FIVE-YEAR REVIEW

UMETCO MINERALS CORPORATION
URAVAN SUPERFUND SITE

URAVAN, COLORADO

Prepared for:

U.S. Environmental Protection Agency, Region VIII
999 18th Street
Denver, Colorado 80202

Prepared by:

Frontier Environmental Services, Inc.
5171 Ward Road, Unit 1
Wheat Ridge, Colorado 80033

Approved By:	 Date:

Max Dodson

Assistant Regional Administrator
U.S. EPA, Region 8


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FIVE-YEAR REVIEW

UMETCO MINERALS CORPORATION
URAVAN SUPERMINI) SITE

11R A VAN, COLORADO

Prepared for;

U.S. Environmental Protection Agency, Region VIII
999 18th Street
Denver, Colorado 80202

Prepared by;

Frontier Environmental Services, Inc.
517! Ward Road, Unit 1
Wheat Ridge, Colorado 80033

/ J/J JL r f / yt/ I /

Approved By: 		1	__ ^Date;

Max Dodson

Assistant Regional Administrator

U.S. EPA, Region 8


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TABLE OF CONTENTS

Section:	Page Number:

Executive Summary	ES-1

1.0 INTRODUCTION	1-1

2.0 SITE BACKGROUND	2-1

3.0	REGULATORY COMPLIANCE	3-1

3.1	Statutory Review	3-1

3.2	ARARs	3-1 to 3-3

4.0	DESCRIPTION OF REMEDIAL ACTION OBJECTIVES	4-1

4.1	Atkinson Creek Crystal Disposal Area	4-1

4.2	Club Ranch Ponds Area	4-3

4.3	River Ponds Area	4-9

4.4	Club Mesa Tailings Piles	4-11

4.5	Club Mesa Area	4-17

4.6	Uravan Mill Areas	4-19

4.7	Town and Adjacent Areas	4-23

4.8	Burbank Quarry	4-27

4.9	Borrow Areas on Club Mesa	4-30

4.10	Hillside Seepage and Tailings Liquids	4-32

4.11	Pond Liquids	4-34

4.12	Storm Water Surface Runoff.	4-35

4.13	Ground Water	4-36

5.0	MISC. REMEDIAL ACTION PLAN REQUIREMENTS	5-1

5.1	Requirements	5-1

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5.2	Environmental Review	5-1

5.2.1	Meteorology	5-1

5.2.2	Ambient Air Quality	5-2

5.2.3	External Gamma	5-2

5.2.4	San Miguel River Sediment, Soil, Vegetation & Grazing Uptake	5-2

5.2.5	Tailings Pile Number 2 and Number 3; and Burbank Repository	5-2

5.2.6	Rim Erosion	5-2

5.2.7	Li qui d Waste Management	5-3

5.2.8	Surface Water	5-3

5.2.9	Groundwater	5-4

5.3	Occupational Health and Safety	5-4

5.4	Quality Assurance and Quality Control	5-5

5.5	Community Relations	5-6

5.6	Compliance	5-8

6.0	RECOMMENDATIONS	6-1

DRAWING:

Drawing Number 1: Uravan Uranium Site Map with Remedial Action Plan Boundary

FIGURES:



Figure 1A:

Uravan Site RAP Area and Orthographic Overlay

Figure IB:

Uravan Site RAP Area Topographic Map

Figure 2:

Atkinson Creek Disposal Area

Figure 3:

Club Mesa and Borrow Areas

Figure 4:

Club Mesa Tailings Piles and Seepage Collection Sumps

Figure 5:

Club Ranch Evaporation Ponds

Figure 6:

Club Ranch Evaporation Pond Number 4

Figure 7:

Historical Buildings and River Ponds Areas

Figure 8:

Mill Site, Mill Hillside and Plant A Areas

Figure 9:

Plant B and Bone Yard Areas

Figure 10:

Burbank Quarry - Title 1 and DOE - Title 2 Repositories

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EXECUTIVE SUMMARY

Frontier Environmental Services, Inc. was tasked by the United States Environmental
Protection Agency (EPA) Region VIII to conduct a Five-Year Review of the Umetco
Minerals Corporation Uravan Superfund Site to evaluate whether the remedial actions
taken at the site to date remain protective of human health and the environment. The
purpose of this review is to confirm that selected remedies remain effective. This is
accomplished through a site visit, a review of the administrative records, and review of
applicable or relevant and appropriate requirements (ARARs).

The Uravan Site was contaminated by radioactive residues resulting from the processing
of vanadium- and uranium-containing ores from the early 1900's through the mid-1980's.
In December 1983, the State of Colorado filed a natural resources damages claim against
Union Carbide and Carbon Corporation and Umetco under the Comprehensive
Environmental Response Compensation and Liability Act (CERCLA). The site was
proposed to the National Priorities List (NPL) in 1984 and was finalized to the NPL in
1986. In 1985, Umetco and the State of Colorado began discussions concerning remedial
action and cleanup of the site. The result of these discussions was the preparation of a
Consent Decree and Remedial Action Plan (RAP) in 1986 that outlined the requirements
for Umetco to remediate the site. This document is the functional equivalent of the U.S.
Environmental Protection Agency Remedial Investigation/Feasibility Study and Record
of Decision. The United States District Court for the State of Colorado approved the
consent Decree and RAP on February 12, 1987.

Solid wastes at the Uravan site are milling and cleanup residues that include: mill
tailings; evaporation crystals and sludges; milling refuse; and mill debris. These wastes
total over 10,000,000 cubic yards and contain radioactive elements, metals and inorganic
compounds. Liquid wastes from seepage collection and ground water extraction systems
total over 350 million gallons through FY2004. These liquids also contain radioactive
elements, metals and inorganic compounds.

Objectives of the ongoing and completed remedial activities are to:

•	Protect surface and ground water resources;

•	Stabilize and control the tailings and other solid waste materials;

•	Minimize radon emissions from the tailings and waste repositories; and

•	Conduct soil cleanup in a safe and environmentally sound manner.

Remedial actions conducted and completed to date include:

•	Removal and cleanup of dispersed materials and contaminated soils from
approximately 401 acres;

•	Relocating more than 3 million cubic yards of mill wastes and contaminated
materials to secure repositories on Club Mesa.

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•	Constructing waste and tailing repository covers, liquid evaporation and retention
ponds, and permanent runoff control structures - utilizing more than 1.7 million
cubic yards of earthen materials;

•	Construction of five (5) double-lined ponds (totaling 40-acres) for the evaporation
of hillside seepage, tailings pile seepage and extracted ground water;

•	Construction and utilization of a new repository in the B-Plant area capable of
disposing in excess of 1.8 million cubic yards of evaporative pond demolition
debris and radioactive waste;

•	Demolition and removal of about 50 major mill facility structures and buildings,
including the process systems and circuits, and removal of over 260 buildings in
the town of Uravan;

•	Collection and control of over 70 million gallons of hillside and tailings seepage,
containing approximately 6,000 tons of contaminated inorganic compounds.
Hillside and tailings seepage that was collected was transferred to Club Ranch
Ponds for management by evaporation;

•	Extraction of approximately 245 million gallons of contaminated liquids from the
ground water remedial program with the removal of approximately 14,500 tons of
contaminated inorganic compounds. Contaminated ground water that was
collected was transferred to Club Ranch Ponds for management by evaporation,
and;

•	Removal of contaminated materials from the Old and New Town Dumps with
placement into the Club Mesa Tailing repository.

Umetco and the State of Colorado Department of Public Health and Environment
(CDPHE) Radiation Control Division review of environmental monitoring data has
indicated that ambient air particulate concentration of radionuclides (including uranium,
thorium and radium) has decreased since the last five-year review (2000).

Surface water quality monitoring measurements indicate that there have been no apparent
adverse impacts from radionuclides, metals, or inorganic compounds to the San Miguel
River at Uravan since the last five year review. Concentrations of constituents in the San
Miguel River during high and low flow conditions demonstrate that currently there is no
demonstrated risk to human health or the environment from hazardous materials located
and managed at the Uravan site.

Concentrations of total dissolved solids in the Kayenta formation beneath Club Ranch
Evaporation Ponds have decreased an average of 80% in the higher permeability zones
and 51% in lower permeability zones in the last thirteen years of ground water extraction.
Present concentrations of total dissolved solids in ground water recovered from the
Kayenta formation demonstrate a state of equilibrium and have essentially reached a
steady-state condition.

Current occupational doses to ionizing radiation are below site established limits. Over
the past five years occupational and public radiation monitoring indicated that exposures

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are well below allowable rates as set by the Nuclear Regulatory Commission (NRC) and
the CDPHE regulations for permissible exposure to radiation.

Environmental conditions identified during this Five-Year Review that remain to be
addressed or completed include:

1.	Providing definitive time-line schedule for the implementation and completion of
RAP construction/closure activities, i.e.;

•	Club Ranch Ponds

•	Club Mesa Tailings Piles

•	B-Plant Area Repository

•	Mill Hillside and Mill Areas

•	Hillside Seepage Management

•	Surface water run-off control features

•	Ground water monitoring and mitigation

2.	Providing continued systematic management of collected site liquids from hillside
seepage collection system(s) and storm water runoff from active repository units;

3.	Providing an updated maintenance and repair program for constructed storm water
management systems;

4.	Continuing to provide inspection, repair and maintenance of in-service Club Ranch
Ponds, and implementing a systematic dosure of the Club Ranch Ponds that are
deemed non-serviceable and/or are no longer required as liquid management systems
supporting other on site RAP activities;

5.	Developing a "Windblown Area" assessment, evaluation and report using as a
minimum "area-averaging methods" as prescribed by the CDPHE - Radiation
Management Program guidance;

6.	Finalizing the determination of the disposition and action on disposal of PCB
containers stored within the RAP boundaries;

7.	Resolving issues with the Colorado Department of Transportation for the
management of radioactive waste materials remaining beneath Colorado Highway
141 and implementing response in accordance with the RAP;

8.	Finalizing the Institutional Control Agreement and its implementation by Montrose
County Board of County Commissioners for Montrose County Roads Y-l 1 and E-22.

In summary, remedial activities at the Umetco Minerals Corporation Uravan Remedial
Action Project are being conducted in accordance with the Consent Decree and the
Remedial Action Plan and are scheduled for completion by the end of December 2007.
Monitoring data indicate that air and ground water resources have improved, that there is
no apparent impact from the site on surface water, and that occupational and public
exposures are below the prescribed regulatory limits. Based on available information, it
appears that the selected remedies remain effective in protecting the environment and the
health of the public.

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1.0 INTRODUCTION

Frontier Environmental Services, Inc. was tasked by the United States Environmental
Protection Agency (EPA) Region VIII to conduct a Five-Year Review of the Umetco
Minerals Corporation Uravan Superfund Site to evaluate whether the response actions
taken at the site to-date remain protective of human health and the environment.

This Five-Year Review was conducted according to procedures outlined in the Office of
Solid Waste and Emergency Response (OSWER) Directive 9355.7-03B-P, June 2001;
Comprehensive Five-Year Review Guidance: and is consistent with the provisions of the
Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA),
and the National Contingency Plan (NCP). Specifically, the Five-Year Review included
an evaluation of documents and standards, an assessment of site conditions, and
preparation of this Five-Year Review Report. This report includes a description of site
background (Section 2.0); a review of site Applicable or Relevant and Appropriate
Requirements (ARARs) (Section 3.0); a discussion of remedial objectives and status of
the remedial actions (Section 4.0); Miscellaneous Remedial Action Plan Requirements,
including an evaluation of environmental and health conditions at the Uravan site
(Section 5.0); and a presentation of recommendations and a discussion of actions taken
by Umetco Minerals Corporation on EPA recommendations presented in the 1999/2000
Five-Year Review Report (Section 6).

This review is conducted no less often than every five years following commencement of
the remedial program. Five-Year reviews were conducted by EPA in 1999/2000. This
report fulfils the 2005 statutory reporting requirement.

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2.0 SITE BACKGROUND

The Uravan Site is located in the western portion of Montrose County, Colorado on
Colorado Highway 141 approximately 13-miles northwest of the Town of Nucla,
Colorado; 81-miles south of the Town of Whitewater, Colorado in Mesa County; and 50
air miles southwest of the City of Grand Junction, Colorado. The site habitat is
characterized by an arid climate, sparse vegetation, and rugged topography. Topographic
features in the site are dominated by broad mesas and incised canyons. The Uravan site
is within the incised San Miguel River Valley and on top of a part of the adjacent Club
Mesa as shown in the below photograph taken in May 2005.

Mining operations in this area of Colorado began in the early 1900's. Mining of radium-
bearing carnotite ore (K.2(U02)(V)4)2) began in approximately 1910 when Standard
Chemical Company first acquired mining claims in the area. The Standard Chemical
Company built a radium mill known as the Joe Junior Mill in 1914. The mill was located
on the -valley floor along the San Miguel River at the site of what later became known as
"A-Plant". The mill produced radium until 1919.

In 1928 Union Carbide Corporation (UCC) purchased the Standard Chemical Company
holdings in Colorado through their subsidiary U.S. Vanadium Corporation (USV). The
Standard Chemical Corporation reserves were reportedly purchased for the recovery of
vanadium. USV expanded the "A-Plant" in 1934, constructing a mill and roasting plant
to recover vanadium from carnotite ore; and aided uranium recovery circuits shortly
thereafter with operations starting in 1937 and 1938 at the Uravan site. The town of
Uravan was established in 1935 to house workers and their families at the mill and mine
facilities.

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During the two-year period of 1937 through 1938, approximately 250,000 pounds of
triuranium octoxide UsOg was produced. The material was refined in Uravan and the
recovered vanadium and uranium concentrates were sold to the U.S. Army.

In the fall of 1942, the Manhattan Project and LBV officials discussed building new
facilities for the U.S. Government to process uranium. Construction began in 1943 for a
new plant at Uravan (termed the WSP Plant) near the existing USV mill (termed the
WAA Plant). USV's WAA Plant was put under government contract by June 1944. The
government's WSP Plant at Uravan was operational in July 1943 and discontinued
operations in 1945; and was subsequently dismantled. In 1945, USV's WAA mill
reverted to private operations.

The mill circuits were continually improved to meet product demand and the "B-Plant"
was constructed in 1955. The B-Plant was located on a bench on Club Mesa several
hundred feet above the San Miguel River. Uranium and vanadium were recovered from
leach liquors with a column ion-exchange process, followed by precipitation and drying
of the uranium containing "yellow-cake". Tailings from "B-Plant" were placed in piles
on a bench of Club Mesa. A radium removal circuit was installed in 1958 to treat waste
solutions. Three unlined Club Ranch Ponds were constructed between 1963 and 1965 to
aid liquid management through a combination of evaporation and seepage. Additional
liquid management units improvement added later included the addition of a
neutralization circuit to permit part of the mill process wastes to be discharged directly to
the San Miguel River and the installation of a spray evaporation system in 1976 on Club
Mesa. Between 1936 and 1984, when Union Carbide and Carbon Corporation operated
the mill complex, approximately 42 million pounds of uranium oxide (U3O8) and 222
million pounds of vanadium oxide (V2O5) were produced. Umetco Minerals Corporation
(Umetco), a subsidiary of Union Carbide (later - a subsidiary of Dow Chemical), has
operated the facility since its closure in 1984.

The Uravan mill's capacity continued to expand into the 1950's to meet the demand for
uranium required by the United States government's weapons programs, pursuant to a
contractual agreement between USV and the United States Atomic Energy Commission
(AEC). Uravan received uranium/vanadium ores from over 200 mines in the area. The
mill operated under a series of licenses issued by the United States Nuclear Regulatory
Commission (NRC) [Subsequently regulated by the Atomic Energy Commission (AEC)]
and from the State of Colorado from 1948 to this date. The amended licenses became
increasingly complex, addressing worker safety and health concerns, public safety and
health, and environmental issues. The Uravan mill was operated under an AEC Source
Material License Number SUA-673 until 1968. In 1968, the State of Colorado became
an agreement state with the AEC, and as such, took over all licensing functions. After
1968, the Uravan mill operated under a radioactive material license issued by the
Colorado Department of Public Health and Environment (CDPHE).

The State of Colorado (State) filed a natural resources damages claim against Union
Carbide and Carbon Corporation and Umetco Minerals Corporation in December 1983

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under CERCLA. The Uravan site was proposed to the National Priorities List (NPL) on
October 15, 1984; 49 Federal Register 40320 (1984). On June 10, 1986, the listing of the
site was finalized on the NPL; 49 Federal Register 21054 (1986).

In 1985, the State and Umetco began discussions regarding remedial activities to be
conducted at the Uravan site. These discussions resulted in the preparation of a Consent
Decree and associated Remedial Action Plan (RAP). The RAP is the functional
equivalent of an EPA Remedial Investigation/Feasibility Study (RI/FS) and Record of
Decision (ROD). The United States District court for the District of Colorado approved
the Consent Decree and RAP on February 12, 1987.

Under the Consent Decree, Umetco is required to complete reclamation activities
specified in the RAP. To complete these activities, construction, health and safety and
environmental documents were prepared by Umetco. These documents were submitted
to the State of Colorado for review and approval. Modification to and approval of these
documents are periodically conducted to reflect changing site conditions as remedial
activities progress. These documents form the basis for conducting, monitoring, and
assessing the remedial activities and determining if the selected remedy is protective of
human health and the environment. These governing site-specific documents include:

•	1995 Uravan Remedial Action Plan (RAP) Policy and Procedures Manual, as
amended, which describes site specific health, safety and environmental policies
and procedures to be used at Uravan.

•	1996 Umetco Minerals Corporation Safety Manual, as amended, which sets forth
the policies and procedures for conducting the remedial activities in a safe,
responsible manner.

•	1987 Quality Plans, as amended, which provide quality assurance and quality
control requirements and set forth site specific mechanisms to evaluate the
performance of the remedial activities.

•	1987 Final Plan and Specifications, as revised, which present basis and technical
data for the remedial activities and provide engineering drawings and
specifications for construction work to be conducted during site reclamation.

Under the Consent Decree, Umetco is required to complete the following general
remedial activities as specified in the RAP:

•	Reshaping the 10 million cubic yard tailings repositories and constructing a long-
term containment cover and appropriate drainage controls.

•	Relocating 1.5 million cubic yards of mill wastes, including evaporative crystals
and wastewater treatment sludges, to a secure on-site repository and constructing
long-term containment controls.

•	Clean-up dispersed soils.

•	Decommissioning and demolition of the milling facilities.

•	Remediation of ground water resources.

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3.0 REGULATORY COMPLIANCE

Consistent with Section 121 of CERCLA, as amended, and 40 CFR §300.430(f) of the
National Contingency Plan (NCP), the EPA is performing this Five-Year Review for the
Umetco Minerals Corporation Uravan Superfund Site. EPA determined the level of
review based upon site-specific considerations including the nature of the response
action, the status of the onsite response activities, proximity to populated areas and
sensitive environments, and the interval since the last review was conducted
(FY1999/2000). The components of this Five-Year Review include:

•	Review of documented operation and maintenance of the Uravan site.

•	Performance of a site visit.

•	Limited analysis of site conditions.

•	Review of the administrative record.

•	Review of Federal and State environmental laws cited in the Consent Decree and
Remedial Action Plan to determine if they remain applicable, relevant and
appropriate requirements (ARARs).

3.1	Statutory Review

A statutory five-year review is required at any site where unlimited use and un-restricted
exposure, based on the Consent Decree and RAP cleanup levels, have not been attained.
A Five-Year Review is required no less often than every five years after initiation of the
selected remedial action. In 1994, EPA issued a 1993 Five-Year Review for the Umetco
Minerals Corporation Uravan Superfund Site for the period of 1988 through 1993; issued
a 1999/2000 Five-Year Review for the Umetco Minerals Corporation Uravan Superfund
Site for the period of 1994 through 1999; and conducted the current review in May 2005.
Another Five-Year Review will be conducted in 2010 or earlier unless existing onsite
contamination is removed to allow unrestricted access and unlimited use of the property.
This document presents the results of the 2005 review.

3.2	ARARs

The Consent Decree for Civil Action Number 83-C-2384 for the State v. UCC and
Umetco and the Remedial Action Plan (RAP) were reviewed for this Five-Year Review.
Applicable or Relevant and Appropriate Requirements (ARARs) discussed in these
documents are presented below:

ARARs for the Uravan site set forth in the Consent Decree Remedial Action Plan (RAP)
are consistent with current cleanup standards. No changes to the ARARs requirements
for site cleanup have been promulgated; however changes in public and occupational
exposure standards are incorporated in the evaluation of remedial activities at the Uravan
Site.

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3.2.1	Transportation of Radioactive Materials

Colorado Code of Regulations 1007-1 Part 17 pertaining to the transportation of
radioactive materials remains unchanged.

3.2.2	Cleanup Criteria for Soils

Code of Federal Regulations 40 CFR §192, Subpart D sets standards for soil cleanup.
Soil criteria of 5 ?Ci/g Ra226 above background in soil as measured 0 to 15-cm below
ground surface remains unchanged and is consistent with the current version of the
Uravan Remedial Action Plan (RAP) Table 4.1.2-1.

3.2.3	Ground Water Quality Protection Standards

Ground water protection standards outlined in 40 CFR §192.32(a)(2) remain unchanged
and consistent with the current version of the Uravan Remedial Action Plan (RAP) Table
5.4.3.2-2.

3.2.4	Public Radionuclide Exposure Standards

Current public ionizing radiation dose standards for the Uravan site are published in the
State of Colorado Rules and Regulations Pertaining to Radiation Control, 1990, as
amended. Applicable standards are in Part 4, specifically in RH 4.14, 4.15, Appendix A
of Part 4, and in Part 18, Criterion 8. Additional public dose limits for airborne
radionuclides other than radon and its daughters are published in 10 CFR 20-1101. The
public dose limits in Part 4 and 10 CFR 20-1101 are regulatory changes that have
occurred following implementation of the Remedial Action Plan (RAP). The public dose
limits specified in Part 18, Criterion 8 are identical to 40 CFR 190 and have been
applicable to reclamation activities at the Uravan site since RAP implementation.

Regulation RH 4.14 limits the Total Effective Dose Equivalent (TEDE) to individual
members of the public from the licensed operation at 100 mrem per year. This regulation
also limits the dose in any unrestricted area from external sources to 2 mrem in any hour.
These standards became effective January 1, 1994.

Regulation RH 4.15 and Appendix A of Part 4 describe methods to show compliance
with dose limits for individual members of the public. This standard became effective
January 1, 1994.

The standards in 10 CFR 20-1101 establish a constraint of 10 mrem per TEDE to
members of the public from airborne radioactive effluents to the environment from
licensees as part of its program to maintain dose As Low As Reasonable Achievable
(ALARA). This rule applies to airborne effluent of radioactive materials to the

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environment, other than radon and its daughters, from licensees except power reactors.
This rule became effective on January 9, 1997.

3.2.5 Occupational Radionuclide Exposure Standards

Current occupational ionizing radiation dose standards for the Uravan site are published
in the State of Colorado Rules and Regulations Pertaining to Radiation Control, 1990, as
amended. Applicable standards are in Part 4, specifically RH 4.6 and Appendix A. In
May 1991, the Nuclear Regulatory Commission published revised 10 CFR Part 20
regulations which were required to become effective in agreement states, like Colorado,
by January 1, 1994.

The standards in Part 4.6 of the State of Colorado Rules and Regulations Pertaining to
Radiation Control require licensees to control the occupational dose to workers to an
annual limit, which is more limiting of:

•	The TEDE being equal to 5 rem; or

•	The sum of the deep dose equivalent and the committed dose equivalent to any
organ or tissue other than the lens of the eye being equal to 50 rem.

•	The annual limits to the lens of the eye and extremities are 15 rem and 50 rem
respectively.

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4.0

DESCRIPTION OF REMEDIAL ACTION AND OBJECTIVES

Solid wastes at Uravan are comprised of milling and cleanup residues that include mill
tailings; evaporation crystals and sludges; milling refuse; and mill debris. These wastes
total over 10,000,000 cubic yards and contain radioactive elements, metals and inorganic
compounds. Liquid wastes from seepage collection and ground water extraction systems
total over 350 million gallons at the end of 2004. These liquids also contain radioactive
elements, metals and inorganic compounds.

Objectives of the remedial activities are to:

•	Protect surface and ground water resources;

•	Stabilize and control the tailings and other waste materials;

•	Minimize radon emissions from the tailings and waste repositories; and

•	Conduct soil cleanup in a safe and environmentally sound manner.

Meeting these objectives assures the protection of human health and environment. The
general site remedies chosen to achieve the remedial objectives include:

•	Reshaping the tailings repositories and constructing a long term containment
cover and appropriate drainage controls;

•	Relocating mill wastes, including evaporation pond generated crystals and
wastewater treatment sludges, to a secure on-site repository and constructing
long-term containment controls;

•	Cleanup of dispersed contaminated soils;

•	Decommissioning and demolition of milling facilities;

•	Remediation of ground water resources by pumping and evaporating
contaminated ground water; and

•	Performing the remediation in a safe manner that minimizes impact on the
environment and to the remediation personnel.

From 1987 through 2004, remedial work included the removal and relocation of the vast
majority of contaminants from the San Miguel River Valley and Club Mesa,
decommissioning and demolition of the mill facility complex, installation and operation
of the ground water withdrawal system and the removal of dispersed contaminated soils
and debris from the Uravan site and nearby locations.

4.1 Atkinson Creek Crystal Disposal Area

4.1.1 History

The Atkinson Creek Crystal disposal area was located downstream from the Club Ranch
Ponds and adjacent to Atkinson Creek. This disposal area was constructed in the early
1970s on the site of a former mobile home park. The mobile homes were removed and
the underlying soils were excavated and stockpiled adjacent to the area. After
preparation of the site, approximately 200,000 cubic yards of raffinate crystals from the
Club Ranch Ponds #1 and #6 were removed and stored in the Atkinson Creek area. No

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liner was placed beneath the crystals to prevent contamination of the underlying soils or
ground water. Natural soils were placed on the raffinate crystals to form a soil cover
approximately twelve inches thick.

4.1.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado selected excavation and on-site
disposal of the raffinate crystals in the Burbank Quarry, an approved raffinate ciystal
storage area, and disposal of other contaminated soils in the Tailings Piles on Club Mesa
as the remedy for the Atkinson Creek Disposal Area. The objectives of this remedy were
to remove the source of potential future ground and surface water contamination by
raffinate crystal dissolution or erosion.

4.1.3	Site Status and RAP Requirements

Remedial action at this site was completed as of October 14, 1999. A Final Completion
Report has been generated and submitted to the State of Colorado Department of Public
Health and Environment (CDPHE). The final completion report has been reviewed and
accepted by CDPHE.

4.1.4	Summary of Site Visit Observations and Findings

The on-site visit of May 11, 3305 found Atkinson Creek Disposal Area to be visually
restored and well vegetated as compared to the surrounding areas not included in the
Atkinson Creek Disposal Area. Crystals, discoloration, or other signs of contamination
were not observed in this area. Visible signs of severe erosion were also not observed.
Vegetation had re-established itself and visually appeared to be veiy healthy. The site is
equipped with a well maintained fence, which aids in keeping grazing animals off the
site.

4.1.5	Photographs

Photographs shown below illustrate the current status of the Atkinson Creek Disposal
Area, showing re-establishment of vegetation.

Reclaimed and vegetated Atkinson Creek Disposal Area, May 2005

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Looking west from Atkinson Creek Disposal Area at Atkinson Creek and
Colorado Highway 141 overpass.

4.1.6 Recommendations

This EPA Five-Year Review makes no recommendations for the Atkinson Creek
Disposal Area.

Table 4.1
Atkinson Creek Disposal Area

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Remove Raffmate Crystals
and Contaminated Soils:
Place in Designated
Disposal Areas; Place Soil
Cover and Re-vegetate.

Completed by
December 1993

Atkinson Creek Disposal
Area Remediated Pursuant
to RAP.

4.2 Club Ranch Ponds Area
4.2.1 History

The Club Ranch Ponds Area consists of six unlined liquid waste disposal ponds located
down valley from the Uravan Mill site and ancillary disposal areas. The Club Ranch
Evaporation Ponds were constructed in the early 1960s to serve as both evaporative and
seepage discharge ponds. The ponds were excavated into gravel terrace deposits of the

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San Miguel River. The depths of the ponds ranged from approximately eight-feet to
almost thirty-feet. At the time of site cessation of operations, Umetco estimated that the
ponds contained approximately 560,000 cubic yards of raffinate crystals and 30 million
gallons of liquid. Contaminants were identified in the alluvial gravels and the underlying
Kayenta Formation. There was no evidence of seepage into the San Miguel River along
the pond.

4.2.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected excavation and on-site disposal of raffinate crystals in the Burbank
Quarry, an approved raffinate crystal storage area, and disposal of other contaminated
soils in the Tailings Piles on club Mesa as the remedy for the Club Ranch Evaporation
Ponds Area. The objectives of this remedy were to remove the source of potential future
contamination of the Kayenta-Wingate aquifer and the San Miguel River.

4.2.3	Site Status and RAP Requirements

New evaporation ponds, called Club Ranch Evaporation Ponds CRP #7 and CRP #8,
were constructed in the fall of 1987 and the spring of 1988 in order to contain hillside
seepage liquids and to contain liquids transferred from the old, unlined Club Ranch
Evaporation Ponds. CRP #7 and CRP #8 ponds were constructed in the former Uravan
housing area called New Trailer Court and H & J Blocks. CRP #7 and CRP #8 were
constructed in conformance with state and federal requirements in order to preclude
discharge of mill related liquids. The liquids remaining in the unlined Club Ranch
Evaporation Ponds were transferred into geo-synthetically lined CRP #7 and CRP #8 in
1988. Three additional Club Ranch lined ponds, CRP #1, CRP #4 and CRP #6 were
constructed during 1991 and 1992 for the management of Uravan collected contaminated
liquids from hillside seepage, surface water run-off, and pumped ground water for
management by evaporation. Evaporative pond construction was completed with these
three additional ponds.

CRP #1, CRP #4, CRP #6, CRP #7 and CRP #8 were lined with a clayey material, a low
permeable geo-membrane with leak detection system. After the liquids are evaporated,
the residues and liners are to be removed and encapsulated in a Club Mesa repository.
Any contaminated soils are to be removed in accordance with criteria set forth in the
Remedial Action Plan and the area re-graded and vegetated.

Initial removal of the raffinate crystals and associated contaminated soils commenced
during the fall of 1989. A total of 408,000 cubic yards was removed by mid-1991.
Removal of raffinate crystals is complete for the previous pond locations. The Remedial
Action Plan required the removal of all crystals and reconstruction of all of the Club
Ranch Ponds by December 31, 1991. A revision to the Remedial Action Plan
implementation schedule for construction of the final Club Ranch Ponds CRP #1, CRP #4
and CRP #6 was approved, which allowed for their delayed construction.

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In 1997, contaminated ground water was encountered in the alluvial materials on top of
the bedrock in the original six unlined Club Ranch Ponds. This ground water was
intercepted and placed in evaporation ponds CRP #7 and CRP #8 for management. Final
reclamation of the area will be undertaken after completion of valley ground water
cleanup and will include re-grading and vegetation of the disturbed areas.

Contaminated alluvial materials totaling about 33,000 cubic yards were removed fom
unlined Club Ranch Ponds CRP #2, CRP #3, and CRP #5 during 1998. Excavation
continued until underlying bedrock was encountered. This action removed a significant
source of contamination from the Club Ranch Evaporation Pond Area. Dikes around
these partially mitigated ponds were permitted to remain in place to collect precipitation
that is collected in dewatering points, e.g., trenches in shallow alluvium, and immediately
transferred to the lined Club Ranch Evaporation Ponds. Final removal of all
contaminated soils will be undertaken during the phased removal of the lined Club Ranch
Evaporation Ponds that will commence following completion of ground water
remediation program in approximately 2007.

In 1999, Umetco installed a manually enhanced evaporation system in Club Ranch Pond
CRP #8 to determine whether water pumped through spray heads would result in a
significant increase in water evaporation. A pilot study indicated that evaporation was
increased from 1 gallon per minute per acre to 2 gallons per minute per acre. Umetco
asked for and received permission for the State of Colorado Department of Public Health
and Environment in 2000 to modify CRP #8 accordingly. Club Ranch Pond CR #8 was
outfitted with the evaporative spray system and operated from 2000 to 2005 with varied
results and operational and maintenance issues.

CRP #7 was taken out of service in 2001 when the liner and leak collection system was
removed. A total of 41,000 cubic yards of contaminated materials was removed from the
dikes of CRP #3, from the banks of the San Miguel River and from CRP #7 in 2001.

Since 2001, exploratory trenches have been excavated into the gravel alluvial materials in
the former pond location and in CRP #6 and CRP #7 for the purpose of determining the
extent of potential contamination and any potential impacts on ground water and the
management of encountered contaminated ground water is in Club Ranch Ponds CRP #1,
CRP #4 and CRP #8. Contaminated materials have been or will be excavated and placed
into the Club Mesa Repositories approved for their disposal.

4.2.4 Summary of Site Visit Observations and Findings

During the site visit on May 11, 2005, the three remaining lined Club Ranch Evaporation
Ponds: CRP #1; CRP #4; and CRP #8 were inspected. CRP #1 and CRP #8 visually
appeared to be in fair condition. While no visible defects were observed during this
inspection, weathering and operational wear was apparent. However, a detailed
inspection conducted by Umetco personnel on May 12, 2005 identified two liner failures

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in CRP #8 and one liner failure in CRP #1. The liner failures of CRP #1 and CRP #8 had
occurred on the pond's crest and were not within the ponds. Club Mesa Evaporation
Ponds CRP #1 and CRP #8 liners failures are not scheduled for repair at the time of this
report, but are scheduled for excavation and removal as soon as possible. Information
obtained from site personnel indicated that the ponds are inspected regularly and the leak
detection system has seen no significant change in collected liquids beyond that which is
expected, i.e. 5 gallons per minute that would require activation of the Liner Failure
Contingency Plan. In addition, site personnel indicated that none of the three lined Club
Ranch Evaporation Ponds had ever overflowed or otherwise released water to the San
Miguel River.

The inspection of May 11, 2005 indicated that Club Ranch Pond CRP #4 had suffered
significant liner failure due to excessive liner tension forces imposed during a period in
which the pond was left empty and allowed to go through a series of temperature
extremes. The temperature extremes created a condition that allowed CRP #4 liner to
"trampoline" or otherwise become stretched beyond the support of its sub-grade. When
the stressed CRP #4 was filled during the winter/spring period of 2004/2005, the stress
liner failed in at least eight locations. Liner failure occurred in parent material, fusion
welds and extruded welds. The majority of the liner failures were on the crest or outside
of CRP #4 containment bowl. Two of the eight liner failures were within CRP #4
containment bowl, but were located approximately two-feet above pond water line.
Inspection of CRP#4 leak detection sump indicated presence of liquids, but not in
quantities or volumes that would trigger Liner Failure Contingency Plan. Club Ranch
Evaporation Pond CRP #4 has been taken out of service, drained and scheduled for
excavation and removal with disposal of its liner and any contaminated materials to an
approved on-site Club Mesa Repository (B-Plant Repository). Reference Umetco Uravan
Club Ranch Ponds Synthetic Liner Inspection Report, dated May 20, 2005.

Ground water is still being pumped into two of the lined Club Ranch Ponds: CRP #1 and
CRP #8. Evaporation of collected water has not generated significant quantities of
raffinate crystals.

4.2.4 Photographs

The photographs taken on May 11, 2005 presented below illustrate the existing
conditions of the three remaining Club Ranch Ponds. Photographs also illustrate some of
the liner failures observed during this Five-Year Review site visit.

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Club Ranch Ponds CRP #8, CRP#1	Club Ranch Pond CRP #8

and CRP#4	Evaporative Spray system

Club Ranch Pond CRP #8	CRP #4 Interior Liner Trampoline Effect

Club Ranch Pond CRP #4	Club Ranch Pond CRP #4

Interior Liner Failure	Exterior Liner Failure

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4.2.5 Recommendations

It is recommended that the Club Ranch Pond CRP #4 be removed from service
immediately (This action was implemented as of May 20, 2005) and be excavated and
removed during the 2005 remediation season with disposal in an on-site approved
repository (B-Plant Repository). Club Ranch Ponds CRP #1 and CRP #8 should be
repaired at the earliest time achievable. Club Ranch Ponds CRP #1 and CRP #8 should
be inspected daily for lner deterioration and failure and their leak detection systems
inspected and evaluated on a weekly basis until removed from operation.

Table 4.2
Club Ranch Ponds Area

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Evaporate all Liquids in
Place; Remove Raffinate
Crystals and Place in
Designated Disposal Areas;
Verify Mitigation with
Radiological Survey;
Remove Sub-Grade
Contaminated Soils and
Place in Designated
Disposal Areas; Recontour
and Revegetate Mitigated
Pond Areas; and Issue
construction Completion
Report.

RAP Modified Completion
by December 1992

Original Club Ranch Ponds
Have Been Mitigated and
Closed Pursuant to RAP
Requirements, except for
final recontouring and
revegetation. Completed by
1992.

Construct New Evaporation
Ponds per Specifications,
Manage Ground Water
Storm Water Run-Off and
Hillside Seepage Liquids;
Properly Close Club Ranch
Evaporation Ponds per RAP
Requirements; and
Recontour and Revegetate
Club Ranch Pond Area

RAP Modified to Allow
On-Going Utilization of
Club Ranch Ponds for
Evaporation of On-Site
Generated Liquids.

Club Ranch Evaporation
Ponds CRP-1 and CRP-8
are in Use. CRP-4
Scheduled for Removal
Summer 2005. Enhanced
Evaporation Systems to Be
Installed in CRP-1 and
CRP-8 During Summer
2005.

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4.3

River Ponds Area

4.3.1	History

The River Ponds Area consisted of seven small ponds constructed along the San Miguel
River adjacent to the mill. Five of the ponds were located on the mill side (south side) of
the river and two ponds were located on the north side of the river adjacent to Colorado
Highway 141. These ponds were constructed within old tailings piles by excavating into
and, in some cases, through the tailings. The exposed surfaces of the excavations were
than mantled/covered with natural soils. The five ponds on the mill side of the river were
used as settling basins for liquids collected within the mill area and stored there prior to
discharge to the river. The two ponds on the north side of the river were used to clarify
treated process liquors prior to discharge. These ponds contained neutralized sludge from
clarification operations. Umetco estimated that about 290,000 cubic yards of mill wastes
and contaminated soils were contained in the River Ponds Area. Seepage of liquids from
the River Ponds Area to ground water, and eventually to the San Miguel River, was
estimated at 10 to 40-gallons per minute when they were in use.

4.3.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected excavation of all sludges and tailings and on-site disposal in the
Tailings Piles of Club Mesa as the Remedy for the River Ponds Area. The objectives of
this remedy were to remove the source of potential future contamination of the ground
water and the San Miguel River.

4.3.3	Site status and RAP Requirements

Initial removal of the River Ponds started in 1988 and was completed in mid-1989, these
materials were placed into Club Mesa Tailings Piles #1, #2 and #3. Excavation was
completed down to the water table. Umetco subsequently constructed rock berms to trap
sediment carried by the San Miguel River during high flows. Vegetation has re-
established itself in the River Ponds Area. The Remedial Action Plan called for final
reclamation by December 31, 1991. A final construction report was submitted to the
State of Colorado Department of Public Health and Environment in Mid-1993. With the
acceptance of the final construction report, this component was 100 percent complete as
of December 1993.

No further activity has been undertaken at this site since the last Five-Year Review
(1999/2000) was prepared.

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4.3.4	Summary of Site Visit Observations and Findings

Visual observations during the site visit of May 11, 2005 found the River Ponds Area to
be restored to a condition comparable to surrounding areas not included in the River
Ponds Area. The San Miguel river has incorporated the River Ponds Area into its course.
Vegetation has re-established itself and visually appeared to be healthy. Tailings,
discoloration, or other signs of vegetation stress and/or contamination were not observed.

4.3.5	Photographs

Photographs taken on May 11, 2005 are presented below and illustrate the completed
status of the River Ponds Area.

River Ponds Area 1 of 2

River Ponds Area 2 of 2

4.3.6 Recommendations

None noted

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Table 4.3
River Ponds Area

RAP Requirement

Required Date of
Completion

Site Status
May 2005

All Tailings, Liquids and
Contaminated Materials to
be Removed and Disposed
of in Designated Disposal
Areas; Pond Area to be
Surveyed for closure
Criteria Using Radiological
Survey Methods; Pond
Areas to be Graded and Soil
Capped; and Revegetated

Milestone Completion Was
Accomplished by 1989

River Ponds Area
Completed Pursuant to RAP
Requirements. Ongoing
Inspection and Monitoring
Continue.

4.4 Club Mesa Tailings Piles

4.4.1	History

The Club Mesa Tailings Piles at Uravan were started in the mid-1950s to store tailings
generated by the Uravan Mill. The Tailings Piles are located on Club Mesa above the
Uravan Mill site. The Club Mesa Tailings Piles were constructed using the upstream
method whereby the tailings slurry was pumped from the mill to the Tailings Piles and
deposited through spigots placed along the tailings delivery line. The embankment raises
are constructed from tailings sands that were regraded, placed, and compacted.

Prior to 1980, the downstream slopes on the tailings embankments varied from
approximately 1.5 (H) : 1 (V) to 3 (H) : 1 (V). As the height of the embankment
increased, there was concern for stability of the embankments. Consequently, in 1980,
rock fill berms including a drainage blanket for seepage control were constructed to
buttress the lower portions of the Tailings Piles. Horizontal drains to promote drainage
of the tailings were also installed but were ineffective.

Observed impacts from the existing tailings disposal system included seepage of
contaminated liquids into the Club Mesa bedrock; erosion and transport of tailings
material away from the disposal area by wind and water action; and radon emanation
from the Tailings Piles.

4.4.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected cessation of discharge to the Tailings Piles, removal of liquids, and
the covering of the slopes of the Tailings Piles material prior to final reclamation as the

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remedy for the Tailings Piles. The objectives of this remedy were to minimize surface
water infiltration, seepage from the Tailings Piles, wind and water erosion, and radon
emanation from the Tailings Piles.

4.4.3 Site Status and RAP Requirements

Remedial activities set forth in the Remedial Action Plan for the tailings piles of Club
Mesa include dewatering, pile reshaping, buttress protection, toe drain system
maintenance, top and side slope cover construction, and storm water drainage diversion.
The Remedial Action Plan calls for dewatering through natural seepage enhanced by
surcharging caused by additional materials placed on the piles. The piles are to be
resloped, contoured, and rock fill buttress covered for increased stability. A final
protective cover is to be placed which is engineered to mitigate radon emanations, to
control erosion and to mitigate seismic motions. Drainage diversion channels will
eliminate storm water and snow melt run-on from up-gradient areas. Seepage liquids are
to be collected where possible and transferred to the Club Ranch Ponds for evaporation.

The Remedial Action Plan describes six components items for the Club Mesa Tailings
Piles:

1.	Surface water removal;

2.	Sloping and Contouring;

3.	Constructing rock fill buttress and toe drain;

4.	Constructing side slope protective cover;

5.	Emplacing top covers; and

6.	Constructing Drainage diversion.

Components 1 through 4 have been completed. The side and top covers, except for
riprap, have been placed on Tailings Pile #3. The storm water diversion channel system
has been constructed for Club Mesa Tailings Piles 1, 2 and 3. Components 4 and 5 have
been constructed, except for placement of portions of the rock cover. Component 6 will
be completed upon the closure of the B-Plant Repository. Geotechnical instrumentation
was installed in the Club Mesa Tailings Piles.

The top of Tailings Piles 1 and 2 is the final repository for tailings and contaminated soils
from the valley areas and Club Mesa. The placement of contaminated soils and other
materials on Tailings Piles 1 and 2 was completed, except for portions of the final rock
cap materials.

Repository construction in the B-Plant area began in 1998 with the starter berm and
return water pond. Operations and placement of contaminated materials in the B-Plant
repository began in 1998 and continues to date. A toe drain system was also installed in
the B-Plant Repository Area. This repository will accept contaminated materials from
the final reclamation of the Club Ranch Ponds and has a designed capacity of
approximately 1.8 million cubic yards of waste material.

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4.4.4 Summary of Site Visit Observations and Findings

The joint separation on Tailings Pile 3 noted in the 1999/2000 Five-Year Review has
been mitigated. Joint separation was due to overlooking and adjoining bedrock
displacement and not movement of the tailings pile. Inspection of Tailings Pile 3
indicated a stable and well drained cap system.

Seeps from Tailings Piles 1, 2 and 3 noted in the 1999/2000 Five-Year Review have been
mitigated to an extent. However, as observed during the May 2005 site visit, collection
of possible tailings piles seeps with meteoric water was present in Sump #1. Prior to the
de-commissioning of the scheduled Sump #1 in FY2005; Umetco needs to confirm
mitigation methods and performance on measures implemented to stop seeps from the
Club Mesa Tailings Piles have been achieved.

Club Mesa Tailings Piles 1, 2 and 3 are constructed well Placement of rock cap material
is not completed as of May 2005. Storm water run-on channels are constructed
sufficiently to divert precipitation events. Storm water run-off channels are essential
complete except for B-Plant Repository and portions of the top rock caps of Tailings
Piles 1, 2 and 3.

A storm water erosion feature of some significance was noted coming off the northeast
face of Tailings Piles 1 & 2 adjoining the Club Mesa Area. This erosion feature should
be inspected and repaired as needed.

4.4.4 Photographs

The below Photographs taken on May 11, 2005 illustrate current visual conditions for the
Club Mesa Tailings Piles.

Club Mesa Tailings Piles	Photo 1 of 4 of Tailings Pile 3 Repair

Cap Materials Stock Pile	of Suspected Joint Separation

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"> . T-;

- C'.J

'"'Ļ * '- I*' - ,

St*.

Photo 2 of 4 of Tailings Pile 3 Repair
of Suspected Joint Separation

Photo 3 of 4 of Tailings Pile 3 Repair
of Suspected Joint Separation

.-1

-4

j2~

Ļ - Ļģ ' w--t:





Photo of Tailings Pile 3 Repair of
Suspected Joint Separation

Club Mesa Storm Water Run-Off
Control Feature

Club Mesa Tailings Piles 1 & 2	Club Mesa Tailings Piles 1& 2

Storm Water Run-Off Control	Storm Water Run-Off control

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Club Mesa Tailings Pile 3 Storm	Club Mesa Storm Water Run-Off

Water Run-Off Control Feature	Erosion/Washout Feature

Operating B-Plant Repository	Club Mesa Tailings Pile 3

Partially Capped Repository

Club Mesa Tailings Pile 1 & 2	Club Mesa Tailings Pile 3

Partially Capped Repository	Partially Capped Repository

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Club Mesa Tailings Pile 1 &2
Seep Collection Sump #1

4.4.5 Recommendations

Example of Club Mesa Tailings
Piles 1 &2 Seepage Staining

Further investigation and mitigation of Club Mesa Tailings Piles seepage is required, as
based upon observations made of continued collection of liquids (rainwater, etc.) within
Sump #1.

Club Mesa Tailings Piles 1 and 2 and Club Mesa Area north facing storm water erosion
features require inspection, maintenance and repair.

Table 4.4
Club Mesa Tailings Piles

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Design and Constmct
Uravan Site Disposal
Repositories on Club Mesa
with Storm Water Run-On
and Run-Off Control
Features; Placement of
Contaminated Materials
Pursuant to RAP
Requirements; Manage and
Inspect Tailings Piles
Pursuant to RAP
Requirements; Place Soil
and Rip Rap Protective
Cover Systems; Revegetate
and Continued Long Term
Inspection and Monitoring.

Initiate Construction and
Operations of Tailings Piles
by 1988. On-Going
Operations, Maintenance,
Inspection Until
Completion of On-site
Remediation Activities.

Tailings Piles Have Been
Constructed and Operated
in Accordance with RAP
Requirements. Ongoing
Activities are Scheduled to
Complete Site Tailings
Piles Cap System
Construction.

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4.5 Club Mesa Area

4.5.1	History

The Club Mesa Area is located upslope from Tailings Piles 1, 2 and 3. This area was
used primarily for evaporation of raffinate. Mounds of raffinate crystals formed around
the spray nozzles within the spray area. As part of the raffinate spray process, two-clay
lined storage ponds were constructed upslope of the raffinate spray area. The purpose of
these ponds was to provide hydrostatic head for the spray system. Neutralized sludge
excavated from the River Ponds Area was also placed in the Club Mesa Area.

Umetco estimated that approximately 484,000 cubic yards of contaminated materials
were present in the Club Mesa Disposal Area. These Materials included 250,000 cubic
yards of raffinate crystals; 150,000 cubic yards of neutralized sludge; 40,000 cubic yards
of contaminated pond material; and 44,000 cubic yards of contaminated soils in the fringe
area.

Superficial and subsurface contamination occurred as a result of the raffinate spray
process. Superficial contamination is due to the presence of the raffinate crystals, in
addition to the windblown spray which contaminated soils in the adjacent fringe area.
Subsurface contamination is caused by seepage of excess spray liquids into the
underlying soils and bedrock through the unlined surface of the spray area.

4.5.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected excavation and on-site disposal of raffinate crystals in the Burbank
Quarry, an approved raffinate crystal storage area, and disposal of other contaminated
soils in the Tailings Piles on the Club Mesa as remedy for the Club Mesa Area. The
objective of this remedy was to remove the source of future potential contamination of
surrounding soils and the underlying soils and bedrock.

4.5.3	Site Status and RAP Requirements

Pursuant to the Remedial Action Plan guidance;

•	Removal of neutralized sludge and other contaminated material began in June

1989	and was completed in 1992;

•	Initial removal of raffinate crystals from the Club Mesa began in the summer of

1990	and was completed in mid-1992; and

•	The final removal of the raffinate crystals that are resting on the bedrock was
completed in 1994.

Approximately 3,750,000 cubic yards of contaminated material was removed from the
Club Mesa Area. Mines and portals encountered during excavation and removal of
materials from Club Mesa were sealed with earthen materials. The Remedial Action Plan

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required that material removal activities be completed by December 31, 1994. This
activity was completed in accordance with the revised milestone Remedial Action Plan
schedule by December 31, 1997 with the acceptance by the State of Colorado Department
of Public Health and Environment of the construction completion report. Final closure
activities for the Club Mesa Area included construction of a storm water diversion
structure and sediment collection areas; placing clean fill rock mulch, and reseeding the
fill areas. This activity is complete.

During 2000, seventeen borings were drilled into the mine workings on Club Mesa for
the purpose of evaluating and managing contained contaminated liquids. Five of the
seventeen borings were selected for pumping and conveyance of mine workings liquid.
Raffmate solution in the mine workings have been extracted and transferred to the Club
Ranch Ponds for evaporation. Approximately 500,000 gallons of raffinate contaminated
liquid was pumped from the mine workings during 2000 and 2001. Umetco has not
reported any additional liquids extracted from the Club Mesa Area mine workings since
the fourth quarter of 2001. Mine Features have been closed and sealed in accordance
with State of Colorado Division of Minerals and Geology mine closure specifications and
guidance documents.

Umetco has stated that the Club Mesa Area is one-hundred percent complete.

4.5.4	Summary of Site Visit Observations and Findings

Visual inspection during the site visit of May 11, 2005 indicated that the Club Mesa Area
is fully remediated. No signs of remaining contamination (raffinate crystals, discolored
soils, ponds, etc.) were observed during the visit. Vegetation has established itself and is
consistent with surrounding non-Club Mesa Area areas. The vegetation appeared to be
healthy. No open mine features were observed in the Club Mesa Area.

4.5.5	Photographs

Club Mesa Area Soil/Rock Cap	Club Mesa Storm Water

and Re-Established Vegetation	Control Feature

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4.5.6 Recommendations

No recommendations are noted.

Table 4.5
Club Mesa Disposal Area

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Remove Raffinate Crystals
and Contaminated Soils and
Place in Burbank
Repository Pursuant to RAP
Requirements; Survey
Mitigated Area Utilizing
Radiological Survey
Methods; Construct Storm
Water Run-On and Run-Off
Control Features; Place
cover Soils and Revegetate.

Club Mesa Disposal Area
Mitigation was Completed
to Modified RAP
Implementation Schedule,
December 1997.

Club Mesa Disposal Area
has been Remediated
Pursuant to RAP
Requirements. Long Term
Inspection and Maintenance
are On-Going.

4.6 Uravan Mill Areas

4.6.1	History

The Mill Areas include the APlant in the valley northwest of the Club Mesa Tailings
Piles; the B-Plant; Ore Stockpile Area; Barrel Storage Area; a Heap Leach site on a
bench below and east of Club Mesa Tailings Pile 2; and a Bone Yard for miscellaneous
scrap equipment located west of Tailings Pile 2. These areas had all been impacted by
the presence of radioactive material as a result of the Uravan operations.

4.6.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Riblic Health and
Environment selected excavation and on-site disposal of contaminated equipment,
structure, waste materials, contaminated soils and ancillary contaminated materials into
the Club Mesa Tailings Piles, the Burbank Quarry, or a disposal site in the Hk Claim
Area as the remedy for the Mill Area. The objectives of this remedy were to remove the
source of future potential contamination of surrounding soils and the underlying soils and
bedrock.

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4.6.3 Site Status and RAP Requirements

Remedial activities in the Mill Area were initiated in 1987. Initial activities included the
removal of the Ore Stockpile, Barrel Storage, Heap Leach site, and the Bone Yard
materials that totaled 160,000 cubic yards. Uranium and /or vanadium ores and mill
reagents were relocated and processed at the United States Nuclear Regulatory
Commission licensed White Mesa uranium/vanadium mill in Utah. These activities are
completed.

The mill process area consisted of the APlant and B-Plant and included the uranium
and/or vanadium milling systems and ancillary facilities located along the San Miguel
River valley floor at the base of Club Mesa and the facilities located on the canyon face
and lower bench immediately next to the Club Mesa Tailings Piles. The mill system
included ore receiving bins and crushing and sampling plant; aerofall grinding circuit;
crushed and ground ore storage bins; hot sulfuric acid leach circuit; counter-current
decantation circuit; sulfuric acid generation plant; uranium ion exchange circuit; uranium
precipitation and calcining circuits; vanadium salt roast leach circuit; vanadium fusion
circuit; metallurgical control laboratory; and solution transfer system. The mill system
also included ancillary facilities such as reagent storage and mix systems, fuel
distribution/storage systems; steam generation systems; electrical distribution systems;
equipment maintenance facilities; and office and warehouse facilities. Mill operations
facilities consisted of maintenance; office; warehouse; electrical; and liquid transfer
systems.

Mill decommissioning was conducted in accordance with a detailed plan submitted to and
approved by the State of Colorado Department of Public Health and Environment.
Decommissioning included the management and handling of such items as PCBs and
asbestos containing materials during on-site abatement operations; and the demolition of
over 50 major Uravan mill site buildings and operations support structures.

Decommissioning of the mill process systems was initiated during 1995 and hvolved
demolition of mill circuits; ancillary mill operations facilities; structural foundations; and
removal and cleanup of associated contaminated soils. Mill demolition is complete and
contaminated soils removal is complete. Contaminated soil removal was completed in
the A-Plant Area during the second quarter of 1999 and in the B-Plant Area in the third
quarter of 1999. Replacement runoff control ponds were constructed in the A-Plant Area
in 1998. The Community Center Building and the Boarding House were remediated and
renovated in 2000.

Tailings materials under County Road EE22 were removed during 2001. Upon
completion of removal activities, the area was inspected and approved by the State of
Colorado Department of Public Health and Environment on-site coordinator and the
roadway was reestablished with borrow fill and placement of road-base gravel material

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A total of 4,760 cubic yards of contaminated materials were removed from the roadbed
and placed in the B-Plant Repository.

A small evapo-transpiration (E/T) test plot was constructed in the facility of the Bone
Yard during the 2001/2002 to evaluate the feasibility of controlling toe drain fluids.
Approximately 29,200 gallons of toe drain fluid were directed to the E/T system during
the spring of 2002 to promote the natural establishment of native vegetation species in the
area.

Mill Area remediation continued with the removal of contaminated soils during 2002.
Contaminated soils and materials were placed in the B-Plant Repository. A-Plant Area
and B-Plant Area confirmation Investigation reports were approved and final reclamation
grading and drainage activities were completed in 2003. Reclamation with seeding and
placement of soil amendments for the A-Plants and B-Plant Areas began in the spring of
2003 and completed in the fourth quarter 2003.

4.6.4 Summary of Site Visit Observations and Findings

A site visit was made on May 11, 2005. Visual observations indicated that remedial
efforts for the Uravan Mill Areas are essentially complete. Storm water diversions and
control features are in place and appear to be functioning as design. Reclamation of the
Uravan Mill Area appears to be established and is similar to other non-Uravan
surrounding area. Except as noted in this review report, the Uravan Mill area remediation
is complete.

4.6.5 Photographs

Reclaimed A-Plant Areas and	Reclaimed Mill Hillside Area with Storm

Mill Hillside Areas	Water Run-Off Erosion Control Features

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Reclaimed B-Plant Areas and
Bone Yard Areas

4.6.6 Recommendations

None noted.

Toe Drain Evapo-Transpiration
Test Plot Near Bone Yard Area

Table 4.6
Mill Areas

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Remove All Contaminated
Equipment, Soils and
Materials and Place in
Designated On-site
Disposal Areas; Demolish
Mill Structures and Place
Demolition Debris in
Designated On-Site
Disposal Areas; Verify
Mitigation Utilizing
Radiological Survey
Methods; Construct Storm
Water Run-On and Run-Off
control Features; and
Recontour and Vegetate
Mill Areas.

Mill Areas were Mitigated
Pursuant to RAP and
Radioactive Materials
License Requirements -
1989.

Mill Areas have been Fully
Mitigated. Ongoing
Inspection and Maintenance
Activities per RAP
Requirements.

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4.7 Town and Adjacent Areas

4.7.1	History

The town of Uravan occupied the San Miguel River valley area just northeast of Tailings
Piles 1 & 2. Adjacent areas are:

•	The town dumps (Old Town Dump and New Town Dump) which are located on
the south side of the San Miguel River, south of Colorado Highway 141; and west
of Club Ranch Pond #4; and

•	Areas adjacent to the town affected by deposition by windblown materials,
including the Hieroglyphic Canyon, San Miguel River, and Atkinson Creek
drainage.

Tailings were used in localized construction activities and were spilled from delivery
pipelines running through the town area. Wind- and surface water transported tailings
were found in the town and adjacent drainages. Remnant tailings were also placed and
located under Colorado Highway 141.

4.7.2	Remedial Objectives

In the Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected excavation and on-site disposal of Town Area contaminated
materials; waste from the Town Dumps; remnant tailings; streams and storm water
drainage deposits; and windblown material into the Club Mesa Tailings Piles repositories,
the Burbank Quarry, or disposal site in the Elk Creek Claim Area as remedy for the Town
and Adjacent Areas. The objectives of this remedy were to remove the source of future
potential contamination of surrounding soils; underlying soils; ground water; and surface
water.

4.7.3	Site Status and RAP Requirements

All housing structures have been removed from the Town of Uravan. Contaminated soils
have been removed and transported to the Club Mesa Tailings Piles. Approximately 260
structures were removed and approximately 210,000 cubic yards of contaminated soils
were excavated from 1987 through 1994. The Town Area was graded and revegetated in
2000 after soil verification studies were completed and accepted. A historic kiosk and
overlook parking lot were constructed for public viewing and information.

Two historic structures (Community Center and Boarding House) in the Town of Uravan
have been fully remediated and renovated. Since the completion of the restoration of the
Uravan historical structures in 2000 and the completion of radiological risk assessments
in 2004, Umetco and the Rimrock Historical Society are in the process of transferring
ownership of the historical structures and associated property to the Rimrock Historical
Society for future use and preservation care. The Rimrocker Historical Society is seeking
a 2005 funding grant for exterior renovation of the Community Center Building. A

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land/structure ownership transfer of the historical properties is being negotiated with
Montrose County, Colorado. The ownership transfer will include the placement of an
institutional control on the property. As part of the transfer due-diligence, an active
radon mitigation system was installed in the Community Center Building during the third
quarter of 2004 and minor cleanup activities were conducted in the non-Remedial Action
Plan areas within the transfer boundary during the fourth quarter of 2004. These minor
general cleanup activities included areas southeast of the Community Center and
Boarding House Buildings, including the former Gym area and E-Block area.

Materials in the Town Dumps have been characterized in accordance with the Remedial
Action Plan requirements. Mill related contamination was identified in the Town Dumps.
These materials were excavated, removed and placed in the Club Mesa B-Plant
Repository. Approximately 260,000 cubic yards of contaminated materials were
removed from the Town Dumps. Final grading and seeding of the area was completed in
2000.

Dispersed deposits adjacent to Uravan were identified, removed and disposed in the Club
Mesa Tailings Repositories. These areas include portions of Colorado Highway 141;
Montrose County Road Y-ll and EE22; the Mill Hillside and Water Storage Ponds
adjacent to Hieroglyphic Canyon. Approximately 65,000 cubic yards were removed
from these areas. Remnant tailings were excavated, removed and placed in the Club
Mesa B-Plant Repository from the entrance road to the Uravan Site and Town and from
within the Town of Uravan - this Remedial Action Plan activity is complete. All tailings
material in the shoulder of Highway 141 was excavated, removed and placed in the Club
Mesa B-Plant Repository in 2000. The remediation and reclamation of these areas are
complete, except for portions of Colorado Highway 141. The State of Colorado
Department of Transportation has elected to remediate portions of Colorado Highway
141 where tailings materials remain underneath the highway roadbed. This area remains
an active site as defined by the Remedial Action Plan and Consent Decree.

Stream and storm water drainage deposits include sediments in Atkinson Creek and
Hieroglyphic Canyon streambeds. Radiological surveys have indicated that no
significant contamination is present within the Atkinson Creek Streambed. Contaminated
materials in the Hieroglyphic Canyon streambed near its confluence with the San Miguel
River have been fully remediated and were completed in 1994. Assessment of the upper
reach of the Hieroglyphic Canyon indicates that no significant contamination is present in
the streambed and excavation of the streambed contaminated materials would result in
significant environmental impacts to the water way and its ecology. Discrete deposits of
radioactive soils were identified near the mouth of Hieroglyphic Canyon and were,
excavated, removed and placed in the Club Mesa Tailings Repositories.

Windblown material identified north and south of the Club Mesa Tailings Piles footprints
have been characterized. An area averaging radiation evaluation of these areas is in the
process of determining risk and any eventual Remedial Action Plan implications. To
date, no remediation has taken place in the Windblown Areas.

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Accept as noted above, the Town of Uravan and Adjacent Areas remediation was
completed in 2003.

4.7.4	Summary of Site Visit Observations and Findings

The site visit of May 11, 2005 visually found the Town of Uravan and the Adjacent
Areas fully remediated, except for the portion of Colorado Highway 141 and the
Windblown Areas. No visible signs of remaining contamination, e.g. buildings; drums;
equipment; discolored soil; tailings; etc. were observed in these areas during the site visit.
Grading and site reclamation and revegetation of the Town of Uravan and Adjacent
Areas appeared to have been completed, and healthy-looking vegetation has been
reestablished in these areas.

The Town Dumps (Old and New) were excavated down to bedrock, covered with top soil
and reclaimed and seeded. Revegetation is fully established and appears to be healthy.

Montrose County Roads Y-ll and EE-22 have been remediated and reclaimed pursuant
to the Remedial Action Plan. The roads have been assessed and evaluated with respect to
future use. A covenant and institutional control instrument needs to be drafted. These
documents need to be finalized to reflect completion of one of the objectives of the
Remedial Action Plan with transfer of control and future use maintenance to Montrose
County.

4.7.5	Photographs

The photographs presented below illustrate site conditions as observed on May 11, 2005.

Reclaimed Area in the foreground	Reclaimed Uravan Adjacent Area

Is the former Town of Uravan	Historic Buildings and Hieroglyphic Canon

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In the distance, Un-remediated Colorado North Windblown Area located above

Highway 141	The San Miguel River Valley

4.7.6 Recommendations

1.	The State of Colorado, Department of Transportation needs to address the tailings
remaining beneath Colorado Highway 141 in accordance with the Uravan Remedial
Action Plan requirements.

2.	Institutional control need to be finalized with Montrose County Board of County
Commissioners for the management and future use maintenance of County Roads Y-
11 and EE-22.

3.	The Windblown Areas still need to be addressed as determined by the completion of
on-going assessments and evaluation.

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Table 4.7
Town and Adjacent Areas

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Remove and/or Excavate
Contaminated Soils, Debris
and Materials and Place in
On-Site Designated
Disposal Areas; Verify
Remediation by Survey
Utilizing Radiological
Methods; Construct Storm
Water Control Features; and
Re-Grade and Revegetate
Remediated Areas.

Town and Adjacent Areas
were Mitigated Pursuant to
RAP Requirements - 1994.

Area Has Been Fully
Remediated. On-Going
Inspection and Maintenance
Activities.

4.8 Burbank Quarry

4.8.1	History

The Burbank Quarry was intended to be the source of riprap for remedial activities.
Random fill and clays were mined from the quarry pit for use in remedial construction.
The Burbank Quarry was also to be used as the raffinate repository and may serve as the
repository for other wastes as approved by the State of Colorado Department of Public
Health and Environment.

4.8.2	Remedial Objectives

In 1he Remedial Action Plan, the State of Colorado Department of Public Health and
Environment selected the placement of raffinate crystals removed from the Atkinson
Creek Crystal Disposal Area; the Club Ranch Evaporation Ponds; and the Club Mesa
Spray Area in below-grade Burbank Quarry locations. Raffinate crystals were to be
dispersed in clay-lined cells that would be capped by earthen materials and riprapped for
erosion control and protection Burbank Quarry cap systems were designed in
consideration of the probable maximum precipitation events and maximum credible
earthquakes.

4.8.3	Site Status and RAP Requirements

Placement of the Raffinate crystals was initiated in 1989 and was completed in 1992.
This RAP activity has been completed.

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The raffinate crystals have been capped with an earthen cover in accordance with the
Remedial Action Plan requirements. The side slope was completed in 1993. The toe
drain was installed in 1998. The top cover was completed in 1999 with the placement of
cover riprap rock. The Burbank Quarry - Uravan Title II activity was completed in
1999/2000.

The Department of Energy (DOE) used the upper portion of the Burbank Repository for
disposing Title I radioactive materials from the Naturita processing site. Approximately
600,000 cubic yards of radioactive materials were placed in the Burbank Quarry
repository. A multi-layered cover, identical to the Uravan Tailings Piles covers, was
constructed on top of the placed contaminated materials. Permanent drainage diversion
structures and control features were constructed for storm water management to and from
the repository. The Burbank Quarry - DOE Title I activity was completed in 1998.

4.8.4	Summary if Site Observations and Findings

A site visit on May 11, 2005 visually found the Burbank Quarry remediation effort
complete, reclaimed and secure. Vegetation has been re-established and storm water
management features have been constructed and are well maintained. The covers of the
upper and lower sections of the Burbank Quarry are contiguous, separated by a fence and
surface water diversion features, which divert surface water off of the abutting mesa on
the west side of the repository.

4.8.5	Photographs

Photograph presented below illustrate the May 11, 2005 status of the Burbank Quarry
Repository:

Burbank Quarry - Uravan Title II	Burbank Quarry - Uravan Title II

Repository Cap	Repository Cap

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Burbank Quarry - Uravan Title II and
DOE Title I Repository Cap Systems

Burbank Quarry - Uravan Title II and
DOE Title I Repository Capped Systems

Burbank Quarry - Uravan Title II and
DOE Title I Repository Cap Systems

Burbank Quarry - Uravan Title II and
DOE Title I Repository Cap Systems

4.8.6 Recommendations

No recommendations are noted.

Table 4.8
Burbank Quarry

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Convert Burbank Quarry to an
On-Site Disposal Repository;
Construct Disposal Repository
meeting RAP and Radioactive
Materials License
Requirements; Construct Storm
Water Run-On and Run-Off
Control Features; Place Soil and
Rip Rap Protective Cover
System; and Revegetate.

Burbank Quarry
Disposal Repository
was Constructed; Filled
and Capped in
Accordance with RAP
Requirements - 1999.

Burbank Quarry Has Been
Fully Remediated. On-
Going Inspection and
Maintenance Activities.

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4.9 Borrow Areas on Club Mesa

4.9.1	History

The Borrow Areas on Club Mesa are not contaminated. They were intended to be used
as sources of the clayey soils and random backfill to be used during remedial activities.
The Club Mesa Borrow Area is operated pursuant to the requirement of a Mine Land
Reclamation permit issued by the State of Colorado Department of Natural Resources,
Division of Minerals and Geology.

4.9.2	Remedial Objectives

Remediation activities at these areas will not be conducted. This area is the intended
resource for clayey soils and random backfill to be used in remedial activities. Final
mine land reclamation will be accomplished pursuant to the requirements established by
the issuance of the Borrow Area Mine land Reclamation Permit.

4.9.3	Site Status and RAP Requirements

Not addressed by this or previous Five-Year Reviews

Three borrow areas exist for the Uravan Site. Two are located on Club Mesa, with one
above the Burbank Repository. The third is located in the San Miguel River valley on the
east side of Colorado Highway 141, across from the Club Ranch Ponds. The borrow
areas on Club Mesa were expanded in 1992, 1997, 2002 and 2003; which includes Kaiser
Quarry.

The Kaiser Quarry produces sandstone suitable for erosion protection materials. The
Kaiser Quarry is located west of the Club Mesa Area within Umetco's patented Kaiser
Claim Boundary.

All of the borrow areas are operated in compliance with the Mine Land Reclamation
Permits.

Umetco is planning to expand borrow operations with the development of the Surprise
Borrow Area. The BLM and the State of Colorado Mine Land Reclamation Division
were contacted for approval to drill exploration borings to locate suitable clay materials
on a Uravan Mill claim located to the southeast of the existing Club Mesa borrow area.
Pending regulatory approval an exploration program was to be initiated during late 2004
and early 2005.

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4.9.4 Summary of Site Visit Observations and Findings

During the site visit of May 11, 2005, the borrow areas on Club Mesa were observed to
be in varying degrees of quarry operations and in conformance with the Mine Land
Reclamation Permit. The valley borrow area has been reclaimed pursuant to the Mine
Land Reclamation Permit.

4.9.5 Photographs

Partially Reclaimed Club Mesa Borrow Area Stockpiled Repository Cap Materials
Taken	From Kaiser Quarry on Club Mesa

4.9.6 Recommendations

No recommendations were noted

Table 4.9
Borrow Areas on Club Mesa

RAP Requirement

Required Date of
Completion

Site Status
May 2005

Prepare On-site Borrow
Areas in Accordance with
State of Colorado Mined
Land Reclamation Division
Requirements; Process
Borrow Area Materials for
use On-Site for Disposal
Area Soil and Rip Rap Cap
Systems; and Reclaim and
Revegetate Borrow Areas.

Borrow Areas are being
Operated Pursuant to RAP
and Colorado Mined Land
Reclamation Requirements.
Borrow Areas will be
Closed at the End of On-site
Remediation Activities.

Ongoing.

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4.10 Hillside Seepage and Tailings Liquids

4.10.1	Hillside Seepage

4.10.2	History

Seepage has been occurring intermittently along approximately 4,600 linear-feet of the
Club Mesa rim. Seepage occurs near the contact between the Summerville and Salt
Wash Formations and exits the valley walls of Hieroglyphic Canyon and the San Miguel
River above the A-Plant Area. Some of the Seepage is presently collected in seepage
collection systems, including Club Mesa Tailings Piles toe drains. Collected seepage is
transferred to the Club Ranch Evaporation Pond for management. The seepage is
composed of geochemically- modified tailings solutions from the Club Mesa Tailings
Piles and the Club Mesa Spray Area.

Liquids will be forced from the Club Mesa Tailings Piles during dewatering and
consolidation; and for some time prior to and after final reclamation activities. Seepage
is collected by toe drain system at the base of the slopes of the Club Mesa Tailings Piles
and conveyed to the Club Ranch Evaporation Ponds with the Hillside Seepage
Collections System liquids.

4.10.3	Remedial Objectives

Remediation activities will minimize the potential for discharge of contaminated surface
waters form the site into the San Miguel River. The State of Colorado Department of
Public Health and Environment has selected collection and transfer of the Hillside
Seepage liquids to the Club Ranch Evaporation Ponds for management.

4.10.4	Site Status and RAP Requirements

Improvements to the Hillside Seepage Collection system were initiated and completed in
1998. The Collection System was removed in 2003. Hillside seepage has declined from
30-gallons per minute to less than 1-gallon per minute. Toe Berm Seepage and Tailings
Dewatering systems initially collected 30-gallons per minute. Current collection volumes
are estimated at less than 2-gallons per minute. Volumes should continue to decrease as
consolidation loads equalize and as remediation and reclamation comes to an end.

The toe drain collection system have been capped and sealed. However, existing toe
drain sumps appear to be still collecting liquids.

4.10.5	Summary of Site Visit Observations and Findings

On May 11, 2005, a site visit was made to visually observe Uravan Site conditions and
status of Remedial Action Plan activities. Observations of the Hillside Seepage and Toe

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Berm Seepage and Tailings Dewatering collection systems areas indicated the presence
of seepage liquids at Sump #1 toe drain collection piping. Observations of hillside
geological formations also indicated the presence of continuing seepage in areas below
the Club Mesa Tailings Piles rim.

4.10.6 Photographs

The photographs presented below illustrate the status of a portion of the Hillside Seepage
Collection System and Toe Berm Seepage and Tailings Dewatering Liquids Collection
System

Hillside Area Seepage Collection Channel Hillside Area Seepage Collection Pond

4.10.6 Recommendations

Assessment and evaluation of the Hillside Seepage and Toe Berm Seepage and Tailings
Dewatering Liquids collections system should be continued on a regular interval to
determine the effectiveness of this collection method.

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4.11. Pond Liquids

4.11.1	History

Contaminated liquid contained in the Club Ranch Evaporation Ponds consisted primarily
of the toe drain and hillside seepage collected liquids since 1985 and raffinate solution
contained in the ponds since the last discharge of raffinate to the ponds in 1984. These
liquids seeped into the subsurface at an undermined rate. Ponded water evaporates at a
rate of approximately two-gallons per minute per acre.

4.11.2	Remedial Objectives

Remediation activities will minimize the potential for contaminated surface water to be
released into the underlying bedrock and aquifer.

4.11.3	Site Status and RAP Requirements

Club Ranch Evaporation Ponds were constructed to manage liquids collected from the
Club Mesa Tailings Areas, Toe Berm Seepage and Tailings Dewatering Liquids
Collection System, Hillside Seepage Collection System, any other contaminated liquid
collected as part of site remedial activities. Collected liquids have been effectively
collected and transferred to the Club Ranch Ponds for evaporation. Club Mesa and the
River Area Ponds have been fully remediated and are complete.

4.11.4	Summary of Site Visit Observations and Findings

On May 11, 2005, a site visit was made to observe site remedial activities and the status
of completed components. Collection of Club Mesa Hillside Seepage and Club Mesa
Tailings Piles Toe Drain Liquids has been terminated.

4.11.5	Photographs

Photographs of these systems are presented in the above sections.

4.11.6	Recommendations

An updated assessment and evaluation of the closed collection systems performance
needs to be reported to the State of Colorado Department of Public Health and
Environment pursuant to the requirements of the Remedial Action Plan.

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4.12 Storm Water Surface Runoff

4.12.1	History

Surface water run-off from the Umetco Uravan Superfund Site will continue to occur
after remediation and reclamation activities of the site have been concluded. Hydrology
studies for the existing and reclaimed facilities were conducted. Water quality of the
storm water run-off is governed by Section 5.3.3 of the Remedial Action Plan.

4.12.2	Remedial Objectives

Remediation activities will minimize the potential for contaminated surface water to be
released into the San Miguel River. The State of Colorado Department of Public Health
and Environment has selected as the remedial choice for surface water management - the
construction of a system of storm water run-on and storm water run-off control features
that will collect and convey storm water run-on away from remediated features; collect
storm water from with the RAP Boundary for management at the Club Ranch
Evaporation Ponds until site remediation and reclamation activities are concluded; and
collect and channel storm water run-off from the capped repositories surface areas in
such a manner to preclude erosion damaged to constructed remedial components and
convey those storm waters to the appropriate surface water drainage system.

4.12.3	Site Status and Rap Requirements

The construction and maintenance of the Uravan Superfund Site storm water
management system continues as site remedial activities progress. The sizing and
materials of construction are consistent with the requirements of the Remedial Action
Plan.

4.12.4	Summary of Site Visit Observations and Findings

On May 11, 2005, a site visit was made to conduct a visual inspection of the Uravan
Superfund Site Storm Water Management System. Visual observations indicated that on-
going construction and lining of surface water run-off control features are consistent with
the Remedial Action Plan. However, an excessive erosion feature was observed on the
north side of the Club Mesa Tailings Piles Repository location. This erosion feature is
not a part of the designed surface water collection system, but i has occurred due to
substantial repository cap run-off into a non-constructed drainage.

4.12.5	Photographs

The photographs of storm water and surface water control features are presented in the
previous sections.

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4.12.6 Recommendations

Continued inspection should be consolidated t) identify and respond to surface water
erosion. Repair of identified erosion features should be conducted in a timely manner to
prevent potential damage of remedial activities in progress and of completed site
remedial components.

4.13 Groundwater
4.13.1 History

4.13.1.1	Salt Wash Member of the Morrison Formation

Seepage from the Uravan Mill operations and waste disposal has infiltrated in to the Salt
Wash and historically created a body of perched fluids on Club Mesa. This infiltration
primarily consists of raffinate from the Club Mesa Spray Area and seepage from the Club
Mesa Tailings Piles. Hydrologic data monitoring wells constructed in the Salt Wash
indicate that the areal extent of the fluids is in the area beneath and down gradient from
the three Club Mesa Tailings Piles and spray evaporation area. The direction of ground
water flow is to the northeast towards the west and south San Miguel River Valley walls
and to the walls of Hieroglyphic Canyon. Perched liquids on top of the Summerville
Formation have dispersed and no significant seepage has been noted along the canyon
valley walls.

4.13.1.2	Kayenta-Wingate Sequence

Umetco's past operations on the Club Mesa and past waste disposal activities pose
potential impact to the ground water quality in the Kayenta-Wingate aquifer beneath Club
Mesa. Past activities which could potentially impact the aquifer were the use of the Club
Mesa Spray Area and Club Mesa Tailings Piles. These activities have ceased and the
areas reclaimed.

The low permeability of the Summerville shale formation above the Kayenta-Wingate
aquifer prevents significant contaminant transport down to the Kayenta-Wingate. In
1986, Umetco drilled ground water monitoring wells V-768 and V-769 into the Kayenta-
Wingate Formation beneath the Club Mesa. These wells showed no contamination at this
time.

4.13.1.3	River Valley: Kayenta-Wingate Sequence

Umetco's liquid waste handling and disposal operations in the San Miguel River valley
released contaminants into the Kayenta-Wingate aquifer. The most significant
contribution to ground water contamination was the disposal of liquid raffinate in the

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unlined Club Ranch Ponds. Seepage from the Club Ranch Ponds has been found in
ground water monitoring wells beneath and down gradient from the ponds.

The ground water system in the San Miguel River valley is a complex, fractured aquifer
that maintains a recharge-discharge relationship with the San Miguel River. The ground
water monitoring well system in the river valley has a measured contamination in the
fractured aquifer system. This contaminated ground water acts as a source of non-point
contamination to the San Miguel River. The sandstone matrix likely produces very little
liquid relative to the fractures, and may contribute contaminants to the fracture system at
a relatively slow rate.

4.13.2	Remedial Objectives

Remedial activities will minimize the potential for contaminated subsurface waters to be
released into the San Miguel River.

Sampling of the Club Mesa ground water wells that monitor the Kayenta-Wingate
Formation shall provide data for continuing confirmation that ground water quality in the
Kayenta-Wingate Formation beneath the Club Mesa is acceptable.

The Remedial Action Plan activities for the mitigation for Kayenta-Wingate aquifer
restoration is to remove and manage fractured bedrock contamination and improve
Kayenta-Wingate Formation contained ground water quality to a beneficial use. As
stated in the Remedial Action Plan, achieving this goal, coupled with the removal of
raffinate crystals and ponded liquids from the San Miguel River valley, will substantially
reduce the contaminated non-point load to the river.

4.13.3	Site Status and RAP Requirements

The six Club Mesa Salt Wash ground water monitoring wells were abandoned in late
2003. The six monitoring wells were completed into the Salt Wash Member of the
Morrison formation under the Club Mesa. To date, ground water monitoring is
performed only with the Points of Compliance monitoring wells.

The Remedial Action Plan requires that Kayenta-Wingate ground water in the Club
Ranch Ponds Area be extracted and evaporated. Ground water pumping is to be
conducted at a rate of 60-gallons per minute and operational adjustments be made as
necessary to maintain optimal system performance. The extracted ground water is to be
conveyed to and evaporated in the lined Club Ranch Ponds. Performance of the ground
water extraction system is to be evaluated annually.

The initial ground water extraction system was installed in 1991 and upgraded in 1996
and again in 1998. Ground water pumping began in 1991 in accordance with Remedial
Action Plan In 1997, the ground water cleanup effort was evaluated in detail and an
optimized system was developed so that contamination liquids from low-permeability

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zones in the Kayenta-Wingate aquifer could be extracted. This optimized system was
installed in 1998 by drilling and completion of 12 new extraction wells. The change in
ground water withdrawal has been effective in reducing contaminant concentrations.

In general, the ground water extraction and Club Ranch Evaporation Pond System has
removed approximately 15,000 tons of contaminants from the ground water flow regime.
This action has helped reduce contaminant loading to the San Miguel River system.
During the past six years, there have been no impacts to the San Miguel River. River
standards for aluminum, cadmium, copper, iron, manganese, selenium, uranium, radium,
sulfate, and unionized ammonia have not been exceeded.

Because of ground water extraction performance, and the overall effectiveness of the
ground water extraction system, Alternate Concentrations Limits (ACL) have been
approved and ground water pumping has been discontinued, except for the shallow
ground water wells developed in the shallow alluvial deposits beneath the old Club
Ranch Ponds. Kayenta-Wingate gmind water extraction ended in the fourth quarter of
2003. Umetco is preparing plans for approval to withdraw ground water extraction
pumping systems and to effectively abandon the extraction wells in the Club Ranch and
San Miguel River valley areas.

4.13.4	Summary of Site Visit Observations and Findings

On May 11, 2005, a site visit was made to the Uravan Superfund site for the purpose of
observing on-site remedial activities. The Kayenta-Wingate ground water extraction
system and the Club Ranch Evaporation Ponds were being operated in conformance with
the Remedial Action Plan. Evaporation of extracted ground water is now limited to Club
Ranch Ponds CRP #1 and CRP #8 with pending closure of CRP #4 during 2005.

4.13.5	Photographs

No Photographs were taken of ground water recovery systems during this scheduled
Five-Year Review Site Visit.

4.13.6	Recommendations

Evaluation of first Quarter FY 2005 Ground Water monitoring data indicates that ground
water has not been adversely affected by Uravan operations when applying Alternate
Concentration Limits. No Recommendations are made.

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5.0 MISCELLANEOUS REMEDIAL ACTION PLAN REQUIREMENTS

5.1	Requirements

The Remedial Action Plan (RAP) sets forth monitoring and reporting requirements to be
performed during the implementation of Uravan Site remedial activities. Environmental
and occupational health and safety data are required to be collected, evaluated and
submitted annually to the State of Colorado Department of Public Health and
Environment for review and approval pursuant to the Consent Decree and Condition 30
of the site radioactive materials license. The five year review process evaluates this
environmental monitoring data and worker protection programs to determine if remedial
activities at the Uravan Site are protective of human health and the environment. This
five year review included the comparisons made by Umetco of the 1987 to 1991; 1992 to
1996 and the 1997 to 2001 data sets for the previous five-year reviews to the current data
set maintained by Umetco-Uravan.

5.2	Environmental Review

The Umetco-Uravan Environmental Review evaluates the data collected and presented in
the Uravan Annual Reports for the following environmental monitoring activities:

•	Metrology

•	Ambient Air

•	External Gamma

•	River Sediment, soils and Grazing Uptake

•	Tailings Pile Number 2 and 3; and the Burbank Repository

•	Rim Erosion Monuments

•	Liquid Waste Management

•	Surface Water Monitoring

•	Ground Water Monitoring

•	Since June of 1988, no point source air and NPDES permit discharges from the
Uravan site have occurred. All remedial activities at the Uravan Site have been
conducted with "zero Point-source" discharges to the San Miguel River.

5.2.1 Meteorology

The Uravan Site meteorological database includes temperature and precipitation records
from 1961. During the most recent period of record, temperatures ranged from 110° to
minus 23° Fahrenheit. Yearly precipitation averages 12inches to 13 inches with a range
of 7.1 inches to 21.2 inches. The maximum 24-hour storm event recorded during the
most recent five-year period was 1-inch of precipitation and did not result in a discharge
from the remedial activities areas to the San Miguel River. Significant precipitation
events near the Uravan Site have caused mud/land slides that have impacted Colorado
Highway 141. Significant storm events within the Uravan Site have not impacted the
Uravan Site adversely.

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5.2.2 Ambient Air Quality

Contaminated material management at the Uravan Site has been ongoing as part of the
remedial activities since 1987. Since 1987, over 3,000,000 cubic yards of uranium mill
tailings; contaminated soils; demolition debris; and raffinate crystals have been excavated
and/or demolished, transported, placed and compacted while conducting remedial
operations. The removal of large volumes of contaminated materials and associated
cleanup of the remedial areas has resulted in improved air quality, as demonstrated by
air-monitoring data collected at the site since 1987.

Air monitoring data collected at the Uravan Site includes total suspended particulates
(TSP), radionuclide particulates and radon-222. This data is collected in accordance with
the site air emissions permit and radioactive materials license. Data collected during this
most recent five-year review period indicates that airborne concentrations are below
levels prescribed for by the State of Colorado Radioactive Materials License and air
emissions permits issued for on-site remedial activities.

5.2.3	External Gamma

External penetrating gamma doses are monitored using location TLD systems that are
exchanged quarterly. Annual average net gamma dose rates recorded for the nearest
resident is 4 mREM per year, which is five percent of the regulatory public dose limit set
forth in Part IV of the State of Colorado's radiation control regulations.

5.2.4	San Miguel River Sediment, Soil, Vegetation, and Grazing Uptake

Routine river sediment, soils, vegetation, and grazing monitoring requirements were
removed from the Uravan's Radioactive Materials License in 1998. Evaluation of the
previous monitoring data indicated that these media were not useful in assessing remedial
efforts undertaken at the Uravan Site.

5.2.5	Tailings Pile Number 2 and Number 3; and Burbank Repository

Tailings Pile Number 2 and Number 3 are monitored for lateral movement, settlement,
phreatic levels and drainage. The Burbank Repository is monitored for lateral surface
movement, surface settlement and seepage. Based upon Umetco's comparison of field
measurements of these geotechnical parameters and as reported to the State of Colorado
Department of Public Health and Environment; there are no unexpected or discernible
trends that would indicate slope instability of the tailings piles or the Burbank Repository.

5.2.6	Rim Erosion Monuments

Due to on-going site remedial activities, rim erosion monitoring activities were curtailed
in 1998 with the concurrence of the State of Colorado Department of Public Health and

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Environment. Rim erosion monitoring will be re-instituted as part of "long-term"
surveillance of the site at the conclusion of site topographical altering remedial activities.

5.2.7	Liquid Waste Management

The Club Ranch Evaporation Ponds were constructed to manage on-site liquid waste
during site remedial activities. The ponds are used to evaporate extracted groundwater;
collected hillside seeps; and surface water run-off from active remedial locations.
Currently, only three lined ponds remain in service; i.e. CRP-1, CRP-4 and CRP-8. Club
Ranch Pond Number 4 was taken out of service in May 2005 due to damage incurred to
its liner system. CRP-4 is scheduled for removal during the summer of 2005.

Run-Off Collection Monitoring: Runoff collection ponds have been monitored according
to the requirements set forth in the Remedial Action Plan and in the Uravan radioactive
materials license. Evaluation of analytical water quality data obtained from these ponds
indicate no significant changes in storm water run-off water quality as compared with
previous monitoring events. Until site remedial activities are concluded and revegetation
matures, storm water run-off chemistries are not expected to change significantly.

Hill side Seepage Collection System Monitoring: Hillside seepage from Club Mesa is
collected, evaluated and managed within the Club Ranch Ponds. The Remedial Action
Plan requires that liquid collected from the Hillside Seepage Collection System be
evaluated. Three technical points for comparison are used to determine the effectiveness
of the collection system; 1) quantity and quality of collected liquids; 2) San Miguel River
monitoring; and 3) ground water monitoring.

Water quality samples are collected and seepage flows are measured from the hillside
monitoring stations. Evaluation of the water quality data shows some variation in
chemistry of the hillside seepage. Umetco has attributed these variations to natural
fluctuations in precipitation, infiltration and run-off from the Club Mesa hillside.
Evaluation of hillside seepage flow rates indicate a continuing decrease, but in volumes
that still require management at the Club Ranch Evaporation Ponds.

Ground water associated with the Wingate Formation is periodically monitored, sampled,
analyzed and evaluated. Evaluation of Wingate Formation monitoring wells indicated no
apparent impact from the hillside seepage. Ground water associated with the Kayenta
Formation is periodically monitored, sampled, analyzed and evaluated. Based upon
water quality data obtained from Kayenta ground water analyzed samples, water quality
appears to be improving, which indicates that the hillside collection system is effective in
intercepting flows to the San Miguel River.

5.2.8	Surface Water

Surface water monitoring data is collected quarterly from six sampling locations along
the San Miguel River to assess potential environmental impacts. The river data include

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stations upstream, downstream, and within the remedial active areas. Total Dissolved
Solids (TDS) concentrations are within prescribed limits. This and other chemical data
would suggest that the Uravan Site does not contribute measurable quantities of salts to
the river system. During the past 15-years, contaminant flux to the San Miguel River has
been reduced to levels that have no measurable impact on the river system.

5.2.9 Ground Water

Ground water at the Uravan Site has been monitored since 1987 in accordance with the
Remedial Action Plan Monitoring activities include wells on Club Mesa and within the
San Miguel River Valley. Since 2003, ground water monitoring has been limited to the
Points of Compliance Wells in accordance with approvals given by the State of Colorado
Department of Public Health and Environment. Except for shallow perched liquids,
ground water pumping and management at the Club Ranch Ponds has been terminated.
Current operations at the Uravan Site appear to not impact ground water.

5.3 Occupational Health and Safety

Umetco has established a documented occupational health and safety program at the
Uravan Site, which includes training; work-place surveillance; program administration
and; quality control/quality assurance review/oversight. Radiological worker protection
programs at the Uravan site meet the requirements of the Colorado Rules and Regulations
Pertaining to Radiation Control as administered by the Colorado Department of Public
Health and Environment. Uravan health and safety policies and procedures conform to
the standards promulgated by the Occupational Safety and Health Administration
(OSHA). Umetco has implemented a self-audit program that routinely evaluates the
effectiveness of the radiological, health and safety programs at the Uravan Site using
internal QA/QC audit procedures and periodically by independent non-Umetco discipline
specific experienced professionals.

5.3.1 Radiological Exposure

Employees of the Uravan Site Operations are exposed to radon progeny, alpha, beta and
gamma radiation, airborne dusts containing natural uranium, thorium-230, radium-226,
and other decay products from the uranium decay chain. The State of Colorado,
Radiation Management Program; regulates occupational exposure levels within the work
place and where the public may be exposed. Umetco implements and completes annual
performance audits, which evaluates the level of radiological occupational exposure at
the Uravan Site. These annual performance audits have indicated that radiological
exposure levels for the Uravan operating period of 1991 to 2001 have been maintained
As Low As Reasonably Achievable (ALARA).

Since 2001 occupational exposure monitoring has not been required for site employees,
in that routine monitoring has indicated that radiological exposures have been met
radiological protection standards established for the Uravan Site. Specifically, the

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potential for radiological exposure for workers at the Uravan Site are less than ten-
percent (10%) of the applicable radiological exposure standard established for the site.

The radiological dose to the nearest resident potentially affected by Uravan Site
operations was 4-mrem, well below exposure standards set for the public.

5.3.2 Worker Occupational Safety and Health

Uravan Site safety and health surveillance programs provide monitoring and management
of potential worker workplace exposures to noise and harmful materials. Remedial
activities at the site generate silica dust from the use of heavy earth moving equipment in
predominantly sandstone-bearing areas. Uravan manages the potential exposure for silica
dust by implementing dust mitigation operations and by providing worker protection
where necessary. Occupational exposure monitoring for silica dust indicates that
exposure levels are below that prescribed for by OSHA.

Site surveillance programs for worker safety and health for potential heavy metal
exposure in the remediation area have indicated that airborne concentrations are presently
being maintained below applicable OSHA standards.

Exposure to elevated noise levels in the Uravan operation areas is anticipated and
observed. Elevated noise exposure is due to the use of heavy earth moving and
construction equipment. As such, hearing protection is mandated for personnel working
in and or around remediation activities where noise levels exceed the OSHA Action
Level of 85dBA.

5.4 Quality Assurance and/or Quality Control (QA/QC)

UMETCO has implemented RAP Quality Assurance and a Quality Control Program
(QA/QC) for the purpose of observing, testing and documenting Uravan Site Remedial
Activities. The QA/QC control of site activities and remediation is accomplished by:

1.	Generation of design, operation history and completion reports for each phase of
the Uravan Site remediation;

2.	Internal and external performance audits against documented permit, license, and
RAP remediation criteria, and;

3.	Umetco funding of a State of Colorado on-site coordinator to review remediation
performance against documented permit, license and RAP remediation criterion.

Umetco generates quarterly reports, which have been filed with the State of Colorado.
These quarterly reports detail the status of ongoing remediation efforts at the Uravan site
and the scheduling of future remediation efforts. As each remedial phase is completed,
Completion Reports are filed with, reviewed and approved by the State of Colorado on-
site coordinator. Annual reports are generated, which detail occupational and
environmental monitoring and/or surveillance observation data during the remediation

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efforts and include QA/QC documentation. Additional QA/QC data is contained in the
project files, which include geotechnical testing related to the site remediation.

5.5 Community Relations

Umetco Minerals Corporation is actively involved with local communities of Naturitia
and Nucla. These activities include preservation of the historic structures of Uravan, the
development of a public recreation area outside the CERCLA Site Boundary, and
decontamination of an office building for future utilization by local communities.

In 1999, Umetco completed restoration work on property owned by the Nature
Conservancy. This work included removing radioactive materials and revegetating the
disturbed areas. Restoration activities included constructing a rest stop for public
viewing and for people visiting the Nature Conservancy property.

5.5.1	Rimrocker Historical Society

Since the completion of the restoration of the Uravan historical structures in 2000 and the
completion of radiological risk assessments in 2004, Umetco and the Rimrock Historical
Society are in the process of transferring ownership of the historical structures and
associated property to the Rimrock Historical Society for future use and preservation
care. The Rimrocker Historical Society is seeking a 2005 funding grant for exterior
renovation of the Community Center Building. A land/structure ownership transfer of
the historical properties is being negotiated with Montrose County, Colorado. The
ownership transfer will include the placement of institutional controls on the property.
As part of the transfer due-diligence, an active ladon mitigation system was installed in
the Community Center Building during the third quarter of 2004 and minor cleanup
activities were conducted in the non-Remedial Action Plan areas within the transfer
boundary during the fourth quarter of 2004. The minor general cleanup activities
included areas southeast of the Community Center and Boarding House Buildings,
including the former Gym area and E-Block area.

5.5.2	Community Relations Interviews
Uravan Five-Year Review Community Relations

As part of the Five-Year Review process; U.S. EPA, Region 8 interviewed four Uravan
area stakeholders on June 1 and 2, 2005.

All of the persons interviewed expressed satisfaction with the remedial actions to date.
The work is well done and the cleanup is a benefit to the areas communities.

Those interviewed believe that future cleanup work will be satisfactory with some
concerns. Because of a large amount of spring moisture, the pond work is behind
schedule. Equipment is being moved to the site to begin the pond work. There are no

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doubts that the work will be completed. Umetco has been responsible and responsive.
As an example, Umetco promptly addressed a recent tear in a pond liner.

The transfer of the property to Montrose County for lease to the Rimrockers Historical
Society has been a slow process. The transfer will occur after the cleanup is completed.
Some buildings will likely need renovation. The Rimrockers will establish a historical
museum about uranium mining in the area.

There is some concern about waste left under the highway. The Colorado Department of
Transportation is working on the issue. There also is concern about what will happen
with the abandoned bridge on the west end of the site.

Those interviewed said that people in the area are generally satisfied with the work.
These Uravan area stakeholders and residents believe that the remedy is protective of
human health and the environment. The comments of the persons interviewed included
the following:

5.5.2.1	Citizen

Citizen comments were:

•	The remedy has been positive. Completed work has been done well.

•	Starting on ponds. Some concern about the ponds: How they will be cleaned up
and when. Behind on work because of spring moisture. Believes the work will
get done ok.

•	Less satisfaction on transfer of property to historical society (Rimrockers). Has
been slow process.

•	Paradox area. County will put restrictions on road but not close it. Umetco will
need to provide a map and information to help process.

•	Need for water assessment and reclamation after site completion.

•	Concerned about supplemental standards for highway - waste under highway.
CDOT is working on this - it will get done. Concerned about the abandoned
bridge on west end. What's going to happen with the bridge?

5.5.2.2	Local Government

Local Government comments were:

•	Good cleanup to this point. Believe that good work will continue. Have the
ponds left to clean up.

•	Historical society waiting for cleanup to be complete so UMETCO can turn the
property over to Montrose County, which will lease it to the Rimrockers. Some
buildings will likely need some renovation.

•	People in area generally satisfied with work. Mayor not sure it all needed to be
done but it's a good cleanup.

5.5.2.3	State Government

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State Government comments were:

•	Remedy is protective of human health and the environment.

•	Local stakeholders are satisfied.

•	Mr. Stoffey maintains contact with locals and hears concerns and opinions.

•	Some concern about leaving waste under the highway and the abandoned bridge.
Umetco has been very responsible.

•	Recent finding of tear in pond liner resulted in Umetco promptly addressing the
problem.

•	Umetco is mobilizing summer 2005 construction equipment on site the week of
May 30, 2005 and starting with the Club Ranch Evaporative Ponds cleanup.

5.5.2.4	Umetco Minerals Corporation

Umetco Minerals Corporation comments were:

•	Commented that this has been so far an 18 year project.

•	There have been three or four public hearings by the State.

•	Has never heard public comment that the cleanup has been done the wrong way.

•	There were concerns from some (the Western Colorado Congress) about
importing waste (such as Shattuck) to the site.

•	Umetco has kept in close contact with locals over the years. Mr. Junge mentioned
the names of some of those local persons as; Leo Large, Mary Helen DeKoebend,
Cameron Riley and his predecessor plus others such as the county attorney, other
commissioners.

•	There may have been a few locals who feel they got a raw deal but most feel that
they got a good deal from the cleanup.

•	Umetco is trying to get the Uravan historical buildings property transferred so the
Rimrockers can set up a historical museum about the uranium mining in the area.

•	Noted that the local historical society had gotten a grant from the state historical
society but could not work on site because of hazard waste training requirements.
Umetco did the work for the local historical society even though the cost
exceeded the grant.

5.6	Compliance

The Uravan Remedial Action Project is in substantial compliance with the Consent
Decree and the Applicable or Relevant and Appropriate requirements as documented in
the Record of Decision for the Uravan Site. All remedial action deadlines as specified by
the RAP, as modified, and as required to date have been met. The remedial activities
conducted at the Uravan Site, thus far, have reduced the release of contaminates from site
source areas by the construction of engineered remedial control features and; as such, the
remedy selections continue to be protective of human health and the environment.

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6.0 RECOMMENDATIONS

The review of the remedial activities and monitoring data indicate that changes to the
selected remedies as outlined by the Remedial Action Plan are not needed. It is
recommended that the Remedial Action Plan continue to be implemented in accordance
with the approved plans, specifications and project procedures.

During the May 11, 2005 Site Visit and subsequent evaluation of remedial activities at
the Uravan Superfund Site, the following recommendations are suggested for review and
implemented where and when appropriate:

1.	Provide a definitive time-line schedule for the implementation and completion of
RAP construction/closure activities, reports i.e.:

•	Club Ranch Ponds.

•	Club Mesa Tailings Piles.

•	B-Plant Area Repository.

•	Mill Hillside and Mill Areas.

•	Hillside Seepage Management.

•	Surface water run-off control features.

•	Ground water monitoring.

Umetco has presented its schedule to complete remedial activities at the Uravan
Superfund Site for the above listed areas. To ensure conformance with the Remedial
Action Plan, a discussion of the balance of the work plan and their objectives needs to
be presented to the regulatory community as a source of information for public
disclosure.

2.	Provide a continued systematic management program of collected site liquids from
hillside seepage collection system(s) and storm water runoff from active repository
units.

Site visit observations indicated the presence of liquids that are still collected by the
Toe Berm and Hillside Seepage collections systems. Collected liquids have not been
characterized as hill side seepage, rain water or snowmelt. As part of the continued
evaluation of the Remedial Action Plan Objectives and the methods by which to meet
those objectives, an assessment and an evaluation of how future post-remediation
Hillside and Toe Berm seepage collection methods and collected liquids management
will be implemented needs to be completed, reviewed and approved by the regulatory
agencies, and implemented.

3.	Provide an updated maintenance and repair program of constructed storm water
management systems.

Site visit observations indicate the need to inspect and repair erosion features created
by storm water run-off from the Club Mesa Areas and Club Mesa Repositories. This
would include those areas that are now part of site drainage patterns because of

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changes in topography by the construction of waste repositories. Storm water
channel construction has modified surface water flows and directed drainage to
existing drainage ways and created the erosion feature noted on the north face of the
Club Mesa Tailings Piles 1 & 2 and The Club Mesa Spray Area Repository.

4.	Continue to provide inspection, repair and maintenance of in-service Club Ranch
Ponds; and implementing a systematic closure of the Club Ranch Ponds that are
deemed non-serviceable and/or are no longer required as liquid management systems
supporting other on site RAP activities.

The May 11, 2005 site -visit inspection initially identified six liner failures in Club
Ranch Lined Evaporation Pond CRP #4. A detailed visual inspection conducted by
Umetco Minerals Corporation was performed on May 12, 2005, which identified two
additional liner failures for CRP #4 and three liner failures for Club Ranch Lined
Evaporation Pond CRP #8. Club Ranch Lined Evaporation Pond CRP #4 was taken
out of service; drained of its contents and is scheduled for removal/remediation
during the summer of 2005. However, CRP #8 has not been schedule for repair. The
use of lined evaporative ponds is to be conducted in a manner that presents them
suitable for service. While the liner failures were noted on the crest of the pond
berm; inspection of the leak detection sump does not indicate excessive collected
liquid volume generation; and does not necessarily present a potential for release of
its contents to the environment. CRP #8 should be maintained in a physical condition
consistent with the requirements of the Remedial Action Plan. CRP # 8 should be
fully inspected and repaired as required to maintain liquid containment. CRP #1
Pond has been removed from service.

5.	Develop a "Windblown Area" assessment and evaluation investigation using as a
minimum "area-averaging methods" as prescribed by the Colorado Department of
Heath - Radiation Management Program Guidance. When the Windblown Area has
been assessed, draft a report summarizing observed observations, assessing the risk to
public health and the environment, and mitigation recommendations, if any.

6.	Verify the proper disposition and action on disposal of PCB containers stored within
the RAP boundaries and have the PCB containing materials managed in a manner
consistent with environmental regulations governing the recordkeeping, storage,
handling and disposal of PCB containing materials.

7.	Resolve issues with the Colorado Department of Transportation for the management
and remediation of radioactive waste materials remaining beneath Colorado Highway
141 and implementing response in concurrence with the RAP.

8.	Finalize Institutional Control Agreement and its implementation by Montrose County
Board of County Commissioners for Montrose County Roads Y-l 1 and EE-22.

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US EPA, REGION 8: MAY 2005
FIVE YEAR REVIEW RECOMMENDATIONS
FOR

UMETCO MINERALS CORPORATION URAVAN SUPERFUND SITE

Item Number:

Issue:

Recommendation:

Due Date:

Responsible Partv:

1

Existing time-line schedule for implementation and
completion of RAP activities is not current.

Issue completion schedule
acceptable to regulatory agencies
consistent with RAP requirements.

December 31,2005

Umetco Minerals Corporation and
CDPHE

2

Presence of liquids inhillside collection sumps.

Make an engineered/technical
assessment of the performance of
closed/capped hillside collection
system.

November 30,2005

Umetco Minerals Corporation

3

Portion of existing Club Mesa storm water
management features show excessive erosion.

Provide systematic Inspection and
O&M Plan for constructed and
existing storm water management
system component features.

November 30,2005

Umetco Minerals Corporation

4

In-service Club Ranch Ponds have numerous liner
failures.

Provide updated and revised
inspection plan requiring the
timely repair and/or
decommissioning of subject
evaporative CR Ponds.

October 31,2005

Umetco Minerals Corporation

5

Inspection, sampling of the wind blown areas north
and south Uravan Site indicate the presence of
airborne dispersed radioactive materials.

Provide for a wind-blown area-
averaging assessment plan and
implementation schedule which
evaluates public health and
environmental risk.

December 31,2005

Umetco Minerals Corporation and
CDPHE

6

Timely management of stored PCB's.

Verify proper transport,
management and disposal of PCB's

October 31,2005

Umetco Minerals Corporation

7

Radioactive materials beneath Colorado Highway
141

Coordinate with the State of
Colorado Department of
Transportation for the timely
removal and mitigation of
Colorado Highway 141 radioactive
materials, which is consistent with
the Remedial Action Plan

December 31,2005

Colorado Department of
Transportation, CDPHE and
Umetco Minerals Corporation.

8

Land use management of Montrose County Roads
Y-ll and E-22 is not consistent with the
requirements of the RAP and Consent Decree.

Provide formalized institutional
control document with Montrose
County which will ensure for the
timely and proper land use control
for future use, repair and
maintenance of County Roads Y-
11 and E-22.

December 31,2005

US-EPA(8), CDPHE, Montrose
County and Umetco Minerals
Corporation

EPA Region VIII Five Year Review
Uravan Site - Umetco Minerals Corporation

6-3

Section 6
September 2005


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