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Typically groundwater is thought of as liquid water flowing through shallow aquifers, but technically it can also include soil moisture, permafrost (frozen soil), immobile water in very low permeability bedrock, and deep geothermal or oil formation water. Groundwater is hypothesized to provide lubrication which allow thrust faults to move. Nearly any point in the Earth's subsurface has water in it, to some degree (it may be very dry or mixed with other fluids). Groundwater is not confined only to the Earth, either; subsurface water on Mars is believed to have given rise to some of the landforms observed there.
Aquifers
An aquifer is a subterranean geologic unit (or layer) of permeable material
(like sand and gravel) that is capable of providing usable quantities of water
to a well. Aquifers can be confined or unconfined. A confined aquifer has
a low permeability confining layer (an aquitard), such as clay, above it that
restricts the upward and downward movement of water. If a confined aquifer
follows a downward grade from its recharge zone, groundwater can become pressurized
as it flows. This can create artesian wells that flow freely without the need
of a pump. The top of the upper unconfined aquifer is called the water table
or phreatic surface, where water pressure is equal to atmospheric pressure.
The porous media in which groundwater occurs are the complex geologic materials near the earth surface; hence local details of porosity and permeability are as complex as those materials. Generally, the more productive and useful aquifers are in sedimentary geologic formations, though weathered and fractured crystalline rocks yield smaller volumes of groundwater in many environments. Among the most productive groundwater environments are unconsolidated to poorly cemented alluvial materials that have accumulated as valley-filling sediments in major river valleys and geologically subsiding structural basins.
The high specific heat capacity of groundwater and the insulating effect of soil and rock averages out climatic fluctuations to maintain groundwater at a relatively steady temperature. Increasingly this effect is used to heat and cool structures. During hot weather, groundwater is sometimes cool enough to be used as is, to be simply pumped through radiators in a home, then returned to the ground in another well. During cold seasons, the water, because it has a high specific heat capacity can be used as a source of heat for heat pumps that is much more efficient than using air. The relatively constant temperature of groundwater can also be used for heat pumps.
Groundwater in the water cycle
Relative groundwater travel times, click to view fullsize.Groundwater can
be a long-term 'reservoir' of the natural water cycle (with residence times
from days to millennia), as opposed to short-term water reservoirs like the
atmosphere and fresh surface water (which have residence times from minutes
to years). The figure shows how deep groundwater (which is quite distant from
the surface recharge) can take a very long time to complete its natural cycle.
Groundwater is naturally replenished by surface water from precipitation,
streams, and rivers when this recharge reaches the water table. It is estimated
that the volume of groundwater is fifty times that of surface freshwater;
the icecaps and glaciers are the only larger sources of fresh water on earth.
Groundwater makes up about twenty percent of the world's fresh water supply, which is about 0.61 percent of the entire world's water supply.
Problems
Overdraft
Groundwater is a highly useful and abundant resource, but in arid or semi-arid
regions it is in a pre-development state. The most evident problem that may
result from this is a lowering of the water table beyond the reach of existing
wells. Wells must consequently be deepened to reach the groundwater; in some
places (e.g., California, Texas and India) the water table has dropped hundreds
of feet from well pumping. A lowered water table may, in turn, cause other
problems such as subsidence.
Subsidence
In its natural equilibrium state, the groundwater in the pore spaces of the
aquifer and the aquitard support some of the weight of the overlying sediments.
Aquitards are composed of materials (silts and clays) that are very compressible,
much more so than aquifers. When groundwater is removed from aquitards and
drawn into adjacent aquifers due to excessive pumping in those aquifers, pore
pressures in the aquitard drop, and compression of the aquitard may occur.
This compression may be partially recoverable if pressures rebound, but much
of it is not. When the aquitard gets compressed it causes land subsidence,
a drop in the ground surface. The city of New Orleans, Louisiana is actually
below sea level today, and its subsidence is partly caused by removal of groundwater
from the various aquifer/aquitard systems beneath it. In the first half of
the 20th Century, the city of San Jose, California dropped 13 feet due to
land subsidence caused by over pumping; this subsidence has been halted with
improved groundwater management.
Contrary to popular belief, the groundwater storage capacity of the aquifer adjacent to the compacted aquitard is not reduced when subsidence occurs.
Seawater intrusion
Generally, in very humid or undeveloped regions, the shape of the water table
mimics the slope of the surface. The recharge zone of an aquifer near the
seacoast is likely to be inland, often at considerable distance. In these
coastal areas, a lowered water table may induce sea water to reverse the flow
toward the sea. Sea water moving inland is called a saltwater intrusion. Alternatively,
salt from mineral beds may leach into the groundwater of its own accord.
Mining
Sometimes the water movement from the recharge zone to the place where it
is withdrawn may take centuries (see figure above). When the usage of water
is greater than the recharge, it is referred to as mining water (the water
is often called fossil water because of its geologic age). Under those circumstances
it is not a renewable resource.
Pollution
Iron oxide staining caused by reticulation from an unconfined aquifer in karst
topography. Perth, Western Australia.Main article: Water pollution
Not all groundwater problems are caused by over-extraction. Pollutants released
to the ground can work their way down into groundwater. Movement of water
and dispersion within the aquifer spreads the pollutant over a wider area,
which can then intersect with groundwater wells or find their way back into
surface water, making the water supplies unsafe. The interaction of groundwater
contamination with surface waters is analyzed by use of hydrology transport
models.
The stratigraphy of the area plays an important role in the transport of these pollutants. An area can have layers of sandy soil, fractured bedrock, clay, or hardpan. Areas of karst topography on limestone bedrock are sometimes vulnerable to surface pollution from groundwater. See environmental engineering and remediation. Water table conditions are of great importance for drinking water supplies, agricultural irrigation, waste disposal (including nuclear waste), and other ecological issues.
Upon commercial real estate property transactions both groundwater and soil are the subjects of scrutiny, with a Phase I Environmental Site Assessment normally being prepared to investigate and disclose potential pollution issues.
Love Canal was one of the most widely known examples of groundwater pollution. In 1978, residents of the Love Canal neighborhood in upstate New York noticed high rates of cancer, and an alarming number of birth defects. This was eventually traced to organic solvents and dioxins from an industrial landfill that the neighbourhood had been built over and around, which had then infiltrated into the water supply and evaporated in basements to further contaminate the air. 800 families were reimbursed for their homes and moved, after extensive legal battles and media coverage.
Another example of widespread
groundwater pollution is in the Ganges Plain of northern India and Bangladesh
where severe contamination of groundwater by naturally occurring arsenic affects
25% of water wells in the shallower of two regional aquifers. The pollution
occurs because aquifer sediments contain organic matter (dead plant material)
that generates anaerobic (an environment without oxygen) conditions in the
aquifer. These conditions result in the microbial dissolution of iron oxides
in the sediment and thus the release of the arsenic, normally strongly bound
to iron oxides, into the water. As a consequence, arsenic-rich groundwater
is often iron-rich, although secondary processes often obscure the association
of dissolved arsenic and dissolved iron.[