Upper Columbia Spring Chinook Salmon, Steelhead, and Bull Trout Recovery



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5.6.2Modeling Approach

All H Analyzer


The “All H Analyzer” (AHA), as used in this plan, describes the integration of in-basin and out-of-basin effects on salmon and steelhead. The analysis explains contributions of harvest, hatcheries, hydropower138, and habitat data and strategies to recovery. The AHA process is an exercise that investigates (simulates) out-of-subbasin effects within the context of tributary habitat improvements.

AHA, as used in this planning exercise, simulates various recovery actions between in-basin and out-of-basin effects. This approach gives planners a means for evaluating various options. The different options include harvest regimes, modifications to existing hatchery programs, and habitat improvement actions. Listed below are preliminary results of the AHA analyses. These results provide only a relative assessment of the cumulative effects of actions among different sectors (Appendix J). SARs were held constant in all simulations.


Preliminary Results

Wenatchee spring Chinook

  1. Preliminary results of AHA analysis suggest that the hatchery environment may have a large effect on the fitness of naturally produced Chinook.

  2. A higher level of integration139 may be possible under the present condition scenario by reducing the number of hatchery produced Chinook on the spawning grounds through removal at collection points or selective harvest.

  3. Scenario 3 habitat improvements may lead to a larger number of naturally produced returns. Additional returns of naturally produced fish may be realized if habitat improvements are coupled with removal of some hatchery produced Chinook.

  4. Scenario 1 habitat improvements may not have a large effect on the integration rate unless the number of hatchery produced Chinook are further reduced on spawning grounds.
Wenatchee steelhead

  1. Preliminary results of AHA analysis suggest that the hatchery environment may have a large effect on the fitness of naturally produced steelhead.

  2. A higher level of integration may be possible by reducing the number of hatchery produced steelhead on the spawning grounds through either removal at collection points or selective harvest.

  3. Scenario 1 habitat improvements (and their effect on the number of naturally produced fish) will probably increase returns of naturally produced fish.

  4. Scenario 3 habitat improvements may lead to a larger number of naturally produced returns. Additional returns could be realized if habitat improvements are combined with removal of some hatchery-produced steelhead.
Entiat spring Chinook

No AHA analysis was run on Entiat spring Chinook. This work will be conducted by the local watershed group and USFWS.
Entiat steelhead

No AHA analysis was run on Entiat steelhead. This work will be conducted by the local watershed group.
Methow spring Chinook

  1. Preliminary results of AHA analysis suggest that the hatchery environment may have a large effect on the fitness of naturally produced Chinook.

  2. A higher level of integration may be possible by reducing the number of hatchery produced Chinook on the spawning grounds through either removal at collection points or selective harvest.

  3. Scenario 3 habitat improvements may lead to a larger number of naturally produced returns. Additional returns could be realized if habitat improvements are combined with removal of some hatchery produced Chinook.

  4. Scenario 1 habitat improvements will probably increase returns of naturally produced Chinook to spawning grounds.
Methow steelhead

  1. Preliminary results of AHA analysis suggest that the hatchery environment may have a large effect on the fitness of naturally produced steelhead.

  2. A higher level of integration may be possible by reducing the number of hatchery produced steelhead on the spawning grounds through either removal at collection points or selective harvest.

  3. Scenario 3 habitat improvements may lead to a larger number of naturally produced returns. Additional returns could be realized if habitat improvements are combined with removal of some hatchery-produced steelhead.

  4. Scenario 1 habitat improvements may increase returns of naturally produced steelhead to spawning grounds.
Okanogan steelhead

  1. Poor productivity of the natural environment currently prevents many naturally produced steelhead from being present in the Okanogan subbasin.

  2. Preliminary results of AHA analysis revealed that the hatchery environment may have a large effect on the fitness of naturally produced steelhead. Potential habitat improvements should increased survival for both naturally and hatchery produced returns and thus supports the transition to an integrated program.

  3. Under present conditions, additional naturally produced steelhead are incorporated as broodstock, which improves integration rate. A higher level of integration may be possible by reducing the number of hatchery produced steelhead on the spawning grounds through either removal at collection points or selective harvest.

  4. Scenario 3 habitat improvements may lead to a larger number of naturally produced returns. Additional returns could be realized if habitat improvements are combined with removal of some hatchery-produced steelhead.

  5. Scenario 1 habitat improvements may allow for 100% use of naturally produced steelhead for hatchery broodstock and increase returns of naturally produced steelhead.

5.6.3Conclusion


Both approaches suggest that the recovery actions recommended in this plan should significantly improve the survival of naturally produced spring Chinook and steelhead in the Upper Columbia Basin. In addition, recommended actions within the habitat sector should improve the spatial structure and habitat quality within major spawning areas, allowing the populations to meet spatial structure requirements. Implementing actions recommended within the hatchery sector should remove the threats associated with diversity and likely lead to a diversity status that would meet the requirements of a VSP.

It is important to note that the integration analysis did not consider potential improvements in the estuary that may improve the survival of Upper Columbia populations. Actions that reduce toxics and predation in the estuary may translate into a relatively large survival benefit for Upper Columbia populations. These issues notwithstanding, it is highly probable that the combined actions within all sectors, including actions within the lower Columbia River and estuary, will move Upper Columbia populations to a more viable state. The monitoring and adaptive management program outlined in Section 8 will be used to demonstrate progress toward recovery of Upper Columbia ESU and DPS.



Table 5.9 Naturally produced Upper Columbia Steelhead run-size criteria and mortality take-limit for recreational harvest fisheries in the Wenatchee River, Methow River, and Okanogan Basin spawning areas. Catch-and-release mortality is assumed to be 5%. From NMFS (2003).

Tier

Priest Rapids count

Estimated escapement
to tributary area


Mortality impact (%)

Wenatchee River and Columbia River between Rock Island and Rocky Reach dams




<837

<599

0

Tier 1

838

600

2

Tier 2

2,146

1,700

4

Tier 3

3,098

2,500

6

Methow River and Columbia River upstream from Wells Dam




<908

<499

0

Tier 1

804

500

2

Tier 2

2,224

1,600

4

Tier 3

3,386

2,500

6

Okanogan Basin upstream of Highway 97 Bridge




<175

<119

0

Tier 1

176

120

5

Tier 2

180

120

7

Tier 3

795

600

10

Table 5.10 Artificial propagation programs in the Upper Columbia Basin in 2005 listed by release basin, primary hatchery facility association, program operators, and funding source

Program

Primary Facility

Operator(s)

Funding Source(s)

Wenatchee River Basin Releases

Chiwawa spring Chinook

Eastbank Hatchery

WDFW

CPUD

White River spring Chinook

WDFW and private

WDFW

GPUD

Carson spring Chinook

Leavenworth NFH

USFWS

BOR

Wenatchee coho

USFWS facilities

YN/USFWS

BPA

Wenatchee sockeye

Eastbank Hatchery

WDFW

CPUD

Wenatchee steelhead

Eastbank Hatchery

WDFW

CPUD

Wenatchee summer Chinook

Eastbank Hatchery

WDFW

CPUD

Entiat River Basin Releases

Carson spring Chinook

Entiat NFH

USFWS

BOR

Methow River Basin Releases

Chewuch spring Chinook

Methow Hatchery

WDFW

DPUD/CPUD/GPUD

Methow Composite spring Chinook

Methow Hatchery

WDFW

DPUD/CPUD/GPUD

Methow summer Chinook

Eastbank Hatchery

WDFW

CPUD

Methow/Okanogan coho

USFWS facilities

YN/USFWS

BPA

Twisp spring Chinook

Methow Hatchery

WDFW

DPUD/CPUD/GPUD

Wells steelhead

Wells Hatchery

WDFW

DPUD

Methow Composite spring Chinook

Winthrop NFH

USFWS

BOR

Methow summer Chinook steelhead

Winthrop NFH

USFWS

BOR

Okanogan River Basin Releases

Colville Tribes Okanogan steelhead

Colville Tribes Hatchery

Colville Tribes

BPA

Carson spring Chinook

Leavenworth Complex

USFWS

BOR

Okanogan summer Chinook

Eastbank Hatchery

WDFW

CPUD

Wells steelhead

Wells Hatchery

WDFW

DPUD

Columbia River Releases

Turtle Rock summer Chinook subyearlings

Eastbank Hatchery

WDFW

CPUD

Turtle Rock summer Chinook yearlings

Eastbank Hatchery

WDFW

CPUD

Wells summer Chinook subyearlings

Wells Hatchery

WDFW

DPUD

Wells summer Chinook yearlings

Wells Hatchery

WDFW

DPUD

Table 5.11 Summary of artificial anadromous fish production in the Wenatchee subbasin

Fish Species

Facility

Funding Source

ESA Listed

Current production level goals

Spring Chinook

Eastbank Fish Hatchery Complex (Chiwawa acclimation pond)

(Operated by WDFW)



Chelan County PUD

Yes

672,000

(will decrease in future)



Leavenworth National Fish Hatchery (Operated by USFWS)

Bureau of Reclamation

No

1,625,000

Captive brood program in Manchester

(Operated by Aquaseed; may expand to facility in White River Basin)



Grant PUD

Yes

200,000

[This obligation may be partially met by other means in the future, current production much lower (< 50,000)]



TBD – Nason Cr. release

Grant PUD

Yes

up to 400,000

(future production)



Steelhead

Eastbank Fish Hatchery Complex

(Operated by WDFW)



Chelan PUD

Yes

400,000

(will decrease in future)



Summer Chinook

Eastbank Fish Hatchery Complex (Dryden acclimation pond)

(Operated by WDFW)



Chelan PUD

No

864,000

(will decrease in future)



Sockeye

Eastbank Hatchery

(Lake Wenatchee net pens; Operated by WDFW)



Chelan PUD

No

200,000

(will increase up to 280,000 in future)



Coho

Leavenworth NFH

(Operated by USFWS for YN)



BPA (Fish & Wildlife Program)

No

> 500,000

Acclimation sites at Nason Creek and Icicle Creek (YN)

BPA (Fish & Wildlife Program)

No

< 500,000

Table 5.12 Summary of artificial anadromous fish production in the Entiat subbasin

Fish Species

Facility

Funding Source

ESA Listed

Production level goals

Spring Chinook

Entiat NFH (Operated by USFWS)

Bureau of Reclamation

No

400,000

Table 5.13 Summary of artificial anadromous fish production in the Methow subbasin

Fish Species

Facility

Funding Source

ESA Listed

Production level goals

Spring Chinook

Methow Fish Hatchery

Acclimation sites at the Methow, Biddle, Twisp, and Chewuch Acclimation ponds

(Operated by WDFW)


Douglas PUD, Chelan PUD, and Grant PUD

Yes

550,000140

Winthrop NFH

(Operated by USFWS)



Bureau of Reclamation

Yes

600,000

Steelhead

Wells Dam Hatchery Complex

(Operated by WDFW)



Douglas County PUD and Grant County PUD

Yes

349,000141


Winthrop NFH

(Operated by USFWS)



Bureau of Reclamation

Yes

100,000

Summer Chinook

Wells Dam Hatchery Complex (Carlton acclimation pond)

(Operated by WDFW)



Chelan County PUD, Douglas County PUD

No

400,000142

Coho

Winthrop NFH

(Operated by USFWS for YN)



BPA (Fish & Wildlife Program)

No

250,000

Table 5.14 Broodstock collection guidelines of the Methow Basin spring Chinook supplementation plan (ESA Section 7 Draft Biological Opinion, Section 10 Permit 1196)

Wells Escapement Projection

Broodstock Collection Objective

<668

WDFW may collect 100% of Wells Dam escapement; place all fish into the adult-based supplementation program.

>668 but <964

Pass a minimum of 296 adults upstream of Wells Dam for natural spawning.

>964

Collection at levels to meet interim production level of

550,000 and 600,000 smolts at Methow Fish Hatchery and

Winthrop NFH, respectively.



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