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Groundwater in the Great Lakes Basin

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2<br />

required to monitor bas<strong>in</strong> groundwater quality and<br />

quantity has decl<strong>in</strong>ed substantially <strong>in</strong> <strong>the</strong> last twenty<br />

years. Although model<strong>in</strong>g has improved and now offers<br />

impressive capability to <strong>in</strong>form decision makers about<br />

groundwater quality and quantity, <strong>the</strong> erosion <strong>in</strong> <strong>the</strong><br />

collection of basel<strong>in</strong>e hydrogeological data precludes<br />

mean<strong>in</strong>gful model calibration or application <strong>in</strong> many<br />

parts of <strong>the</strong> bas<strong>in</strong>.<br />

The most press<strong>in</strong>g scientific issues are:<br />

• Better characterization of subsurface conditions,<br />

especially <strong>the</strong> hydraulic conductivity of geologic<br />

materials.<br />

• Identification of aquifer boundaries.<br />

• Estimation of recharge rates.<br />

• The l<strong>in</strong>k<strong>in</strong>g of data and models collected at<br />

different spatial scales.<br />

• Ensur<strong>in</strong>g uniformity of data records across jurisdictions,<br />

for example, through <strong>the</strong> adoption of uniform<br />

well-logg<strong>in</strong>g procedures and implementation of<br />

quality control protocols.<br />

• Focused attention on areas of greatest hydrogeological<br />

uncerta<strong>in</strong>ty.<br />

The follow<strong>in</strong>g are some of <strong>the</strong> research, data collection and<br />

mapp<strong>in</strong>g programs be<strong>in</strong>g undertaken <strong>in</strong> bas<strong>in</strong> jurisdictions:<br />

• In 2000, Ontario restarted a prov<strong>in</strong>ce-wide 450-well<br />

monitor<strong>in</strong>g program with costs shared between <strong>the</strong><br />

prov<strong>in</strong>cial government and conservation authorities.<br />

With fund<strong>in</strong>g from a new carbon tax, Quebec <strong>in</strong> 2008<br />

re-established its groundwater monitor<strong>in</strong>g network.<br />

• Michigan is now digitiz<strong>in</strong>g approximately 400,000<br />

well logs. When completed, <strong>the</strong> data will greatly<br />

improve capacity to del<strong>in</strong>eate aquifers and model<br />

groundwater processes. However, quality assurance<br />

and quality control issues persist.<br />

• The United States Geological Survey (USGS) has<br />

embarked on a pilot study of water availability <strong>in</strong><br />

<strong>the</strong> U.S. portion of <strong>the</strong> <strong>Great</strong> <strong>Lakes</strong> Bas<strong>in</strong> (USGS,<br />

2008). The study focuses on understand<strong>in</strong>g <strong>the</strong><br />

dynamics of water quantity <strong>in</strong> <strong>the</strong> bas<strong>in</strong>, <strong>in</strong>clud<strong>in</strong>g<br />

flows and yields of both ground and surface water.<br />

• The Geological Survey of Canada has developed<br />

an <strong>in</strong>teractive Web-based geologic mapp<strong>in</strong>g tool<br />

that can be used for extensive characterization on<br />

a site-by-site basis. The tool also helps communicate<br />

f<strong>in</strong>d<strong>in</strong>gs to <strong>the</strong> public, by allow<strong>in</strong>g a user<br />

to “see” aquifer prospects at specific sites. It has<br />

only been used on a limited basis. For <strong>the</strong> Oak<br />

Ridges Mora<strong>in</strong>e area near Toronto (10,000 km2),<br />

geological content was collected over 10 years at a<br />

cost of $1 million per year.<br />

• The USGS undertook detailed model<strong>in</strong>g of <strong>the</strong><br />

groundwater system <strong>in</strong> sou<strong>the</strong>astern Wiscons<strong>in</strong>,<br />

adjacent to Lake Michigan. Results established<br />

<strong>the</strong> major features of <strong>the</strong> groundwater system <strong>in</strong><br />

<strong>the</strong> region and quantified <strong>the</strong> impact of municipal<br />

pump<strong>in</strong>g from <strong>the</strong> complex system of aquifers<br />

<strong>in</strong> <strong>the</strong> area. Municipal pump<strong>in</strong>g <strong>in</strong> this region of<br />

Wiscons<strong>in</strong> and Ill<strong>in</strong>ois has created a “world-class<br />

drawdown cone” <strong>in</strong> <strong>the</strong> sandstone aquifer, with<br />

water level decl<strong>in</strong>es of more than 250 m. Pump<strong>in</strong>g<br />

has shifted <strong>the</strong> divide <strong>in</strong> <strong>the</strong> aquifer to <strong>the</strong> west,<br />

far<strong>the</strong>r away from Lake Michigan, and also has<br />

caused some deterioration <strong>in</strong> water quality,<br />

particularly with respect to radium and radon<br />

concentrations. The USGS model<strong>in</strong>g will be used<br />

to help resolve water management issues <strong>the</strong>re.<br />

3. <strong>Groundwater</strong> Quality<br />

<strong>Groundwater</strong> quality is generally very good but is<br />

threatened <strong>in</strong> many locations <strong>in</strong> <strong>the</strong> <strong>Great</strong> <strong>Lakes</strong> Bas<strong>in</strong>.<br />

<strong>Groundwater</strong> contam<strong>in</strong>ation is a threat to <strong>the</strong> health<br />

of residents <strong>in</strong> <strong>the</strong> bas<strong>in</strong> via <strong>the</strong>ir dr<strong>in</strong>k<strong>in</strong>g water.<br />

Contam<strong>in</strong>ated groundwater is also a source of surface<br />

water contam<strong>in</strong>ation.<br />

Threats to groundwater quality come from po<strong>in</strong>t<br />

sources and non-po<strong>in</strong>t sources. These sources are<br />

generally localized but occur <strong>in</strong> all jurisdictions and<br />

affect <strong>the</strong> bas<strong>in</strong>’s water resources at a regional scale.<br />

These sources <strong>in</strong>clude: fail<strong>in</strong>g septic systems, leak<strong>in</strong>g<br />

underground storage tanks, landfills, hazardous<br />

waste sites, abandoned wells, leak<strong>in</strong>g sanitary sewers,<br />

conf<strong>in</strong>ed animal feed<strong>in</strong>g operations, land application<br />

of septage and manure, agricultural practices, spills,<br />

urbanization (atmospheric deposition, <strong>in</strong>filtration of<br />

vehicle fluids, de-ic<strong>in</strong>g practices), cemeteries, petroleum<br />

ref<strong>in</strong>eries and <strong>in</strong>jection wells.<br />

Specific threats to groundwater <strong>in</strong> <strong>the</strong> bas<strong>in</strong> <strong>in</strong>clude:<br />

pathogens, nutrients, toxic chemicals (<strong>in</strong>clud<strong>in</strong>g chlor<strong>in</strong>ated<br />

solvents, petroleum-based products, pesticides,<br />

metals, radionuclides), household products, hormones,<br />

antibiotics, pharmaceuticals and road salt.<br />

Due to <strong>the</strong> vast number of sources and threats, it was<br />

necessary to limit <strong>the</strong> focus of our study. The issues<br />

<strong>in</strong> Appendices B through K were selected due to <strong>the</strong>ir<br />

press<strong>in</strong>g and substantial nature. The most significant<br />

ones are highlighted below, with <strong>the</strong> full reports <strong>in</strong> <strong>the</strong><br />

appendices. O<strong>the</strong>r activities affect<strong>in</strong>g groundwater,<br />

<strong>in</strong>clud<strong>in</strong>g landfills, cemeteries and road kill carcass<br />

burial, airborne deposition, pit and quarry operations,<br />

water bottl<strong>in</strong>g operations and ethanol production<br />

should not be forgotten, and as more data are ga<strong>the</strong>red<br />

could be <strong>the</strong> subject of future reports.

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