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Oregon Coast Coho Conservation Plan 

For the State of Oregon 

 

 

 

 

 

 

 

 

 

 

 

 

 

Prepared by 

Oregon Department of Fish and Wildlife 
In Partnership with State and Federal Natural Resource Agencies 

 

 

 

 

 

 

 

 

 

March 16, 2007 

 

 

 


Table of Contents 

 

Executive Summary......................................................................................3 
Introduction.................................................................................................10 
1. ESU Population Structure....................................................................16 
2. Current ESU Status...............................................................................18 
3. ESU Desired Status: Vision, Goals, Measurable Criteria, and Gaps20 
4. ESU Limiting Factors............................................................................23 
5. Conservation Strategy for the Coast Coho ESU.................................26 
6. Population-Based Actions and Associated Cost Estimates................32 
7. Agency Actions to Support the Conservation Plan............................34 
8. Research, Monitoring, and Evaluation................................................52 
9. Application of Adaptive Management.................................................54 
10. Implementation and Oversight...........................................................56 
11. Reaching Desired Status � Time Frame Expectations.....................59 
12. Conclusion............................................................................................60 


Appendices 

 

Appendix 1 � Oregon Coastal Coho Stakeholder Team 
Facilitators� Report 

 Attachment I � Comments on First Draft of the Plan 

Attachment II � Comments on Second Draft of the Plan 

 Attachment III � Protocols of the Stakeholder Team 

 Attachment IV � Summaries of Stakeholder Team Meetings 

 Attachment V � Stakeholder Team Meeting Locations, Issues 

Attachment VI � Comments from Public Meetings 

Appendix 2 � Desired Status: Measurable Criteria for the Oregon Coast 
Coho Conservation Plan for the State of Oregon 

Appendix 3 � Description of Oregon and Federal Commitments to the 
Oregon Coast Coho Conservation Plan for the 
State of Oregon 

Appendix 4 � Description of Research Topics Identified in the Oregon 
Coast Coho Conservation Plan for the State of Oregon 


Executive Summary 

 

Introduction 

 

The purpose of this Conservation Plan is to ensure the continued viability of the Oregon 
Coast Coho Evolutionary Significant Unit (ESU) and to achieve a desired status that 
provides substantial ecological and societal benefits. The Oregon Coast Coho ESU is 
viable (see Table 2; State of Oregon 2005) and does not currently require protection 
under the federal Endangered Species Act (ESA) (NOAA Fisheries 2006). The current 
status of this ESU reflects a reduction in fishery harvest, improved hatchery management, 
and extensive habitat restoration work initiated or maintained under the Oregon Plan for 
Salmon and Watersheds (Oregon Plan). This Conservation Plan maintains and enhances 
support of the Oregon Plan and meets the requirements of Oregon�s Native Fish 
Conservation Policy (NFCP) (OAR 635-007-0502 to 0509). This Conservation Plan does 
not propose new land-use regulations, maintains existing regulatory programs, and 
enhances support for non-regulatory cooperative conservation. A key element of this 
Plan is to provide a higher and more effective level of support to local conservation 
groups and private landowners (e.g., Soil and Water Conservation Districts, watershed 
councils, industrial forestland owners, Salmon and Trout Enhancement Program (STEP) 
volunteers, and other individuals and groups). These community-based organizations 
have demonstrated an impressive record of planning, prioritizing, and implementing 
habitat improvement projects through their participation in the Oregon Plan. 

 

This document is the State of Oregon�s Conservation Plan for the Oregon Coast coho 
Evolutionary Significant Unit (ESU). It was prepared by the Oregon Department of Fish 
and Wildlife (ODFW) in partnership with other state and federal natural resource 
agencies. The Conservation Plan incorporates findings presented in the Oregon Coastal 
Coho Assessment (State of Oregon 2005; hereafter referred to as the 2005 OCCA) and 
extensive experience implementing the Oregon Plan since 1997. Oregonians have 
demonstrated extensive and diverse support for non-regulatory, community-based, habitat 
improvement work under the Oregon Plan. Participants in this effort include watershed 
councils, Soil and Water Conservation Districts, Salmon-Trout Enhancement Program 
volunteers, industrial and private landowners and a variety of non-governmental 
organizations and individuals. Information put together for the 2005 OCCA show that 
implementation of the Oregon Plan across this ESU has included significant investments 
($107 million from 1997 to 2003) in restoration work by private landowners and state and 
federal agencies; private landowners voluntarily contributed about one-third of these 
funds; Oregon Watershed Enhancement Board restoration grants supported roughly $13 
million during this timeframe. 

 

The Conservation Plan was developed during an iterative process by considering 
substantial review, discussion, critique, and recommendations from three primary groups: 
a diverse public Stakeholder Team (see Appendix 1), the Oregon Plan Core Team, and 
the federal Technical Recovery Team (TRT) established for this ESU. The Conservation 
Plan describes commitments by the State of Oregon that will conserve the sustainability 
of this ESU and restore biological attributes necessary to achieve a science-based, 


socially established desired status goal. Achievement of the desired status goal will 
provide significant ecological, economic and cultural benefits for all Oregonians. 
Hereafter, the Oregon Coast Coho Conservation Plan for the State of Oregon will be 
referred to as the Conservation Plan or simply the Plan. 

 

This Conservation Plan, in supporting the Oregon Plan, is a dynamic strategy that will 
adapt and be modified over time in response to learning from monitoring data and 
implementation experience. The intent of this Plan is to conserve1 and enhance Oregon 
Coast coho. The primary strategy, like the Oregon Plan, is to support efforts to improve 
habitat for coho salmon and other native fish2 and wildlife species through on-the-
ground, non-regulatory work by community-based entities and individuals. 

 

This Plan meets the requirements for conservation plans described in Oregon�s Native 
Fish Conservation Policy (NFCP). The NFCP was adopted by the OFWC in 2002 to 
support and increase the effectiveness of the 1997 Oregon Plan. The Conservation Plan 
does not replace or supersede the Oregon Plan. Fundamentally, the Conservation Plan is 
designed to improve the status of the ESU and virtually all of its constituent populations 
by increasing the productive capacity of the coho and their habitat to levels significantly 
higher than where the ESU could be considered a potential candidate for listing under 
federal ESA. Significantly, Oregon notes that all of the actions in this Conservation Plan 
are expected to benefit co-existing native species and water quality across the ESU. 

 

The NFCP employs conservation plans to identify and implement appropriate strategies 
and actions necessary to restore native fish in Oregon to levels that provide benefits to the 
citizens of the state. This is achieved through a sequential process: 

1. Define the management unit, or ESU. 
2. Determine its current status. 
3. Define a desired status. 
4. Determine any gap between current and desired status and the factors causing the 
gap (limiting factors). 
5. Identify and implement strategies and actions that address the limiting factors. 
6. Monitor and evaluate the ESU status and actions implemented and use adaptive 
management to make adjustments necessary to achieve desired status. 


The Conservation Plan contains the elements identified above and is also intended to be 
consistent with and contain most of the elements required by a federal ESA Recovery 
Plan. The primary required elements of a federal Recovery Plan include 1) objective and 
measurable criteria for delisting, 2) site-specific actions required for recovery, and 3) 
estimates of the time and cost of implementing the plan. A key distinction between this 
Plan and a federal Recovery Plan is the ESU is currently viable; the measurable criteria 
therefore establish biological objectives well beyond de-listing requirements, more akin 
to �broad sense� recovery goals in federal recovery plans. 

1 As defined in Oregon Administrative Rule (OAR), the term conservation means managing for 
sustainability of native fish so present and future generations may enjoy their ecological, economic, 
recreational and aesthetic benefits (OAR 635-007-0501-10). 

2 Native fish are defined as indigenous to Oregon and include both naturally and hatchery produced fish 
(OAR 635-007-0501-36). 


 

Structure and Biology of the Oregon Coast coho ESU 

The Oregon Coast coho ESU includes naturally produced coho salmon in 56 populations 
� as defined by the National Oceanic and Atmospheric Administration (NOAA) TRT 
(Lawson et al. 2004) � from the Necanicum River near Seaside to the Sixes River near 
Port Orford. Twenty one of these populations are classified as potentially or functionally 
independent because they occur in basins with sufficient historical habitat to have 
persisted through several hundred years of normal variations in marine and freshwater 
conditions. These anadromous salmon spawn in rather small low-gradient streams from 
November through March, the offspring spend the next summer and following winter in 
freshwater, and then migrate through estuaries to the ocean in the spring of their second 
year of life. The vast majority of coho salmon then spend one and one half years (two 
summers) in the ocean, remaining principally off the Northern California and Oregon 
coast, before returning to their home streams to spawn. 

 

Current Status of the ESU 

The Oregon Coast coho ESU is not currently listed for protection under federal or state 
endangered species acts. Following a comprehensive assessment, Oregon concluded the 
ESU is currently viable and sustainable (2005 OCCA). In other words, Oregon Coast 
coho populations generally demonstrate sufficient abundance, productivity, distribution, 
and diversity to be sustained under the current and foreseeable future range of 
environmental conditions, even including conditions somewhat more adverse than were 
observed during the 1990s, a period characterized by adverse ocean survival conditions, 
drought, and flood across the ESU. NOAA�s Federal Register Notice (NOAA Fisheries 
2006) contained the following statement: 

 

After considering the best available scientific and commercial 
information available, we have concluded that the ESU is not in 
danger of extinction throughout all or a significant portion of its 
range, nor is it likely to become so within the foreseeable future. (page 
3033) 

 

Desired Status and Measurable Criteria 

This Conservation Plan describes a desired status for future condition and performance of 
the Coast coho ESU that goes substantially beyond minimum viability to achieve social 
objectives. The desired status vision statement for this ESU is: Populations of naturally 
produced coho salmon are sufficiently abundant, productive, and diverse (in terms of life 
histories and geographic distribution) such that the ESU as a whole is 1) self-sustaining 
into the foreseeable future, and 2) providing significant ecological, cultural, and 
economic benefits. This vision statement is consistent with the mission statement for the 
Oregon Plan. 

 

The vision statement and measurable, scientifically-based objectives for desired status 
were developed collaboratively with the Stakeholder Team and represents consensus 
among members. The goal targets an average return of spawners to the ESU that ranges 
from a low of greater than 100 thousand spawners when marine survival is extremely low 


(this is about twice the spawners observed during 1993-1996) to a high of over 800 
thousand spawners when marine survival is high (this is about three or four times the 
spawners observed in 2002 and 2003). This Plan describes a set of measurable criteria 
that will be monitored and evaluated to determine if and when the desired status goal has 
been achieved (see Appendix 2). These measurable criteria include parameters such as 
abundance, productivity, distribution, persistence, diversity, and habitat. 

 

 Oregon�s Coho Conservation Strategy 

Oregon is relying on a combination of existing regulatory programs plus effective long-
term participation in non-regulatory conservation work to achieve the desired status goal 
for the Coast coho ESU. The existing regulatory programs were not intended to improve 
habitat to the extent needed to achieve the desired status goal outlined in this plan. The 
state has determined that the best way to increase the quantity and quality of coho habitat 
throughout the ESU, and achieve desired status, is through the voluntary participation of 
landowners and local groups. 

 

Thus, the primary strategy to achieve the desired status in this Conservation Plan is based 
on the following general premise: Habitat management and improvement is the key to 
protecting and enhancing coastal coho; much of the most important coho habitat is on 
private land; habitat improvement on private land is most likely to occur through 
incentive-based cooperative partnerships with landowners; and the Oregon Plan 
provides the best vehicle for securing these partnerships and implementing habitat 
improvements. 

 

Policies and actions in this Plan will address the potential effects of human activities, or 
threats, across the full life-cycle of the Coast coho ESU including management activities 
upstream from the distribution of coho salmon, downstream through tributaries, 
mainstems, estuaries where coho reside and/or migrate, and the ocean. Principal 
activities that could potentially limit or support achievement of the desired status goal for 
the ESU include fishery harvest, hatchery operation, land use management, and on-the-
ground work to increase the productive capacity of coho habitat. These policies and 
actions are framed to 1) conserve the existing productivity, distribution, diversity of coho 
salmon and habitat across the ESU and 2) improve the productive capacity of coho 
populations and habitat. Both elements are considered essential to achieve Oregon�s 
desired status goal. 

 

The long-term effectiveness of this Conservation Plan requires developing and 
implementing conservation and restoration strategies at scales within populations. 
Oregon will continue to support local watershed entities as they implement population-
specific actions at scales appropriate for conservation. These finer resolution strategies 
will include prioritized and time sequenced action plans across all land ownerships. This 
conservation plan is not intended to prescribe habitat actions at local scales, but instead, 
establish direction and sideboards to help local conservation entities custom tailor 
restoration activities to address specific limiting factors within their watersheds. 

 


Key Conservation Commitments 

Oversight 

� Desired status goal. This Conservation Plan establishes policy regarding the 
desired status for the ESU and constituent populations within the ESU. The 
desired status goal (and measurable criteria) in this Conservation Plan is 
significant because it provides a quantitative target for the ESU that can be used 
to evaluate the Plan�s effectiveness over time. 
� Regulatory programs. State and federal agencies will continue to implement, 
monitor compliance with, and enforce their existing, legislatively mandated, 
regulatory programs. 
� The Oregon Plan Core Team is responsible for providing policy guidance and 
accountable for implementation of conservation efforts statewide (i.e., the Oregon 
Plan), including this Conservation Plan. An Oregon Plan Regional Management 
and Implementation Team will be responsible for tracking and coordinating 
implementation and preparing reports described as part of Oregon�s adaptive 
management commitment in this Plan. 


 

Implementation 

� Modified hatchery programs with minimal impact to fisheries. Two coho 
hatchery programs are being altered in a manner that is designed to achieve 
viability for the affected populations while having little or no impact on the 
selective coho sport fishery in the ocean and increasing commercial and sport 
harvest opportunities in the lower Columbia River. 
� Conservation priorities. The plan provides information intended to guide funding 
and action investments in watershed conservation by diverse management entities. 
� Oregon Plan Habitat Strategy. The strategy is to provide more effective financial 
and technical support and outreach to private landowners to maintain and increase 
participation in cooperative conservation actions. Implementing the strategy will 
support the viability of the ESU and will help achieve the desired status for 
habitat � roughly a doubling in the amount of high quality habitat across the ESU. 
The habitat strategy enhances the Oregon Plan approach for developing 
cooperative conservation partnerships and conducting effective habitat restoration 
projects. 


 

The habitat strategy of this Conservation Plan will provide additional resources to 
community-based conservation networks (e.g., watershed councils, Soil and 
Water Conservation Districts, STEP volunteers, and other community groups) and 
private landowners engaging in voluntary, cooperative conservation projects. 
Oregon has over ten years of positive experience implementing habitat restoration 
under the Oregon Plan (State of Oregon 2005). Specifically, this strategy will 
provide 1) a better understanding of coho�s ecological needs, 2) a better 
understanding of where and how habitat restoration can be most effective, 3) 
improved financial incentives to conduct voluntary habitat restoration, and 4) 
more technical support for project designs, permits, monitoring and reporting for 
restoration projects. Although this is not a new initiative, it will better focus 


assistance and support for Oregon Plan participants so that their involvement can 
be most effective. 

 

This strategic approach � recognizing and building upon the good work already 
completed under the Oregon Plan and a growing level of participation in Oregon 
Plan programs � is currently supported by the Oregon Forest Industries Council, 
Oregonian�s for Food and Shelter, and the Oregon Farm Bureau. Enhanced 
partnerships among private forest and agricultural landowners represent a 
powerful means of increasing the level of investment and participation in 
effective voluntary habitat-improvement work on private lands. The Oregon Plan 
Core Team will coordinate this strategy among participating entities and seek to 
gain support from other groups throughout the ESU. 

 

The Oregon Plan Habitat Strategy will focus on a bottom-up approach for 
developing and implementing actions, effectively utilizing the Oregon Plan 
network of conservation groups and partners. Regional or ESU-wide projects and 
programs that span multiple local jurisdictions can be brought directly to the 
Oregon Plan Regional Management and Implementation Team for consideration 
and implementation. 

 

� Multi-agency effort. State and federal agencies provided detailed descriptions of 
their respective contributions to the Conservation Plan along with abstract 
summaries of their actions. Abstracts are in the main body of this Conservation 
Plan, detailed descriptions are in Appendix 3 to the Conservation Plan. Funding 
available to support conservation infrastructures (especially SWCDs and 
watershed councils) will be maintained and most likely, modestly increased 
during the next biennium (2007-2009). 


 

Research, Monitoring and Evaluation 

� Research. Although not comprehensive, eight topics that merit research are 
identified, including ocean conditions, pinnipeds and a better understanding of 
high quality coho habitat. These topics include information needs that are 
particularly relevant to achieving Oregon�s desired status goal for this ESU. 
� Monitoring. Monitoring within the ESU has been modified to improve estimates 
of coho spawners; juvenile coho density and distribution; and habitat quality. 
� Evaluation to support adaptive management. First, Oregon commits to assess the 
ESU and the effectiveness of the Conservation Plan (in 6 years, every 12 years 
thereafter, or as needed). Second, Oregon will produce a succinct annual report � 
an early warning system �that will alert Oregon to the need to reconsider the 
status of the Coast coho ESU, monitoring, and management systems in place 
throughout the ESU. 


 

Reaching Desired Status � Time Frame Expectations 

Whereas immediate benefits to coho are expected as the actions identified in the Plan are 
implemented, the desired status goal for this ESU is ambitious and unlikely to be 
achieved in the near term. Achieving the desired status goal will require 


institutionalization of the cooperative conservation commitments embedded in the 
Oregon Plan and this Conservation Plan, sustained leadership, extensive non-regulatory 
participation by private landowners, funding, reassessment, and adaptive management. 
With the enhanced level of habitat monitoring proposed in this plan, Oregon will be able 
to determine the trajectory of habitat condition and the approximate time-frame required 
to achieve the desired status goal. A 50 year time-frame is probably the most realistic 
scenario to achieve the desired status goal for the ESU, given likely levels of funding, the 
time required to resolve scientific uncertainty, and the time required for habitat actions to 
effect fish survival and production. 

 

Oregon is relying on a combination of the current regulatory programs plus effective 
long-term participation in non-regulatory, cooperative conservation work to achieve the 
desired status goal for the Coast coho ESU. The Oregon Plan habitat strategy is designed 
to support effective work by the existing cooperative conservation network (including 
SWCDs, watershed councils, STEP volunteers and others) across the ESU. This effort is 
expected to increase participation in non-regulatory cooperative conservation work by 
private landowners, especially landowners in areas with the greatest potential to create 
high quality coho habitat and support achievement of the desired status goal for the ESU. 

 

Oregon is generally optimistic that the elements of this Conservation Plan will achieve 
the desired status goal for the ESU, based on the following observations. 

� Coho salmon are broadly distributed across all 21 independent populations within the 
ESU and spawning escapements during recent years of relatively favorable ocean 
survival have been higher on average than in the last 5 decades. 
� The ESU is currently viable and adaptive management has virtually eliminated 
significant adverse impacts of fishery harvest and hatchery programs on the ESU. 
� Practical methodologies exist to improve the environmental conditions currently 
limiting productive capacity of the ESU. 
� An extensive and diverse locally-based infrastructure of committed groups and 
individuals has demonstrated a decades-long track record of restoration commitment 
and action. The fiscal support for restoration efforts and infrastructure support in the 
ESU is likely to increase. 


 


 

Introduction 

 

The purpose of this Conservation Plan is to ensure the continued viability of the Oregon 
Coast Coho Evolutionary Significant Unit (ESU) and to achieve a desired status that 
provides substantial ecological and societal benefits. The Oregon Coast Coho ESU is 
viable (State of Oregon 2005) and does not currently require protection under the federal 
Endangered Species Act (ESA) (NOAA Fisheries 2006). The current status of this ESU 
reflects a reduction in fishery harvest, improved hatchery management, and extensive 
habitat restoration work initiated or maintained under the Oregon Plan for Salmon and 
Watersheds (Oregon Plan). This Conservation Plan maintains and enhances support of 
the Oregon Plan and meets the requirements of Oregon�s Native Fish Conservation 
Policy (NFCP) (OAR 635-007-0502 to 0509). This Conservation Plan does not propose 
new land-use regulations, maintains existing regulatory programs, and enhances support 
for non-regulatory cooperative conservation. A key element of this Plan is to provide a 
higher and more effective level of support to local conservation groups and private 
landowners (e.g., Soil and Water Conservation Districts, watershed councils, industrial 
forestland owners, Salmon and Trout Enhancement Program (STEP) volunteers, and 
other individuals and groups). These community-based organizations have demonstrated 
an impressive record of planning, prioritizing, and implementing habitat improvement 
projects through their participation in the Oregon Plan. 

 

The Oregon Plan is a comprehensive partnership between government, communities, 
private landowners, industry and citizens funded by the Oregon Legislature. Efforts 
under the Oregon Plan include regulatory and non-regulatory programs designed to 
restore native salmon runs, improve water quality and maintain healthy watersheds and 
human communities throughout Oregon. 

 

State agencies that participate in the Oregon Plan have the legal and regulatory 
authorizations, staffing, and commitment to carry out their conservation commitments 
(e.g., Oregon Coastal Coho Assessment (State of Oregon 2005; hereafter referred to as 
the 2005 OCCA)). Oregonians have demonstrated extensive and diverse support for non-
regulatory, community-based, habitat improvement work under the Oregon Plan. 
Participants in this effort include watershed councils, Soil and Water Conservation 
Districts, Salmon and Trout Enhancement Program volunteers, industrial and private 
landowners and a variety of non-governmental organizations and individuals. 
Implementation of the Oregon Plan across this ESU from 1997 to 2003 included 
significant investments ($107 million) in restoration work by private landowners and 
state and federal agencies; private landowners voluntarily contributed about one-third of 
these funds; Oregon Watershed Enhancement Board restoration grants supported roughly 
$13 million during this timeframe. In addition, the Pacific Coast Salmon Recovery Fund 
constitutes a small, but important, portion of the money used by OWEB to carry out 
conservation activities. These dollars are used mostly for non-capital expenditures 
(assessment, monitoring, education, and outreach). 

 


In concert, these regulatory and non-regulatory elements support the Oregon Plan 
mission: 

 

To restore the watersheds of Oregon and to recover the fish and wildlife 
populations of those watersheds to productive and sustainable levels in a manner 
that provides substantial environmental, cultural and economic benefits. 

 

This document is Oregon�s Conservation Plan for the Oregon Coast coho ESU and has 
been prepared by the Oregon Department of Fish and Wildlife (ODFW) in partnership 
with state and federal natural resource agencies. The Conservation Plan incorporates 
findings presented in the 2005 OCCA and extensive experience implementing the Oregon 
Plan since 1997. The Conservation Plan was developed during an iterative process by 
considering substantial review, discussion, critique, and recommendations from three 
primary groups: a diverse public Stakeholder Team, the Oregon Plan Core Team, and a 
Technical Recovery Team (TRT). This active participation has helped improve the 
Conservation Plan. A report by the facilitation contractor and a record of written critique 
submitted regarding each draft of the Conservation Plan is included as Appendix 1. 

 

This document is the Conservation Plan for the Oregon Coast Coho ESU. Oregon�s 
NFCP stipulates developing conservation plans for Species Management Units (SMUs) 
that will be formally defined by adoption of each respective conservation plan. ESU and 
SMU are both terms that refer to a group of populations from an area that share similar 
genetic and ecological characteristics. Because the Oregon Coast Coho ESU and the 
SMU are identical, the remainder of this Conservation Plan will refer only to the Oregon 
Coast Coho ESU or the ESU. 

 

This Conservation Plan represents a significant step forward for the Oregon Plan through 
implementation of the NFCP. The Plan gives Oregon the ability to immediately 
implement an effective conservation program across this ESU. Oregon has established a 
desired status goal for the ESU that, by a very large margin, will exceed a level where the 
ESU would be considered viable (see Table 2). Oregon�s conservation commitments are 
designed to improve the productive capacity of the coho and their supporting habitat. 
The Plan contains measurable criteria by which progress may be evaluated in the future. 
The Conservation Plan describes commitments by the State of Oregon and its federal 
partners that ensure the sustainability of this ESU and will restore biological attributes 
necessary to achieve a science-based, socially established desired status goal. 
Achievement of the desired status goal will provide significant ecological, economic and 
cultural benefits for all Oregonians. 

 

Native Fish Conservation Policy 

The Native Fish Conservation Policy (NFCP) was adopted by the Oregon Fish and 
Wildlife Commission (OFWC) in 2002 as an essential policy refinement that supports 
implementation of the Oregon Plan. The NFCP employs conservation plans as a means 
to identify and implement appropriate strategies and actions to restore and maintain 
native fish in Oregon to levels that provide benefits to the citizens of the state. As 
defined in Oregon Administrative Rule (OAR), the term conservation means managing 


for sustainability of native fish so present and future generations may enjoy their 
ecological, economic, recreational and aesthetic benefits (OAR 635-007-0501-10). 
Native fish are defined as indigenous to Oregon and include both naturally and hatchery 
produced fish (OAR 635-007-0501-36). 

 

The NFCP focuses on the conservation of naturally produced fish because they are the 
basis for federal ESA listings and are the foundation for productive hatchery programs. 
The NFCP represents a maturation of the Oregon Plan by providing monitoring data, 
scientific analyses, and focused restoration priorities that improve the effectiveness of 
conservation efforts under the Oregon Plan. 

 

The NFCP employs conservation plans to identify and implement appropriate strategies 
and actions necessary to restore native fish in Oregon to levels that provide benefits to the 
citizens of the state. This is achieved through a sequential process: 

1. Define the management unit, or ESU. 
2. Determine its current status. 
3. Define a desired status. 
4. Determine any gap between the two and the factors causing the gap (limiting factors). 
5. Identify strategies and actions that address the limiting factors. 
6. Monitor and evaluate the ESU status and actions implemented and use adaptive 
management to make adjustments. 


 

The Oregon Coast Coho Conservation Plan also considers and adds support to Basin Fish 
Management Plans that were developed in the 1990�s. These Basin Fish Management 
Plans provide fish management guidance for most freshwater fish species in the basins of 
the Coos, Salmon, Siletz, Yaquina, Alsea, Yachats, Siuslaw, Tenmile Lakes, and Mid-
Coast Small Ocean Tributaries. While these basin plans provide guidance just for ODFW 
fish management, this Conservation Plan documents management strategies, actions, and 
commitments for all Oregon natural resource agencies. 

 

Salmon Management Planning � Historical Perspectives 

Declines in salmon populations, salmon catch, and the adverse impacts of various 
traditional land and water use practices have been the subject of successive restoration 
plans since the late 1800s. Each of these plans proposed actions to improve the 
abundance of salmon available for harvest. Essentially, all of these plans failed to 
achieve their stated intent. All of the salmon restoration plans created prior to the Oregon 
Plan noted the adverse effects of traditional land and water uses, but none offered any 
substantive means of protecting or restoring habitat. These historical salmon 
management plans were created solely by an Oregon fisheries agency, independently, and 
without support of the various state and federal management agencies that directly 
affected the watersheds that support salmon throughout their life cycle. Oregon fishery 
agencies historically proposed to employ legally authorized management action, namely, 
hatchery production and harvest management. 

 

Consistent with the management philosophy of the time, historical salmon management 
plans proposed to employ hatchery production 1) to replace lost or altered salmon habitat 


and 2) to maintain or increase salmon harvest. These historical salmon management 
plans also tended to treat each salmon species (i.e., coho salmon, chinook salmon, 
steelhead, and so on) as rather homogeneous animals � the philosophy was that a fish is a 
fish and fish from one river were exchangeable with fish from another river. Science and 
experience has shown that these philosophies and management practices were overly 
optimistic and technically inaccurate. 

 

A Coho Salmon Management Plan adopted by ODFW in1982 represented a change in 
thinking and set the management stage for subsequent development of the Oregon Plan, 
because it introduced the importance of stock differences, impacts of hatchery 
production, potential to over-harvest naturally produced salmon, and noted the impacts of 
various land use management practices on production potential. The Oregon Plan and 
this Conservation Plan are very different than the salmon management plans created prior 
to the 1982 plan because these and other recent plans 1) recognize natural production as 
the foundation of ESU sustainability; 2) recognize effects of fishery harvest, hatchery 
programs, marine survival, predation, and various land use practices across the entire life 
cycle of the fish; and 3) include commitments from the management entities that affect 
the fish. 

 

Recent Conservation Planning for the Oregon Coast Coho ESU 

The Oregon Coast coho ESU has, since 1995, been subject of extensive conservation 
planning; data gathering; scientific and policy analysis; restoration action by government 
and private landowners using public and private funds; and contentious debate and 
litigation regarding whether the ESU should or should not be listed. Since 1997, the ESU 
has been provisionally not-listed, listed, held in abeyance from being listed, and most 
recently not-listed by NOAA. 

 

In January 2006, the National Marine Fisheries Service published in the Federal Register 
their finding that the Oregon Coast coho ESU does not warrant listing as an endangered 
or threatened species under the ESA (NOAA Fisheries 2006). This decision by NOAA is 
currently being contested in Federal court. Oregon does not expect the outcome of the 
current litigation to be the final chapter in the ongoing debate over the ecological and 
policy status of the ESU. 

 

Considering the ongoing debate and litigation, the Conservation Plan contains the 
elements required under NFCP and is also intended to contain most of the elements 
required by a federal ESA Recovery Plan. The primary required elements of a federal 
Recovery Plan include 1) objective and measurable criteria for delisting, 2) site-specific 
actions required for recovery, and 3) estimates of the time and cost of implementing the 
plan. A key distinction exists between this Conservation Plan and a federal Recovery 
Plan. Specifically, whereas ESA Recovery Plans focus on criteria actions needed to 
achieve delisting of species, this Conservation Plan is developed for a species that is not 
listed under federal ESA. This Plan, therefore, establishes criteria and identifies actions 
needed to achieve a socially established desired status goal that reaches substantially 
beyond minimum viable status, similar to broad sense recovery objectives identified in 
some federal recovery plans. This Conservation Plan would need to be modified 


somewhat in order to serve as a federal Recovery Plan, such as revising delisting criteria 
and actions. 

 

Biological Features of the Oregon Coast Coho ESU 

Coho salmon are widely distributed, essentially ubiquitous, in large and small Oregon 
Coastal river basins in this ESU and were historically well distributed in Oregon 
tributaries to the Columbia River. During pre-development times (circa 1850) coho 
salmon were far more abundant than Chinook salmon in the majority of Oregon coastal 
streams, and the runs of coho salmon to these areas was likely only approached or 
exceeded by runs of chum salmon in rivers along the northern portion of the Oregon 
coast. 

 

Coho were the most abundant salmon species in rivers of the Oregon Coast Coho ESU 
and were the most numerous species in commercial and recreational catches off the 
Oregon coast during the 1950s through the 1970s. Whereas spawning runs of naturally 
produced Chinook salmon in Oregon coastal streams have demonstrated a stable or 
increasing trend since 1950, production (catch plus spawning escapement) of naturally 
produced coho salmon declined to historically low levels since the 1950s. However, 
returns of spawning coho to the Coast coho ESU since 2000 have been higher than 
decadal averages since the 1950s. This improvement is primarily related to two factors: 
1) harvest related mortality in ocean fisheries has decreased from levels of over 80% to 
levels generally less than 15%, and 2) marine survival improved from the very low levels 
observed during the 1990s. 

 

When compared to Chinook salmon and steelhead, coho salmon exhibit a relatively less 
complex life history. The vast majority of coho migrate as juveniles through estuaries to 
the ocean after spending one winter in freshwater and then spend two summers in the 
ocean before returning to spawn as 3-year old adults in the autumn and winter. Coho 
salmon normally spawn in relatively small tributaries with moderate to low gradient 
stream reaches and, as adults, return to spawning areas close to where they were hatched. 
Juvenile coho salmon migrate to the ocean as smolts in the spring, typically from late 
April, May, and early June. As smolts, coho may be present in estuaries for a period of 
weeks to perhaps a month during their migration to the ocean. As noted elsewhere in this 
Conservation Plan and in the 2005 OCCA, production of coho smolts in the Coast coho 
ESU is particularly limited by the availability of complex stream habitat that provides 
shelter to over-wintering juveniles during periods when flows are high, water 
temperatures are low, and food availability is limited. Oregon notes, however, that 
considerable uncertainty exists regarding the duration and value of estuarine residence by 
juvenile and adult coho; and the potential to improve estuarine habitat to the benefit of 
coho and other native species. 

 

Oregon coastal coho tend to make relatively short ocean migrations. Coho from this ESU 
are present in the ocean from northern California to southern British Columbia, but the 
bulk of the ocean harvest of coho from this ESU would be expected to be off the Oregon 
coast. This ESU is strongly influenced by ocean conditions off the Oregon Coast, 
especially by the timing and intensity of upwelling (a condition characterized by near-


shore ocean currents providing cool, nutrient-rich water that stimulates production of 
food that supports coho and other fish species). 

 

Various estimates have been proposed to represent the size of the coho runs returning to 
the Oregon Coast during the 1800s and early 1900s. For the purposes of this discussion, 
the Conservation Plan accepts that historical (pre-development) coho runs to the Coast 
coho ESU may have been in the range of one to two million fish during periods of 
favorable ocean conditions. If true, and if the runs were not fished (harvested) this 
represents concentrations of several hundred spawners per mile across the ESU, assuming 
that roughly 4,000 miles of spawning habitat was available to these fish. Such densities 
of coho spawners are within the range with spawner densities that have been observed for 
this species in many undisturbed watersheds throughout the Pacific Northwest. 

 

Densities of spawning coho from 1993 - 1999 (a period characterized by very poor 
marine survival of coho salmon) often averaged in the range of 10 to 15 spawners per 
mile. Densities of spawning coho during 2000 - 2006 (when ocean survival was better) 
have averaged in the range of 30 to 60 fish per mile. These recent densities of coho 
spawners are far below historical numbers; however the density of naturally produced 
coho in most populations has been higher in recent years than in the past five decades. 

 

2005 Oregon Coastal Coho Assessment: Key Findings 

� ESU population structure. The TRT identified 56 coho populations as components of 
the ESU; 21 are classified as functionally or potentially independent (hereafter 
independent) and 35 are classified as dependent populations. 
� Viability analysis. The ESU is viable and sustainable. 
� Population limiting factors. Stream complexity and water quality are the primary 
limiting factors for the vast majority of, but not all, populations. The term stream 
complexity refers to any of the various combinations of conditions that result in over-
winter shelter conditions sufficient to support sustainable populations through adverse 
marine survival periods. Habitats with higher levels of complexity also tend to 
provide benefits to all coho life stages. 
� Current regulatory programs. A wide variety of Oregon and federal laws and conservative 
management practices related to watershed function, stream and estuary alteration, fish 
harvest management, and hatchery practices have been implemented since the 1950s and, 
most significantly, from the 1970s through the present. Taken as a whole, these laws and 
policies represent a significant improvement over legal protections and management 
practices that were historically common across the ESU. Oregon concluded that the 
framework of existing regulatory programs is sufficient to maintain or slightly improve the 
viability of the ESU (2005 OCCA). 
� Threats to ESU viability. The most significant threats to this ESU noted in the 2005 OCCA 
would be if 1) a significant decrease occurred in marine survival of coho (compared to what 
was observed during 1993 � 1999), and/or 2) a significant reduction occurred in the 
availability of high quality, complex stream habitat to support over-wintering juvenile coho. 
� Coho distribution and conservation opportunities. A very high proportion (~90%) of 
stream reaches with the highest potential to produce coho is on private lands, 
including forest, agricultural, and urban lands. Land use practices and management 



objectives vary considerably across the distribution of coho from high gradient 
headwaters to estuaries. 


 

 

1. ESU Population Structure 

 

Oregon has adopted the population structure proposed by the NOAA Technical Recovery 
Team (Lawson et al. 2004) for the Coastal coho ESU. The NOAA TRT identifies 57 
populations comprising five population strata within the ESU. Within these 5 strata, 21 
populations (Figure 1) are thought to occur in basins with sufficient historical habitat to 
have persisted through several hundred years of normal variations in marine and 
freshwater conditions These have been classified as potentially independent and 
functionally independent populations. Potentially independent populations were 
historically self-sustaining but also likely were demographically influenced by 
neighboring functionally independent populations. Functionally independent populations 
were historically self-sustaining and likely had relatively little demographic influence 
from neighboring populations (Lawson et al. 2004). This Plan will subsequently refer to 
all of the 21 previously mentioned populations as independent populations. Independent 
populations identified by the NOAA TRT are listed in Table 1; their location within the 
ESU is shown in Figure 1. 

 

Table 1. Geographic strata and independent populations that comprise the Oregon Coast 
coho ESU. 

Geographic Stratum 

Populations 

Northern 

 

 

Necanicum 

Nehalem 

Tillamook 

Nestucca 

 

 

North-Central 

 

 

Salmon 

Siletz 

Yaquina 

Beaver 

Alsea 

Siuslaw 

Umpqua 

 

 

Lower Umpqua 

Mid Umpqua 

North Umpqua 

South Umpqua 

 

Lakes 

 

Siltcoos 

Tahkenitch 

Tenmile 

South-Central 

 

 

Coos 

Coquille 

Floras 

Sixes 



 

 

Future analysis may support a revised ESU population structure, perhaps changing the 
classification of some dependent populations to independent status. The 21 independent 


populations are grouped into five strata. The vast majority (~ 95%) of the coho 
historically produced in this ESU probably originated from these independent populations 
(Lawson et al. 2004). The remaining 36 dependent populations, in concept, are thought 
to be largely sustained by periodic reproductive contribution of strays from adjacent 
larger populations in order to naturally persist for periods longer than 100 years. 
Populations are the basic elements of the ESU and population strata are used to represent 
clusters of populations that share ecological or geographic similarities. 

 

Figure 1. Independent populations and geographic strata of the Oregon Coast coho ESU. 

 

 

 

 


2. Current ESU Status 

 

Conceptual Classification of ESU Status 

A conceptual partitioning of various levels of species performance into progressive 
classifications � from very poor to very good � permits development of specific criteria 
for status assessment. A conceptual classification of various levels of ESU status 
(performance) used in this Conservation Plan is illustrated in Table 2. Currently, the 
Oregon Coast coho ESU is classified as viable. The goal of this Conservation Plan is to 
improve the productivity of the fish and their supporting habitat to a level where desired 
status classification is achieved. 

 

Table 2. Conceptual steps of biological status for a species from pristine to extinct and 
associated definitions. 

 

Classification 

Definition 

 

Pristine 

All historical populations within the ESU are healthy and 
adverse impacts from human activities are insignificant at the 
population and ESU scale. 

 

Desired status 

(aka: broad-sense 
recovery/Oregon Plan 
goal) 

Populations of naturally produced fish comprising the ESU are 
sufficiently abundant, productive, and diverse (in terms of life 
histories and geographic distribution) that the ESU as a whole 
will: a) be self-sustaining, and b) provide environmental, 
cultural, and economic benefits. 

 

Viable 

Populations of naturally produced fish comprising the ESU are 
sufficiently abundant, productive, and diverse (in terms of life 
histories and geographic distribution) that the ESU as a whole is 
sustainable into the foreseeable future. 

Threatened 

The ESU is likely to become endangered within the foreseeable 
future throughout all or a significant portion of its range. 

Endangered 

The ESU is likely to become extinct within the foreseeable 
future throughout all or significant portion of its range. 

 

Extinct 

Means an ESU contains so few members that there is no chance 
their evolutionary legacy will ever re-establish itself within its 
native range. 



 

Conservation Plan Considers the ESU as Viable 

Based on Oregon�s assessment of the status of coastal coho relative to viability criteria 
presented in the 2005 OCCA, the ESU is viable (Table 3). Specifically, coho populations 
generally demonstrate sufficient abundance, productivity, distribution and diversity to be 
sustained under the current and foreseeable range of environmental conditions. In fact, 
the ESU retains sufficient productivity and is supported by sufficient habitat to be 
sustainable through a future period of adverse ocean, drought and flood conditions 
similar to or somewhat more adverse than the most recent period of poor survival 
conditions (late 1980s and 1990s). 

 


Table 3. Conclusions from the 2005 OCCA viability analysis for Oregon Coast coho at 
the population, strata and ESU level. 

ESU criteria 
conclusion 

Geographic 
stratum 

Stratum criteria 
conclusion 

Population 

Population criteria 
conclusion 

Pass 

Northern 

Pass 

Necanicum 

Pass 

 

 

 

Nehalem 

Fail 

 

 

Tillamook 

Fail 

 

 

Nestucca 

Pass 

North-Central 

Pass 

Salmon 

Fail 

 

 

Siletz 

Fail 

 

 

Yaquina 

Pass 

 

 

Beaver 

Pass 

 

 

Alsea 

Fail 

 

 

Siuslaw 

Pass 

Umpqua 

 

 

 

Pass 

Lower Umpqua 

Pass 

 

Mid Umpqua 

Pass 

 

North Umpqua 

Fail 

 

South Umpqua 

Pass 

Lakes 

Pass 

Siltcoos 

Pass 

 

 

Tahkenitch 

Pass 

 

 

Tenmile 

Pass 

South-Central 

Pass 

Coos 

Pass 

 

 

Coquille 

Pass 

 

 

Floras 

Pass 

 

 

Sixes 

Fail 



 

NOAA Concludes that the ESU does not Warrant Listing 

NOAA was recently required to consider ESA listing status of 27 ESUs across the Pacific 
Northwest. NOAA�s conclusion regarding the Oregon Coast coho ESU (NOAA 
Fisheries 2006) contained the following statement. After considering the best available 
scientific and commercial information available, we have concluded that the ESU is not 
in danger of extinction throughout all or a significant portion of its range, nor is it likely 
to become so within the foreseeable future. 

 

Uncertainty Regarding ESU Viability 

Although Oregon concluded that the ESU is viable and sustainable; and NOAA 
concluded that the Coast coho ESU does not warrant listing under federal ESA, the 
NOAA TRT provided the following cautionary perspective regarding the status of the 
ESU (letter to Robert Lohn, August 19, 2005). �We have preliminary indications for the 
recovery status of the Oregon Coast coho Salmon ESU. At this time our evaluation 
indicates, with a moderate degree of uncertainty, that the ESU is persistent (persistence 
is relevant to Endangered status). Our evaluation of biological sustainability (relevant to 
Threatened status) based on current and recent past conditions shows a high degree of 
uncertainty with respect to the statement that the ESU is sustainable. Again these are 
preliminary results and are subject to change upon further testing and review�. 

 


3 Self-sustaining (ORS 496.430) means having a sufficient proportion and distribution of constituent 
populations that: (a) are likely to survive prolonged periods of habitat, oceanic, climatic and environmental 
conditions that are detrimental to a population; and (b) have habitat of sufficient quality and quantity that is 
likely to provide survival rates adequate to maintain associated ecological, cultural and economic benefits. 

Oregon recognizes the TRT�s uncertainty regarding their preliminary assessment that the 
ESU is sustainable and also recognizes that litigation has been filed contesting NOAA�s 
decision to not list the ESU under the federal ESA. 

 

Relevance of Viability and Listing Status Uncertainty 

Debate or uncertainty regarding the listing status of the ESU is not a lynch-pin of the 
Conservation Plan. Why? Simply stated, this Conservation Plan is designed to improve 
the status of the ESU and virtually all of its constituent populations and to improve the 
productive capacity of the coho and their habitat to levels significantly higher than a level 
where the ESU could be considered a potential candidate for listing under the federal 
ESA. 

 

This Conservation Plan maintains effective management protections and initiates 
additional actions that are intended to produce a significant improvement in the 
productive capacity of the ESU � regardless of how the ESU�s current viability and 
listing status under federal ESA is defined. 

 

The most important aspect of the Conservation Plan is its commitment to ensure that the 
trajectory for the coho salmon ESU and the habitat that supports the fish is improving � 
that the productive capacity of the habitat and the fish will be substantially greater in the 
future than they are today. 

 

3. ESU Desired Status: Vision, Goals, Measurable Criteria, 
and Gaps 

 

Oregon�s Vision for ESU Desired Status 

General Description of Desired Status for the Coast Coho ESU: Populations of naturally 
produced coho salmon are sufficiently abundant, productive, and diverse (in terms of life 
histories and geographic distribution) that the ESU as a whole 1) will be self-sustaining3 
into the foreseeable future, and 2) will provide significant ecological, cultural, and 
economic benefits. 

 

Oregon�s desired status goal for this ESU is ambitious. What will Oregon look like 
across this ESU if the desired status goal is achieved? Here are some characteristics of 
the ESU, the watersheds, the fish, and the communities that should be observable when 
this desired status goal is achieved. 

� There will be, on average, abundant numbers of coho salmon in our coastal streams 
including adults in the fall and winter and juveniles throughout the year. 
� During return years affected by extremely poor marine survival conditions (similar to 
the 1990s), roughly twice as many coho will return to the ESU, compared to the 



numbers that were observed spawning in the 1990s; during return years affected by 
favorable marine survival there will be well over a half a million spawners returning 
to the ESU. 
� Tributary, mainstem, estuarine, and wetland reaches of coastal rivers will provide 
sufficient high-quality habitats and water quality to support increased numbers of 
ocean-bound coho smolts. 
� Some hatcheries in coastal basins (with program guidance provided in this 
Conservation Plan, NFCP, and Fish Hatchery Management Policies), will be 
producing hatchery coho to support consumptive fisheries that achieve societal and 
cultural needs not met by the natural production goals of this plan. 
� Ample opportunity will exist for people to fish-for and keep naturally produced coho 
in the ocean and in many streams, again, consistent with population-based 
conservation goals. 
� There will be on average, 2 to 4 times more coho carcasses in the spawning streams 
as there have been in the last 5 decades and these carcasses will provide ecological 
benefits to native fish and wildlife and the ecosystem. 
� There will be a wide variety of traditional land use activities throughout the ESU, 
including forestry, agriculture, recreation, and industrial and housing development. 
� Coho salmon will be a far more significant feature of the cultures of Native 
Americans across the ESU than has recently been possible. 
� Coho salmon will be a far more significant factor in the cultures and employment in 
coastal communities across the ESU than has recently been possible. These 
biological, social, and economic benefits will be widely shared across the ESU. 
Societal values of coho salmon will include intrinsic values (based simply on the 
knowledge of the resource's existence) and bequest values (which confer value to the 
resource for the benefit of future generations). 


 

Desired Status Goal 

The description of the goal and the gap between current and desired status presented in 
this Chapter emphasizes abundance. Other physical and biological aspects of desired 
status (see list under Measurable Criteria for Independent Populations section) are 
described in Appendix 2. 

 

Oregon�s desired status for the Coast Coho ESU is a science-based, socially established 
goal. As previously noted, this goal represents a condition of the ESU that is 
significantly higher than a level where it could be considered a potential candidate for 
listing under federal ESA. The desired status goal targets a return of spawners to the 
ESU (at 1.1% survival from smolt-to-adult in the marine environment) that is roughly 
twice the number of coho spawners observed during 1993-1999 (i.e., about 100 thousand 
versus about 50 thousand). The desired status goal for this ESU is consistent with the 
mission of the Oregon Plan, namely, to create conditions in which coho across the ESU 
are sufficiently abundant, productive, and diverse that the ESU is self sustaining and 
provides substantial environmental, cultural, and economic benefits. Desired status 
represents a level of population performance that exceeds the level at which an ESU is 
considered viable and is a goal that is based on a combination of legislative mandates, 
social values, and non-regulatory contributions. 


 

 

Measurable Criteria for Desired Status 

The Native Fish Conservation Policy requires each conservation plan to include 
measurable criteria of species performance. Achievement of the desired status goal for 
the Coast coho ESU will be based on measurable criteria defined in Appendix 2. The 
desired status goal will be met under the following conditions: 1) all independent 
populations pass the six measurable criteria for independent populations and 2) the 
aggregate of dependent populations within a biogeographic stratum pass the two 
measurable criteria for dependent populations. 

 

Measurable Criteria for Independent Populations. 

Measurable criteria (Appendix 2) to evaluate achievement of the desired status for the 
Coast Coho ESU are presented for the following attributes of species performance: 

1. Abundance � the number of naturally-produced spawners. 
2. Persistence � the forecast likelihood that the population will persist in the 
future. 
3. Productivity � the number of recruits (progeny) produced per spawner 
(parent). 
4. Distribution � the distribution of spawners among habitats within a 
population�s home range. 
5. Diversity � indices of genetic variability related to a population�s ability to 
adequately respond to unpredictable natural variations in the environment and 
retain those adaptive genetic characteristics that promote optimum survival in 
basin specific habitats. 
6. Habitat � The amount of available high quality habitat across all freshwater 
and estuarine life stages. 


 

Gap (Difference between Current and Desired Status) 

Achieving the desired status goal for the overall ESU will result in having roughly one 
hundred thousand coho (on average) return to spawning streams in the ESU during an 
extended period of extremely poor ocean survival (<1.1%) like was observed during 
1993-99 when the average return to these streams was about fifty thousand coho. During 
periods of high ocean survival (>15%), returns of spawning coho to the ESU would be 
expected to range around eight hundred thousand fish (see Appendix 2, Desired Status 
Measurable Criteria). The overall ESU gap does not necessarily relate directly to the 
gaps for individual independent populations. Some populations are currently well below 
half of their desired status goal for extremely poor ocean survival, whereas other 
populations have a much smaller relative gap (Appendix 2). 

 

Achieving the desired status for the ESU will require a combination of improving 
productive capacity of the fish and the habitat that supports them in amounts that will 
lead to twice the number of spawning adults that were seen in the 1990�s for the overall 
ESU. This Conservation Plan assumes that most of the improvement will require 
enhancing the productive capacity of the habitat, although significant improvement in the 


productive capacity of the populations across the ESU will also accrue from recent 
changes to harvest and hatchery management programs. 

 

4. Limiting Factors 

 

Numerous factors contribute to the gap between current and desired status of populations 
comprising the Oregon Coast Coho ESU. Primary factors that currently constrain the 
ESU, or limiting factors, were identified in the 2005 OCCA (State of Oregon 2005). In 
general, ocean condition is the primary factor influencing coho abundance, and stream 
habitat complexity is the primary factor limiting achievement of desired status. 

 

Ocean Conditions as a Limiting Factor 

Although marine survival of coho associated with ocean conditions is the largest single 
factor regulating coho productivity and abundance, it is not considered a primary factor 
limiting the ESU�s ability to reach desired status. This is because desired status criteria 
are scaled appropriately for variable marine survival and because management has little 
influence on marine survival. 

 

Ocean conditions, or the availability of food sources for coho in the marine environment, 
determine the rate at which coho smolts will survive to become adults. These conditions 
are influenced by cyclic and periodic fluctuations in ocean currents and cannot currently 
be predicted or managed. For this reason, this Conservation Plan recognizes the 
importance of ocean conditions on coho survival and abundance, but focuses on those 
limiting factors that can be influenced by management actions. Understanding and 
predicting ocean conditions have been identified as a research need in this Conservation 
Plan. 

 

Although Oregon cannot currently influence ocean conditions, the state will be able to 
determine whether improvements or declines in ESU status are attributable to the ocean 
or to the effectiveness (or lack thereof) of actions taken under this plan. The desired 
status criteria were developed to provide for measurable goals at varying ocean survival 
rates. This will allow status assessments to be put in the context of recent ocean 
conditions. 

 

Stream Complexity Defined 

Stream complexity is a term that refers to the ability of a stream to provide a variety of 
habitats. The type of habitat most limiting in the Coast coho ESU is high quality over-
winter rearing habitat. In the context of factors most limiting coho in this ESU, stream 
complexity and high quality over-winter rearing habitat refer to the same thing: habitat of 
sufficient quality to produce over-winter survival at rates high enough to allow coho 
spawners to replace themselves at full-seeding during periods of poor ocean conditions 
(3% smolt to adult survival). Both terms refer to a variety of habitat conditions that 
create shelter for juvenile coho salmon during the over-winter rearing period. During this 
critical period, high stream flows can flush juvenile coho out of streams into saltwater 
where they perish. Based on several years of studying coho streams and determining 
how many smolts are produced out of each type of habitat (Nicholson et al. 1992a, 


1992b), habitat capable of producing 2,800 coho smolts per mile is classified as high 
quality over-winter habitat. 

 

High quality over-wintering habitat for juvenile coho is usually recognizable by one or 
more of the following features: large wood, a lot of wood, pools, connected off-channel 
alcoves, beaver ponds, lakes, connected floodplains and wetlands, and other conditions: 
therefore, more than one set of habitat conditions is capable of providing high over-
winter survival. High quality over-wintering habitat is almost always present only in 
areas where the stream is fairly low gradient and there are broad valley areas alongside 
the stream. 

 

Because high quality over-winter rearing habitat can take many forms, the term stream 
complexity is used to define this limiting factor. 

 

Limiting Factors for Coast Coho Populations 

Several limiting factors are identified for individual independent coho populations in this 
ESU (Table 4), including stream complexity (high quality habitat), water quality, water 
quantity, hatchery impacts, spawning gravel and exotic species. Stream complexity is the 
predominant limiting factor for populations in the Oregon Coast coho ESU. 

 

It should be noted that factors that are listed as secondary, such as water quality, are 
important to address or maintain, and may become the most limiting as efforts are made 
to achieve the desired status goal. It is expected that many of the actions taken through 
this Conservation Plan to address the primary limiting factor stream complexity will 
support maintenance or improvement of water quality suitable to native aquatic species, 
including coho salmon. 

 


Table 4. Primary and secondary limiting factors for independent populations in the 
Oregon Coast coho ESU. (Source: 2005 OCCA) 

Population 

Primary 

Limiting Factor 

Secondary 

Limiting factor 

Necanicum 

Stream Complexity 

-- 

Nehalem 

Stream Complexity 

Water Quality 

Tillamook 

Stream Complexity 

Water Quality 

Nestucca 

Stream Complexity 

-- 

Salmon 

Hatchery Impacts 

Stream Complexity 

Siletz 

Stream Complexity 

-- 

Yaquina 

Stream Complexity 

Water Quality 

Beaver 

Spawning Gravel 

Stream Complexity 

Alsea 

Stream Complexity 

Water Quality 

Siuslaw 

Stream Complexity 

Water Quality 

Lower Umpqua 

Stream Complexity 

Water Quality 

Middle Umpqua 

Water Quantity 

Stream Complexity Water Quality 

North Umpqua 

Hatchery Impacts 

Stream Complexity 

South Umpqua 

Water Quantity 

Stream Complexity Water Quality 

Siltcoos 

Exotic Fish Species 

Stream Complexity Water Quality 

Tahkenitch 

Exotic Fish Species 

Stream Complexity Water Quality 

Tenmile 

Exotic Fish Species 

Stream Complexity Water Quality 

Coos 

Stream Complexity 

Water Quality 

Coquille 

Stream Complexity 

Water Quality 

Floras 

Stream Complexity 

Water Quality 

Sixes 

Stream Complexity 

Water Quality 



 

The limiting factors identified above for each independent coho population were 
determined for the population as a whole. The state recognizes that analyses done at a 
smaller spatial scale than the population will likely determine limiting factors in some 
areas that are contrary to those found for the population. These smaller spatial scale 
analyses have not been conducted in all areas of the ESU and therefore did not allow this 
Conservation Plan to identify limiting factors at such scales. To achieve the desired 
status goal for the ESU as efficiently as possible, it is imperative that such smaller scale 
analyses occur. The state will support work by local groups to conduct such analyses. 
As an example, the Oregon Watershed Enhancement Board (OWEB) will soon issue a 
Request for Proposals for the compilation of limiting factors in the Oregon Coast Coho 
ESU. The compilation will be conducted at the 5th field spatial scale. The results will be 
used to review and prioritize restoration activities and guide future funding decisions. 

 

Predation as a Limiting Factor 

The state acknowledges that there is some uncertainty about how much of a threat 
predation poses to coastal coho populations, but Oregon�s 2005 Assessment of the Coast 
Coho ESU, based on the best available scientific information, did not rank predation as a 
key limiting factor for any coastal coho populations. Scientific evaluations currently 
available do not confirm or refute the possibility that predation by marine mammals 
and/or birds is a significant limiting factor for coastal salmon populations. Better 
understanding of this issue has been identified as a research need in this plan. 

 


The exception to this generalization is that coho populations in the Lakes basins 
(Tahkenitch, Siltcoos, and Tenmile) are primarily limited by interactions (including 
predation) with exotic (warmwater) fish species. Current ODFW fish management for 
these Lake basins recognizes 1) that coho populations are currently highly viable, 2) 
negative effects of warm water fish species on coho salmon, 3) ecological difficulties of 
removing warmwater species, and 3) various social and economic entities that support 
continuing fisheries associated with the warmwater species. 

 

 

5. Conservation Strategy for the Coast Coho ESU 

 

This Conservation Plan depends on a strategy of effective implementation by multiple 
entities, of complex programmatic and non-regulatory efforts at multiple spatial scales, 
including the following. 

1. Continue statewide implementation of the Oregon Plan with emphasis on addressing 
potential limiting factors via management action across the entire freshwater, 
estuarine, and ocean life cycle of the species. 
2. Maintain the productive capacity of the ESU and populations by conserving and 
increasing the amount of high quality habitat across the ESU and insuring adequate 
dispersal corridors between areas with high quality habitat. 
3. Implement the Oregon Plan habitat strategy: (see abstracts of Agency Commitments 
in Chapter 7 and Appendix 3). The Oregon Plan habitat strategy will provide more 
and better technical and administrative support to local cooperative conservation 
work by SWCDs, watershed councils, STEP volunteers, private landowners and 
others. 
4. Restore processes that create and sustain high quality habitat. Where necessary, 
implement both short term and long term habitat restoration projects. The goal of 
these activities is to significantly increase the productive capacity of coho salmon 
habitat across the ESU. 
5. Provide guidance to support policy decisions regarding prioritization of conservation 
investments to achieve the desired status goal for the Coast coho ESU. 
6. Implement ESU-wide evaluation of Coho Winter High Intrinsic Potential Habitat 
(CWHIP) models and mapping methodologies (see Research, Monitoring, and 
Evaluation chapter). 
7. Support development � in consultation with community-based watershed entities � of 
long-term conservation strategies that address limiting factors at scales within 
populations. 
8. Continue participation in regional conservation and monitoring strategies including 
various state and federal managers (NW Forest Plan, Pacific Northwest Aquatic 
Monitoring Partnership, various Oregon Conservation Strategies, etc.). 


 

ESU Conservation Principles 

Managing the potential adverse impacts of human activities (also called threats) across 
the life-cycle (e.g., fish harvest, hatchery, and habitat management) is an essential 
element of efforts to achieve the desired status goal for the ESU. Achieving Oregon�s 
desired status goal will require a combination of efforts to integrate scientific principles 


of conservation biology and ecosystem management with the practical economic, social, 
and political constraints of Oregon as it exists today and into the future. 

 

In general, effective management actions have already been taken to minimize adverse 
impacts of harvest and hatcheries on the ESU, therefore, this Conservation Plan will 
primarily focus on 1) protecting the existing productive capacity of habitat to maintain 
viability of the ESU and 2) improving this productive capacity in order to achieve the 
desired status goal. In this context, the term protecting does not necessarily imply that all 
existing high quality habitats will be preserved in their current state and location, because 
watershed conditions naturally evolve over time. Protection of existing productive 
capacity of the ESU implies that no long-term loss of productive capacity of habitat will 
occur across the ESU. Oregon�s diverse regulatory and non-regulatory efforts to 
conserve and restore watershed processes and functioning stream reaches are applicable 
from headwaters above the range of coho distribution downstream and including 
estuaries. 

 

Conservation programs for salmon should recognize the dynamic nature of ecosystems. 
Ecosystems are not static. A variety of natural disturbances create a wide range of 
conditions over time in any given location and across diverse geographic areas at any 
point in time. Effective conservation strategies must account for these dynamics. 

 

Spawning and rearing coho salmon are not evenly distributed throughout a watershed, 
because high quality spawning and rearing habitats are not uniformly distributed within 
watersheds. The spatial concentration of high quality spawning and/or rearing habitat is a 
characteristic referred to as patchiness and is also characteristic of dynamic, productive 
river basins that are unaltered by human activities. Effective habitat conservation 
strategies for salmon require 1) sufficient patches of high quality habitat to sustain 
population viability; and 2) suitable dispersal corridor habitat that allows coho to migrate 
from one area of high quality habitat to another. Conservation of the existing amount of 
high quality coho habitat and suitable dispersal habitats within populations and across the 
ESU is the essential first-step that will provide a basis for achieving Oregon�s desired 
status goal. Increasing the amount of high-quality coho habitat via conservation is the 
essential next stage required to achieve the desired status goal. 

 

The productive capacity of coho habitat is maintained (in a dynamic process over space 
and time) in watersheds unaffected by human development through a variety of natural 
ecological processes (wildfire, landslides, stream meandering, forest vegetation 
succession, etc.). Protecting those natural ecological processes, ensuring that they occur 
throughout a watershed, and adjusting land use management to restore natural ecological 
processes where they are absent, are all elements of conservation biology that support 
conservation of native fish and wildlife. This Conservation Plan recognizes these 
scientific principles and also recognizes values associated with conserving and restoring 
the vitality of coastal cultures, economies and communities. It is not feasible to conserve 
or restore natural ecological processes without regard to the existing social and economic 
infrastructures throughout the ESU. This Conservation Plan attempts to achieve a 


4 The impact of Measure 37 on this trend is unknown at this time. 

balance between legitimate efforts to achieve the desired status goal for the Coast coho 
ESU consistent with social and economic values of Oregon citizens and communities. 

 

Oregon�s Regulatory Programs 

The framework of regulatory programs to manage the impacts from hatchery, harvest and 
land-use management is a key element of the conservation strategy for this Conservation 
Plan. Changes to regulatory programs implemented from the 1950s through 2004 were 
noted in the 2005 OCCA (harvest, hatchery, and habitat management laws). These more 
conservative management regulations undoubtedly served to support the Coast coho 
ESU�s viability through the poor marine survival conditions observed during the mid-to-
late 1990�s. The agencies that are mandated to implement, monitor compliance with and 
enforce these programs are committed to maintaining the effectiveness of their programs. 

 

Current conditions across the Coast coho ESU have been influenced by historical 
management practices of one sort or another. Whereas past practices related to land-use 
and fish harvest management were extensive and broadly distributed across the ESU, the 
impact of historical practices related to hatchery management varied greatly by 
population. Changes were made in both harvest and hatchery practices in the 1990�s that 
have reduced or eliminated significant impacts of these practices on the Coast coho ESU. 
Harvest and hatchery regulation will continue under the current framework provided by 
the Pacific Fisheries Management Council�s Fishery Management Plan (an international 
agreement on allocating fishery impacts between California, Oregon, Washington, British 
Columbia and Alaska), Oregon�s Native Fish Conservation and Hatchery Management 
policies, and guidance provided in this plan. 

 

Land-use regulations in Oregon have been strengthened in the last few decades and have 
reduced the effect of land-use practices on coho habitat, especially estuarine habitat and 
watershed riparian habitat. The regulatory regime and management practices that cause 
habitat alterations that are unfavorable to coho salmon were very different historically 
than the regulatory programs and management practices that have evolved since the 
1950s, and most significantly since the 1970s (see 2005 OCCA). The positive effects of 
these laws and practices are expected to continue to accrue and land-use regulations in 
Oregon have been further strengthened in the last few decades4. Oregon�s contemporary 
land use regulatory regime and management practices have clearly established a different 
habitat management climate than was in effect for over a century and have reduced the 
impact that land-use practices have on coho habitat. These regulatory changes did not 
completely remediate conditions created by historical practices, but have reduced the 
threat of future impacts. Regulatory programs by their very nature are limited to 
preventing future habitat alteration; they do not address legacy conditions resulting from 
more than 12 decades of relatively unregulated land altering activities. 

 

Oregon concluded that the existing conservation framework of regulatory programs and 
non-regulatory elements is sufficient to sustain and slightly improve the current viability 
of the ESU (see 2005 OCCA). The existing regulatory structure was not designed to 
support achievement of the desired status goal for this ESU and no changes to that 


regulatory structure are being proposed here. The significant improvements in the 
productive capacity of coho and their habitat needed to achieve the desired status goal 
will be pursued through non-regulatory, cooperative, conservation actions. 

 

Strategy Elements 

Starting from the baseline of current management and regulatory programs, Oregon�s 
intent is to integrate conservation principles with site-specific habitat improvement across 
the ESU �noting many implementation challenges; for example: 

� the existing infrastructure (cities, roads, land-use, industry, and so on) including 
the location of these infrastructures within watershed areas that are most 
important to coho salmon, 
� considerable variation in the current condition of coho and habitat conditions at 
local spatial scales across the ESU (some populations and habitats are in better 
condition than others) 
� the existing patchwork of public and private land ownerships, with differing 
management goals, practices, and decision-making capacity; 
� a strong traditional and socially supported practice of natural resource utilization 
for economic benefit of private citizens, and 
� widely diverse values among Oregonians regarding the relative importance of 
salmon conservation in relation to other social and economic issues. 


 

The practical feasibility, given the challenges stated above, of conserving and restoring 
ecosystem processes that support strong coho salmon populations may be highest on 
federal lands, followed, respectively, by state forestlands, private industrial forestlands, 
non-industrial forest lands, and non forestlands (including agricultural and urban lands). 
Whereas coho salmon depend on habitat conditions across entire basins from headwaters 
to the estuary at some point in their life, a high proportion of habitat most suitable to 
over-wintering coho juveniles is located on private lands in lowland areas where 
historical alterations have been significant. Since this type of habitat has been identified 
as the predominant limiting factor across the ESU, these lowland areas on private lands 
will be one area of focus for habitat protection and restoration. 

 

Improving the quality and quantity of over-winter rearing habitat for coho in these areas 
will not be achieved by toughening land-use laws. The state has determined that the best 
strategy for protection and restoration of high quality over-winter rearing habitat in these 
privately-owned, lowland areas that have potential (Coho Winter High Intrinsic Potential, 
or CWHIP) is to seek the voluntary participation of the landowners in activities under the 
Oregon Plan. A greater quantity of effective protection and restoration projects will be 
implemented on the ground through willing landowners than could be achieved through 
enforcement of laws. Incentives to participate in Oregon Plan projects need to be 
expanded in order to recruit more landowners (see Oregon Plan habitat strategy in 
Chapter 7 and Appendix 3). Greater participation from landowners will be needed to 
substantially increase the productive capacity of coho and their habitat. Thus, the 
effectiveness of non-regulatory and incentive-based cooperative conservation efforts on 
private lands is extremely important to achieving Oregon�s desired status goal. 

 


Using Hatchery Fish as a Conservation Strategy 

Utilizing hatchery fish from a conservation hatchery program was considered and 
rejected as a primary strategy to achieve the desired status goal for the ESU. The 
objective of such a strategy would be to plant hatchery or wild adults, juveniles or eggs 
into streams with limited natural production to increase the number of naturally produced 
fish quickly. Stocking additional coho into streams is unlikely to address or compensate 
for the primary factors currently limiting coho numbers. These population �bottlenecks� 
generally occur during the over-winter stage of development prior to ocean entry of 
juveniles in the spring. Stocking adult or juvenile hatchery or wild coho into coastal 
streams without addressing the quality and quantity of over-winter rearing habitat is 
unlikely to produce the sustained increase in natural production needed to achieve 
Oregon�s Desired Status goal for the ESU. The use of the hatchery tool as a conservation 
�safety net� to avoid extinction is also inappropriate because the ESU is currently viable 
and not currently at risk of extinction. 

 

Salmon River is the one exception to this generalization, and is the one location where 
use of a conservation hatchery approach may be appropriate to restore natural production 
in the basin. Oregon has identified research to evaluate restoration of a viable coho 
population at Salmon River as a high priority research topic; conservation hatchery 
technologies and the role of the Oregon Hatchery Research Center in such an evaluation 
will be explored. The State�s current approach to recovering the Salmon River 
population is to focus efforts on the primary and secondary limiting factors that currently 
constrain natural production. This will be accomplished by re-programming the hatchery 
production to Youngs Bay and restoring stream complexity. If after 3-4 generations, 
natural production has not improved and the number of spawners or juveniles is limiting 
re-building, the use of a conservation hatchery program will be considered. Recent 
experience with lower Columbia coho and coastal coho has demonstrated that when 
limiting factors are eased, these populations are quite capable of rebounding to some 
degree on their own. 

 

Prioritizing Conservation Investment 

Prioritized conservation action is more likely to produce timely and beneficial results 
than the alternative � not prioritizing. Priority setting is also an extremely sensitive 
matter that may be informed by science, but ultimately requires policy choices. 
Imposition of a single, rigid prioritization system is likely to impair the overall 
effectiveness of this or any conservation plan because it could not adequately integrate all 
of the diverse science and policy aspects of decision making. Prioritizing conservation 
efforts and investments is extremely complicated. No single system is currently or ever 
will be available to propose priorities for conservation investments for all species, 
ecological processes, spatial scale, and policy strategies across this or any other ESU. 
Thus, funding entities will be required to consider a variety of complex information when 
making investment decisions. 

 

Prioritizing conservation investment is not new or limited to this ESU Conservation Plan. 
OWEB has been developing restoration priority guidance across Oregon based on local 
assessments of limiting factors at the 5th field HUC scale. The prioritization guidance in 


this Conservation Plan provides additional information for consideration relative to 
Oregon�s commitments to achieve a desired status goal for the coast coho ESU. 
Conservation action that supports the desired status for coho is expected also to benefit 
other native fish and wildlife species and improve watershed and ecological processes. 
For example, efforts to increase stream complexity for juvenile coho are likely to 
improve water quality and benefit associated native species. 

 

Prioritizing Conservation Investments in the Coast coho ESU 

Many factors merit consideration in prioritizing conservation investments related to this 
Conservation Plan and achieving the desired status goal for the ESU. There is no single 
method to assign value to each of these factors and objectively derive a relative 
investment merit score. None-the-less, the following factors would tend to indicate 
conservation investments that particularly merit funding, relative to achieving the desired 
status goal for this coho ESU. 

� Work that will improve viability status of a coho population from fail to pass (see 
2005 OCCA and ESU Status Chapter, Table 3) 
� Work that supports remediation of population-scale limiting factors identified for 
coho populations in the 2005 OCCA (Table 4). 
� Work that is based on watershed assessments and limiting factor analysis conducted 
by local watershed conservation entities (or others) at scales finer than the population-
scale limiting factors in the 2005 OCCA. 
� Work that supports restoration of ecological processes rather than providing a short-
term substitution for ecological processes. 
� Work that supports conservation of multiple native fish and wildlife species. 
� Work that supports maintenance or enhancement of life-history diversity in coho and 
other native fish and wildlife species. 
� Work that supports conservation of unique or rare functioning habitats and habitat 
diversity. 
� Work that supports conservation of unique or rare life histories and or genetic 
attributes of coho or other native fish and wildlife species. 
� Work that capitalizes on time-sensitive opportunities (e.g., willing landowners, time-
association with land-use action, etc.) 
� Work that is likely to produce a large (rather than a small) increase in productive 
capacity of a coho population or is likely to produce a lot more (rather than a few 
more) coho salmon. 
� Work that is likely to generate an increased level of participation by private 
landowners in non-regulatory cooperative conservation work. 


 

Future Refinement of ESU Conservation Strategy 

Oregon will support development � in consultation with community-based watershed 
entities � of long-term conservation strategies at scales within populations, including the 
following products and policy decisions. 

1. Participation in an ESU-wide evaluation and ground-verification of coho CWHIP 
maps. 
2. Mapping the best sites for reach-based conservation activities. 
3. Time-sequenced priorities for addressing population and reach scale limiting factors. 



 

Participation in Regional Conservation Strategies 

Conservation efforts under the Oregon Plan, ODFW Basin Management Plans, this Plan, 
and future ESA recovery plans will be integrated with and supported by regional, state, 
and federal conservation policies and programs (e.g., NW Forest Plan, Pacific Northwest 
Aquatic Monitoring Partnership, the Oregon Conservation Strategy, etc.). 

 

 

6. Population-Based Actions and Associated Cost Estimates 

 

 

This Conservation Plan provides guidance to make priority decisions and implement an 
effective conservation strategy that supports achieving the desired status for the ESU. 
The Plan also encourages local conservation entities, with support from the Regional 
Management and Implementation Team (see Implementation and Oversight Chapter), to 
develop future refinements of conservation strategies. Much of this work is well 
underway in a wide variety of locations across the ESU. Conservation strategies 
developed at spatial scales within populations will support refined priorities and time-
sequenced action plans at appropriate ecological and spatial scales (see Future 
Refinement of ESU Conservation Strategy in the Conservation Strategy for the Coast 
Coho ESU Chapter). This effort represents a significant undertaking, yet is a logical 
next-step and maturation of work already being conducted by local conservation entities 
across the ESU and throughout Oregon. Oregon�s specific commitments regarding this 
next step are listed following. 

 

Population-Based Habitat Restoration: Interim Goals and Funding Needs 

Achievement of the desired status goal for this ESU will require significant improvement 
in the amount and quality of habitat available to support juvenile coho. Individual 
populations are naturally characterized by different capacities to provide high quality 
habitat and in the amount of high quality habitat currently available. Therefore, goals for 
the amount of high quality habitat needed to achieve desired status goals should be 
established for each population. Interim goals for creating high quality habitat, by 
population, may be used as a basis to estimate costs associated with habitat improvement 
work; these cost estimates may be considered by policy makers to guide conservation 
investments across the ESU. 

 

Methodologies for estimating needed miles of high quality habitat to achieve desired 
status goals in each population are described under Criteria 6 � Habitat Conditions in 
Appendix 2: Desired Status Measurable Criteria. 

 

Three time-frame and cost scenarios for conducting habitat improvement work to achieve 
the desired status goal are presented in Table 5. As currently implemented, habitat 
monitoring will be capable of detecting only a change of >30% in the availability of high 
quality habitat. This means that changes in the amount of high quality habitat (thus 
progress towards achieving desired status) will only be detectable when there has been a 
30% or greater change (increase or decrease). The three alternate scenarios presented in 


Table 5 assume that there would be a 30% increase in the availability of high quality 
habitat in 5 years (scenario 1), 10 years (scenario 2), and 15 years (scenario 3). These 
three scenarios are based on the monitoring program design (five-year rotating panel) that 
requires a five-year period to evaluate habitat status in each population or the ESU. 
Under the assumptions in each of these scenarios, desired status would be achieved in 17 
years under scenario 1, 33 years under scenario 2 and 50 years under scenario 3. 

 

Key assumptions used to estimate the miles of high quality habitat and funds needed to 
achieve the desired habitat conditions include: 

� Smolts during poor ocean conditions are only produced from high quality habitat. 
� High quality habitat is defined as habitat that can produce 2,800 smolts-per-mile. 
� Only instream habitat restoration work is needed to achieve high quality habitat. 
In other words, no benefits will accrue to the populations from recent and future 
modifications to harvest and hatchery management programs. 
� Instream habitat complexity is the only factor limiting smolt production. 
� All instream habitat restoration projects create high quality habitat. 
� Habitat converted to high quality habitat is sustained for 50 years. 
� From 1997 � 2003, approximately $13.2 million dollars was invested on instream 
habitat restoration in 524 miles of stream: a cost/mile of approximately $25,000. 
This cost is applicable to future habitat improvement work. 


 

The assumptions required to calculate the values in Table 5 are tenuous and merit 
revision based on future research and monitoring. Consequently, the habitat goals 
and associated funding presented here are provided as interim goals that will be 
revised as better information is available in the future. 

 


Table 5. Three time-frame and cost scenarios under which habitat improvement work 
may be conducted across the ESU, by population, to achieve the desired status goal for 
the ESU. Under the assumptions in each of these scenarios, desired status would be 
achieved in 17 years under scenario 1, 33 years under scenario 2 and 50 years under 
scenario 3. 

Miles/
yearCost per 
BieniumMiles/
yearCost per 
BienniumMiles/
yearCost per 
BieniumNecanicum412.4$120,1791.2$61,9100.8$40,861$1,021,518Nehalem31118.3$915,8809.4$471,8176.2$311,399$7,784,982Tilllamook1267.4$371,2763.8$191,2632.5$126,234$3,155,844Nestucca452.6$131,5101.4$67,7480.9$44,714$1,117,838Salmon160.9$46,8210.5$24,1200.3$15,919$397,982Siletz794.6$231,7142.4$119,3681.6$78,783$1,969,570Yaquina1368.0$400,1224.1$206,1232.7$136,042$3,401,038Beaver110.7$33,6470.3$17,3330.2$11,440$286,001Alsea1297.6$378,8813.9$195,1812.6$128,820$3,220,493Siuslaw38122.4$1,120,60211.5$577,2807.6$381,005$9,525,115Lower Umpqua19511.5$574,4845.9$295,9463.9$195,325$4,883,117Middle Umpqua30117.7$886,1169.1$456,4846.0$301,280$7,531,990North Umpqua513.0$150,6351.6$77,6001.0$51,216$1,280,399South Umpqua34920.5$1,025,55110.6$528,3147.0$348,687$8,717,182Coos583.4$169,3181.7$87,2241.2$57,568$1,439,203Coquille21312.5$626,3016.5$322,6404.3$212,942$5,323,561Floras422.5$123,4811.3$63,6120.8$41,984$1,049,593Sixes161.0$48,3870.5$24,9260.3$16,451$411,287Total2,501147.1$7,354,90775.8$3,788,89250.0$2,500,668$62,516,711PopulationNew Miles 
HQH 
NeededScenario 1Scenario 2Scenario 3Total Cost 


 

 

7. Agency Actions to Support the Conservation Plan 

 

 

Abstracts of Oregon and Federal Agency Contributions to the Conservation Plan 

This section provides a summary of key commitments by state and federal agencies to 
support the Oregon plan and this Conservation Plan. Each agency has identified 
commitments that will support achievement of the desired status goal for the Coast coho 
ESU. A detailed description of these commitments is provided in Appendix 3; a 
description of current agency programs is reported in the 2005 OCCA. 

 

The following state and federal agencies have made commitments that support this 
Conservation Plan and achievement of the desired status for the Coast coho ESU. 

� Oregon Department of Fish and Wildlife 
� Oregon Watershed Enhancement Board 
� Oregon Department of Forestry 
� Oregon Department of Agriculture 
� Oregon Water Resources Department 
� Oregon Department of Environmental Quality 
� Oregon Department of State Lands 



� Oregon Department of Land Conservation and Development 
� Oregon Department of Geology and Mineral Industries 
� Oregon Department of Transportation 
� Oregon Parks and Recreation Department 
� U. S. Environmental Protection Agency 
� U. S. Forest Service and Bureau of Land Management 


 

Several state agencies have identified proposals in their abstracts below that would add 
staff positions to existing programs, or create new programs, that could support 
implementation of the Conservation Plan. All of these proposals were developed prior to 
the development of the Conservation Plan and were intended to help agencies fulfill their 
statutory missions statewide. During Conservation Plan development, the agencies 
recognized that these proposed staff positions would have benefits in the Oregon Coast 
ESU, as well as other areas of the state. 

 

To help implement the Oregon Plan Habitat Strategy in the Oregon Coast ESU, the 
Oregon Department of Agriculture has dedicated an existing position and the Oregon 
Watershed Enhancement Board has created a limited duration position. These temporary 
dedications of positions are the only commitment by state agencies to adjust staffing 
solely to implement the Conservation Plan. 

 

Abstract: Oregon Plan Habitat Strategy 

The Oregon Plan engages the voluntary participation of citizens, organizations with an 
interest in salmon restoration, landowners, and industry in a cooperative effort to assure 
sustainable salmon populations and local economies. The Oregon Plan habitat strategy 
for this Conservation Plan is to continue to implement the Oregon Plan and this section 
provides detail regarding one aspect of Oregon�s overall conservation strategy (see 
Chapter 4). The strategy is to provide more effective financial and technical support to 
private landowners to maintain and increase participation in cooperative conservation 
actions. Under the Oregon Plan and this Conservation Plan, Oregon will improve the 
level and effectiveness of support to cooperative conservation through a multi-agency 
effort to address key habitat factors that limit Coastal coho populations, including the 
following actions. 

� Support for voluntary actions includes, education and outreach, coordinated delivery 
of state agency services, funding, monitoring of coho populations and habitats, and 
adaptive evaluation of restoration efforts. 
� Provide a better understanding regarding the ecological needs of coho salmon and 
where those needs may best be provided. This will involve focusing restoration 
across coastal watersheds in areas that have the highest potential for developing high 
quality winter coho habitat. 
� Maintaining support for the local conservation groups and private landowners (e.g., 
Soil and Water Conservation Districts, watershed councils, industrial forestland 
owners, STEP volunteers, and other individuals and groups) that have demonstrated 
an impressive record of planning, prioritizing, and implementing habitat improvement 
projects. 



� Continuing support from the Oregon Forest Industries Council (OFIC) and the 
Oregon Forest Resources Institute (OFRI) to conduct habitat improvement activities 
on industrial forestland and educational work as part of their commitment to the 
Oregon Plan. 
� Providing funding for enhanced levels of technical and administrative support for 
community-based conservation efforts. 
� Support for voluntary habitat restoration work on private lands is based on confidence 
in Oregon�s scientific assessment of the ESU. There is a common desire to 
implement effective measures that support fish conservation and maintain oversight 
within Oregon rather than under the federal Endangered Species Act. 
� Participation in non-regulatory habitat improvement work on private lands in the 
Coast coho ESU will be strengthened with ongoing support by Oregonian�s for Food 
and Shelter (OFS) and the Oregon Farm Bureau (OFB). These organizations will 
lead efforts to establish partnerships with farmers and other rural landowners to 
conduct voluntary habitat improvement projects. 
� Oregon Department of Agriculture and Oregon Watershed Enhancement Board each 
have dedicated a position to help implement this strategy. 
� The Oregon Plan Core Team will coordinate this strategy among participating 
entities. 


 

Abstract: State of Oregon � Data sharing and collaborative interagency analyses. 

The State of Oregon commits to improve collaborative data analyses (between ODFW, 
ODF, OWEB, ODA, ODEQ, OWRD and/or ODSL) through the following actions: 

� Lead Entity: OWEB: Oregon Plan Monitoring Team (OPMT). 
� Ensure that all data collection on fish (abundance, distribution, densities) and habitat 
(stream, riparian, water quality and quantity) utilizes consistent and compatible 
protocols. 
� Improve the state agency capability to store, retrieve, and share data collected by all 
parties � especially including private landowners, watershed councils, watershed 
associations, STEP, and SWCDs. 
� Convene annual meetings with representatives of these agencies to establish 
guidelines, protocols, and implementation procedures for gathering and sharing data, 
as well as providing a forum to discuss information needs 


 

Interagency Mapping and Assessment Project (IMAP) is another interagency cooperative 
which will be used to build mid-to broad-scale planning and assessment models with 
'wall-to-wall' existing vegetation data and associated data. 

� Lead Entity: ODF: Project collaborators include the Oregon Department of Forestry, 
Bureau of Land Management, and Pacific Northwest Research Station, and include a 
Policy Oversight Group and a Technical Team. 
� The IMAP project will produce consistent, landscape-wide vegetation mapping across 
Oregon and Washington. This project improves upon previous efforts such as the 
Coastal Landscape Analysis and Modeling Study (CLAMS) discussed and used to 
help with land use analyses in the earlier Coho Assessments. The land use data, for 
the first time, will be collected in polygons as well as point samples. Overall, the 
results are the same, but using real polygons rather than computer generated Thiesen 



polygons (A polygon bounding the region closer to a point than to any adjacent point) 
has real advantages in being able to look at land use at a much finer scale. 
� The project will also produce a series of land use and other needed maps, and land 
use, vegetation, wildlife, and socioeconomic models that can be used to assess current 
conditions and trends and implications of alternative policies and management 
actions. 
� A Central Oregon Landscape Analysis (COLA) will be used as the research and 
development laboratory area for IMAP. COLA will be used to develop and test new 
science that fits directly into IMAP. 


 

Abstract: Oregon Department of Fish and Wildlife 

Hatchery Management 

ODFW commits to implementing the following actions related to hatchery management: 

� Discontinue hatchery coho smolt releases in the Salmon and North Umpqua rivers 
while minimizing the impacts to the ocean selective sport coho fishery. (These 
changes are described in Appendix 3 and represent a reduction of less than one half of 
one percent of the total hatchery coho that contribute to the ocean fishery.) 
� Adhere to the clear guidance provided in this Conservation Plan regarding conduct of 
future hatchery programs. 
� Maintain releases of hatchery coho in the Coast coho ESU in numbers and locations 
as outlined in this plan � these production levels represent an incremental reduction 
from about 520 thousand to 260 thousand coho smolts (200,000 of this reduction will 
be released into the lower Columbia River). 
� Apply research results from the Oregon Hatchery Research Center to future 
management of hatchery programs. 


 

Hatchery Management � limiting factors and achievement of desired status 

� Discontinuation of hatchery coho releases in the North Umpqua and Salmon address 
the primary limiting factor for the two populations and are essential first-steps to 
achieving viability for the populations. 
� Shifting most (200,000) of the discontinued hatchery coho releases (262,500 total) 
proposed in this plan to Youngs Bay will have little or no impact on the ocean 
selective sport coho fishery, which maintains one of the expected outcomes of desired 
status (ocean fishery opportunities) and increases another expected outcome of 
desired status (commercial fishery opportunities). 
� Guidance for future hatchery coho programs within this ESU will ensure hatchery 
coho programs will not become a limiting factor in other populations. 
� Maintaining the proposed levels of coho salmon releases (these are historically low 
numbers for coastal rivers since the 1980s) is expected to yield productivity 
improvements in several populations (e.g., Nehalem, Tillamook, Siletz, Alsea) that 
recently failed Oregon�s viability criteria. The viability of these populations will be 
re-assessed in the next 6 to 12 years. 
� Future application of research conducted at the Oregon Hatchery Research Center in 
addition to relevant research throughout the Pacific Northwest will be incorporated in 
future revisions of this Conservation Plan, future hatchery release levels, and 
attainment of the desired status goal for this ESU 



 

Harvest Management 

ODFW commits to implementing the following actions related to harvest management: 

� Continue to implement the revised harvest management matrix in PFMC Amendment 
13: this management structure regulates impact rates of fisheries on Oregon Coast 
naturally produced coho. 
� Implement, as feasible, future terminal-area fisheries on healthy populations of 
naturally produced coho, consistent with Amendment 13 and building to desired 
status for the populations and ESU. 
� Reallocate the 200,000 coho smolts produced at Salmon River Hatchery to be 
released in Youngs Bay (Columbia River stock reared at Salmon River) to maintain 
the level of hatchery coho available in the ocean selective sport coho fishery and to 
provide more hatchery fish for commercial coho fisheries. 


 

Harvest Management � limiting factors and achievement of desired status 

� Fishery harvest is not currently a key limiting factor for any populations in the ESU. 
However, continued application of conservative harvest rates under Amendment 13 is 
essential to ensure that rebuilding of the ESU is not significantly constrained in the 
future. 
� Amendment 13 allows coho to escape fisheries and return to spawning streams at a 
wide range of ocean survival rates: these escapements will support building towards 
desired status and will provide greater contribution of ocean derived nutrients (from 
salmon carcasses) than has been experienced during at least the past 5 decades. 
� Minimizing the reduction in hatchery coho smolt releases allows for the maintenance 
of the ocean selective sport coho fishery and increases the hatchery fish available to 
commercial coho fisheries. Both types of fisheries are expected outcomes of 
achieving the desired status goal in this plan. (Proposed reductions in hatchery coho 
releases in this plan (62,500 smolts) represent less than one half of one percent of the 
hatchery smolts (14 million) that migrate off of the Oregon Coast and provide for the 
ocean selective sport coho fishery, while the addition of 200,000 hatchery smolts into 
Youngs Bay represents a 16 percent increase in the number of coho released there for 
commercial and sport coho fisheries.) 


 

Western Oregon Stream Restoration Program (WOSRP) 

ODFW commits to implementing the following actions related to the WOSRP: 

� Continue to provide technical support to watershed councils, Soil and Water 
Conservation Districts, STEP, and private landowners. 
� Place a high priority on developing and implementing restoration projects that 
address one or more of the key limiting factors to Oregon Coast coho. 
� Partner with related efforts under the Oregon Plan habitat strategy and ODF technical 
assistance programs. 


 

WOSRP � limiting factors and achievement of desired status 

� Habitat restoration projects implemented by the WOSRP are designed to increase 
availability of complex instream and off-channel habitat that are essential to 



overwintering coho juveniles; this was the key or secondary limiting factor in all 21 
independent populations within the ESU. 


 

Habitat Protection 

ODFW commits to implementing the following actions related to habitat protection: 

� Continue to work collaboratively with state and federal permitting agencies to 
provide comments and alternatives to permitted habitat altering activities (fill and 
removals, water rights, forest operations) that minimize or eliminate the loss of 
fish habitat. 
� Continue to train Fish and Wildlife Biologists on methods to minimize and avoid 
losses of habitat and current permitting processes. 


 

Habitat Protection � limiting factors and achievement of desired status 

Habitat protection addresses key limiting factors by preventing the deterioration of 
existing good quality habitat, which will be essential to achieving the desired status. 
Additionally habitat protection can create additional good quality habitat by protecting 
habitat that has high potential and enabling it, through succession, to develop into good 
quality habitat. 

 

Beaver (Castor canadensis) 

ODFW commits to implementing the following actions related to beaver: 

� Expand Oregon Plan non-regulatory commitments that generally involve outreach 
and education, informal conversations with trappers, landowners, and land 
managers and informal exploration of alternative damage control methods for 
private landowners; the intended outcome of these activities is to achieve an 
increase in beaver dams to create high quality coho rearing habitat. 
� Develop tools (e.g.: maps, incentives) to identify key areas for beaver dams and to 
help landowners address beaver damage. 


 

How do these actions address limiting factors and support achievement of desired status 
for the Oregon coast coho ESU? 

� Increasing the number of beaver dams in areas where dams are limited that create 
high quality rearing habitat will create stream complexity and increase the coho 
smolt capacity of populations and the ESU, which will help the populations and 
ESU build towards desired status. 


 

Research, Monitoring and Evaluation (RME) 

ODFW commits to the following actions related to RME: 

� Beginning in 2006, ODFW and ODEQ will begin implementing a modified 
monitoring program designed to provide population scale, statistically rigorous data 
on the status and trend of: 1) abundance and distribution of naturally produced and 
hatchery coho; 2) physical habitat; 3) riparian conditions; and 4) water quality. 
� Collaborate with appropriate entities regarding the development of research and 
monitoring proposals described in the RME Section of this plan 


 


RME � limiting factors and achievement of desired status 

� RME provides the basis for adaptive management based on future assessments of the 
ESU; its supporting habitat; and the management and regulatory programs that are 
intended to achieve desired status. 
� Future assessments of the ESU and habitat will determine if progress is being made 
toward achieving the desired status goal. 


 

Conservation Plan Outreach 

ODFW commits to implementing the following actions related to outreach for this 
Conservation Plan: 

� Two FTEs are currently funded and assigned principally to Oregon Plan outreach. 
� Place a high priority on outreach regarding this Conservation Plan and the non-
regulatory actions that Oregonians take to implement the Plan. 


 

Conservation Plan Outreach � limiting factors and achievement of desired status 

� Maintaining and increasing public support for this Conservation Plan are an essential 
element to improve availability of complex instream and off-channel habitats on 
private lands. 


 

Abstract: Oregon Watershed Enhancement Board 

OWEB Responses to Coastal Coho Recovery Needs 

1. Dedication of approximately $2,000,000 to put displaced fishers to work to address 
high priority limiting factors in coastal watersheds. These are new funds for the 
2005-2007 biennium, are targeted to coastal basins and high intrinsic potential habitat 
or other limiting factors. Funds are identified to hire fishers to conduct restoration 
work, develop projects and conduct field data gathering to provide for better focusing 
of future restoration. The funding was approved by the Legislative Emergency Board 
on June 23, 2006. 
2. Dedication to work with ODFW, Dept. of Agriculture and others to develop a coastal 
lowlands strategy that directly addresses high intrinsic potential habitats on non-
forested lands. The effort could include an addition to the incentives provided for the 
Conservation Reserve Enhancement Program (CREP) or other strategies to be 
developed and implemented late in this biennium and next biennium. 
3. Funding of displaced fishers to provide outreach for the Conservation Plan and the 
Oregon Plan habitat strategy. 
4. Commitment to work with local conservation entities to develop restoration priorities 
that address watershed limiting factors to be used in the grant process. 
5. There is an increasing amount of Measure 66 Lottery funds available for restoration 
by the increase use and expansion of the state lottery games. The projected lottery 
revenues will likely increase next biennium providing an increased amount of funds 
available to the coastal coho ESU. 
6. OWEB and ODA are collaborating to request policy option packages requesting an 
increase in funding for watershed councils and soil and water conservation districts 
for the 2007-2009 biennium. The request will be for a significant increase in funding 



for capacity statewide. This will provide additional resources to both councils and 
districts in the coastal coho ESU. These groups are critical for developing 
relationships in local communities that will allow projects to be implemented on 
private lands. 


 

Abstract: Oregon Department of Forestry 

ODF will continue implementing existing strategies to protect, maintain, and improve 
riparian area function. The following agency actions and needs apply statewide and 
benefit coho conservation as well as other species. All actions and needs identified here 
are new or significant modifications as of May, 2005. 

Agency Actions 

Private Forest Regulatory Actions: At the direction of the Board of Forestry, ODF is 
developing implementation guidance for two new rules which 1) provide for protection as 
if a stream already had fish but is currently above an artificial barrier and 2) provide for 
leaving trees along debris torrent prone streams. A new rule to make FPA authority over 
certain types of large wood placement was also adopted to streamline the efforts of forest 
landowners to place large wood. Implementation guidance and a variety of educational 
materials are planned to let landowners know of this new opportunity to place large wood 
during forest operations governed by the FPA without additional permits. Rule concepts 
to address riparian function for fish bearing and non-fishbearing streams (Rule Concepts 
8 and 11) are planned to be addressed. 

 

Private Forest Voluntary Measures: Non-regulatory actions are being developed to 
complement and add to the foundation provided by the Forest Practices Act to improve 
incentives for the active placement of large wood and include an array of strategies to 
manage riparian stands to accelerate the growth of large wood. 

 

State Forest Actions: Apply FMP-based management standards to all management 
activities for aquatic and riparian areas, landslide hazards, transportation planning, and 
road construction. Continue with watersheds level riparian and aquatic strategies that 
contribute to Oregon Plan objectives including watershed analysis. 

Legislative Concepts and Policy Option Packages 

The Oregon Department of Forestry (ODF) proposed Legislative Concepts and Policy 
Option Packages directly relate to the Governor�s 2007-09 Biennial Budget principles- 
�We Value a Balance between Growth, Infrastructure Development and Environmental 
Protection.� The proposals support the Oregon Board of Forestry�s 2003 Forestry 
Program for Oregon strategies and actions that include protection, maintenance and 
enhancement of soil and water resources of Oregon�s forests and health of Oregon�s 
forest ecosystems. 

 

The (ODF) packages address two essential program service level needs; 1) restoration of 
permanent positions to meet workload demands and statutory obligations. Past budget 
reductions have reduced the current workforce necessary to maintain essential service 
levels and 2) creation of new positions to address the existing staffing constraints to meet 


the needs of serving the residents of Oregon as identified in the Forestry Program For 
Oregon 2003 document. These proposals were developed to fulfill agency missions, no 
specific positions were dedicated to the Conservation Plan, but the agency recognizes that 
these proposed positions would have benefits to the Conservation Plan. Specific POPs 
include: 

 

POP 152 Add capacity to the Private Forests Program to increase monitoring and field 
staff to achieve the Board of Forestry�s strategies and actions as articulated in the 
Forestry Program for Oregon including strategies to support the Oregon Plan. Funding 
proposal: $1,607,497 60% General Fund/40 Harvest Tax. 12 FTE positions 

 

Legislative Concept 629-14, POP 154A � Reinvigorate the Forest Resource Trust to 
provide voluntary cost share programs which will improve forest environment including 
projects that benefit coho habitat. Funding proposal: $1,500,000 lottery funds. 4.58 FTE 
positions 

 

POP 154B - Create a non-regulatory incentive program that would support additional 
investments in resource protection, carbon sequestration and timber management. 
Funding proposal: $2,845,912 lottery funds. 8 FTE positions 

 

POP 156 Fund field-based research, education, and outreach activities on the cumulative 
impacts from contemporary forest practices on water quality, fish and other aquatic biota 
including funds for the Hinkle Creek Research and Demonstration Area Project and the 
South Fork Trask River paired watershed study. Funding proposal: $1,500,000 General 
Fund 0 FTE positions 

 

Legislative Concept 140. Create the Department of Forestry�s, Community and 
Cooperative Forestry Program to help local governments, community organizations, and 
small forest landowners improve the stewardship of forest resources within urban growth 
boundaries and rural residential zones. Funding proposal: $400,000 Federal funds, 
$1,400,000 Other Funds. 7 FTE positions. 

 

Monitoring, Research & Evaluation 

Research and monitor high aquatic potential (HAP) streams to help prioritize stream 
protection and enhancement opportunities. 

 

Effectiveness of Riparian Strategies (Riparian Function and Stream Temperature) project 
addresses the adequacy of riparian rules and strategies to maintain water quality and large 
wood recruitment to streams; measures trends in riparian condition; and evaluates the 
relationship between riparian and instream characteristics. 

 

State Forest Program implementation monitoring of riparian strategies to determine 
whether timber operations are conducted consistently with the riparian management 
standards in the Forest Management Plan. 

 


The Watersheds Research Cooperative (WRC) was chartered in 2002 as a research and 
demonstration program to fill gaps in scientific knowledge identified through the Oregon 
Plan for Salmon and Watersheds. It is a cooperative and collaborative public-private 
program of research and outreach that has been initiated through local support. The long-
term vision is to establish three major paired watershed study installations across Oregon, 
as well as to help facilitate other smaller projects. Each major study will evaluate the 
environmental effects of contemporary forestry practices on water quality, native fish, 
amphibians, and aquatic insects. Federal funds are being sought to enhance local support 
and achieve the full scientific potential for this effort. 

 

Located near Sutherlin, Oregon, the Hinkle Creek Paired Watershed Study has been a 
visible and successful initial effort by the Cooperative. Established in 2002, the study 
area is a 5,000-acre watershed owned and managed by Roseburg Forest Products. A 
multi-disciplinary team of scientists is studying the linkages between management 
activities and effects on soil and water quality, fish, amphibians, and aquatic insects. 
Initial harvest treatments were conducted in fall 2005 and winter 2006. 

 

Data collection technology provides for continuous measurement of water quality and 
fish behavior and enables an unprecedented ability to study the immediate and continuous 
response of native fish to management activities as they affect water quality. The site is 
also serves as a demonstration area for the public to learn about the effects of modern 
intensive forest management on watershed health. Many policy makers, government 
officials, natural resource scientists, and Douglas County school children have benefited 
from tours. 

 

Two additional installations were established in FY2007. A second major study is in the 
Trask River watershed west of McMinnville on land managed by the Oregon Department 
of Forestry and Weyerhaeuser Company. The Trask River Watershed Study seeks to 
understand a variety of stream ecosystem responses to forest harvest impacts, including 
impacts on salmonid fishes (salmon and trout). This project will be on a scale and scope 
similar to Hinkle Creek. The third site is a reactivation of the historic Alsea Watershed 
study near Newport in the central Oregon Coast Range. It was originally conducted more 
than 30 years ago, before the Oregon Forest Practices Act was in place. While smaller in 
scale, re-grown forests are ready for a second harvest using modern management 
approaches and will provide an unprecedented comparison of the environmental impacts 
of current practices against those in the mid-1900s. Peer review of WRC study plans 
highlighted the need for multiple study sites across diverse environmental conditions for 
broadest application of the data. 

 

Abstract: Oregon Department of Agriculture 

In addition to ongoing efforts in the following programs: 1.) Agriculture Water Quality 
Management; 2.) Confined Animal Feeding Operations; 3.) Weeds and Invasive Species; 
and 4.) Pesticides, ODA and OWEB are collaborating to request policy option packages 
requesting an increase in funding for watershed councils and soil and water conservation 
districts for the 2007-2009 biennium. The request will be for a significant increase in 
funding for capacity statewide. This will provide additional resources to both councils 


and districts in the coastal coho ESU. These groups are critical for developing 
relationships in local communities that will allow projects to be implemented on private 
lands. ODA also commits to devote an existing position to specialize in providing 
technical assistance coordinated with ODF and ODFW to support conservation and 
restoration in non-regulatory settings on private lands that are best suited to providing 
over-winter habitat for juvenile coho salmon. This strategy will provide considerably 
improved opportunities to enlist active participation by private landowners in areas of 
greatest potential to support juvenile coho salmon, the most significant limiting factor 
identified across the ESU. 

 

Abstract: Oregon Water Resources Department 

Oregon Water Resources Department (OWRD) � New Statewide Concepts 

OWRD has a number of existing programs and agency actions that contribute to Coast 
Coho Conservation efforts. In addition to these ongoing actions, OWRD has identified 
new statewide concepts that will also support the Conservation Plan, increase our 
understanding of water quantity as a limiting factor and benefit instream flows. The 
majority of these new statewide concepts are dependent on securing additional funding 
through grants or policy option packages (POP) proposed in the 2007-2009 Agency 
Request Budget. These concepts are described below as they relate to existing agency 
actions. 

 

Water Distribution and Regulation 

� Support statewide monitoring and reporting of instream water rights and water 
use through a 2007-2009 POP to restore the Department�s Water Measurement 
and Reporting Specialist (POP 401, 1 FTE, GF- $138,114) 
� Add statewide capacity and modernize equipment for flow monitoring through a 
2007-2009 POP request (POP 304, GF - $100,000) 
� Enhance monitoring and distribution capacities via a 2007-2009 POP to fund a 
Field Water Right Technician position in each of 5 regions (POP 303, 5 FTE, GF 
- $686,965). 
� Coordinate with OWEB to secure funding for volunteer streamflow monitoring 
and flow monitoring equipment. 


 

Flow Restoration Programs 

� Explore opportunities with OWEB to offset application costs for CREP 
participants that lease or transfer water rights associated with CREP enrolled 
lands. 


 

Public Outreach and Education 

� Assess opportunities to report regulation activities and other relevant data at the 
ESU or other scale in support of adaptive management under this and other 
Conservation Plans. 
� Seek funding to add instream leasing, transfer, and allocation of conserved water 
data to the OWRD on-line data base. (National Fish and Wildlife Foundation 
Funding Awarded September 2006) 



� Encourage responsible water management and conservation by irrigation districts 
and other agricultural water suppliers by developing a guidebook on preparing 
Agricultural Water Management and Conservation Plans and through outreach 
and workshops for irrigation district managers. (Bureau of Reclamation Funding 
Awarded July 2006) 


 

Improvement of Resource Understanding 

� Seek funding via a 2007-2009 POP and other sources to better understand long 
term statewide water supply needs (instream and out-of-stream), potential above 
and below ground storage opportunities, and conservation opportunities. (�Oregon 
Water Supply and Conservation Initiative,� POP 403, 3 FTE, GF $891,025 ) 


 

Abstract: Oregon Department of Environmental Quality 

Summary 

DEQ has several ongoing efforts to improve water quality within the Oregon Coast coho 
ESU: 

1. Implementing Total Maximum Daily Loads (TMDLs): TMDLs for three basins 
within the ESU have been completed, and by the end of 2008 TMDLs for seven more 
basins are scheduled for completion. 
2. Updating NPDES discharge permits: NPDES discharge permits are scheduled to be 
updated and reissued within eleven basins in the ESU by the end of 2007. 
3. DEQ will continue to work in partnership with watershed councils, SWCDs, STEP, 
and city, state, and federal agencies throughout the ESU to provide technical 
assistance and grant money for restoration work to improve water quality. 
4. DEQ will continue to work with the Oregon Plan Monitoring Team to find ways to 
collect needed water quality data and coordinate data with other state agencies. 


 

Abstract: Oregon Department of State Lands 

Addressing Limiting Factors or Threats to Oregon Coast Coho 

DSL protects and conserves waterways and wetlands through administration of Oregon's 
Removal-Fill Law, Scenic Waterways Law, and the Wetland Conservation Program. 

 

The 50 cubic yard exemption to the Removal-Fill Law does not apply in Essential 
Indigenous Anadromous Salmonid Habitat Areas (ESH). ESH streams contain fish 
species that have been listed as sensitive, threatened or endangered by a state or federal 
agency. Oregon Coast Coho streams have been designated ESH. Unless exempt, 
projects that involve work in waters of the state in the ESU will require an authorization 
from DSL. As part of the permit review process, natural resource agencies including 
ODFW have an opportunity to review and comment on the project design and/or to 
request that certain project-specific conditions be included in the authorization. These 
project-specific conditions, as well as the standard conditions, are designed to protect and 
conserve water resources. All permits issued by DSL include water quality permit 
conditions that require that sediment and erosion control measures are implemented and 
that turbidity monitoring is conducted in order to meet turbidity standards. These water 
quality conditions effectively address the key limiting factor of water quality, which has 
been identified as a primary limiting factor for many coho populations. 


 

DSL conducts compliance monitoring and enforcement to ensure compliance with DSL 
permit conditions. In recognition of the importance of compliance monitoring, DSL has 
recently added a full-time position dedicated to compliance monitoring and salmon 
recovery planning (funded by the U.S. Environmental Protection Agency or EPA and 
OWEB). As part of a pilot program, this staff person will cross reference the Coho 
Winter High Intrinsic Potential Habitat maps with DSL�s removal-fill permit data for 
those areas. Depending on the results of the pilot program, DSL may consider program 
changes to more effectively protect those areas. 

 

All authorized permanent impacts to wetlands, and most impacts to waterways, are 
required to be offset with compensatory mitigation. In most cases, the result of 
compensatory mitigation is a net benefit to water resources. 

 

In the past few years, DSL has undertaken efforts to streamline the Removal-Fill Permit 
Process. A current management priority at DSL is to further streamline the process, 
specifically for fish habitat enhancement and wetland restoration projects. A streamlined 
permit process for restoration projects will help to address the key limiting factor of 
stream complexity, which has been identified as a primary limiting factor for many coho 
populations. 

 

 

DSL�s Wetland Conservation Program seeks to maintain a stable base of wetlands and to 
encourage wetland restoration and creation, through programs including the wetland 
land-use notification program and public outreach. DSL has added two new EPA-funded 
positions for a new Voluntary Restoration Strategy to provide technical assistance for 
wetland restoration projects. As part of this Voluntary Restoration Strategy, DSL staff 
will participate in and provide technical support for the Oregon Plan habitat strategy. 
DSL staff will also be available to provide education and public outreach on wetland 
restoration. In addition, DSL may be able to provide funding for wetland restoration 
projects in the ESU through the Wetland Mitigation Bank Revolving Fund Account 
Program. 

 

The research being conducted at the South Slough Research Reserve (SSNERR) on how 
coho utilize restored estuarine marshes and large woody debris complexes is a valuable 
asset in increasing our understanding of the ecology of the species, and how restoration 
can aid in recovery by addressing the key limiting factor of stream complexity. SSNERR 
staff is also conducting long-term water quality monitoring of the South Slough estuary. 
This water quality monitoring will be a key metric for determining whether the key 
limiting factor of water quality is being addressed effectively. 

 

Abstract: Oregon Department of Land Conservation and Development 

The Department of Land Conservation and Development will take several actions to 
address limiting factors or threats to Oregon coast coho. These include work with coastal 
local governments to review and update comprehensive land use plans and ordinances to 
incorporate policies and standards aimed at reducing impacts to salmon habitat from the 


effects of development. The Department will work with local governments and other 
entities such as Oregon Sea Grant to promote salmon-friendly development practices by 
extending current work with local governments to adopt or improve stormwater 
management standards, identify and protect wetlands and riparian areas, and promote 
education of local staff, appointed and elected officials as to voluntary techniques or 
practices. 

 

The Department, through the Coastal Management Program, will provide financial and 
technical assistance to local governments for a variety of improvements that result in 
improvements in protecting salmon habitat. These improvements include developing or 
improving GIS capacity to support local land use decisions, to conduct wetland and other 
inventories and assessments, and to carry out special planning projects that. The Coastal 
Management Program will also make available detailed aerial photo images of coastal 
estuaries via the Oregon Coastal Atlas 
http://www.coastalatlas.net/learn/settings/estuary/index.asp 

 

The Department, through the Coastal Management Program, will review and approve 
federal permits and actions that can affect coastal salmon habitat. The Department also 
provides a key coordination role to ensure that state and federal agency permits and 
approvals comply with the enforceable policies of the state�s Coastal Management Plan, 
including protection of estuarine habitats. 

 

Abstract: Oregon Department of Geology and Mineral Industries 

Important Contributions 

DOGAMI�s main contribution to the Conservation Plan is to maintain the current 
strength of the regulatory compliance to avoid off-site impacts during mine-site 
reclamation and ensure reclamation of mine sites meets the secondary beneficial use 
established for the site. 

 

Address Limiting Factors 

None of the primary or secondary limiting factors identified for the Coast coho ESU were 
related to regulation of mining or energy minerals in Oregon. Sediment is the main 
potential impact associated with the regulation of mining and energy minerals. Sediment 
was not identified as a primary limiting factor for any population. DOGAMI has and will 
continue to explore floodplain mining activity for opportunities for habitat enhancement 
benefiting the at-risk populations. 

 

Abstract: Oregon Department of Transportation 

The Oregon Department of Transportation (ODOT) is responsible for providing and 
maintaining the safe and efficient state and federal transportation system in Oregon. In 
addition, ODOT is committed to the protection and conservation of all native migratory 
fish species in the state; and the recovery of those listed as threatened or endangered 
under state and federal statutes. 

 


ODOT is a participant in Oregon Coast coho recovery domain planning efforts. The 
following items summarize actions that ODOT implements to conserve and enhance 
environmental limiting factors for coastal coho salmon as well as other species. 

 

� ODOT implementation of Routine Roadside Maintenance Manual, Water Quality and 
Habitat Guide (ESA 4(d) Limit 10(i); revised 2004 with NMFS and ODFW) 
� Statewide Fish Passage Program, $4.2 million/year to restore/improve fish passage 
� Comprehensive Mitigation/Conservation Strategy (establishes Ecoprovince-level 
ecological priorities for the ODOT Bridge Delivery Program) 
� Project specific coordination and consultation with state and federal regulatory 
agencies (implementation of section 7, Endangered Species Act and Magnuson-
Stevens Fishery Conservation and Management Act compliance) to ensure natural 
resource avoidance, minimization, and mitigation 
� Project/program specific permit monitoring and reporting to regulatory agencies 
� ODOT Regulatory Agency Liaison Program � partnering with state and federal 
agencies for ODOT Environmental, Construction, Bridge, and Highway Maintenance 
Programs to partner and work collaboratively on ODOT projects and programs. 
ODOT funds 13 FTE liaisons with regulatory agencies ODFW, NMFS, USFWS, 
DSL, USCOE, DEQ, and APHIS Wildlife Services 
� Use of state and federal regulatory programmatic permits that emphasize natural 
resource avoidance, minimization and mitigation procedures 
� ODOT-Animal & Plant Health Inspection Service (APHIS) Liaison (adaptive 
management of beaver & road conflicts) 
� Finalization of revisions to the ODOT Statewide Hydraulics Manual (that provides 
hydraulic design guidance and recommendations for hydraulic facilities (culverts and 
bridges) to promote natural stream processes (bed load and large woody material 
transport and fish passage). 


 

Abstract: Oregon Parks and Recreation Department 

The mission of the Oregon Parks and Recreation Department (OPRD) is to provide and 
protect outstanding natural, scenic, cultural, historic and recreational sites for the 
enjoyment and education of present and future generations. In addition to operating a 
statewide network of parks and natural areas, the department is also responsible for 
managing Oregon's's Recreation Trails, the Ocean Shores Recreation Area, Scenic 
Waterways and the Willamette River Greenway. 

 

OPRD is a participating agency in the Oregon Plan for Salmon and Watersheds. The 
following items highlight some of the actions we will be taking to address the limiting 
factors for Oregon coastal coho salmon as well as other native salmon species in coastal 
watersheds. 

 

OPRD Actions 

� Fund fish habitat improvement projects in state parks within the range of Oregon 
coastal coho salmon using revenue from the sale of salmon license plates. 



� As part of OPRD�s Investment Strategy, seek opportunities, utilizing Measure 66 
funding, to acquire land and conservation easements that will assist in the recovery of 
coastal coho salmon. 
� Research locations at coastal parks where interpretive signing could be used to make 
citizens more aware of the value of preserving habitat for naturally spawning wild 
salmon. 


 

Abstract: U.S. EPA Region 10 Support for Salmon Recovery in the Coastal Coho 
ESU 

Limiting Factor - Water Quality 

EPA will implement, provide oversight, or provide technical and/or financial support for 
the implementation of the following program activities which contribute to the recovery 
of Coho Salmon in the Coastal Coho ESU: 

 

� Development and revision of State water quality standards; 
� Development and implementation of Total Maximum Daily Loads (TMDLs); 
� Implementation of non-point source projects through CWA Section 319 funding; 
� Interaction with federal and state land management agencies to improve forest 
practices on state and federal lands; 
� Water quality and aquatic habitat monitoring; 
� Implementation of the NPDES point source pollution control program; 
� Coastal Zone Management Program implementation; 
� NEPA review of environmental impacts from federal actions; 
� Wetlands Program and project implementation; 
� Technical and financial assistance through grants and loan programs; 
� Implementation of Pesticides Program Cooperative Agreement with Oregon 
Department of Agriculture; and 
� Emergency Response Program support and implementation for oil and hazardous 
materials spills. 


 

Abstract: USDI Bureau of Land Management and USDA Forest Service 

The USDI Bureau of Land Management (BLM) and USDA Forest Service (FS) manage 
about 20 percent of the stream miles currently occupied by OC coho salmon. The 
majority of the BLM and FS land is in headwater areas, and includes land within Key 
Watersheds. Key Watersheds are a network of refugia receiving special management 
emphasis to maintain and restore good habitat conditions for salmon stocks at risk. 
Consequently, BLM and FS lands play a large role in helping to maintain downstream 
water quality and habitat conditions for coho-bearing streams in non-federal ownership. 

 

The BLM and FS have worked closely with the State and many partners since the 
inception of the Oregon Plan. Land use plans, laws, regulations and policies guide BLM 
and FS activities. While the land use plans may vary by administrative unit, those within 
the OC Coho ESU currently incorporate common features of a planning framework 
known as the Northwest Forest Plan (NWFP). The NWFP has been implemented since 
1994 and includes an Aquatic Conservation Strategy (ACS) specifically designed to 
protect salmon, steelhead and other aquatic habitat on federal lands managed by the BLM 


and FS. The BLM is currently revising its land use plans in Western Oregon and a 
decision is expected in 2008. While the ACS may change, the new BLM plans will retain 
an emphasis on water quality and fish habitat. 

 

Land administered by the BLM and FS is being managed to achieve nine ACS objectives 
designed to maintain and restore watershed, water quality, riparian, and habitat processes 
important to the conservation of OC coho salmon. There are four components of the 
ACS: (1) Riparian Reserves; (2) Key Watersheds; (3) Watershed Restoration; and (4) 
Watershed Analyses. The ACS also includes extensive standards and guidelines for 
project design and implementation within Riparian Reserves and Key Watersheds. All 
four of the ACS components are designed to operate together to maintain and restore the 
productivity and resiliency of watersheds and their riparian and aquatic ecosystems. 
Descriptions of the four components and recent accomplishments are found in Appendix 
3. 

 

In addition to implementing land use plans, the BLM and FS will continue to implement 
and coordinate the following activities with the State and our many partners in support of 
salmon recovery in the OC Coho Salmon ESU: 

 

Watershed/Habitat Restoration. Continue comprehensive, whole watershed, conservation 
and restoration programs. These programs are community based and rely upon close 
working relationships with partners. When appropriate, the BLM and FS will utilize an 
authority to expend federal funds on private lands when the funded activity will benefit 
resources on the federal lands (Wyden amendment). An example is a culvert replacement 
that would allow fish passage upstream onto federal land. 

 

Research. Work to improve coordination, integration, and information sharing on key 
research topics. This includes cooperative long-term studies for coastal watersheds, the 
development of localized habitat capability models, and validation of priority restoration 
treatments. 

 

Monitoring and Evaluation. Continue to monitor the accomplishment of objectives under 
their management plans relating to aquatic and riparian health. Explore expanded 
coordination with the state and watershed councils on plan implementation and 
effectiveness monitoring. 

 

Inventories. Collect riparian, aquatic habitat and resource data compatible with state 
efforts. This combined data has been used to describe aquatic and hydrological 
conditions across whole watersheds, regardless of land ownership. Continue to work 
with the State to ascertain the health of aquatic systems within priority watersheds and 
critical lands. Information will be shared and used as a basis for watershed analysis and 
other assessments. 

 

Planning and Assessment. Continue to plan for the restoration and maintenance of 
riparian and aquatic health as part of all federal planning. In addition, seek to expand 
opportunities for State and watershed council involvement in watershed analyses and 


continue to share the results of these analyses with all interested and involved parties. 
The agencies will also work with State and other federal agencies, Tribal governments, 
and watershed councils to establish the priorities for management and restoration 
treatments. 

 

Technical Training. Continue to coordinate technical training of resource management 
personnel to ensure a high level of competency is available to define restoration and 
recovery treatments. This training includes modules in: stream inventory techniques; 
data interpretation; channel classification and fluvial dynamics; watershed restoration; 
monitoring and evaluation; and Proper Functioning Condition assessment for riparian 
areas. 

 

Cooperative Funding. Continue to seek opportunities to cost-share resource assessments, 
restoration prescriptions and prioritization, treatments across whole watersheds, and 
monitoring, regardless of ownership. 

 

Education/Interpretation/Outreach. Continue to work with the State and watershed 
councils to expand ongoing cooperative outreach and environmental education programs. 

 

Coordination. Continue to work with other federal, State, and county agencies and Tribal 
governments to ensure coordination and sharing of information between the involved 
entities. 

Continue to work with watershed councils to ensure a high degree of coordination for 
actions occurring on both public and private lands. The agencies will also continue to 
share technical expertise to help the councils effectively plan and implement priority 
watershed restoration projects. 

 

Key Aquatic Habitat Acquisition. Continue to work within existing policies with willing 
sellers to acquire parcels with key aquatic and riparian habitat. 

 

Hydropower Licensing and Relicensing Coordination. The BLM and FS have authority 
under Section 4(e) of the Federal Power Act to prescribe mandatory terms and conditions 
for Federal Energy Regulatory Commission-licensed projects. The terms and conditions 
can range from establishing minimum flows to other protective measures such as channel 
maintenance flows, habitat maintenance, and restoration. 

 

Clean Water Act Section 303 Compliance. The BLM and FS develop Water Quality 
Restoration Plans (WQRPs) for streams placed on a 303(d) list for failure to meet state 
water quality standards. The federal WQRPs are incorporated into Water Quality 
Management Plans, which are written by the Oregon Department of Environmental 
Quality to implement Total Maximum Daily Loads. 

 

 


8. Research, Monitoring, and Evaluation 

 

Research, monitoring, and evaluation (RM&E) are essential to the adaptive management 
of this Conservation Plan. RM&E for this Conservation Plan should: 1) monitor the 
status and trend of coho populations and their habitat; 2) validate key assumptions and 
clarify critical uncertainties associated with the identification of primary limiting factors; 
and 3) evaluate the effectiveness of key habitat protection, management, and restoration 
actions. 

 

Long-Term Monitoring Programs 

Currently, Oregon funds five long-term programs that monitor the status and trend of 
coastal coho populations and their habitat. These programs are: 

 

1. Spawner surveys (ODFW): Spatially balanced, random surveys that provide annual 
estimates of the spatial distribution and abundance of natural and hatchery origin 
coho spawning in each independent population and in dependent populations 
combined by strata. These surveys provide data that are the basis for evaluating 
desired status criteria for independent populations and criterion 1 for dependent 
populations. More information on the specific details of these surveys may be 
obtained at: https://nrimp.dfw.state.or.us/crl/default.aspx?p=382 
2. Habitat Surveys (ODFW): Spatially balanced, random surveys that provide estimates 
of a broad array of instream physical habitat and riparian conditions. The surveys are 
designed to annually assess the condition of coho habitat in wadeable streams at the 
ESU and strata scale as well as every five years for each independent population and 
for dependent populations combined by strata. These surveys provide data that is the 
basis for evaluating desired status for independent and dependent coho populations. 
More information on the specific details of these surveys may be obtained at: 
https://nrimp.dfw.state.or.us/crl/default.aspx?pn=AIProjOrPlnSalWtrshd 
3. Juvenile Surveys (ODFW): Spatially balanced, random surveys that provide annual 
estimates of the summer distribution, density, and habitat occupancy rate of juvenile 
coho within four of the five strata in the ESU. These surveys supply data that may be 
used to expand desired status criteria in the future. More information on the specific 
details of these surveys may be obtained at: 
http://oregonstate.edu/dept/pacrim/index.htm 
4. Life Cycle Monitoring (ODFW): Annual estimates of freshwater and marine survival 
of coho from seven coastal streams. This information is used to determine the marine 
survival category to which observed spawner abundances should be assigned. It is a 
critical component of evaluating independent population criterion 1. More 
information on specific details of this monitoring may be obtained at: 
https://nrimp.dfw.state.or.us/crl/default.aspx?p=369 
5. Water Quality Monitoring (ODFW & ODEQ): Spatially balanced, random surveys 
designed to provide information on the spatial pattern of water temperature, fine 
sediment, and other water quality conditions in wadeable streams. Surveys are 
conducted every year at the same sites sampled for juvenile coho (#3 above). Every 
five years, these data will be analyzed to provide information on the status and trend 
of water quality in wadeable streams in each independent coho population. The 



project is based on sampling macroinvertebrates and calibrating the observed 
assemblages to relationships developed with temperature, fine sediment, and other 
water quality parameters. These surveys provide data that are a component of 
desired status criteria. In addition to this program, ODEQ has established a series of 
long-term water quality monitoring stations as part of its TMDL program. Recently, 
this program was upgraded to insure that at least one water quality monitoring station 
is located in each independent population. More information about the TMDL 
program may be found at: http://www.deq.state.or.us/wq/tmdls/tmdls.htm 


 

Restoration Action Effectiveness 

Monitoring the implementation of habitat restoration projects and evaluating their 
subsequent effectiveness are other key elements of an RME program that will ensure the 
success of this Conservation Plan. OWEB conducts implementation monitoring of all 
restoration projects it funds. Implementation monitoring ensures that each project is 
completed in accordance with the grant agreement developed for the project. 
Effectiveness monitoring is conducted for a subset of OWEB restoration projects. 
OWEB also requires annual effectiveness reports from the Western Oregon Stream 
Restoration Program, which is funded with state lottery funds. Effectiveness monitoring 
ensures that a project�s restoration objectives are met. OWEB tracks its projects via the 
Oregon Watershed Restoration Inventory database. OWEB also awards grants solely for 
the purpose of conducting monitoring work, at project and watershed scales. The Oregon 
Plan monitoring team coordinates among state natural resources agencies and other 
entities to identify monitoring needs and funding for monitoring, and to refine the Oregon 
Plan�s monitoring strategy. OWEB recently began developing rigorous monitoring 
protocols for livestock exclusion, riparian planting, and tide gate projects that will help 
ensure that these types of projects are effective. OWEB has also begun working with 
Oregon state natural resources agencies (e.g., ODF) to identify large-scale, high level 
indicators of ecosystem function and determine how to track changes through time. 

 

Collectively, the programs identified in this chapter provide comprehensive information 
on the status and trend of coastal coho populations, their habitat (primarily in wadeable 
streams), and the effectiveness of actions taken. Under the current paradigm that habitat 
conditions in these wadeable streams are the primary limitation to achieving recovery 
goals for most coastal coho populations, these programs provide information that is 
sufficient to address the measurable criteria for desired status and help ensure that 
effective actions are being taken. However, there are a number of research and 
evaluation needs currently unfunded or under-funded. These are needed in order to chart 
course corrections that should be undertaken if the core monitoring programs 
demonstrate inadequate progress towards reaching desired status goals. 

 

Research and Evaluation needs 

Eight topics for research and evaluation have been identified as having significant 
potential to contribute to efforts to achieve desired status for the Coast coho ESU (see 
Appendix 4). All of these research and evaluation needs merit funding. However, the 
reality is that these needs must be considered in context with the need to improve RM&E 


for ESA listed species statewide. The eight high priority topics for research and 
evaluation related to coastal coho are listed following. 

 

� Research on the mechanisms that cause poor ocean survival of coho and methods to 
predict ocean survival conditions. 
� Research on the relative importance of potential limiting factors throughout the entire 
freshwater and estuarine residence of coho. 
� Evaluate the contribution that habitat protection, management, and restoration 
programs have toward achieving desired status goals. 
� Validate and refine of Coho Winter High Intrinsic Potential Model. 
� Evaluate methods to maintain, enhance, or promote beaver dams in areas where they 
can create or maintain high quality coho rearing habitat. 
� Evaluate cause and impact of marine mammal, avian and exotic fish predation on 
Coastal salmonids and coho in particular. 
� Evaluate re-establishment of a self-sustaining population of coho in Salmon River. 
� Develop tools to identify and prioritize restoration projects at local watershed and 
stream-reach scales. 


 

Additional research and evaluation needs may be identified through the adaptive 
management process of this plan. 

 

 

9. Application of Adaptive Management 

 

Oregon�s track-record demonstrates that the Oregon Plan has an effective adaptive 
management component. New data and information have been considered and 
management and regulatory programs have been changed to provide needed 
environmental protections (e.g., implementation and revision of fishery harvest 
management programs; implementation of revised hatchery management policies and 
programs; adoption of and periodic revision of forest practices rules; and implementation 
of the Agricultural Water Quality management Act (frequently referred to as Senate Bill 
1010), to address agricultural impacts on water quality; adoption and modification of fill-
and-removal laws, etc.). Oregon�s adaptive management process may be characterized as 
follows. 

1. Natural resources are managed under existing statute, rule, or policy guidance. 
2. Monitoring provides data for future analysis. 
3. Periodically, monitoring data are assessed. 
4. Results of data analyses are considered by a responsible agency, board, or 
commission regarding the need or appropriateness of changes to statutes, rules, or 
management policies. Occasionally the deliberation may involve a broader 
Legislative and public policy discussion. 


 

Adaptive Management of the Conservation Plan 

Oregon commits to reassess the status of coastal coho populations and their supporting 
habitat on a periodic basis, providing information that may be considered in an adaptive 
management process as described below. These commitments include the following. 


1. Six-year status report. Produce a succinct status report regarding implementation of 
commitments by agencies, restoration work accomplished, and summarizing coho 
and habitat data available by population, strata, and for the ESU. This status report 
may be produced in concert or incorporated in the OWEB Biennial Report. 
2. Twelve-year ESU assessment. Produce a comprehensive assessment of ESU status 
including performance of the coho, trends in habitat, and implementation and 
effectiveness of restoration and management commitments. This assessment would 
be similar in scope to the 2005 OCCA. Depending on the outcome of this thorough 
12-year assessment, the periodicity of future detailed assessments may be adjusted. 
3. Annual status reports. The Regional Management and Implementation Team that is 
responsible for implementing this Conservation Plan will direct production of a very 
brief annual report that reviews the most recent data available for the ESU (see 
example format Table 6). This annual report will serve as an early warning system 
that will alert Oregon to unexpectedly adverse marine conditions; management 
conditions; biological characteristics of the coho populations; or the habitat that 
supports the ESU. 


 

Table 6. Proposed content of annual status report (early warning system). 

Oregon Coast Coho Conservation Plan Annual Report Card 

 

Summary Regarding Overall Status of this ESU 

Short paragraph regarding the overall status of the ESU � are there any alarming data or observations 
that would call Oregon�s conservation assumptions or programs into question? Are there indications that 
the ESU is at greater risk than anticipated in the Conservation Plan? Is additional monitoring or scientific 
evaluation warranted? If so, how and when should the analysis be conducted? 

 

Data Reviewed 

� Coho adult counts � are data regarding adult distribution and abundance available? If so, are the 
values within previously observed and/or expected values and are they consistent with expectations 
based on marine survival? 
� Coho juvenile monitoring data � are data regarding juvenile distribution and abundance available? If 
so, are the values within previously observed and/or expected values? 
� Habitat data � is habitat trend data available? If so, what does the trend indicate? 
� Coho harvest impact data � are harvest impacts consistent with conservation, progress towards desired 
status, and recovery guidelines? 
� Coho hatchery survival data � is survival of hatchery fish within previously observed and/or expected 
values? 
� Coho natural fish survival rates data � is survival of naturally produced fish within previously observed 
and/or expected values? 
� Information from local entities and landowners � e.g. Rapid BioAssessments; restoration efforts; and 
results of effectiveness monitoring. 
� Conservation project implementation data � are agencies meeting commitments in an effective and 
timely manner? 


 

Recommendations regarding the ESU 

Note key recommendations, if any, regarding new monitoring, implementation emphasis, management 
action, and or scientific analysis that should receive priority during the next year. 

 

Date Conservation Plan adopted: 

Date review: 



 


The Oregon Coast Coho Conservation Plan is intended to describe key elements for 
immediate implementation and also provide a strategic means of improving management 
decisions in the future � in essence, to be a living document. This will be done through 
an adaptive management process that will allow for the continual assessment of the 
effectiveness of management strategies and actions to improve the status of coho in the 
ESU. Through the analysis of research, monitoring and evaluation (RM&E) data, the 
Oregon Plan Core Team will be able to determine if the premise of the plan - that the 
management strategy will be able to help the ESU achieve desired status � is accurate. If 
not, the adaptive management process will allow for the state to consider a different 
premise. 

 

The adaptive management process will play out on different levels as the Conservation 
Plan is implemented. Annual research, monitoring and evaluation information collected 
will be reviewed to determine the effectiveness of site-specific actions (e.g., enhancing an 
area to promote the development of beaver dams). Those actions found to be ineffective 
will be discouraged. New actions based on the results of research may be proposed to 
more effectively implement a strategy. The state will make these responsive adjustments 
as more information is collected. Considering changes to strategies will be a more 
deliberative process. 

 

Assessing the effectiveness of the Conservation Plan, including its strategies, will be 
conducted in 2019, and every 12 years thereafter. An assessment will also be considered 
if the ESU becomes ESA listed, or information suggests there has been a significant 
decline in the health of the ESU (the annual report will serve as an early warning system). 
Assessments of the Conservation Plan will be conducted by the Oregon Plan Core Team 
and will include public participation. 

 

The adaptive management process can lead to changes in all aspects of the Conservation 
Plan besides strategies or actions. The review of information may suggest revision of one 
or more of the desired status measurable criteria, their metrics, or thresholds for passing. 
The population delineations in the Plan could also be revised in the future. 

 

 

10. Implementation and Oversight 

 

Effective implementation of this Conservation Plan requires leadership at the community 
level, by individuals with local knowledge and passion for salmon, watersheds, and their 
local communities. The desired status goal of this Conservation Plan will not be 
achieved under existing regulatory programs, but by a combination of these plus 
significant and effective non-regulatory cooperative conservation efforts. Successful 
implementation of this Conservation Plan depends on achieving a productive balance 
where state and federal government provides science analysis, policy guidance, and 
technical expertise that strengthens the existing community-based cooperative 
conservation work in non-regulatory settings. 

 


Implementation of Conservation Plan Actions 

This Conservation Plan does not provide lists of site-specific actions that are necessary to 
achieve the desired status goal. This is partially due to the scarcity of detailed watershed 
assessments at small spatial scales throughout the ESU that would be needed to identify 
actions at the site-specific level. 

 

The lack of site-specific actions was also intentional. This Conservation Plan was 
intended to provide structure and guidance to local efforts to protect and restore coho and 
their habitat throughout the ESU while providing the flexibility for actions to be 
determined at the grassroots level. 

 

Implementation of this Conservation Plan will focus on efforts to address key factors that 
limit the productivity of coho and will utilize the existing Oregon Plan infrastructure. 
Most of these efforts will start at the local level with landowners or the general public 
contacting watershed groups, or groups contacting landowners, to develop projects to 
protect or enhance coho habitat. Natural resource agencies may provide technical 
support to help develop a project proposal or provide matching funds to implement the 
project. These projects will then be brought to funding entities, such as OWEB, to fund. 
Once funded, the project will be implemented by the local group, the landowner or their 
agent. 

 

While most actions under this plan will be implemented through this �bottom-up� 
approach, there will be situations where necessary actions cannot be effectively handled 
at the local level. In such cases (e.g.; where a regional or ESU-wide project is developed 
to help achieve the desired status goal), proposals will be brought by the public, 
landowners or watershed groups to the Oregon Plan Regional Management and 
Implementation Team for consideration and implementation. 

 

Conservation Plan Accountability 

The Oregon Plan Core Team, chaired by the Governor�s Natural Resources Office and 
comprised of state and federal natural resource agency policy staff, holds ultimate 
accountability for implementation of conservation efforts statewide (i.e., the Oregon 
Plan), including this Conservation Plan for the Oregon Coast Coho ESU. An Oregon 
Plan Regional Management and Implementation Team, comprised of state, federal, and 
tribal management staff and local restoration organizations (e.g., watershed councils, Soil 
and Water Conservation Districts), will be responsible for coordinating and tracking 
implementation actions and preparing reports of progress described as part of Oregon�s 
adaptive management commitment in this Plan. All Oregon Plan teams (Core Team, 
Monitoring Team, Outreach Team, and Regional Management and Implementation 
Team) are linked and unified in a common and collaborative effort to conserve, restore, 
and protect habitats and watersheds for salmon as part of the Oregon Plan. 

 

Implementation Funding 

Funding to support implementation of this Conservation Plan consists of base budget 
allocations to government agencies assigned tasks identified under this Plan and the 
Oregon Plan. Discretionary funding for infrastructure support (e.g., Soil and Water 


Conservation Districts, watershed councils) are provided by OWEB via Oregon Lottery 
funds, federal Pacific Coast Salmon Recovery Funds, and private funding entities. 

 

Funding available from Lottery revenue is expected to increase in 2007-2009, based on 
revenue predictions by the Oregon Department of Administrative Services. If true, the 
potential exists to increase funding available to support restoration grants within this 
ESU. OWEB has invested roughly 2 million dollars in restoration grants annually in this 
ESU since 1997. Recently approved funds related to the 2006 Ocean Fishery closure are 
also being directed towards activities that support watershed restoration in this ESU. 
OWEB and ODA are also planning to request an increase in statewide allocation for 
support of both SWCDs and watershed councils from 4 million to 6 million dollars per 
biennium. 

 

Oregon has a reliable long-term source of Lottery Funds dedicated to restoration under 
Ballot Measure 66 and Oregon voters will have the opportunity to consider continuing 
Ballot Measure 66 after 2014. In the 2007-2009 biennium, Oregon expects to at least 
maintain or slightly increase funding for restoration infrastructures and on-the-ground 
work across the ESU. 

 

Implementation Schedule 

This Conservation Plan will be implemented in a general sequence of actions intended to 
support achievement of the desired status goal. The general sequence is described as 
follows. 

 

Immediate and urgent implementation 

� Support conservation action that will improve the status of all populations that failed 
viability criteria (2005 OCCA) so that they meet or exceed viability criteria. 
� Implement consideration of limiting factor and other investment guidance in 
decisions to prioritize funding and conduct of conservation work. 
� Implement effective on-the-ground cooperative conservation work. 
� Enforce existing natural resources regulatory programs. 
� Implement monitoring commitments. 
� Monitor implementation of conservation commitments. 
� Provide support to local conservation entities to implement demonstration projects on 
private lands in specified basins. 
� Provide annual feedback to evaluate the efficacy of fishery harvest and hatchery 
management programs and consider whether modifications could accelerate 
achievement of desired status goal. 


 

Near- and mid-term implementation 

� Prepare annual (early warning system) reports. 
� Support conservation action that will improve the productive capacity of virtually all 
coho populations. 
� Increase participation by and effectiveness of cooperative conservation work on 
private lands in areas most suitable to support juvenile coho. 
� Support development of local conservation strategies at scales within populations. 



� Evaluate effectiveness of oversight and accountability system. 


 

Long term implementation 

� Conduct comprehensive assessment of the Coast coho ESU; populations; habitat 
status and trend; and rate of progress toward desired status (12 yrs from Plan 
adoption). 
� Evaluate potential need for modified management or regulatory programs to conserve 
productive capacity of habitat. 
� Provide data and analyses that will inform legislative consideration regarding long-
term dedication of Lottery Funds to Watersheds and Salmon conservation. 


 

 

11. Reaching Desired Status � Time Frame Expectations 

 

The desired status goal for this ESU is ambitious. Significant changes to harvest 
management and hatchery programs have already been implemented and have 
significantly diminished harvest and hatchery management as limiting factors. Habitat 
remains the primary limiting factor for the majority of coho populations in the ESU that 
can be influenced by Oregon�s management. 

 

Two principle factors must be considered in the process of predicting the time-frame 
required to achieve Oregon�s desired status goal for this ESU. 

1. Ecological processes. Addressing habitat limiting factors (insufficient stream 
complexity, water quality, etc.) to achieve desired status for the ESU will require 
significantly increasing the productive capacity of coho and their habitat. Restoration 
of ecological processes that support high quality habitat requires time and is 
constrained by patchwork landownership patterns, different regulatory structures, and 
historical land use practices. Even given an expected increase in the level of non-
regulatory participation in habitat improvement work, it will take time to 1) produce 
detectable improvements in habitat quality and 2) restore the biological and 
ecological processes across the ESU. 
2. Scientific uncertainty. There currently are many uncertainties related to the 
effectiveness of restoration actions; the cause and impact of predators; the relative 
importance of all phases of juvenile rearing and habitats; the potential role of beaver 
dams to increase productive capacity of coho habitat; and the total amount of CWHIP 
actually available. These scientific uncertainties will require both funding and time to 
provide information that may be considered in future management programs. 


 

Three time-frame and cost scenarios for habitat work required to achieve desired status 
(see Population-based Actions and Associated Cost Estimates Chapter) present general 
time-frame scenarios under which desired status might be achieved. Scenario 3 (a 50 
year time-frame) is probably the most realistic, given likely levels of funding, the time 
required to resolve scientific uncertainty, and the time required to restore ecological 
processes. 

 


Achieving the desired status goal will require an institutionalization of the conservation 
commitments embedded in the Oregon Plan and this Conservation Plan, sustained 
leadership, extensive non-regulatory participation by private landowners, funding, 
reassessment, and adaptive management. With the enhanced level of habitat monitoring 
proposed in this plan, Oregon will be able to determine the trajectory of habitat condition 
and the approximate time-frame that the observed trajectory would require to achieve the 
desired status goal. 

 

 

12. Conclusion 

 

The purpose of this Conservation Plan is to ensure the continued viability of the Oregon 
Coast Coho Evolutionary Significant Unit (ESU) and to achieve a desired status that 
provides substantial ecological and societal benefits. The Oregon Coast Coho ESU is 
viable (State of Oregon, May 6, 2005) and does not currently require protection under the 
federal ESA (NOAA Fisheries 2006). The current status of this ESU reflects a reduction 
in fishery harvest, improved hatchery management, and extensive habitat restoration 
work initiated or maintained under the Oregon Plan. This Conservation Plan maintains 
and enhances support of the Oregon Plan and meets the requirements of Oregon�s Native 
Fish Conservation Policy (NFCP). This Conservation Plan does not propose new land-
use regulations, maintains existing regulatory programs, and enhances support for non-
regulatory cooperative conservation. A key element of this Plan is to provide a higher 
and more effective level of support to local conservation groups and private landowners 
(e.g., Soil and Water Conservation Districts, watershed councils, industrial forestland 
owners, Salmon and Trout Enhancement Program volunteers, and other individuals and 
groups). These community-based organizations have demonstrated an impressive record 
of planning, prioritizing, and implementing habitat improvement projects through their 
participation in the Oregon Plan. 

 

Oregon concluded that the existing conservation framework of regulatory programs and 
non-regulatory actions is sufficient to sustain and slightly improve the current viability of 
the ESU (see 2005 OCCA). One key principle of the Oregon Plan is that Oregonians will 
strive to obey existing laws that protect water quality, watershed health, and salmon. 
This commitment was noted in Executive Order 99-01: �agencies with regulatory 
programs that are included in the Oregon Plan will determine levels of compliance with 
regulatory standards and identify and act on opportunities to improve compliance levels.� 
Oregon agencies remain committed to evaluate compliance with environmental 
protection laws and seek constructive means of improving compliance with these laws as 
may be warranted. 

 

Oregon�s existing regulatory structure was not designed to support achieving the desired 
status goal for this ESU. Oregon�s management philosophy regarding regulation and 
enforcement of laws on private lands is clear: that, given Oregon�s extensive natural-
resources regulatory programs, additional cooperative conservation stewardship action on 
private lands will be most effectively achieved by willing participation of private 
landowners in voluntary and non-regulatory settings. This management philosophy is a 


conscious decision by executive leadership, based on the current realities of public 
values; state agency board and commission actions; legislative direction; and funding 
priorities. Thus, the primary strategy to achieve the desired status in this Conservation 
Plan is based on the following general premise: Habitat management and improvement 
is the key to protecting and enhancing coastal coho; much of the most important coho 
habitat is on private land; habitat improvement on private land is most likely to occur 
through incentive-based cooperative partnerships with landowners; and the Oregon Plan 
provides the best vehicle for securing these partnerships and implementing habitat 
improvements 

 

Oregon is relying therefore on a combination of Oregon�s current regulatory programs 
plus long-term participation in non-regulatory cooperative conservation work to achieve 
the desired status goal for the Coast coho ESU. The Oregon Plan habitat strategy is 
designed to support effective work by the existing conservation network across the ESU. 
This effort is expected to increase participation in non-regulatory cooperative 
conservation work by private landowners, especially landowners in areas with the 
greatest potential to create high quality coho habitat and support achievement of the 
desired status goal for the ESU. A partnership of private forest and agricultural 
landowners represents a powerful means of increasing the level of investment in effective 
voluntary habitat-improvement. 

 

Oregon is generally optimistic that the elements of this Conservation Plan will achieve 
the desired status goal for the ESU, based on the following observations. 

1. The ESU is currently viable and adaptive management has virtually eliminated 
significant adverse impacts of fishery harvest and hatchery programs on the ESU. 
2. The ESU is comprised of many populations and many fish. This means that there is 
more diversity, more opportunity for the ESU to demonstrate resiliency during future 
adverse environmental conditions. 
3. Habitat improvement work is currently supported by extensive and diverse 
community-based conservation networks. For decades, watershed councils, Soil and 
Water Conservation Districts, STEP volunteers, and other community groups and 
landowners have been actively engaged in restoring fish habitat and watershed health. 
4. Private landowners, especially the timber industry, have demonstrated a significant 
and sustained commitment to participate in restoration in a non-regulatory setting, 
especially since implementation of the Oregon Plan in 1997 (approximately $32 
million dollars invested in restoration work across the Coast coho ESU from 1997 to 
2003 (2005 OCCA). This track-record suggests that private landowners will continue 
to support non-regulatory cooperative conservation and restoration work in this ESU 
and statewide. The Oregon Plan habitat strategy is expected to increase participation 
by private landowners in non-regulatory conservation measures across the ESU. 
5. Significant upland reaches of stream systems in the ESU are in federal or state 
ownerships with levels of regulatory protection that are expected to provide improved 
water quality and stream complexity in upstream spawning areas and downstream 
rearing areas used by juvenile coho. 
6. Information has been provided to guide prioritization of conservation investments to 
address limiting factors and focus conservation work in areas where it is most needed 



and will be most effective. Development of more refined population-based 
conservation strategies for independent populations will improve the effectiveness of 
future conservation investments. 
7. Increased levels of participation in non-regulatory cooperative conservation activity 
by private landowners that control the vast majority of the lowland, low gradient 
streams most important to overwintering juvenile coho are expected. This increased 
level of non-regulatory participation is expected also to ensure that this ESU does not 
become eligible for listing under federal ESA. 


 

Achieving the desired status goal for this ESU will require roughly a doubling of the 
productive capacity of the coho and their supporting habitat. Monitoring and evaluation 
will reveal if Oregon�s commitments and expectations will be sufficient to achieve this 
ambitious goal for the ESU. Modified management and regulatory programs will be 
considered, as may be appropriate, by Oregon and the various governing boards and 
commissions as future monitoring data are available to track trends and rates of 
improvement in coho and habitat conditions across the ESU. 

 


References 

 

 

 

Lawson, P. W., E. Bjorkstedt, M. Chilcote, C. Huntington, J. Mills, K. Moore, T. E. 
Nickelson, G. H. Reeves, H. A. Stout, and T. C. Wainwright. 2004. Identification 
of Historical Populations of Coho Salmon (Onchorhynchus kisutch) in the Oregon 
Coast Evolutionarily Significant Unit. Review Draft. Oregon Northern California 
Coast Technical Recovery Team. NOAA/NMFS/NWFSC. 129 p. 

Nickelson, T. E., M. F. Solazzi, S. L. Johnson, and J. D. Rodgers. 1992a. An approach to 
determining stream carrying capacity and limiting habitat for coho salmon 
(Oncorhynchus kisutch). In Proceedings of the coho workshop. Edited by L. Berg 
and P.W. Delaney. Nanaimo, B.C., May 26-28, 1992. pp. 251-260. 

 

Nickelson, T. E., J. D. Rodgers, S. L. Johnson, and M. F. Solazzi. 1992b. Seasonal 
changes in habitat use by juvenile coho salmon (Oncorhynchus kisutch) in Oregon 
coastal streams. Can. J. Fish. Aquat. Sci. 49:783-789. 

 

Nickelson, T. E. 1998. A Habitat-Based Assessment of Coho Salmon Production 
Potential and Spawner Escapement Needs for Oregon Coastal Streams. Oregon 
Dept. Fish and Wildlife, Fish Div., Fish. Info. Rep. 98-4 Portland, OR. 

 

NOAA Fisheries. 2006. 71 FR 3033: Endangered and Threatened Species: Withdrawal of 
Proposals to List and Designate Critical Habitat for the Oregon Coast 
Evolutionarily Significant Unit (ESU) of Coho Salmon. Federal Register 71 pages 
3033-3048. January 19, 2006. 

 

ODFW (Oregon Department of Fish and Wildlife). 2003. Fisheries Management and 
Evaluation Plan. Oregon Coastal Coho, Siltcoos and Tahkenitch Lakes Coho 
Fishery. Salem, Oregon. November, 2003. 

 

State of Oregon. 2005. Oregon Coastal Coho Assessment. Parts 1, 2, 3A and 3B. Oregon 
Department of Fish and Wildlife. Salem, Oregon. 
http://nrimp.dfw.state.or.us/OregonPlan/default.aspx?p=152&path=ftp/reports/Final%20Reports&title=&link= 

 

Zhou, S. 2000. Stock Assessment and Optimal Escapement of Coho Salmon in Three 
Oregon Coastal Lakes. Information Report Number 2000-7. Oregon Department 
of Fish and Wildlife. Portland, Oregon. 

 

 


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