4/14/2000 “Restoration
Grant Funding – A Pilot Year”
Carol Fox, Restoration Program Chief, Natural Resource
Damage Program
Introduction
This presentation summarizes the past accomplishments and
present activities of the State of Montana’s Natural Resource Damage
Program’s (NRDP) restoration initiative and provides a glimpse into the
future. I first review the damage
lawsuit and partial settlement that lead to funding opportunities for
restoration in the Basin. Next I
review the major aspects of the Restoration Plan.
I finish by addressing the questions provided by Dr. Vicki Watson that
focus on overall visions/goals and coordination possibilities.
The NDRP Restoration Initiative covers the entire Upper
Clark Fork River Basin (UCFRB), not just the Clark Fork River.
The initiative involves restoring or replacing natural resources that
were injured, and/or services provided by those resources that were lost, due
to releases of hazardous substances from ARCO and its predecessor’s mining
and mineral processing operations in the UCFRB. In addition to surface water
and fisheries, public natural resources covered by the initiative include
groundwater, wildlife, and wildlife habitat.
In its NRD lawsuit (Montana v. ARCO) filed in
1983, the State asserted a restoration damages claim against ARCO for the cost
of restoring to baseline, or replacing, the natural resources that it had
documented were injured or lost as a result of releases of hazardous
substances in the UCFRB. The goal
of remediation is to clean up the hazardous substances at a Superfund site so
that the public health and environment are protected against further harm from
those substances. Restoration
activities encompass the additional effort beyond remediation to return
injured natural resources to their uncontaminated condition.
The State also asserted a damage claim seeking compensation for the
lost use and intrinsic value of the injured natural resources (compensable
damages).
In 1998, the State and ARCO reached a partial settlement
of the natural resource damage lawsuit via a two-step consent decree that
settled some of the state’s claims and set up a process by which remaining
claims would be resolved. Among
other provisions, the state received approximately $130 million to restore or
replace the injured natural resources and lost services and $80 million to
implement the Superfund remedy on Silver Bow Creek (SBC).
The State reserved its restoration damages claims for Butte Area One,
the Clark Fork River, and the Anaconda Uplands.
For a summary of all the major provisions of settlement, see Attachment
1.
In 1995, the State issued
its Report of Assessment, which included about 40 separate reports describing
and quantifying the injury to natural resources in the UCFRB and the damages
that the state would seek at trial. The
groundwater injury reports found that more than 600,000 acre-feet of
groundwater in areas of Anaconda, Butte, Milltown, and Rocker have been
contaminated. The aquatics injury
reports found that the CFR should have 5 times more fish than it currently
has, and that Silver Bow Creek, which has no fish, should have a healthy
fishery. The terrestrial injury
reports found a loss of approximately 1000 acres of wildlife habitat and
wildlife in SBC and CFR, 3400 acres of riparian habitat in Opportunity ponds,
and a loss of upland wildlife & habitat in approximately 18 m2 of
Anaconda uplands areas. The
compensable damage assessment covered the services lost or impaired by these
injured natural resources, such as hunting, fishing, boating, hiking, camping,
observing wildlife, bird watching, and domestic and industrial consumption and
uses of groundwater. (Refer to
Attachment 2).
In 1999 the State of Montana developed a draft UCFRB Restoration Plan Procedures and Criteria (hereafter referred to as the Restoration Plan) that provided the framework for expending restoration funds obtained from the 1998 settlement. The State revised the draft based on input from the UCFRB Remediation and Restoration Education Advisory Council (“Advisory Council”) and other public comments and finalized the Restoration Plan in February 2000. Major aspects of this plan and public comment included:
Applications submitted by the April 14th
deadline for Pilot Year 2000 grant funding include are for the following
projects: a recreational corridor
along SBC (a.k.a. the Greenway); conservation easements and land acquisitions;
revegetation/weed management, best management practices;
stream channel and stream bank restoration;
wetland enhancement; watershed planning, modeling and monitoring; and
restoration research.
Major observations of this initiative process so far:
The on-going litigation and pending remedy decisions
complicate the process and will affect the type of projects that receive
funding in the initial years greatly. While
many of the criteria give preference to actual restoration in the injured
areas, projects will be disfavored if ARCO may be required under Superfund to
perform the activity. Since many unknowns remain regarding what will and
won’t be done in and along the CFR under Superfund remedy, actual
restoration projects for the river itself are disfavored and thus replacement
projects are more likely. This
“mismatch” exists not only for sites where remedy has not been determined,
but also for sites where the remedy is of such a general nature that many
unknowns remain about what will be done under Superfund, such as the Anaconda
Regional Wastes, Water, and Soils Operable Unit.
A policy is needed regarding large-expense, multi-year projects. Should the State commit future years’ available funding to such projects or should applicants seek funding each year? What about multi-million $$ projects that are only beneficial if fully completed vs. ones that can be beneficial if even completed in phases?
The
funding selection process is indeed complex with what many perceive to be
difficult requirements. Mentioned
examples include the requirement that state procurement and contracting
procedures be met; the application of the same criteria to projects of varied
types and costs; and confusion over just what constitutes eligible restoration
and replacement activities. We
tried to ease some of the difficulty for applicants by only requiring readily
available information for some of the criteria.
But even with improvements based on lessons learned, the process will
remain complex given the complexity of the problems to be addressed with the
funding, the regulatory framework, and the variety of eligible projects.
I will now address the questions Dr. Vicki Watson
requested we cover in our presentations.
1. What are
the Guiding Visions and Goals and Specific Objectives?
We received a lot of public comment about the lack of
these in the Restoration Plan.
The State believes a comprehensive planning effort, while worthwhile,
is premature given potential interference with litigation and on-going
Superfund remedy process. Instead, the State and Advisory Council have drafted a
general vision statement and goals for restoration expenditures (refer to
Attachment 4) that will be revisited after “testing” of the first grant
cycle.
The State’s litigation
documents, in particular the 1995 Restoration
Determination Plan, and the NRD regulation themselves all set out the
underlying and overriding goal of this initiative: to restore injured natural resources in the Basin to baseline
conditions. In those
documents, the State recognizes that restoration to baseline conditions will
take decades to centuries and may never occur in some injured areas such as
the bedrock aquifers in Butte and Anaconda.
The NRD Restoration Initiative is for the entire Basin,
not just River – a superior watershed approach.
It provides significant funding for restoration of injured natural
resources to baseline conditions and the aquatic injuries to Silver Bow Creek
and the River were a major component of the NRD claim.
Baseline conditions do not mean pristine condition; they are the
condition of the resource had the hazardous substance release not occurred.
Some folks view that these restoration funds should only
be spent on river projects. But
eligible projects may address other natural resources besides surface water
(e.g. wildlife, groundwater) and also replace lost services.
The service projects are less oriented towards river’s overall health
and more oriented to improving the public’s use of resources.
For example, water supply developments for the communities overlying
contaminated aquifers could be funded.
However, criteria do establish preferences for those projects that
actually restore injured resources and by doing so, lost services provided by
those injured resources.
When considering projects that involve improving the
river’s overall health, interested applicants should pay close attention to
the overriding legal threshold on how these funds be spent:
To restore or replace injured natural resources and/or services lost as
a result of releases of hazardous substances from ARCO and its predecessors’
mining activities in the Basin. Some actions may be worthwhile in improving
the CFR’s overall health but could not be legitimately funded with
Restoration Funds.
2. How to
you hope to achieve goals?
We hope to achieve goals by developing project evaluation
criteria that match the goals and by ensuring selected projects are
implemented as approved. We are
supported by strict legal restrictions on how restoration monies be spent, and
the funding selection process has been developed based on those legal
restrictions.
3.
How will you evaluate success?
We require that prospective applicants identify specific
goals and objectives for their projects, document the likelihood that the
project will meet these, and provide a monitoring component to evaluate
accomplishment. The Restoration
Plan also envisions long-term monitoring of injured resources (e.g.
whether they are improving or whether there are constraints on recovery), but
we have not yet planned that effort. We
feel we have time to do so given the on-going Superfund monitoring.
Examples of measuring accomplishment of goals on a project specific
basis and overall Basin are included in Attachment 4.
4. How will you coordinate with
other restoration initiatives?
We currently coordinate with
Tribes and DOI through a Memorandum of Agreement; with various stakeholders
and the general public through proceedings of the Advisory Council; with EPA
and DEQ through our “watch-dog” participation in Superfund processes; with
DFWP under terms of the Consent Decree; and with DEQ and DFWP as agency
partners with DOJ as NRD Trustee representatives.
Some coordination with other initiatives may occur through our criteria
evaluations, particularly the Results of Superfund Response Actions; Ecosystem
Consideration, Coordination, and Integration; and Matching Funds.
5. How will you involve the public? We provide ample opportunity for public input. A major opportunity for input exists through the proceedings of the Advisory Council, whose mission is to facilitate public dialogue, promote public understanding, and advise the Governor on remediation and restoration activities in the Basin. There are multiple informal and formal opportunities for public review in the funding selection process – both on pre-draft and draft annual work plans for restoration projects as well as on revisions to the Restoration Plan. The Trustee Restoration Council meetings also offer an opportunity for public input. We conduct public outreach such as application workshops. And…the public can submit proposals.
Adaptive Management
Based on lessons learned from what does
and does not work well in the Pilot Year, the State, in consultation with the
Advisory Council and other entities, will propose revisions to the Restoration
Plan for the next grant cycle that will be subject of public comment.
Stay tuned as we evolve a process that, combined with other
restoration initiatives, will lead to a
healthier UCRFB ecosystem.
For more information contact:
Carol Fox, Restoration Program Chief
Natural Resource Damage Program
Montana Department of Justice
P.O. Box 201425
Helena, MT 59620-1425
cfox@state.mt.us
ATTACHMENT 1 – SETTLEMENT SUMMARY
The consent decree up a two step process settling some of the state’s
claims against ARCO and setting up a process by which Montana’s remaining
claims would be resolved. Therefore,
this was called a two step settlement.
STEP 1
Under STEP 1 of the consent
decree, Montana receives from ARCO:
$15 million for assessment and enforcement costs, which were used to
reimburse the state general fund and the coal tax trust fund.
$118 million and $2 million in real property to be used to restore or
replace the injured natural resources in the Upper Clark Fork River Basin, and
services that would have been provided, absent the injury to natural
resources.
Step 1 also settled the state’s claims against ARCO for the cost of
implementing the Streamside Tailing Operable Unit (Silver Bow Creek) remedy
for $80 million. That money is to
be used solely to implement the remedy, as set forth in the ROD, on Silver Bow
Creek.
Under STEP 1, ARCO received
from the state:
A release of Montana’s assessment and enforcement cost claim
A release of Montana’s compensable damage claim
A release of Montana’s restoration damages claims for
Butte Hill, Silver Bow Creek,
Montana Pole, Rocker, Milltown, and the Anaconda Area (excluding the Uplands
area encompassing Stucky Ridge, Smelter Hill, and Mount Haggin.)
For all of the STEP 1 sites, save Milltown, a ROD had been issued at the time of settlement.
STEP 2
Under STEP 2, Montana reserved its restoration
damages claims for Butte Area One, the Clark Fork River, and the Anaconda
Uplands. At the time of
settlement, a ROD had not been issued for any of these “step 2” sites.
Step 2 of the consent decree also includes an agreement between Montana
and ARCO that, following the issuance of each of the RODs for the step 2
sites, the parties would enter into settlement negotiations to attempt
settlement of the state’s restoration damages claim for that site.
If after 60 days the parties have failed to settle the claim, they
would seek a trial date and proceed to try the damages claim for that site.
As many of you are aware, subsequent to the settlement, a ROD was
issued for the Anaconda Uplands area. The
state and ARCO failed to settle the state’s restoration damages claim for
this area, and are currently preparing for trial once again.
ü
Surface
Water Resources:
Surface water concentrations of copper and zinc exceed aquatic life
criteria virtually all of the time in Silver Bow Creek and periodically along
the 120 miles of the Clark Fork River.
ü
Sediments:
Sediments are highly contaminated along Silver Bow Creek and
the Clark Fork River. Bed sediments contain copper concentrations that exceed
baseline conditions by, on average, factors of 25 on the Clark Fork River and
a factor of 500 on Silver Bow Creek.
ü
Benthic
Macroinvertebrates: Benthic Macroinvertebrates contain elevated concentrations of metals in both Silver Bow Creek
and Clark Fork River. Particular
species have been reduced in quality, or along Silver Bow Creek, eliminated.
ü
Fish:
Trout populations are absent from Silver Bow Creek and are
about one-fifth of the population found in Clark Fork River baseline streams.
Silver Bow Creek should contain about 190 trout/mile according to the
1994 survey. Clark Fork River has
lost about 1100 fish/mile. The
average trout population in the 1994 sampling was only 250/mile on the Clark
Fork River whereas baseline is 1350/mile.
ü
Services:
The services lost or impaired by aquatic injuries include lost
fishing and many other recreation
opportunities that accompany fishing such as boating, hiking, camping, and
observing wildlife.
ü
Aquatic
terrestrial injuries: 750
acres of floodplain along Silver Bow Creek and 215 acres along Clark Fork River
(Warm Springs Ponds – Deer Lodge) contain tailings which have eliminated
riparian wildlife habitat. There
are additional acres of floodplain on Silver Bow Creek and Clark Fork River
which contain metals enriched soils which are a source of metals to surface
water and are phytotoxic to vegetation. Baseline vegetation contains a mixture
of riparian forest/shrub communities and agricultural land uses.
Populations
of otter, mink and raccoons have been eliminated from Silver Bow Creek and
severely reduced in the Clark Fork River.
Baseline reference sites on the Big Hole River had significantly more
sign of otter, mink and raccoon. Populations of other types of wildlife have
also been significantly reduced along Silver Bow Creek and Clark Fork River.
ü
Opportunity
ponds: Riparian resources
(soils, vegetation, wildlife and wildlife habitat) have been lost on the 3400
acre ponds.
ü
Upland
terrestrial injury: Approximately
17.8 square miles (11,366 acres) of upland soils, vegetation, wildlife habitat,
and wildlife have been injured. These
phytotoxic soils are lacking major indigenous plant associations.
These areas are Mount Haggin (6.7 square miles); Smelter Hill (7.2 square
miles); and Stucky Ridge (3.8 square miles).
As a result, wildlife populations in these areas have been significantly
reduced.
Baseline areas have vegetative cover consisting of approximately 70% forest and 30% grassland for the Mt. Haggin and Smelter Hill areas. Stucky Ridge area was mostly grassland.
ü
Services:
The services lost or impaired due to injuries to vegetation, wildlife
and wildlife habitat include the many activities that revolve around them, such
as hunting, birdwatching, hiking, observing wildlife and general recreation.
ü
Butte
Area: The bedrock
groundwater injury covers 7 square miles (4500 acres) and has a volume of
some 250,000 acre feet. Less
than half of this injured groundwater is in the Berkeley Pit at the present
time. However, when the critical
water level is approached the volume of contaminated ground water in the pit
will exceed the total volume of contaminated bedrock groundwater in the aquifer
outside of the pit.
The
alluvial groundwater in the Butte Hill area has some 5000 injured acre feet
over a square mile. Injury at Butte's
Area One alluvial aquifer also extends over a mile and is some 10,000 acre feet
in volume.
The groundwater in both the alluvial and bedrock
aquifers contain groundwater concentrations many times over baseline for
arsenic, cadmium, copper, lead, zinc, sulfate, iron and manganese.
ü
Montana
Pole & Rocker: Montana
Pole has 350 acre feet of groundwater injury (organics) over 44 acres.
Rocker has 190 acre feet of injury (organic and inorganic) over
a 26-acre area.
ü
Anaconda
Area: Groundwater
contamination (inorganics) at Anaconda extends over 40 square miles (25,000
acres) and totals more than 400,000 acre feet.
Most of the injury is in the alluvial aquifer, with the remaining injury
found in the Bedrock. Exceedences
of drinking water standards exist for arsenic, cadmium, iron, manganese,
sulfate, zinc, and TDS. EPA
has found more groundwater contamination in the upland bedrock areas since the
State=s
injury report was released.
ü
Milltown:
The volume of injured groundwater at Milltown is approximately
6500 acre feet and extends over about 110 acres.
Drinking water exceedences exist for arsenic, iron and manganese.
ü
Services:
Services lost or impaired by
injuries to groundwater include domestic and industrial consumption and uses.
For more detailed
information, refer to the:
·
February
2000 UCFRB Restoration Plan Procedures and
Criteria
·
February
2000 State of Montana’s Responses to
Public Comment on the UCFRB Restoration Plan Procedures and Criteria
The
following are the 5 steps of the NRPD grants selection process and entities
involved in that funding selection decisions.
a. Phases
1. Minimum Qualification Screening
2. Project Evaluation and Ranking
3. Pre-Draft Restoration Work Plan
4. Draft Restoration Work Plan
5.
Final Proposed Restoration Work Plan to Governor
b. Multiple Entities Involved:
1. NRDP and other state entities
2. Advisory Council (citizens appointed by governor)
3. Trustee Restoration Council (DEQ, DNRC, DFWP)
4. federal agencies (EPA, DOI, Tribes)
5.
general public
Project Criteria
Summary (summarized from Feb. 2000 Procedures
& Criteria)
Threshold
criteria: Projects must restore or replace injured natural resources or lost
services.
“Balancing
Criteria”: The existing criteria
give preference to projects that:
·
are
technically feasible
·
are cost
effective
·
have a
positive impact human health or the environment
·
meet
applicable policies, rules, laws
·
have a
reasonable cost/benefit relationship
·
actually
restore an injured resource
·
are
closest to areas of injury
·
coordinate
with ongoing or planned remedies
·
connect
services lost to services restored
·
benefit
the original user group (person or natural resources)
·
are
integrated with other restoration efforts in the Basin
·
share
project costs
·
have
public support
ATTACHMENT 4 – DRAFT VISION STATEMENT AND GOALS
4/7/2000 Draft Vision Statement being considered by State and UCFRB
Advisory Council
“The Upper Clark Fork River Basin Remediation and Restoration
Education Advisory Council supports investing restoration funds into returning
the UCFRB to a healthy ecosystem by restoring the natural resources and quality
of life damaged by mining operations in the Basin.
Restoration funds must be spent on projects that restore or replace
natural resources which were injured and/or services which were lost or impaired
as a result of releases of hazardous substances from ARCO’s and its
predecessors mining and mineral processing activities in the Upper Clark Fork
River Basin. In determining restoration priorities, the Council advocates an
ecosystem approach to restoration that views each restoration project as part of
a whole basin effort. Restoration
projects should not interfere with on-going natural resource damage
litigation.”
Draft
General Goals
The
following are the general goals for restoration projects in the Basin.
These goals are for the entire Basin, not just the Clark Fork River.
Baseline conditions are set out by the State in its litigation documents,
particularly the 1995 Restoration Determination Plan.
In those documents, the State recognizes that restoration to baseline
conditions will take decades to centuries and may never occur in some injured
areas such as the bedrock aquifers in Butte and Anaconda.
·
Improve
surface water quality to baseline conditions.
·
Improve
aquatic habitat and fisheries to baseline conditions.
·
Increase
instream flows to help improve surface water quality and support native
fisheries.
·
Improve
riparian and upland area wildlife habitat and wildlife to baseline conditions.
·
Improve
groundwater quality.
·
Improve
or provide replacement of recreational services lost or impaired in riparian and
upland areas.
·
Improve
or provide replacement of lost groundwater use services.
Measuring
Accomplishment of Goals
Examples
of measuring goal realization on a project specific basis and overall Basin
basis include:
·
reduction
in pollutant levels in surface waters
·
volume of
surface water improved
·
increase
in instream flows
·
miles of
restored aquatic habitat (e.g. spawning, rearing, overwintering habitat)
·
increases
in fish density
·
reduction
in pollutant levels in groundwater
·
volume of
groundwater improved
·
acres of
restored wildlife habitat
·
acres of
restored native vegetation
·
increase
in wildlife variety and density
·
increase
in recreational uses, users, and access
·
increase
in groundwater uses and users