals.org/cgi/reprint/50/2/489 Takai, K., Sugai, A., Itoh, T., and Horikoshi, K. "''Palaeococcus ferrophilus'' gen. nov., sp. nov., a barophilic, hyperthermophilic archaeon from a deep-sea hydrothermal vent chimney". ''International Journal of Systematic and Evolutionary Microbiology''. 2000. Volume 50. p. 489-500.]
[Sample reference] [http://ijs.sgmjournals.org/cgi/reprint/50/2/489 Takai, K., Sugai, A., Itoh, T., and Horikoshi, K. "''Palaeococcus ferrophilus'' gen. nov., sp. nov., a barophilic, hyperthermophilic archaeon from a deep-sea hydrothermal vent chimney". ''International Journal of Systematic and Evolutionary Microbiology''. 2000. Volume 50. p. 489-500.]

Revision as of 22:04, 4 April 2011

Water stored underground in cracks and pores, from Natural Resources Canada.

Introduction

Surface water moves downward through unsaturated zones –typically tiny pores and cracks in the soil, sand, or rock, and then reaches a stable and completed water saturated layer named water table. Groundwater is beneath the water table. Groundwater provide about 0.6 percent of the world’s total water and 20 percent of the available fresh water resources. Microbial organisms play important role in groundwater ecosystem and affect drinking water quality significantly. Microbial contamination of groundwater is a big concern.

Typical aquifer cross-section, from wikipeida.

Physical environment

Substrate and sediment

In the shallow aquifers where generally groundwater is located, typically, there is soil, sand, plant roots, hardpan and low permeability bedrock.

Temperature

The temperature of groundwater is quite steady because the specific heat capacity of water is high and also because the soil, rock and up layer water protect groundwater from heat changing with the climate.

Hydrogeology

Groundwater is relatively stable compared to surface water. In the aquifer and other porous media, groundwater not only follows gravity, but also follows pressure gradients. The movement of groundwater also depends on the porosity, water content and hydraulic conductivity of aquifer.

groundwater contaminatioin plume, from earth science australia.

Groundwater contamination

Pollutants, such as gasoline, oil, road salts and chemicals seep into groundwater can hurt animals, plants, or humans. Two major contaminate sources are Hazardous waste site leaking and landfills. Since groundwater is part of hydrologic cycle, contaminates released to the groundwater could create a contaminant plume within an aquifer and also can be transferred to the other parts of the cycle.


Microorganisms

Bacteria

Gram-negative bacteria are found extensively in groundwater system. Balkwill (1989) studied the aerobic, chemoheterotrophic bacteria in deep aquifers and other subsurface sediments at a site in South Carolina. They found that 95% of the platable colonies contained nonstreptomycete bacteria, more than 80% of which were gram-negative rods. Gram-positive bacteria are not many in groundwater system; however, the gram-positive bacteria include many important human pathogens such as micrococcus, staphylococcus, and streptococcus.

Virus

It is estimated that 65% of the water borne disease are caused by enteric viruses. For example, norovirus (also known as Norwalk agent) causes approximately 90% of epidemic non-bacterial outbreaks of gastroenteritis around the world. Infectious hepatitis is the most intensively studied disease that is caused by water borne virus. Virus adsorption to soils and other solids could prolong survival of viruses in the groundwater. Research showed that Viruses originating from wastewater infiltration units are able to migrate horizontal in groundwater for hundreds of meters and vertically as great as 67 meters.

Eucarya

Groundwater eukaryotes are comprised of many species, range from single-celled heterotrophic nanoflagellates and fungi to amphipod crustaceans. The location of groundwater eukaryotes might be close to the vadose (unsaturated) zone, the soil or the bottom sediments of surface waters.

Archaea

Groundwater Archaea have been found throughout depths of several thousand meters. Ammonia-Oxidizing Archaea and methanogenic Archaea are two major groups in the groundwater.

Microbial processes

Ammonia oxidation

Both bacteria and archaea are able to carry out ammonia oxidation in the groundwater. The ammonia oxidation rate is limited by the available oxygen.

Denitrification

Denitrification reduce nitrate in the groundwater. Denitrifying bacteria Burkholderia, Bacillus, and Pseudomonas play an important role in groundwater.

Manganese, Iron and sulfate Reduction

Anaerobic condition is dominant in groundwater. In anaerobic zone, microbial communities could carry out decomposition through Manganese, Iron and sulfate reduction.

Dehalogenation

Synthetic halogenated organic compounds in the groundwater could persist for very long time and are recognized as a serious health concern. Dehalogenation removes halogens from organic compounds. Anaerobic dehalogenation reactions can effectively degrade a wide variety of halogenated contaminants in ground water.

Current Research

Enter summaries of recent research here--at least three required

References

Groundwater treatment 1. W.W.J.M de Vet et al characterized the microbial populations in groundwater sources and sand filters for drinking water production. They found that both bacteria and archaea, especially Nitrospira, are important in ammonia nitrification. No nitrifying organisms were detected in subsurface aerated groundwater; therefore, the nitrifying capacity is low. Iron-oxidizing bacteria Gallionella ferruginea was detected in subsurface aerated groundwater. It indicted the iron oxidation could be existed and thereby could improve nitrification in groundwater. 2. Sven Jechalke et al developed a novel aerated treatment pond for enhanced biodegradation of groundwater contaminants. They use coconut fibre and polypropylene textiles to grow contaminant-degrading biofilms. The results showed that the efficiencies for benzene, MTBE and COD were 99.9%, 38% and 61% respectively. Ammonium degradation rates were low.


[Sample reference] Takai, K., Sugai, A., Itoh, T., and Horikoshi, K. "Palaeococcus ferrophilus gen. nov., sp. nov., a barophilic, hyperthermophilic archaeon from a deep-sea hydrothermal vent chimney". International Journal of Systematic and Evolutionary Microbiology. 2000. Volume 50. p. 489-500.

Edited by <your name>, a student of Angela Kent at the University of Illinois at Urbana-Champaign.