xvEPA

United States
Environmental Protection
Agency

Public comment period

EPA will accept comments on its
revised cleanup plan proposal during
the public comment period that runs
from Nov. 15 to Dec. 15. Written
comments may be submitted through
these methods:

•	By mail (see enclosed
comment form).

•	Electronically via the Web
at www.epa.gov/region5/
publiccomment/oconomowoc-
pubcomment.htm.

•	By fax to Susan Pastor at
312-385-5344.

•	E-mail to Susan Pastor at
pastor.susan@epa.gov.

Potential public meeting

If there is sufficient interest, EPA
will hold a public meeting on this
proposed plan so the public can ask
questions and provide comments.
Contact Susan Pastor by Nov. 22 to
request a meeting.

For more information

Susan Pastor

Community Involvement Coordinator
800-621-8431, Ext. 31325,
9 a.m. - 4:30 p.m., weekdays
pastor.susan@epa.gov

Bill Ryan

Remedial Project Manager
800-621-8431, Ext. 34374,
9 a.m. - 4:30 p.m., weekdays
ryan. williamj @epa.gov

Aristeo Pelayo
WDNR Project Manager
608-267-3539

aristeo.pelayo@wisconsin.gov

EPA Proposes Revisions
to Cleanup Plan	

Oconomowoc Electroplating Co., Inc

Ashippun, Wisconsin	November 2010

U.S. Environmental Protection Agency and state partner Wisconsin Department
of Natural Resources want to revise the original cleanup plan for the
Oconomowoc Electroplating Co., Inc. site because the active treatment system
is no longer effective in removing the leftover contamination. Under Superfund
law, EPA needs to officially amend the original cleanup plan called a "record of
decision."7 This proposed plan fact sheet outlines the site history, explains the
recommended changes to the original plan, describes the cleanup alternatives
that were considered, and discusses the pros and cons of making changes to the
original cleanup plan.

In 1990, EPA adopted a plan for cleaning up on-site ground water (underground
supply of fresh water) that was contaminated by toxic metals and volatile organic
compounds, commonly known as VOCs. The VOCs included trichloroethylene
or TCE, used in electroplating and degreasing operations, and vinyl chloride,
produced when TCE degrades in the natural environment. EPA documented that
plan in a record of decision or ROD, and based on new information, expanded
that plan in 1991 to include cleanup goals for the wetlands and nearby Davy
Creek. EPA expanded the plan again in 1994 to accommodate the removal of the
abandoned electroplating building and hazardous chemicals inside.

The 1991 cleanup plan for the Oconomowoc site included a ground water
pumping system to remove contamination, which had been pumping and
treating contaminated ground water from 1997 until 2004 when the system was
shut down after EPA determined it was no longer effective. The type of soil at
the site limits the ability of the ground water treatment system to remove the
contamination. EPA and WDNR shut down the system based on these findings:

•	The ground water treatment system has removed much of the
contamination but some remains in certain places where pumping is no
longer effective.

•	Conditions in the ground water are favorable for bacteria that naturally
eliminate TCE and other contaminants.

Since shutdown of the treatment system, this process of "natural attenuation" has
been lowering TCE concentrations. Natural attenuation means that a variety of
physical, chemical, or biological processes are acting without human intervention
to reduce the amount and limit the expansion of contamination in the ground
water. With natural attenuation as effective at the site as the more expensive
active pump-and-treat system, the 1990 record of decision needs to be officially
amended. EPA and WDNR recommend a revised cleanup plan that includes
monitored natural attenuation, or MNA, because it is not part of the 1990 plan.

Site history

The 10.5-acre Oconomowoc site includes the former electroplating plant,
waste lagoons and a section of wetlands. The property is located in the
unincorporated town of Ashippun, a rural area about 35 miles west of

1 Section 117(a) of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA,
known as the Superfund Law) requires publication of a notice describing the proposed modifications to
the cleanup plan. Information supporting the decision, such as the focused feasibility study, must also be
made available to the public for comment. This fact sheet is a summary of information contained in the
administrative record for the Oconomowoc Electroplating Co., Inc. site.


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Figure 1 - Site Location Map

Info repository

Site-related documents and files may
be viewed at:

Ashippun Town Hall
W1266 Highway 0
Oconomowoc, Wis.

An administrative record, which
contains detailed information that will
be used in the selection of the cleanup
plan, is located at Ashippun Town Hall,
Oconomowoc Public Library, 200 W.
South St., and at EPA's Chicago office.

On the Web

www.epa.gov/region5/sites/oconomowoc

Milwaukee. The industrial facility used metals, chemicals
and organic compounds in its production process from
1957 to the early 1980s. During that time the company
discharged untreated wastewater into nearby wetlands
and Davy Creek. Two unlined lagoons on the property
contained electroplating sludge. These lagoons leaked and
sometimes overflowed. Contaminants made their way into
the ground water beneath and downstream of the site. After
the plant closed, the location was added to the National
Priorities List, a roster of the nation's most hazardous waste
sites eligible for cleanup under EPA's Superfund program.
Environmental investigations began in the mid-1980s.

Current plan

The current cleanup, plan adopted in 1990, involved
cleaning up the vacated buildings, soil, lagoons, Davy
Creek and wetlands on the site. Based on that approved
plan, from 1992 to 1996 EPA removed dilapidated
buildings; installed a fence around the property; removed
and disposed of soil contaminated with heavy metals;
pumped out and treated contaminated ground water and
lagoon water; removed and disposed of contaminated
concrete and sludge from the lagoons; removed and
disposed of contaminated sediment (mud) from the creek
and lagoons; and removed and disposed of some plant
material from the wetlands and portions of the creek. As a
result, the levels of metals in the ground water were greatly
decreased. By the summer of 2002, they were low enough
that EPA and WDNR decided to stop treating metals with
the ground water treatment system.

Summary of cleanup alternatives

Since shutdown of the ground water treatment system,
EPA evaluated additional cleanup alternatives for the
Oconomowoc site. The potential alternatives included
various treatment options to reduce the toxicity, mobility,
or volume of wastes.

Based on the risks present at the site and the cleanup

options available, the following five alternatives were
assembled and then evaluated against nine criteria required
by federal law (see P. 3 box for explanation of criteria).
Alternative 1—No Further Action

EPA uses the no-action option as a baseline for comparison
of other cleanup alternatives. Alternative 1 does not
include any further ground water cleanup, monitoring
or other site controls. The cost will cover reviews of the
site every five years as required by the Superfund law.

Cost: $77,000 *

Alternative 2—Monitored Natural Attenuation (MNA)

Alternative 2 relies on MNA to use natural processes
to treat ground water contaminants. Based on site data,
conditions are favorable for removal of VOCs through
biological processes. This alternative also includes
sampling at various locations to ensure that MNA continues
to work until cleanup goals are met. Cost: $1.3 million

Alternative 3—Source Removal or In-Place Treatment

and MNA (this is EPA's recommended cleanup method)

Under Alternative 3, source areas would be investigated to
determine the extent of contamination. This information
would then be used to select either excavation or in-place
chemical treatment to enhance source-area biological
activity and further remove VOCs. This alternative also
includes MNA from Alternative 2. Cost: $1.2 million

Alternative 4—Source Removal or In-Place Treatment,
Ground Water Extraction and Treatment, and Long-
Term Monitoring

Alternative 4 targets the source areas by excavation or
in-place chemical treatment, similar to Alternative 3.

This would be followed by ground water extraction and
treatment, which targets the remaining VOCs. A long-
term monitoring program would then be implemented that
evaluates natural attenuation and ensures compliance with
state and federal standards. Cost: $2.2 million

OECI Property Boundary

OECI Ground Water
Treatment Facility

Davy Creek
Area

Former Location of
Electroplating Building

2


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Figure 2 - EPA's proposed plan includes permanently shutting
down its pump and treat system in the town of Ashippun.

Evaluation criteria

EPA uses nine criteria to evaluate cleanup options. A table
comparing the alternatives against these criteria is on the
next page.

1.	Overall protection of human health and the
environment addresses whether an option adequately
protects human health and the environment. This criterion
can be met by reducing or eliminating contaminants or by
reducing people's exposure to them.

2.	Compliance with applicable or relevant and
appropriate requirements, referred to as ARARs,
ensures that each project complies with federal, state, and
local laws and regulations.

3.	Long-term effectiveness and permanence evaluates
how well an option will work in the long term, including
how safely remaining contaminants can be managed.

4.	Reduction of toxicity, mobility, or volume through
treatment addresses how well the cleanup option
reduces the harmful effects, movement, and amount of
contaminants through permanent treatment methods.

5.	Short-term effectiveness evaluates how quickly the
cleanup can be done, as well as its potential impacts on
cleanup workers, area residents, and the environment.

6.	Implementability evaluates the technical difficulty in
building and operating the cleanup system and whether
materials and services are routinely available to complete
the project.

7.	Cost includes estimated capital or startup costs. An
example is the cost of buildings, treatment systems and
monitoring wells. It also considers cost to implement the
cleanup and operate and maintain it over time. Examples
include laboratory analysis, repairs, and personnel hired to
operate equipment. A cleanup is considered cost effective
if its costs are proportionate to its overall effectiveness.

8.	State acceptance is whether the state environmental
agency, in this case WDNR, agrees with EPA's
recommended option.

9.	Community acceptance evaluates if the community
near the site accepts the option. EPA and WDNR

will evaluate community acceptance after the public
comment period.

Alternative 5—Source Removal or In-Place Treatment,
Nutrient Injection, and MNA

Alternative 5 targets the source areas by excavation or
in-place chemical treatment, similar to Alternative 3.

This would be followed by biological treatment of the
VOC contaminants. MNA, as described in Alternative
2, along with long-term monitoring of the ground
water contaminants would also be done. An alternate
water supply for nearby residents would be included if
contaminant levels in private wells rise to unsafe levels.
Cost: $980,000

Comparing the current and proposed plans

EPA evaluated the two cleanup plans (1990 plan versus the
revised plan) against several evaluation criteria required
by law (see the box explaining the criteria on this page and
the table comparing the two plans on the back page). State
and community acceptance will be evaluated after the
public comment period. The table shows how the current
and proposed plans meet EPA's evaluation criteria.

This revised plan would be equally effective in protecting
people and the environment over the long term. Both plans
comply with state and federal laws. Both also require some
site controls such as barring residential use for areas where
soil was cleaned up and prohibiting ground water use
until cleanup goals are met. The revised plan will require
continued long-term monitoring and controls. Both plans
would meet EPA's cleanup goals and provide long-term
effectiveness. The revised plan, however, may take less
time to complete, is easier to implement, and costs less.

Recommended cleanup alternative

EPA's recommended alternative for cleaning up the
Oconomowoc Electroplating Co., Inc. site is Alternative 3
because it will remove contaminated materials, protect
human health and the environment, provide long-term
reliability, and comply with state and federal regulations in
a cost-effective manner.

Revised cleanup plan

Under the revised cleanup plan proposed by EPA and
WDNR, the ground water treatment system would remain
shut down and MNA would be allowed to work after either
excavation or in-place chemical treatment was completed.
Since 2004, ground water monitoring has shown steady or
declining contaminant levels in key monitoring wells. EPA
determined that conditions are favorable for MNA after
confirming the presence of bacteria that break down the
contamination. The site would still be monitored to make
sure VOC levels continue to decrease. EPA will also put
into place site controls, such as barring residential use for
areas where soil was cleaned up and prohibiting ground
water use until cleanup goals are met.

EPA and WDNR encourage the public to comment on the
revised cleanup plan. Based on public comments, they
can modify the proposed plan, choose a new plan, or keep

3


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Evaluating the cleanup alternatives

Evaluation Criteria

Alternative 1*

Alternative 2

Alternative 3
(recommended alternative)

Alternative 4

Alternative 5

Overall protection of human health and the environment

~

¦

¦

¦

¦

Meets federal and state requirements

~

¦

¦

¦

¦

Long-term effectiveness and permanence

¦

¦

¦

¦

¦

Reduction of toxicity, mobility, or volume through treatment

~

¦

¦

¦

¦

Short-term effectiveness

~

¦

¦

¦

¦

Implementability

¦

¦

¦

¦

¦

Cost (Present worth)

$77,000

$1.3 million

$1.2 million

$2.2 million

$980,000

State acceptance

Will be evaluated after the public comment period

Public acceptance

Will be evaluated after the public comment period

¦ Fully meets criteria	~ Does not meet criteria

* Alternative 1—No Action was dropped from consideration because it does not protect human health and the environment.

the cleanup plan as proposed. Read the left-hand box on
Page 1 to find out how you can participate in the decision-
making process.

Next steps

EPA, in consultation with WDNR, will evaluate all
comments received during the public comment period
before deciding whether to adopt the revised plan.
Responses to public comments will be in a document
called a responsiveness summary that is typically attached
to the final record of decision amendment. The final

cleanup decision will be announced in a local newspaper
and a copy of the amendment will be sent to the Ashippun
Town Hall for public review. The amendment will also be
posted at www.epa.gov/region5/sites/oconomowoc.

After a final plan is selected, contractors will monitor the
cleanup with oversight by EPA and WDNR. They will also
oversee institutional controls, such as deed restrictions, to
minimize residents" possible exposure to contamination in
the future.

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Comment Sheet

EPA is interested in your comments 011 the revised cleanup plan for the Oconomowoc Electroplating Co., Inc. site.
EPA will consider public comments before selecting a final cleanup plan. Please use the space below to write your
comments, then fold and mail this form. Comments must be postmarked by December 15. If you have general
questions, contact EPA Community Involvement Coordinator Susan Pastor at 800-621-8431, Ext. 31325. Those
with Internet access may submit their comments to EPA at www.epa.gov/region5/publiccomment/oconomowoc-
pubcomm ent .htm.

Name	

Address	

City	State

Zip


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Fold on Dashed Lines, Tape, Stamp, and Mail

Name 	

Address 	

City 	State

Zip 	

Place
Stamp
Here

Susan Pastor

Community Involvement Coordinator
EPA Region 5 (SI-7J)

77 W. Jackson Blvd.

Chicago, IL 60604-3590


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