vvEPA

United States
Environmental Protectior
Agency

Share your opinion

EPA encourages you to comment on
this proposed plan. The Agency will
only select a final cleanup plan after
reviewing comments received
during the public comment period,
which runs from March 28 -
September 2, 2016.

There are several ways to submit
comments:

•	Orally or in writing at the
public meeting (see

below).

•	Fill out and mail the enclosed
comment sheet to Heriberto Leon.

•	Send an email to Heriberto
Leon at

leon.heriberto@epa.gov.

•	Fax your comments to
Heriberto Leon at 312-
697-2754.

Attend a public meeting

There will be public meeting to
discuss the cleanup:

Wednesday, August 10
6:30 p.m.

Cass Lake-Bena Elementary School
15 4th St. NW
Cass Lake
After a brief presentation, EPA
officials will hold a public
hearing to accept comments on
the proposed cleanup plan. A
court reporter will record all
public comments.

(See EPA contact information on
P. 3)

Cleanup Plan Removes Pollution
From Residential Area	

St. Regis Paper Co. Superfund Site

Leech Lake Reservation, Cass County, Minnesota June 2016

The U.S. Environmental Protection Agency is proposing a plan to clean up
soil contamination in the residential areas at the St. Regis Paper Co. site on
the Leech Lake Band of Ojibwe Reservation. EPA refers to the residential
areas as "Operable Unit 7," or OU7. To help keep track of the different
cleanup areas at the wide-ranging site, sections were assigned operable unit
numbers. The contaminants of concern include dioxin and polycyclic
aromatic hydrocarbons, or PAHs. (See Summary of site risks on Page 2.)

The following steps are proposed as part of the cleanup plan:1

•	Removing contaminated soil from affected residential areas and
replacing it with clean soil.

•	Managing most of the removed soil at an on-site facility.

•	Disposing a small amount of heavily contaminated soil at an off-site
facility.

•	Monitoring soil stored on-site.

EPA arrived at this recommendation after extensive study of the site and after
considering a number of cleanup alternatives in consultation with Minnesota
Pollution Control Agency and tribal officials. The LLBO, however, does not
fully support EPA's recommendation.

The cleanup steps described in this fact sheet represent Alternative S15-B (see
Page 3), which is EPA's recommended option. This cleanup option protects
people and the environment, meets the applicable regulations, is cost-effective
and will be effective in the long term.

Background

The St. Regis site is in Cass Lake within the boundaries of the Leech Lake
Band's reservation. The site is the location of a former Champion International
Inc. facility now owned by International Paper Co. The property included a
former operations area located on 125 acres south of the BNSF railroad tracks
and east of Highway 371.

Creosote and other chemicals were used to treat wood, and wastewater was
placed in ponds and occasionally used for irrigation. Sludge from the wood
treatment process was disposed of on the eastern edge of the site and was also
burned in a waste pit at the Cass Lake city dump.

In 1984, EPA placed the site on the National Priorities List, making it
eligible for cleanup under EPA's Superfund program. The site is divided into
four primary sections:

•	OU1 consists of the northern former facility operations area.

•	OU2 is the former operations area southwest of OU 1 and the location
of an on-site contaminated soil vault.

1Section 117(a) of the Comprehensive Environmental Response, Compensation, and
Liability Act (CERLCA, known as the Superfund law) requires the publication of a notice
announcing the proposed plan. It also requires a public hearing and public comment
period. This fact sheet summarizes the technically written proposed plan and other site-
related environmental reports that can be viewed at the information repositories listed in
the box on the back page and the EPA Region 5 office in Chicago.


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•	0U3 is the city dump area.

•	0U7 is the residential neighborhood next to
the former operations areas and the LLBO
Department of Resource Management
property. This is the area targeted in this
proposed cleanup plan.

EPA early response actions

Several cleanup activities have been done since EPA
became the lead agency for the site in 1995. In 2000,
EPA issued a Five-Year Review report for the site in
which the Agency raised concerns about remaining
contaminant levels in site soil. In 2001, EPA
sampled site soil, sediment (mud), surface water,
fish and groundwater (underground water supplies)
to look for contamination.

In 2003 and 2004, EPA required International Paper
to collect additional samples and prepare a Human
Health and Ecological Risk Assessment to find out
what effects the contamination may have on people
and the environment.

Between 2004 and 2006, more than 3,900 tons of
contaminated soil were removed from the site on
city-owned, BNSF Railway and commercial
property. Clean soil was put in the locations where
contaminated soil was removed. Other areas were
covered or fenced to reduce exposure to the
pollution.

In 2005, EPA found indoor dust samples collected from
five homes were above EPA's safe levels for dioxin.
EPA issued a cleanup plan that called for cleaning
residence interiors, putting a 3-inch layer of clean soil
and grass on yards and applying dust suppressant to
unpaved roads. IP continues to periodically clean the
inside of affected homes and apply the dust suppressant
to the unpaved roads as required.

In 2011, IP completed a study that estimated the
potential health risks for exposure to site contaminants.
EPA issued a proposed cleanup plan to manage these
potential health risks posed by the contaminated soil. A
final cleanup plan was not issued because MPCA, LLBO
and members of the public requested further soil
sampling to better determine the extent of
contamination.

EPA worked with the LLBO, MPCA, IP and other
interested people to take additional soil samples to better
determine the extent of contamination. IP conducted
additional sampling in 2012 and 2013 and submitted its
findings in November 2013. The additional soil

sampling confirmed EPA's original analysis on what
pollutants were present and how they were distributed.

Summary of site risks

The main way people in and around the St. Regis site are
exposed to potentially harmful pollutants is by direct
contact with dioxin-contaminated soil in the residential
areas.

The contaminants of concern include dioxin and
poly cyclic aromatic hydrocarbons, or PAHs. One of
the groups of PAHs found at the site is expressed in
scientific shorthand as benzo(a)pyrene equivalent, or
B(a)PE. These contaminants are troublesome because
they are persistent and present in soil at concentrations
above what EPA considers safe.

Dioxin was a pollutant in the chemical
pentachlorophenol used at the site in the wood-
treatment process as a preservative and insecticide.

Dioxin can cause skin problems. It has been shown to
be very toxic in animal studies and probably causes
cancer.

PAHs are a group of chemicals formed during the
incomplete burning of coal, oil, gasoline, wood, garbage
or any plant or animal material. They are also found in
cigarette smoke, soot and creosote. Breathing such
chemicals or having long periods of skin contact with
mixtures that contain PAHs can cause cancer. Animal
studies have shown some PAHs caused birth defects and
decreased body weight.

EPA has established cleanup goals for the site. These
are referred to as "preliminary remedial goals," or
PRGs, and are separated into two levels. Level 1 goals
are cleanup levels established by the LLBO for
properties within the reservation, and Level
2-Residential goals are the cleanup levels established to
deal with the site-specific risk from the chemicals of
concern at the site.

Proposed cleanup alternatives

EPA considered six alternatives for cleaning up the
residential surface soil at the St. Regis site, each of which
was evaluated against seven of the nine criteria required
by the Superfund law (see box on Page 4). The table on
the next page gives a description of each alternative.

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Alternative

Description of Alternative

(PRG = preliminary remedial goals)

Estimated
Cost
Soil Disposal
Method A

Estimated
Cost
Soil Disposal
Method B

S10

No action.

$0

$0

Sll

Excavate soil on properties exceeding Level 2-R PRGs.

$12.1 million

$8 million

S12

Excavate soil on properties exceeding Level 2-R PRGs;
place a 12-inch clean soil cover on properties exceeding
Level 1 PRGs.

$14.3 million

$10 million

S13

Excavate soil on properties currently in residential use
exceeding Level 1 PRGs and place a 12-inch clean soil cover
on other properties exceeding Level 1 PRGs.

$13.6 million

$10.3 million

S14

Excavate soil on properties not owned by IP exceeding Level
1 PRGs, and place 12-inch clean soil cover on properties
owned by IP exceeding Level 1 PRGs.

$22.5 million

$15.4 million

S15

Excavate soil exceeding Level 1 PRGs throughout OU7

(EPA preferred option)

$30 million

$18.5 million

All the alternatives except for Alternative S10, the no
action alternative, share some common features:

•	Soil on some or all properties in the residential
area will have to be dug up to the depth needed to
reach the selected PRG. The sections dug up will
have clean soil put back in. The portion would
then be replanted.

•	Each of the alternatives have two methods for
managing the removed soil.

1.	For the 'A" method, the contaminated
dirt removed would be trucked to an off-
site landfill. Before taken off-site, the
soil would be tested to determine what
type of approved disposal facility would
be appropriate.

2.	For the "B" method, the contaminated
dirt removed would be tested to
determine if the soil could be stored on-
site.

•	All residential properties would be suitable for
future residential use.

•	Monitoring and control of air quality (dust) will
be done during the cleanup.

•	Soil samples will continue to be taken from the
residential area until the soil is cleaned up in
OU1 and OU2 to confirm that no
recontamination is occurring.

covered by a layer of uncontaminated fill and top
soil, followed by replanting with vegetation.
Activities in the covered portions of the
residential area would be restricted to
preserve the soil cover. For example, a deed
notice might be filed on a covered property
that notifies future owners of the
contamination below the cover, and prohibits
any digging below the cover unless
precautions are taken.

EPA contact information

Heriberto Leon

Community Involvement Coordinator

312-886-6163

leon.heriberto@epa.gov

Leslie Patterson

Remedial Project Manager

312-886-4904

patterson.leslie@epa.gov

EPA Region 5 toll-free

800-621-8431, 8:30 a.m. - 4:30 p.m., weekdays

Alternatives S12, S13 and S14 also share the following
features:

• In some areas, a clean soil cover will be used to
cover contaminated soil instead of being dug up.
The cover would be made of marker material,

(continued on next page)

3


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EPA's recommended alternative

EPA recommends Alternative S15-B because the
Agency believes this option is the best balance of the
evaluation criteria.

Alternative S15-B protects people and the environment
and it meets applicable rules and regulations by removing
all contaminated soil in the residential area that is above
the LLBO limits, replacing with clean dirt and managing
the soil on-site. A major plus for the S15 options: there
will be no need for any property restrictions in the
residential area under this plan.

Alternative S15-B provides long-term and permanent
protection against exposure to site-related contaminants

by removing the contaminated soil. On-site management
of the excavated soil significantly reduces short-term
impacts due to increased truck traffic that would be
needed if the contaminated soil was taken off-site.

None of the alternatives reduces toxicity, mobility or
volume of contamination through treatment because
effective alternative treatment technologies or
resource recovery technologies are not practical for
large quantities of soil containing low levels of
dioxin contamination. Alternative S15-B is
implementable. Finally, Alternative S15-B meets the
evaluation criteria at a much lower cost than
alternatives that dispose of soil off-site.

Explanation of evaluation criteria

EPA compares each cleanup option or alternative with these nine criteria established by federal law:

1.	Overall protection of human health and the environment examines whether an option protects living things.
This standard can be met by reducing or removing pollution or by reducing exposure to it.

2.	Compliance with applicable or relevant and appropriate requirements, or ARARs, ensures options comply
with federal, tribal, state and local laws.

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

4.	Reduction of toxicity, mobility or volume through treatment determines how well the option reduces the
toxicity (the chemical makeup of a contaminant that makes it dangerous), movement and amount of pollution.

5.	Short-term effectiveness compares how quickly an option can help the situation and how much risk exists while
cleanup is done under this option.

6.	Implementability evaluates how feasible the option is and whether materials and services are available in the area.

7.	Cost includes not only buildings, equipment, materials and labor but also the cost of maintaining the option for
the life of the cleanup.

8.	State and tribal acceptance is whether the state environmental agency, in this case the Minnesota Pollution
Control Agency, and the tribal government, the LLBO, agree or disagree with EPA's recommended
alternative.

9.	Community acceptance considers the opinions of nearby residents and other stakeholders about the proposed
cleanup plan. EPA evaluates this standard after a public comment period.

4


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Public Comment Sheet

Use this space to write your comments

EPA is interested in your comments on the proposed cleanup plan for the St. Regis Superfund site. You may use the space
below to write your comments and hand it in at the public meeting on August 10, 2016, or detach, fold, stamp and mail to EPA
Community Involvement Coordinator Heriberto Leon. Comments must be postmarked by September 2, 2016. If you have
questions, contact Mr. Leon at 312-886-6163, or toll-free at 800-621-8431, Ext. 66163, 8:30 a.m. - 4:30 p.m., weekdays.
Comments may also be emailed to leon.lieriberto@epa.gov or faxed to Mr. Leon at 312-697-2754.

Name:

Affiliation:

Address:

City:
State:

Zip:


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St. Regis Superfund Site - Comment Sheet

Fold on dashed lines, seal, stamp, and mail

Name		

Address		

City		

State			Zip

Heriberto Leon

Community Involvement Coordinator
U.S. EPA Region 5
Superfund Division (SI-7J)
77 W. Jackson Blvd.

Chicago, IL 60604-3590


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Chart comparing cleanup options (Soil Disposal Method A - off-site disposal)



Alternative

Alternative

Alternative

Alternative

Alternative

Alternative

Evaluation Criteria

S10-A

Sll-A

S12-A

S13-A

S14-A

15-A

Overall Protection of













Human Health and the

~

¦

¦

¦

¦

¦

Environment













Compliance with ARARs

~

~

¦

¦

¦

¦

Long-Term Effectiveness
and Permanence

~

~

~

~

¦

¦

Reduction of Toxicity,













Mobility, or Volume

~

~

~

~

~

~

through Treatment













Short-Term Effectiveness

~

~

~

~

~

~

Implementability

¦

~

~

~

~

~

Cost

$0

$12.1

$14.3

$13.6

$22.5

$30





million

million

million

million

million

State Acceptance

Will be evaluated after the comment period.

Community Acceptance

Will be evaluated after the comment period.

B - Meets criterion ~ - Does not meet criterion ~ - Partially meets criterion N/A - Not applicable

Chart comparing cleanup options (Soil Disposal Method B - on-site disposal)



Alternative

Alternative

Alternative

Alternative

Alternative

Alternative

Evaluation Criteria

S10-B

Sll-B

S12-B

S13-B

S14-B

S15-B**

Overall Protection of













Human Health and the

~

¦

¦

¦

¦

¦

Environment













Compliance with ARARs

~

~

¦

¦

¦

¦

Long-Term Effectiveness
and Permanence

~

~

~

~

¦

¦

Reduction of Toxicity,













Mobility, or Volume

~

~

~

~

~

~

through Treatment













Short-Term Effectiveness

~

~

~

~

~

~

Implementability

¦

~

~

~

~

¦

Cost

$0

$8 million

$10 million

$10.3
million

$15.4
million

$18.5
million

State Acceptance

Will be evaluated after the comment period.

Community Acceptance

Will be evaluated after the comment period.

B - Meets criterion ~ - Does not meet criterion ~ - Partially meets criterion N/A - Not applicable
** EPA's preferred cleanup alternative

7


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Next steps

Before it makes its decision final, EPA, in
consultation with both the LLBO and MPCA, will
review comments received during the public
comment period and at the public meeting. Based
on new information presented in the comments,
EPA ma)' modify its recommended alternative or
choose another.

EPA encourages you to review and comment on
the proposed cleanup plan. Much more detail on
the cleanup options is available in the Proposed
Plan and other official documents on file at the
information repositories (see box, right) or EPA's
website at www.epa.gov/superfand/st-regis-paper.

EPA will respond to the comments in a document
called a "Responsiveness Summary." This will be
part of another document called the "Record of
Decision," or ROD, that describes the final cleanup
plan. The Agency will announce the selected
cleanup plan in a local newspaper and will place a
copy in the information repositories and post it on
EPA's website.

Information repositories

To find more detailed information about the site
and to view technical documents, visit one of
the information repositories below.

Leech Lake Band of Ojibwe

Division of Resource Management
6530 Highway 2 NW
Cass Lake

Cass Lake City Clerk

332 Second St. NW
Cass Lake

Cass Lake Library

223 Cedar Ave.

Cass Lake

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