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Guidance on mainstem planning
Related link: general Oregon guidance
prepared by Oregon Coordination Group, February 20, 2003
Introduction
Subbasin plans are required for mainstem reaches of both the Columbia
and Snake rivers. Mainstem reaches are typically comprised of the mouths
of tributaries, small tributaries to the mainstem that do not warrant
their own subbasin plans, and habitat along the mainstem and small
tributaries (general descriptions for these reaches can be found in the
Council's Fish and Wildlife Program). In Oregon, mainstem reaches
include the Columbia River Estuary, Lower Columbia, Columbia Gorge,
Columbia Lower Middle, Snake/Hells Canyon, Snake Upper Middle and Snake
Lower Middle.
Subbasin Summaries have previously been prepared for major sections of
mainstem reaches in the Columbia and Snake rivers.
Mainstem Plan
The Council is currently preparing Mainstem
Amendments to its Fish and Wildlife Program (Program) that will define
management objectives and action measures for the mainstem Columbia and
Snake rivers, including general objectives and strategies for mainstem
habitat protection and enhancement, and detailed measures for system-wide
water management and dam passage. The Council's draft Mainstem
Amendments, which were released for public review and comment in October
2002, include objectives and strategies relating to, among other matters:
- Protection and enhancement of mainstem habitat, including spawning,
rearing, resting and migration areas for salmon and steelhead and
resident salmonids and other fish;
- System water management;
- Passage spill at mainstem dams;
- Adult and juvenile passage facility modifications at mainstem dams;
- Juvenile fish transportation;
- Adult survival during upstream migration through the mainstem;
- Reservoir elevations and operational requirements to protect
resident fish and wildlife;
- Water quality conditions; and
- Research, monitoring, evaluation and in-season decision-making.
Planning Focus
Any subbasin planning for specific mainstem reaches should take the
objectives and strategies in the Council's draft Mainstem Amendments
into consideration. Once adopted by the Council, the final Mainstem
Amendments should be taken as a given. However, because the final Mainstem
Amendments will likely not describe specific objectives, strategies or
measures to protect and restore habitat, nor will they describe specific
objectives, strategies or measures for natural and artificial production
for mainstem reaches, the need exists for reach-specific plans. The focus
of these reach-specific plans should be on the land and water in the
mainstem corridor itself and, presumably, on the small tributaries that
feed into these reaches but which, because of their size, will not be the
subject of individual planning efforts.
Functional Distinctions and Planning Areas
Columbia and Snake River mainstem reaches fundamentally differ in how
they function and the threats to their ecological integrity. Because of
these distinct differences, mainstem planning areas can be geographically
divided based upon their ecologies or ecosystems:
- Below Bonneville Dam ? estuarine/tidal-influenced ecosystem
- Hanford Reach ? free-flowing, ?big? river ecosystem
- Above Bonneville Dam, excluding the Hanford Reach ?
reservoir ecosystem
Based upon these ecosystems, it is recommended that Oregon mainstem
reaches be combined when feasible for planning purposes within the same or
similar ecological systems. Specifically, it is recommended that subbasin
plans be prepared as follows:
- Combined, single plan for the Columbia River Estuary and the Lower
Columbia reaches;
- Combined, single plan for the Columbia Gorge and Columbia Lower
Middle reaches;
- Stand-alone plan for the Snake/Hells Canyon unblocked reach; and
- Combined, single plan for the Upper Mid Snake and Lower Mid Snake
blocked reaches.
Focal and Indicator Species
Subbasin plans for mainstem reaches should address both focal and
indicator species. Focal species are a limited set of species for which
management objectives are established that describe a future desired
condition for the species. Indicator species are a broader set of species
whose status is monitored and evaluated to track and assess how the
community at large (ecosystem) responds to subbasin management strategies.
The subbasin plan should focus primarily on describing objectives,
strategies and measures for protecting and restoring habitat and for
natural and artificial production and include technical information on
focal species. The emphasis should primarily be on species that spend the
majority or critical stages of their lifecycles within the mainstem,
rather than in subbasin tributaries.
For each of the three ecosystems identified, mainstem planning should
focus on the following key species and factors for decline.
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Location/Ecology |
Key Species |
Factors For Decline |
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Aquatic
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Wildlife (1)
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Focal
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Indicator
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Below Bonneville Dam
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Sturgeon (green and white), chum, smelt, fall chinook
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Starry flounder, American shad, peamouth
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Avian species (waterfowl, birds of prey, and song birds),
migratory deer and elk, reptiles, amphibians
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Habitat loss and degradation associated with shoreline
development, dredging and spoils, and upriver hydropower project
operations.
|
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Hanford Reach
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Sturgeon (white), fall chinook
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Pike minnow, bridgelip sucker, large-scale sucker, American shad,
chiselmouth
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As above.
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Effects of mid-Columbia hydropower project operations and
impoundments on habitat.
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Above Bonneville Dam
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Sturgeon (white), small-mouth bass, walleye
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Bridgelip sucker, large-scale sucker, pike minnow, channel
catfish, American shad, burbot chiselmouth
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As above.
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Habitat inundated by impoundments and fragmentation of
populations caused by passage problems at dams.
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(1) Focal species have not yet been identified.
Coordination
By definition, mainstem reaches include areas in more than one state.
Subbasin planning project managers have agreed that a single, unified
subbasin plan for a mainstem reach (or combination of reaches as discussed
above), rather than separate plans for each state, is desirable. The
states have several options for producing a unified plan: (a) they
may designate a single lead entity to prepare a single subbasin
plan; (b) they may create a new bi-state entity to lead the planning
effort; or (c) one state may defer to the other to produce the plan.
Finally, (d) where designating a single lead entity is not feasible, the
following procedures and standards apply:
- The states may designate separate lead entities, each with its
separate work plan.
- Work plans and budgets must be demonstrably integrated to show
delivery of a single subbasin plan, including coordinated mechanisms
for public involvement.
- Work plans and budgets must be accompanied by a letter of support
from the other state(s).
- Joint approval by the respective state coordinating groups will be
required before contracting can be initiated.
- A single, coordinated subbasin plan must be jointly submitted by the
lead entities to the Council.
- Each state coordinating group must recommend approval of the plan
before Council will consider initiation of the appropriate Program
amendments.
- Equitable distribution of funding is expected.
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