&EPA

United States
Environmental Protection
Agency

ARSENIC IN DRINKING WATER
COMPLIANCE SUCCESS STORIES

Wisconsin: Geologic Solution for
Private Wells in Outagamie and
Winnebago Counties

Case Study Contact Information

Tom Riewe

(thomas.riewe@dnr.state.wi.us)

Wisconsin Department of Natural Resources
(608) 266-8697

The experiences of Wisconsin Department of Natural Resources (DNR) show that
stringent construction standards and requirements for private wells (in Outagamie and
Winnebago counties) successfully reduced the number of private wells with elevated
levels of arsenic.

Background

In northeastern Wisconsin, arsenic in the groundwater is associated with two types of
bedrock aquifers - the St. Peter sandstone and the Prairie du Chien Dolomite. Both of
these aquifers are tapped by many water wells. The arsenic may be released to well water
at high concentrations when it is exposed to air, primarily through the well drilling
process and through the lowering of the regional water table.

In 1987, arsenic contamination of groundwater supplies was first discovered in northeast
Wisconsin as part of a routine feasibility study for a proposed landfill. Sampling results
for private wells adjacent to the landfill showed that several wells had arsenic levels >5
ppb.

Further sampling from 1997 to 2000 revealed that 24% of samples had arsenic levels >10
ppb, and 7% of samples had arsenic levels >50 ppb based on 1,661 samples.


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In 2000 and 2001, the county public health departments conducted sampling surveys to
further evaluate arsenic levels in private wells constructed in the 1990s. These sampling
results showed that of 3,905 wells sampled, 3% had arsenic concentrations >50 ppb and
20% had arsenic levels >10 ppb.

County statistics

Outagamie County

Winnebago County

Total population

155,000

160,177

Population served by public water

139,500

120,133 (75%)

supply

(90% total population)



Population served by private wells

15,500 (10%)

40,044 (25%)

Treatment Alternatives

A coagulation/pressure filtration system was considered as an alternative to the
coagulation/microfiltration treatment system but was found to be more expensive as
shown in Table 1. The pressure filtration alternative has a higher estimated capital cost
but lower annual O&M costs. The pressure filtration alternative also has a higher unit
cost of water produced based on a present worth analysis of capital and O&M costs ($ per
1,000 gallons produced).

Non-Treatment Alternatives

In 1993, the Wisconsin DNR first established an Arsenic Advisory Area, a 10-mile wide
strip through both counties where special well construction methods were recommended
to reduce or eliminate arsenic contamination. From 1993 to 2004, few wells were
constructed to these standards, however, because the recommended deeper well casings
were too expensive and not a requirement.

In response to the high levels of arsenic found in the 2000-2001 sampling survey, the
county public health departments issued advisories to well owners on the arsenic testing
results and the possible health impacts. The advisory gave well owners two options -
they could install an arsenic treatment system on their existing well, or drill a new well
according to county standards that specify well casing depths to assure that the well water
is not drawn from the arsenic-laden bedrock. Various options for providing alternate
water supplies are summarized in Table 1. Note the estimated costs are shown as a range
since the cost for developing a well will vary based on the required well casing depth for
a particular site.


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Table 1

Non-Treatment Options for Individuals and Communities in Outagamie and

Winnebago Counties, Wisconsin

Option

Advantages

Disadvantages

Cost

New

Homeowner has

High initial cost due to extra

$7,000-17,000

individual

control of water

casing and other construction

per home

well (deep

supply; effective for

requirements; well owner



aquifer)

minimizing arsenic

responsible for water testing.





level if







specifications







followed.





New

Lower initial costs

This option is only available in

$4,000-7,000

individual

than deep well;

certain areas; water supply is

per home

well (shallow

homeowner has

more susceptible to surface



aquifer)

control of water

contamination; water





supply.

conservation is required







because shallow aquifer may







not provide adequate supply;







well owner responsible for







water testing.



Shared, cluster

Lower initial costs

Homeowners need to agree to

$4,000-7,000

well for 2-6

per home than an

share well (contract is

per home

homes (deep

individual well;

advised); water use may not be



aquifer)

effective for

proportional among





minimizing arsenic

homeowners; water testing by





level if

homeowners; well location





specifications

may affect subdivision layout;





followed.

potential legal issues on







sharing costs.



Connection to

Regulated supply of

High initial costs; homeowner

Initial costs

public water

safe drinking water,

pays annual water bill.

vary

supply

fluoridation;







improved aesthetic







water quality (iron,







manganese)





Well Construction and Disinfection Standards

In 2004, the DNR created a "Special Well Casing Depth Area" under the provisions of
the State Private Well Code (NR 812.12(3)). The special area includes all of Outagamie
and Winnebago counties. The DNR decided to apply stringent requirements to all of
Outagamie and Winnebago counties because these specifications worked satisfactorily
for replacement wells funded by DNR's Well Compensation program (described below
under Funding Process).


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All new wells drilled within this area are required to meet the following stringent
standards for well construction, grouting, and disinfection:

1.	Private wells must be constructed with a cement-grouted steel casing that extends
at least to the top of the Cambrian sandstone aquifer which lies below the St. Peter
sandstone. Township maps show the required casing depth for any particular
location.

2.	The well cannot be drilled by a rotary-air method because it allows too much air
into the subsurface zone and may cause arsenic to be released to the groundwater.
The allowed drilling methods include rotary-mud circulation and cable-tool
methods.

3.	The cement grouting must meet stringent specifications as outlined in the new
law.

4.	Disinfection standards, designed to minimize oxidation of sulfide minerals,
require use of a liquid bleach solution at a low chlorine concentration.

The complete specifications can be viewed at the following website: Special Casing Area
Requirements for Arsenic - Well Construction Specifications I exit Disclaimer]

All new private wells drilled in Outagamie and Winnebago counties
are required to meet stringent standards for well construction, grouting,
and disinfection to prevent arsenic contamination.

In the first year after the new specifications went into effect, 131 wells
were constructed according to the more stringent specifications. Only
eight of these (6%) produced water with arsenic concentrations
exceeding the new drinking water standard of 10 ppb. None of these
wells produced water with arsenic concentrations exceeding 50 ppb.

Treatment Alternatives

As an alternative to drilling a new well or connecting to the public water supply, private
well owners have the option of installing a treatment system such as a point-of-use
reverse osmosis system to remove arsenic from an existing well. For treatment to be
effective, regular system maintenance is required. The costs to install a treatment system
for a private well range from $4,000 to $7,000 for the equipment plus annual
maintenance costs of $400 to $500.

Funding Process

Wisconsin has a Well Compensation Program to assist private well owners in replacing
contaminated wells including wells contaminated with arsenic at concentrations higher
than 50 ppb. Grant recipients must also meet income eligibility criteria. Grants may be
used for the following purposes:

•	Develop a new well that meets DNR's specifications;

•	Reconstruct an existing well to the new specifications;


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•	Connect to a nearby well that meets DNR's specifications; or

•	Connect to a community water supply.

If none of the alternate water supply options are feasible, grants may be used to install a
treatment system to reduce arsenic levels in the existing well.

Conclusion

The Wisconsin Department of Natural Resources has developed a unique solution to
reduce arsenic contamination of private wells in Outagamie and Winnebago counties. All
new wells must be developed using stringent construction standards including a site-
specific well casing depth to ensure that water will not be drawn from the St. Peter
sandstone aquifer or the Prairie du Chien Dolomite aquifer which are both sources of
arsenic. Sampling results show a reduced number of new private wells have arsenic levels
greater than 10 ppb since the new requirements were implemented. Private well owners
that need to replace a well due to arsenic contamination may be eligible for a state grant.
Alternatives to developing a new well include connection to a public water system,
connection to a shared cluster well, and installing treatment for the existing well.

For More Information

Naturally Occurring Arsenic in Well Water in Wisconsin Iexit Disclaimer]

Special Casing Area Requirements for Arsenic IlllpilcIIImii]


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