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Groundwater in the Great Lakes Basin

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The cost of plugg<strong>in</strong>g abandoned water wells is largely<br />

dependent on <strong>the</strong> geology of <strong>the</strong> area, <strong>the</strong> type of well<br />

and if <strong>the</strong>re has been any contam<strong>in</strong>ation (Michigan<br />

DEQ, 2005). If <strong>the</strong> proper steps for plugg<strong>in</strong>g wells are<br />

taken before contam<strong>in</strong>ation occurs, <strong>the</strong> costs can be<br />

significantly reduced. The cost of plugg<strong>in</strong>g a typical<br />

residential abandoned well generally ranges from $300<br />

to $700. The cost is significantly higher for plugg<strong>in</strong>g<br />

public water supply wells, rang<strong>in</strong>g from $2,000 to<br />

$10,000 (McEwan, 2006). A number of programs have<br />

been established to provide f<strong>in</strong>ancial aid to owners <strong>in</strong><br />

order to properly close abandoned wells. For example,<br />

<strong>the</strong> Clean Michigan Initiative awarded over $3 million<br />

<strong>in</strong> grants to 64 communities <strong>in</strong> 2005 (McEwan, 2006).<br />

Significant numbers of abandoned wells have been<br />

deemed “orphan wells.” These wells do not have a<br />

viable owner or an owner who does not have sufficient<br />

funds to pay for <strong>the</strong> proper decommission<strong>in</strong>g and reclamation<br />

of <strong>the</strong> site (Turcza, 2004). These sites result <strong>in</strong><br />

significant expenses be<strong>in</strong>g placed on <strong>the</strong> government<br />

and states. In <strong>the</strong> United States <strong>the</strong>re are more than<br />

57,000 orphan oil and gas wells (Turcza, 2004). With<br />

an average clos<strong>in</strong>g cost of $5,400, it is estimated that<br />

over $560 million will be needed to properly plug <strong>the</strong>se<br />

known wells (Turcza, 2004). The number of orphan<br />

wells <strong>in</strong> Canada is unknown but Environment Canada<br />

estimates it to be <strong>in</strong> <strong>the</strong> thousands (Environment<br />

Canada, 2004). In Pennsylvania <strong>the</strong>re are estimated to<br />

be 7,500 orphan wells. The cost to <strong>the</strong> state to properly<br />

close <strong>the</strong>se known orphan sites is over $64 million.<br />

Also, over 184,000 additional wells are believed to exist<br />

with unknown status and location, likely <strong>in</strong>creas<strong>in</strong>g<br />

<strong>the</strong> number of orphan sites (Pennsylvania Department<br />

of Environmental Protection, 1998). Proper well clos<strong>in</strong>g<br />

can be much more costly. For example, <strong>the</strong> Peace River<br />

Well <strong>in</strong> Alberta, drilled <strong>in</strong>to a high-pressure sal<strong>in</strong>e<br />

aquifer, cost over $6 million to be properly decommissioned<br />

(Turcza, 2004).<br />

Large numbers of abandoned wells whose locations<br />

are unknown, and may never be known, exist across<br />

<strong>the</strong> U.S. and Canadian <strong>Great</strong> <strong>Lakes</strong> Bas<strong>in</strong>. A number<br />

of key identifiers can be used to determ<strong>in</strong>e if <strong>the</strong>re is<br />

an abandoned well on a property (Figure 14). The first<br />

step is to try to f<strong>in</strong>d old drill<strong>in</strong>g records or bill<strong>in</strong>g statements<br />

that would <strong>in</strong>dicate <strong>the</strong> depth and location of a<br />

well (Michigan DEQ, 2005). Often, <strong>the</strong>re are no records<br />

of older wells and o<strong>the</strong>r means must be used to discover<br />

<strong>the</strong>ir locations (Michigan DEQ, 2005; Shortt, 2004).<br />

These <strong>in</strong>clude:<br />

• Distressed vegetation<br />

• Settled ground<br />

• Oily or salty water seeps<br />

• Smell of natural gas or crude oil (sulphurous<br />

odour)<br />

• Water well contam<strong>in</strong>ated with hydrocarbons<br />

Figure 14.<br />

Old w<strong>in</strong>dmills are beacons for<br />

locat<strong>in</strong>g abandoned water wells<br />

Photo by: D.W. Alley, 2007.<br />

• Piles of rock and o<strong>the</strong>r debris<br />

• Concrete slabs and old foundations<br />

• Metal pipes protrud<strong>in</strong>g from <strong>the</strong> ground (both<br />

<strong>in</strong>doors and outdoors)<br />

• Old pumps<br />

• Electrical switch boxes<br />

• Hand pumps<br />

• Old barns, w<strong>in</strong>dmills, pump houses and o<strong>the</strong>r brick<br />

or stone structures<br />

Unfortunately, discover<strong>in</strong>g abandoned wells can sometimes<br />

be difficult or nearly impossible. Wells get built<br />

and paved over. Because many people view abandoned<br />

wells as eyesores, pipes are sawed off below ground<br />

level often leav<strong>in</strong>g only a slight ground depression to<br />

<strong>in</strong>dicate <strong>the</strong>ir presence. The use of metal detectors can<br />

sometimes aid <strong>in</strong> <strong>the</strong>ir discovery and resistivity, and<br />

magnetics were utilized <strong>in</strong> a recent study as a costeffective<br />

method for locat<strong>in</strong>g abandoned wells (Borton,<br />

V<strong>in</strong>cent and Onasch, 2007; Michigan DEQ, 2005).<br />

RECOMMENDED ACTION<br />

Several measures must be implemented to help alleviate<br />

<strong>the</strong> stresses and dangers that improperly abandoned<br />

wells are plac<strong>in</strong>g on groundwater quality <strong>in</strong> <strong>the</strong> <strong>Great</strong><br />

<strong>Lakes</strong> Bas<strong>in</strong>:<br />

103

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