This page provides a read-only view of a Proposal. The sections below are organized to help review teams quickly and accurately review a proposal and therefore may not be in the same order as the proposal information is entered.
This Proposal Summary page updates dynamically to always display the latest data from the associated project and contracts. This means changes, like updating the Project Lead or other contacts, will be immediately reflected here.
To view a point-in-time PDF snapshot of this page, select one of the Download links in the Proposal History section. These PDFs are created automatically by important events like submitting
your proposal or responding to the ISRP. You can also create one at any time by using the PDF button, located next to the Expand All and Collapse All buttons.
Archive | Date | Time | Type | From | To | By |
6/14/2010 | 3:06 PM | Status | Draft | <System> | ||
Download | 7/30/2010 | 5:07 PM | Status | Draft | ISRP - Pending First Review | <System> |
10/15/2010 | 5:54 PM | Status | ISRP - Pending First Review | ISRP - Pending Final Review | <System> | |
1/14/2011 | 10:42 AM | Status | ISRP - Pending Final Review | Pending Council Recommendation | <System> | |
7/7/2011 | 10:19 AM | Status | Pending Council Recommendation | Pending BPA Response | <System> |
Proposal Number:
|
RMECAT-1983-350-00 | |
Proposal Status:
|
Pending BPA Response | |
Proposal Version:
|
Proposal Version 1 | |
Review:
|
RME / AP Category Review | |
Portfolio:
|
RM&E Cat. Review - Artificial Production | |
Type:
|
Existing Project: 1983-350-00 | |
Primary Contact:
|
Steve Rodgers-NPT (Inactive) | |
Created:
|
6/14/2010 by (Not yet saved) | |
Proponent Organizations:
|
Nez Perce Tribe |
|
|
||
Project Title:
|
Nez Perce Tribal Hatchery Operations and Maintenance (O&M) | |
Proposal Short Description:
|
The Nez Perce Tribal Hatchery Complex (NPTHC) mitigates for the effects of the Federal Columbia River Hydropower System on naturally-reproducing salmon in the Clearwater River Subbasin. The goal is to release fish that survive to adulthood, contribute to natural production and provide long term harvest opportunities. NPTHC utilizes best management practices (BMP) and Natural Rearing Enhancement Systems (NATURES) techniques to produce 1.4M fall and 825K spring Chinook salmon annually. | |
Proposal Executive Summary:
|
The Northwest Power Planning Council (NPPC) authorized construction of Nez Perce Tribal Hatchery Complex (NPTHC) on May 17, 2000 in Helena, MT. Construction began July 2001 and was essentially completed in October 2002. The main hatchery was dedicated October 9, 2002 and began operation in 2003. NPTHC is comprised of two rearing facilities (NPTH and SWS), and 5 acclimation facilities (Luke's Gulch, Cedar Flats, North Lapwai Valley, Newsome Creek and Yoosa/Camp Creek). It is staffed by 16 permanent employees, fulfilling work and standby duties at all seven facilities. Only NPTH is operational all year, the other facilities operate from 2 to 6 months annually. Work area is the Clearwater River, South Fork Clearwater River and Selway River for Fall Chinook Salmon (FCS), and Clearwater River, Lolo Creek (Tributary of the Clearwater River), and Newsome Creek (tributary of the South Fork Clearwater River) for Spring Chinook Salmon (SCS). All work is done on or adjacent to Tribal Treaty lands, supporting historical NPT fishing areas. The primary goal is to release fish that survive to adulthood, spawn in-basin and produce offspring supporting natural production and genetic integrity. The general fishery management principles governing NPTHC are: * Protect, mitigate, and enhance Columbia River Subbasin anadromous fish resources; * Develop, increase, and reintroduce natural populations of spring, early-fall, and fall Chinook in the Clearwater River Subbasin; * Provide long-term harvest opportunities for Tribal and non-Tribal anglers within Nez Perce Treaty lands within four generations (20 years) following project completion; * Sustain long-term preservation and genetic integrity of target fish populations; * Keep the ecological and genetic impacts of nontarget fish populations within acceptable limits; * Promote Nez Perce Tribal Management of NPTHC and production areas within Nez Perce Treaty lands. Snake River Fall Chinook Salmon (FCS) are listed as an Evolutionary Significant Unit (ESU) and considered to be part of a single genetically similar aggregate and are managed as a single population. The NPTHC program is integrated with production from Lyon's Ferry Hatchery (LFH), the Fall Chinook Acclimation Project (FCAP), and the Idaho Power Company (IPC) mitigation program. For FCS, returning adults are trapped at Lower Granite Dam and NPTH to meet production goals (532 males & 532 females total). Fish are spawned and early-reared at NPTH. Fish destined for release from Lukes Gulch or Cedar Flats AF's are intermediate reared at Sweetwater Springs (SWS), while all other FCS continue to be cultured at NPTH. After marking/tagging in spring, all fish are transferred to final rearing ponds at NPTH,NLV, Luke's Gulch and Cedar Flats, where they acclimate prior to release by June 15th each year. The specific annual FCS production release goals for NPTHC are: * 500K subyearling FCS released at 50 fpp from Nez Perce Tribal Hatchery (NPTH) into the Clearwater River; * 500K subyearling FCS released at 50 fpp from North Lapwai Valley (NLV) Acclimation Facility (AF) into the Clearwater River; * 200K subyearling FCS released at 50 fpp from Cedar Flats AF into the Selway River; * 200K subyearling FCS released at 50 fpp from Lukes Gulch AF into the South Fork Clearwater River. Specific FCS hatchery adult return goals (from the Snake River Fall Chinook Management Plan pgs. 2-3) for NPTHC are: * Interim goal of 2,290 hatchery-origin adults above Lower Monumental Dam (LMO) annually from NPTHC production; * Long-term goal of 3,750 hatchery-origin adults above LMO annually from NPTHC production; * Provide ~1,000 adults annually for broodstock; * Develop an early-returning run to the Selway River and South Fork Clearwater Rivers. Specific FCS natural adult return goals for NPTHC are: * Interim goal is to achieve a self-sustaining population of 1,250 natural origin adults to the Clearwater River annually; * Long-term goal is to assist in achieving self-sustaining population of 14,360 natural-origin adults above LMO. * Assist in achieving ESA delisting. Spring Chinook Salmon (SCS) in the Clearwater River Subbasin were essentially extirpated by Lewiston Dam (Schoen et al. 1999; USFWS 1999; Murphy and Metsker 1962). However, naturalized populations have been re-established in Lolo Creek and mainstem/tributary reaches of the Lochsa, Selway and South Fork (S.F.) Clearwater rivers (Larson and Mobrand 1992). Founding hatchery stocks used to re-colonize SCS were primarily obtained from the Rapid River Hatchery. Genetic analysis has confirmed that existing natural SCS in the Clearwater River Subbasin are derived from reintroduced Snake River stocks. The intent of this program is to develop localized brood sources to supplement Lolo Creek, Newsome Creek and Meadow Creek. Because no weir is installed on Meadow Creek (a temporary weir proved ineffective), an agreement was reached with IDFG, whereby they annually early-rear 200K SCS at Clearwater Hatchery for NPTHC. In September, these fish are transferred to NPTH, where they are final-reared until release as smolts the following April into the Clearwater River. Adults returning to the NPTH trap from this release provide broodstock for the Meadow Creek program, and also act as a backup source for the other NPTHC SCS programs. For SCS, returning adults (from smolts released at NPTH into the Clearwater River) for the Meadow Creek program are trapped at NPTH (146 males and 146 females). Newsome Creek adults are trapped at the temporary weir on Newsome Creek (28 males and 28 females). Lolo Creek adults are trapped at two temporary weirs on Lolo Creek (55 males and 55 females). All three of these temporary weirs are operated by NPTH M&E project 1983-350-03. In 2011, a permanent weir will be constructed on Lolo Creek replacing the two temporary weirs. In the event of a broodstock shortage, adults for any of these SCS production programs may be provided by Rapid River stock SCS trapped at other Clearwater Basin hatcheries. The specific annual SCS production release goals for NPTHC are: * 400K parr SCS released at 117 fpp from NPTH into Meadow Creek (trib. of Selway River) by helicopter - no acclimation; * 150K pre-smolt SCS released at 35 fpp from Yoosa/Camp Creek AF into Lolo Creek (trib. of Clearwater River); * 75K pre-smolt SCS released at 29 fpp from Newsome AF into Newsome Creek (trib. of South Fork Clearwater River); * 200K smolt SCS released at 20 fpp from NPTH into the Clearwater River. Specific SCS adult return goals taken from the Nez Perce Tribal Hatchery Program Enivronmental Impact Statement (BPA et al. 1997) comprised of a broodstock, natural spawning and harvest component for NPTHC are: * 329 adults returning to Lolo Creek from NPTHC production; * 171 adults returning to Newsome Creek from NPTHC production; * 676 adults returning to Meadow Creek from NPTH production. Production targets, and performance in-hatchery are monitored by NPTHC Management and NPTH M&E Project 1983-350-03. Released fish performance and treatment stream impacts are monitored by the NPTH M&E Project 1983-350-03. Hatchery fish health is monitored by NPTHC staff and USFWS fish pathologists from the Idaho Fish Health Center. All significant program changes are negotiated and agreed to within the NPT and by the comanagers, which include USFWS, IDFG, CTUIR, WDFW, and others. Project duration is until natural production in target streams can support exclusively the fishery management principles, goals and objectives listed above. The NPT's Department of Fisheries Rersource Management (DFRM) now has the equipment infrastructure necessary to ensure efficient and timely exchange of science-based information on regionally accepted performance measures. With additional funding for a data steward, DFRM annual reports, metadata, and performance measure data will be available on the new DFRM website http://www.nptfisheries.org. Appropriate components of program data and results will also be provided to the following websites: Snake Basin Data Group; Pacific States Marine Fisheries Commission (PSMFC), including: PIT Tag Information System (PTAGIS), the Regional Mark Information System (RMIS); Integrated Status and Effectiveness Monitoring Program (STEM); Fish Passage Center (FPC); StreamNet; and NOAA Northwest Science Center. This proposal seeks to enable DFRM participation in regional data management and sharing forums and processes (e.g. PNAMP) as required by RPAs 71 and 72. |
|
|
||
Purpose:
|
Artificial Production | |
Emphasis:
|
Supplementation | |
Species Benefit:
|
Anadromous: 100.0% Resident: 0.0% Wildlife: 0.0% | |
Supports 2009 NPCC Program:
|
Yes | |
Subbasin Plan:
|
||
Fish Accords:
|
None | |
Biological Opinions:
|
Contacts:
|
|
Hydroelectric and flood control dams extirpated the Clearwater River salmon runs. In 1910, construction of the Harpster Dam blocked fish passage into the South Fork Clearwater from 1911 to 1935 and from 1949 until 1963 when the dam was removed (Clearwater Subbasin Summary 2001). In 1927, Lewiston Dam was built at the mouth of the Clearwater River and prevented passage of spring, summer and fall Chinook from at least 1927 to 1940 (Fulton 1970). Passage facilities were upgraded in the 1950’s, but Chinook salmon counts between 1950 and 1957 ranged from only 7 to 63 fish, indicating that the indigenous run was probably eliminated (Cramer and Neeley 1992). Harpster Dam was removed in 1963, and Lewiston Dam was removed in 1973, which made most of the Clearwater River once again a free-flowing system. But a year later, in 1974, Dworshak Dam was completed at the mouth of the North Fork Clearwater River resulting in blocked passage from that large river. As described in the Clearwater Subbasin Plan (Subbasin Plan)(Ecovista 2003), historical numbers of Chinook salmon entering the Clearwater were thought to be substantial. The impact on the people and biota caused by the loss of salmon from this 9,600 square mile watershed must be a defining characteristic of the Snake River Basin.
Efforts to restore naturally, spawning, spring Chinook have created small, scattered populations and fall Chinook recolonized the lower river to a limited extent by 1987. Still these runs are limited in number (Arnsberg 1992) and are subject to the same overall conditions affecting all anadromous species of the Snake River. The Subbasin Plan finds that re-introduction of hatchery origin spring Chinook, following removal of the Lewiston Dam, has resulted in naturally reproducing runs in Lolo Creek, and in the mainstem and tributaries of the three principal head-water rivers; i.e., the Lochsa, the Selway and the South Fork Clearwater. As described in the Subbasin Plan, spring Chinook salmon are classified as “present – depressed” in all areas of the subbasin where status information is available. The Subbasin Plan also indicates that fall Chinook returns appear to show some improvement as a result of recolonization and supplementation actions of the Fall Chinook Acclimation Project (Project No. 199801005). However, these runs are still subject to the same obstacles depressing all naturally spawning salmon runs in the Snake River Basin, which according to the Subbasin Plan is primarily due to out-of-subbasin factors (e.g. dams and ocean conditions).
The Nez Perce Tribe has a biological, legal, historic, economic, social, and cultural need to restore salmon runs. The Nez Perce Tribe’s indigenous territory consisted of north-central Idaho, southeastern Washington and northeastern Oregon. The Tribe is a federally recognized entity with sovereign status over its lands, people and resources. Its governmental rights and authorities extend to any natural resources that are reserved and protected in treaties, executive orders, and federal statutes. The United States also has a trust obligation toward the Nez Perce Tribe to protect these rights and authorities. Salmon and other migratory fish species are an invaluable food resource and an integral part of the Nez Perce Tribe’s culture. Anadromous fish have always made up the bulk of the Nez Perce tribal diet and this dependence on salmon was recognized in the treaties made with the Tribe by the United States. The historic, economic, social, and religious significance of fish to the Nez Perce Tribe continues to this day, which means that the declining fish populations in the Columbia River Basin has caused a substantial, unique, and detrimental impact on the Nez Perce way of life.
The Nez Perce Tribal Hatchery responds directly to a need to mitigate the effects of the Federal Columbia River Hydropower System on naturally-reproducing salmon in the Clearwater River subbasin. The overall goal is to produce and release fish that will survive to adulthood, spawn in the Clearwater River subbasin and produce viable offspring that will support future natural production and genetic integrity.
Supplement Snake River Fall Chinook Salmon. (OBJ-1)
Meet defined adult FCS escapement goals identified in the draft Snake River Fall Chinook Management Plan, specific to NPTHC production.
Interim annual hatchery-origin escapement goal is 2,290 adults from NPTHC production above Lower Monumental Dam. Long-term annual goal is to return 3,750 hatchery-origin adults above Lower Monumental Dam from NPTHC production. Natural-origin goals of this plan include maintaining an abundance threshold (hatchery and/or natural origin) of 7,500 naturally spawning adults, achieving ESA delisting, meeting a long term goal of 14,360 natural-origin adult FCS above Lower Monumental Dam, and maintaining out of basin straying above Lower Granite Dam at levels less than 5%. NPTHC seeks to assist in meeting these natural goals with other Snake River FCS production programs. Should NPTHC, as a supplementation hatchery program, meet its objectives, it will also work towards achieving the biological objectives defined in the Clearwater Subbasin Plan. Supplement Clearwater Spring Chinook Salmon (OBJ-2)
The intent of this program is to develop localized brood sources to supplement Lolo Creek, Newsome Creek and Meadow Creek.
Specific adult return goals from NPTH production are: Lolo Creek: 329 adults from hatchery production (136 for broodstock, 63 for natural spawning, and 130 for harvest). Newsome Creek: 171 Adults from hatchery production (69 for broodstock, 42 for natural spawning, and 60 for harvest). Meadow Creek: 676 Adults from hatchery production (322 for broodstock, 248 for natural spawning, and106 for harvest). Coordinate project activities, data management, and communicate findings to resource managers. (OBJ-3)
Data management and summary reporting will be conducted by performing specific project tasks (both O&M and M&E). This information will be shared with managers through several ongoing regional communication and review processes such as website databases, summary reports, annual operation plans, and management meetings. Every five years, materials will be summarized to facilitate a performance review of the hatchery program. Successful attainment of this objective will be measured through the timely completion of contractual deliverables related to information dissemination.
|
Project Maintenance and Capital Improvements (OBJ-4)
Maintain all buildings, grounds, systems, equipment and other project assets. Maximize efficiency and quality through capital improvements.
Regional Decision-Making From Science-Based Shared Data (OBJ-5)
The Nez Perce Tribe's Department of Fisheries Resource Management (DFRM) annual reports, metadata, and performance measure data will be available on the new DFRM website http://www.nptfisheries.org. Appropriate components of program data and results will also be provided to the following websites: Snake Basin Data Group; Pacific States Marine Fisheries Commission (PSMFC), including: PIT Tag Information System (PTAGIS), the Regional Mark Information System (RMIS); Integrated Status and Effectiveness Monitoring Program (STEM); Fish Passage Center (FPC); StreamNet; and NOAA Northwest Science Center. This proposal seeks to enable DFRM participation in regional data management and sharing forums and processes (e.g. PNAMP) as required by RPAs 71 and 72.
Meeting this objective will allow managers immediate access to the NPT's science-based data to assist in making management decisions affecting basin-wide populations. |
To view all expenditures for all fiscal years, click "Project Exp. by FY"
To see more detailed project budget information, please visit the "Project Budget" page
Expense | SOY Budget | Working Budget | Expenditures * |
---|---|---|---|
FY2019 | $2,175,835 | $2,229,989 | |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,148,321 | $2,201,790 | |
General - Within Year | $27,514 | $28,199 | |
FY2020 | $2,148,321 | $2,246,419 | $2,240,104 |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,246,419 | $2,240,104 | |
FY2021 | $2,214,227 | $2,254,227 | $2,507,710 |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,214,227 | $2,463,212 | |
Cost Savings | $40,000 | $44,498 | |
FY2022 | $2,214,227 | $2,493,020 | $2,230,073 |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,453,020 | $2,194,292 | |
General - Within Year | $40,000 | $35,781 | |
FY2023 | $2,214,227 | $2,449,343 | $2,121,368 |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,354,343 | $2,039,089 | |
General - Within Year | $95,000 | $82,279 | |
FY2024 | $2,311,653 | $2,311,653 | $2,521,646 |
|
|||
BiOp FCRPS 2008 (non-Accord) | $2,311,653 | $2,521,646 | |
FY2025 | $0 | $621,133 | |
|
|||
BiOp FCRPS 2008 (non-Accord) | $0 | $621,133 | |
Capital | SOY Budget | Working Budget | Expenditures * |
FY2019 | $0 | $0 | |
|
|||
FY2020 | $0 | $0 | |
|
|||
FY2021 | $0 | $0 | |
|
|||
FY2022 | $0 | $0 | |
|
|||
FY2023 | $0 | $0 | |
|
|||
FY2024 | $0 | $0 | |
|
|||
FY2025 | $0 | $0 | |
|
|||
* Expenditures data includes accruals and are based on data through 31-Mar-2025 |
Cost Share Partner | Total Proposed Contribution | Total Confirmed Contribution |
---|---|---|
There are no project cost share contributions to show. |
Annual Progress Reports | |
---|---|
Expected (since FY2004): | 34 |
Completed: | 21 |
On time: | 21 |
Status Reports | |
---|---|
Completed: | 79 |
On time: | 47 |
Avg Days Late: | 1 |
Count of Contract Deliverables | ||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Earliest Contract | Subsequent Contracts | Title | Contractor | Earliest Start | Latest End | Latest Status | Accepted Reports | Complete | Green | Yellow | Red | Total | % Green and Complete | Canceled |
BPA-11032 | FY01 land acquisition | Bonneville Power Administration | 10/01/2000 | 09/30/2001 | Active | 0 | 0 | 0 | 0 | 0 | 0 | 0 | ||
4504 | 20668, 25513, 30513, 36059, 40151, 45237, 50764, 55489, 60242, 63480, 67318, 71275, 75325, 74017 REL 17, 74017 REL 35, 74017 REL 60, 74017 REL 77, 74017 REL 92, 84044 REL 9, 84044 REL 31, 84044 REL 53 | 2025-003-00 EXP NPT ARTIFICIAL PRODUCTION O&M | Nez Perce Tribe | 01/01/2001 | 12/31/2025 | Issued | 80 | 275 | 35 | 0 | 17 | 327 | 94.80% | 1 |
Project Totals | 80 | 275 | 35 | 0 | 17 | 327 | 94.80% | 1 |
Contract | WE Ref | Contracted Deliverable Title | Due | Completed |
---|---|---|---|---|
25513 | J: 162 | Interpret data for Hatchery Operations | 12/28/2006 | 12/28/2006 |
30513 | K: 132 | 06 Annual Report | 8/13/2007 | 8/13/2007 |
30513 | E: 158 | Marking/Tagging of Juvenile Fish | 10/31/2007 | 10/31/2007 |
30513 | G: 157 | Seasonal Collection & Recording of Data | 12/31/2007 | 12/31/2007 |
30513 | H: 162 | Interpret data for Hatchery Operations | 12/31/2007 | 12/31/2007 |
30513 | C: 176 | Production of spring Chinook | 12/31/2007 | 12/31/2007 |
30513 | D: 176 | Production of fall Chinook | 12/31/2007 | 12/31/2007 |
30513 | F: 61 | Facility & Equipment Maintenance | 12/31/2007 | 12/31/2007 |
36059 | G: 157 | Seasonal Collection & Recording of Data | 12/31/2008 | 12/31/2008 |
36059 | H: 162 | Interpret data for Hatchery Operations | 12/31/2008 | 12/31/2008 |
36059 | B: 176 | Production of spring Chinook | 12/31/2008 | 12/31/2008 |
36059 | C: 176 | Production of fall Chinook | 12/31/2008 | 12/31/2008 |
36059 | F: 61 | Facility & Equipment Maintenance | 12/31/2008 | 12/31/2008 |
40151 | K: 174 | Attach Annual Operation Plan in Pisces | 11/15/2009 | 11/15/2009 |
40151 | L: 132 | Attach 2008 Progress Report in Pisces | 12/20/2009 | 12/20/2009 |
40151 | F: 157 | Seasonal Collection & Recording of Data | 12/31/2009 | 12/31/2009 |
40151 | G: 162 | Interpret data for Hatchery Operations | 12/31/2009 | 12/31/2009 |
40151 | B: 176 | Production of spring Chinook | 12/31/2009 | 12/31/2009 |
40151 | C: 176 | Production of fall Chinook | 12/31/2009 | 12/31/2009 |
40151 | E: 61 | Facility & Equipment Maintenance | 12/31/2009 | 12/31/2009 |
45237 | L: 132 | Attach 2009 Progress Report in Pisces | 5/14/2010 | 5/14/2010 |
View full Project Summary report (lists all Contracted Deliverables and Quantitative Metrics)
Explanation of Performance:NPTHC began full operation in January, 2003. Current production goals are:
1.4M fall Chinook salmon (FCS) annually
825,000 spring Chinook salmon (SCS) annually
Initially, a temporary weir on Meadow Creek was to provide broodstock for the Meadow Creek program. Because of high flows, inaccesibility, and other issues, the weir proved ineffective in adult capture, and was abandoned as a broodstock collection tool. An agreement with IDFG was reached to resolve this challenge. Beginning in 2007, Clearwater Hatchery on the Clearwater River raises 200,000 Rapid River stock SCS for NPTH. In September each year at ~150 fpp, these fish are transferred to NPTH, where they are cultured to release into the Clearwater River as smolts at 20 fpp the following April. Adults returning to the trap at NPTH provide broodstock for the Meadow Creek program, and also act as a backup brood source for other NPTHC SCS programs.
Because this program was new in 2003, and to avoid unnecessary fish losses, a cautious approach was taken in moving toward full production. Facilities and operational systems were tested and changes were made based on real experience. Staff were trained at other facilities and then began work at NPTH once construction was completed and facilities became operational. Broodstock was secured from other facilities, as was production initially. Production has slowly increased based on testing the actual capabilities of the projects facilities, water sources, equipment, etc. NPTHC has targeted and met full FCS production in 2009 and 2010. NPTHC has targeted full SCS production for the first time in 2010, and will either meet or be near that goal.
FALL CHINOOK:
The first year of NPTH fall Chinook releases began in 2003 with Snake River fall Chinook salmon eggs and fry being transferred from Lyons Ferry Hatchery. A total of 505,978 fall Chinook subyearlings were released at NPTH on-station to the Clearwater River and at North Lapwai Valley (NLV) Acclimation Pond in 2003. During 2004, releases were limited to broodstock only from volunteers to the NPTH fish ladder in 2003. Since that time, broodstock has been from both trapping and hauling from Lower Granite Dam along with volunteers to NPTH. The two upriver acclimation sites at Lukes Gulch on the S.F. Clearwater River and Cedar Flats on the Selway River acclimated and released a test group of about 25,000 subyearlings each beginning in 2006 and again in 2007 (Figure 1). Broodstock shortages and facility testing precluded NPTH from reaching full production of fall Chinook until 2009 when there were 1.534 million subyearlings released, slightly over the 1.4 million goal. During 2010, NPTH released just short of 1.4M release goal (1.39M). During all years, target marking goals were met with unique CWTs applied on approximately 43% and CWTs plus adipose clip applied to about 29% of all NPTH and associated releases with the rest being released unmarked.
FCS RELEASE SUMMARY:
This graph below clearly demonstrates a trend of moving toward and now meeting (in 2009 and 2010) the full phase one goal for FCS production at NPTH.
In 2008 and 2009, the NPTH trap was intentionally closed part of the year to target Lower Granite Dam trapped adults, ensuring natural contribution to broodstock for the program. This is important to note because the HSRG suggested avoiding use of Clearwater River adults trapped at Lower Granite Dam for this project. NPTH could trap exclusively at NPTH, and given increasing adult returns may be able to meet full production from NPTH trapping only in future years. However, managers are hesitant to trap only at NPTH because of the desire to incorporate natural fish (captured at Lower Granite Dam) into the broodstock. AT this point, NPTH will continue to prioritize Lower Granite Dam trapped adults ensuring natural contribution and allowing for maximized spawning by both natural and hatchery fish in the Clearwater Subbasin.
2009 eye-up for all FCS eggs at NPTH was 90.8%.
No fish were acclimated or released at North Lapwai Valley in 2004 or 2005 due to broodstock shortages and facility mechanical problems.
SPRING CHINOOK:
NPTH spring Chinook releases began in 2003 with a portion of the broodstock deriving from adult returns to Lolo and Newsome creeks. A total of 615,530 spring Chinook parr and presmolts were released at Lolo, Newsome, and Meadow creeks that year (below). Since that time, broodstock has been contributed from Lolo and Newsome creeks, volunteers to NPTH and additional fish from the Dworshak National Fish Hathcery and Clearwater Fish Hatchery ladders. No fish were released into Meadow Creek in 2005 because flooding that year necessitated early release from NPTH (391,920 parr). Since 2008, a direct smolt release of spring Chinook from NPTH has occurred to provide broodstock for the Meadow Creek program.
SCS RELEASE SUMMARY:
2010 SCS full production should be met for the Lolo Creek and Newsome creek programs. Meadow Creek release was 278,580 after significant losses during early rearing from fungus, cold-water disease, Trichodina, and other pathogens.
Other Performance Measures:
In 2006, basin wide brood shortages meant the Lolo Creek program could not be met.
No Meadow Creek program in 2006 due to broodstock shortages.
The previous information was taken from various NPTH presentations given in 2009 during the NPT's Department of Fisheries Resource Management Symposium held in Orofino Idaho. For additional performance indicators, please see NPTH M&E project #1983-350-03. That projects primary purpose is monitoring and evaluation of this project, and has a host of performance measures and results from NPTH operations.
Regarding meeting deliverables listed above, all AOP's and Annual Progress Reports have been submitted in Pisces on time. Most monthly and quarterly progress reports have also been submitted and uploaded on time. NPTHC has been very effective in meeting reporting and other requirements by BPA and others.
Facility maintenance has been excellent, despite a highly complex primary facility (NPTH) with inherent mechanical and water delivery issues from day one. Staff have learned how to operate and maintain NPTH efficiently within its limitations, and have made changes allowing for full production targets beginning in 2009-10. Remote site challenges have been overcome, and all facilities are now expected to handle the full production they were built for.
Data collection, storage and dissemination has slowly developed from awkward and inconsistent to robust and timely. As mentioned in other sections of this proposal, the NPT's Department of Fisheries Resource Management has invested in technology, time and effort to dramatically improve data access for all interested parties. This includes NPTH, where the manager is currently researching possible database systems for use within NPTHC. This database would interface with others utilized within and outside the NPT, and would allow staff efficient and accurate input of raw data. It would also generate summaries, trends, reports, and other analysis snapshots that would help improve efficiency and drive sound decision making.
Assessment Number: | 1983-350-00-NPCC-20230309 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | 2022 Anadromous Fish Habitat & Hatchery Review |
Approved Date: | 4/15/2022 |
Recommendation: | Implement with Conditions |
Comments: |
Bonneville and Sponsor to consider condition #1 (goals) and #2 (objectives/timeline), and address in project documentation if appropriate. This project supports hatchery mitigation authorized under the Northwest Power Act (Council’s Fish and Wildlife Program) for the Nez Perce Tribal Hatchery and reconditioned steelhead kelt programs. See Policy Issue I.b., II.a. and II.b. [Background: See https://www.nwcouncil.org/2021-2022-anadromous-habitat-and-hatchery-review/] |
Assessment Number: | 1983-350-00-ISRP-20230324 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | 2022 Anadromous Fish Habitat & Hatchery Review |
Completed Date: | None |
Documentation Links: |
|
Assessment Number: | 1983-350-00-NPCC-20110125 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | RME / AP Category Review |
Proposal: | RMECAT-1983-350-00 |
Proposal State: | Pending BPA Response |
Approved Date: | 6/10/2011 |
Recommendation: | Fund (Qualified) |
Comments: | Implement with condition through 2016: Implementation subject to regional hatchery effects evaluation process described in programmatic recommendation #4. |
Conditions: | |
Council Condition #1 Programmatic Issue: RMECAT #4 Hatchery Effectiveness—Subject to regional hatchery effects evaluation process |
Assessment Number: | 1983-350-00-ISRP-20101015 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | RME / AP Category Review |
Proposal Number: | RMECAT-1983-350-00 |
Completed Date: | 12/17/2010 |
Final Round ISRP Date: | 12/17/2010 |
Final Round ISRP Rating: | Meets Scientific Review Criteria |
Final Round ISRP Comment: | |
This meets criteria but also see comments on the M&E proposal 198335003.
Now that the program has shown that it can produce fall and spring Chinook that return to the Clearwater River as adults, perhaps it is time to begin to consider whether (and to what extent) the effort will yield self-sustaining runs of natural origin. The next iteration of the project needs to begin to address whether and how self-sustaining Clearwater River salmon runs will be achieved. Thus, while the NPT has done a good job in guiding the NPTH to this point, the ISRP’s longstanding concerns about the viability of the supplementation approach to rebuild self-sustaining natural reproduction in Idaho rives and streams remains unanswered. 1. Purpose, Significance to Regional Programs, Technical Background, and Objectives The proponents do a good job of describing the history of the project and how it fits into regional Fish and Wildlife Program and AP planning. Technical background, along with the growth and evolution of the NPTH program is well described. 2. History: Accomplishments, Results, and Adaptive Management Past ISRP concerns that project results were not being adequately described have been effectively dealt with by the very commendable January 2009 Orofino symposium. The current proposal summarizes material presented at the symposium but often provides inadequate narrative for those who did not have the opportunity to attend the symposium. The proponents do a very good job of describing the project’s history and evolution, as well as to a lesser degree, how they went about solving unforeseen problems, mostly associated with low return of adults or with limited water supply. It is evident that the hatchery was built at a site having unsuitable water supply. The hatchery is reported to be operating better than in its first few years, however. Within the last year or so, production has increased to the point that objectives are being met or nearly so in terms of numbers of released fish. One of the four or so apparent current “issues” with the project is whether the basic requirements for fish production are adequate at the NPTH facility. From the proposal it appears that ongoing improvements (of a wide variety) are adequate for the near future and that issue no longer exists. Another issue is survival of juveniles immediately after release. It was mentioned at the symposium that results from tagging juveniles at Newsome Creek showed very high mortality by Lower Granite dam. It is important to understand relationships among fish size at release, time of movement from acclimation site, whether release is volitional or forced, and the habitat used by those fish as they overwinter. Granted, such monitoring should be (is?) done by another project (NPT M&E) but results need to be closely linked to this project so the best release strategies can be developed. Currently it does not appear that is receiving adequate attention. Production goals for both spring and fall Chinook, in terms of numbers of juveniles leaving the various acclimation facilities, now seem close to being met. The obvious question now is whether those are the most appropriate production goals. Because the ultimate goal must be natural production, and the project duration is “until natural production in target streams can support exclusively the fishery management principles, goals and objectives listed above,” the key issue is whether the project is indeed moving toward that goal. Objectives are not being met in terms of proportion of natural influence (PNI). The proportions of natural-origin adults in hatchery broodstocks (pNOB) are too low, and the proportions of hatchery-origin adults among naturally spawning fish (pHOS) are too high, therefore the PNI values are too low. For the ISRP to evaluate progress toward meeting PNI objectives, it would help for the proponents to provide the pNOB, pHOS, and PNI results for each year of hatchery operation. SARs for the FCS and SCS components are roughly 0.1% and 0.3%, respectively. For natural production to be self-sustaining, SARs will have to increase by an order of magnitude. How can this be achieved? The next iteration of the project should start to address these issues and describe a plan for achieving them, otherwise, there will never be a termination date for the artificial production efforts on this project and the ultimate goals will never be achieved. 3. Project Relationships, Emerging Limiting Factors, and Tailored Questions for Type of Work (Hatchery, RME, Tagging) Adequately described. 4. Deliverables, Work Elements, Metrics, and Methods Adequately described. |
|
First Round ISRP Date: | 10/18/2010 |
First Round ISRP Rating: | Meets Scientific Review Criteria |
First Round ISRP Comment: | |
This meets criteria but also see comments on the M&E proposal 198335003. Now that the program has shown that it can produce fall and spring Chinook that return to the Clearwater River as adults, perhaps it is time to begin to consider whether (and to what extent) the effort will yield self-sustaining runs of natural origin. The next iteration of the project needs to begin to address whether and how self-sustaining Clearwater River salmon runs will be achieved. Thus, while the NPT has done a good job in guiding the NPTH to this point, the ISRP’s longstanding concerns about the viability of the supplementation approach to rebuild self-sustaining natural reproduction in Idaho rives and streams remains unanswered. 1. Purpose, Significance to Regional Programs, Technical Background, and Objectives The proponents do a good job of describing the history of the project and how it fits into regional Fish and Wildlife Program and AP planning. Technical background, along with the growth and evolution of the NPTH program is well described. 2. History: Accomplishments, Results, and Adaptive Management Past ISRP concerns that project results were not being adequately described have been effectively dealt with by the very commendable January 2009 Orofino symposium. The current proposal summarizes material presented at the symposium but often provides inadequate narrative for those who did not have the opportunity to attend the symposium. The proponents do a very good job of describing the project’s history and evolution, as well as to a lesser degree, how they went about solving unforeseen problems, mostly associated with low return of adults or with limited water supply. It is evident that the hatchery was built at a site having unsuitable water supply. The hatchery is reported to be operating better than in its first few years, however. Within the last year or so, production has increased to the point that objectives are being met or nearly so in terms of numbers of released fish. One of the four or so apparent current “issues” with the project is whether the basic requirements for fish production are adequate at the NPTH facility. From the proposal it appears that ongoing improvements (of a wide variety) are adequate for the near future and that issue no longer exists. Another issue is survival of juveniles immediately after release. It was mentioned at the symposium that results from tagging juveniles at Newsome Creek showed very high mortality by Lower Granite dam. It is important to understand relationships among fish size at release, time of movement from acclimation site, whether release is volitional or forced, and the habitat used by those fish as they overwinter. Granted, such monitoring should be (is?) done by another project (NPT M&E) but results need to be closely linked to this project so the best release strategies can be developed. Currently it does not appear that is receiving adequate attention. Production goals for both spring and fall Chinook, in terms of numbers of juveniles leaving the various acclimation facilities, now seem close to being met. The obvious question now is whether those are the most appropriate production goals. Because the ultimate goal must be natural production, and the project duration is “until natural production in target streams can support exclusively the fishery management principles, goals and objectives listed above,” the key issue is whether the project is indeed moving toward that goal. Objectives are not being met in terms of proportion of natural influence (PNI). The proportions of natural-origin adults in hatchery broodstocks (pNOB) are too low, and the proportions of hatchery-origin adults among naturally spawning fish (pHOS) are too high, therefore the PNI values are too low. For the ISRP to evaluate progress toward meeting PNI objectives, it would help for the proponents to provide the pNOB, pHOS, and PNI results for each year of hatchery operation. SARs for the FCS and SCS components are roughly 0.1% and 0.3%, respectively. For natural production to be self-sustaining, SARs will have to increase by an order of magnitude. How can this be achieved? The next iteration of the project should start to address these issues and describe a plan for achieving them, otherwise, there will never be a termination date for the artificial production efforts on this project and the ultimate goals will never be achieved. 3. Project Relationships, Emerging Limiting Factors, and Tailored Questions for Type of Work (Hatchery, RME, Tagging) Adequately described. 4. Deliverables, Work Elements, Metrics, and Methods Adequately described. |
|
Documentation Links: |
|
Assessment Number: | 1983-350-00-NPCC-20090924 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | FY07-09 Solicitation Review |
Approved Date: | 10/23/2006 |
Recommendation: | Fund |
Comments: | Flat line '07 requested amount - this level was reflected in the Step 3 NPTH decision (May 17, 2000). Other associated life histories (coho) not prioritized. |
Assessment Number: | 1983-350-00-ISRP-20060831 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | FY07-09 Solicitation Review |
Completed Date: | 8/31/2006 |
Final Round ISRP Date: | None |
Final Round ISRP Rating: | Meets Scientific Review Criteria |
Final Round ISRP Comment: | |
While the ISRP recommends the project as fundable, the ISRP also expects the sponsors to do a better job of reporting results in their future proposals. The Project History reports only actions performed, e.g., the planning and creation of the hatchery, and numbers of fish of different sorts stocked each year since releases began in 2003. Adult return rates cannot yet be reported, of course, but it would be helpful to have information for each released group on egg-to-smolt survival and on smolt survival to points downstream. Reasons for variation in such results should be discussed, including comparison with literature values.
In their response, the sponsors provided additional data and explanations, and these seem adequate; however, in future review cycles, sponsors could do a better job of following the topical outline for proposals. |
|
Documentation Links: |
|
ID | Title | Type | Period | Contract | Uploaded |
36809-1 | Nez Perce Tribal Hatchery | Progress (Annual) Report | 10/1990 - 09/1991 | 3/1/1992 12:00:00 AM | |
36809-2 | Monitoring and Evaluation Plan for the Nez Perce Tribal Hatchery | Progress (Annual) Report | 10/1995 - 09/1996 | 8/1/1996 12:00:00 AM | |
00004504-2 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 01/1998 - 12/1998 | 4504 | 1/27/2000 12:00:00 AM |
00004504-1 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 01/1999 - 12/1999 | 4504 | 8/17/2001 12:00:00 AM |
00004504-3 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 10/1999 - 09/2000 | 4504 | 12/31/2002 12:00:00 AM |
00004504-7 | Nez Perce Tribal Hatchery Complex | Progress (Annual) Report | 01/2004 - 12/2004 | 4504 | 2/1/2005 12:00:00 AM |
00004504-5 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 10/2001 - 09/2002 | 4504 | 12/1/2005 12:00:00 AM |
00004504-6 | Nez Perce Tribal Hatchery Complex | Progress (Annual) Report | 01/2003 - 12/2004 | 4504 | 12/1/2005 12:00:00 AM |
00020668-1 | Nez Perce Tribal Hatchery Complex | Progress (Annual) Report | 01/2005 - 12/2005 | 20668 | 2/1/2006 12:00:00 AM |
00020668-2 | Nez Perce Tribal Hatchery Complex | Progress (Annual) Report | 01/2005 - 12/2005 | 20668 | 2/1/2006 12:00:00 AM |
00004504-4 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 10/2000 - 09/2001 | 4504 | 3/1/2006 12:00:00 AM |
00004035-1 | Nez Perce Tribal Hatchery Project | Progress (Annual) Report | 10/2002 - 09/2004 | 4035 | 6/1/2006 12:00:00 AM |
P102763 | NPTH 2006 Annual Report Final | Progress (Annual) Report | 01/2006 - 12/2006 | 30513 | 7/11/2007 10:52:45 AM |
P103727 | NPTH 2007 Annual Operations Plan | Management Plan | - | 30513 | 9/26/2007 9:00:29 AM |
P105453 | 2007 Nez Perce Tribal Hatchery Complex Annual Report | Progress (Annual) Report | 01/2007 - 12/2007 | 36059 | 2/1/2008 2:13:58 PM |
P107762 | 2004 Clearwater Coho Master Plan | Management Plan | - | 8/13/2008 3:45:43 PM | |
P109352 | Water Permit from Idaho | Other | - | 12/8/2008 1:50:03 PM | |
P112435 | 2008 NPTHC Annual Operation Report 5 May 09.doc | Progress (Annual) Report | 01/2008 - 12/2008 | 40151 | 7/13/2009 1:15:53 PM |
P113226 | Lamprey being innoculated | Photo | - | 45237 | 8/27/2009 10:40:10 AM |
P113784 | FY2009 NPTHC Annual Operation Plan | Management Plan | - | 40151 | 10/15/2009 8:33:55 AM |
P116359 | Nez Perce Tribal Hatchery Complex | Progress (Annual) Report | 01/2009 - 12/2009 | 45237 | 5/14/2010 2:14:07 PM |
P116505 | NPTH Two Residence BOG May 26 2010 | Other | - | 5/26/2010 3:31:17 PM | |
P116545 | Oct 2002 letter from NPT to BPA RE: future housing needs at NPTH | Other | - | 6/1/2010 1:22:13 PM | |
P116550 | 2000 letter from Council to BPA re: NPTH | Other | - | 6/1/2010 2:34:08 PM | |
P116551 | September 2000 letter from BPA to Council re: NPTH | Other | - | 6/1/2010 2:34:57 PM | |
P120489 | 1-28-2011 letter from Steve Wright to Chairman McCoy Oatman re. Housing | Other | - | 3/16/2011 3:28:23 PM | |
P120791 | NPTHC 2009 Annual (Progress) Report FINAL | Progress (Annual) Report | 01/2009 - 12/2009 | 50764 | 4/11/2011 2:07:08 PM |
P121795 | 2010 NPTHC Annual Report | Progress (Annual) Report | 01/2010 - 12/2010 | 50764 | 6/28/2011 11:40:55 AM |
P123237 | Nez Perce Tribal Hatchery Complex, 1/08 - 12/08 | Progress (Annual) Report | 01/2008 - 12/2008 | 40151 | 10/10/2011 10:48:52 AM |
P131033 | Nez Perce Tribal Hatchery Complex; 1/10 - 12/10 | Progress (Annual) Report | 01/2010 - 12/2010 | 55489 | 3/4/2013 3:05:16 PM |
P132646 | Nez Perce Tribal Hatchery Complex; 1/11 - 12/11 | Progress (Annual) Report | 01/2011 - 12/2011 | 60242 | 7/9/2013 9:57:03 AM |
P147463 | Nez Perce Tribal Hatchery Complex; 1/12/- 12/12 | Progress (Annual) Report | 01/2012 - 12/2012 | 67318 | 2/18/2016 9:40:41 AM |
P160598 | Nez Perce Tribal Hatcher Complex; 1/13 - 12/13 | Progress (Annual) Report | 01/2013 - 12/2013 | 74017 REL 17 | 5/25/2018 2:31:18 PM |
P160770 | Nez Perce Tribal Hatchery Complex; 1/14 - 12/14 | Progress (Annual) Report | 01/2014 - 12/2014 | 74017 REL 17 | 6/11/2018 11:19:40 AM |
P160771 | Nez Perce Tribal Hatchery Complex; 1/16 - 12/16 | Progress (Annual) Report | 01/2016 - 12/2016 | 74017 REL 17 | 6/11/2018 11:20:51 AM |
P162056 | Nez Perce Tribal Hatchery Complex; 1/15 - 12/15 | Progress (Annual) Report | 01/2015 - 12/2015 | 74017 REL 17 | 9/19/2018 11:48:16 AM |
P169583 | Nez Perce Tribal Hatchery Complex; 1/18 - 12/18 | Progress (Annual) Report | 01/2018 - 12/2018 | 74017 REL 35 | 12/16/2019 2:40:41 PM |
P175075 | 2010 NPTHC Annual Report | Photo | - | 5/7/2020 5:44:05 PM | |
P180361 | FINAL NPTH 2019 Annual Report 1/19-12/19 | Progress (Annual) Report | 01/2019 - 12/2019 | 74017 REL 60 | 12/4/2020 11:40:29 AM |
Project Relationships: |
This project Merged To 2025-003-00 effective on 10/1/2024
Relationship Description: Work and budgets from projects: 1983-350-00 NPT Hatchery O&M, 1996-043-00 Johnson Creek Artificial Prop. O&M, and 1998-007-02 Grand Ronde Supplementation O&M are merging to become project 2025-003-00. |
---|
Additional Relationships Explanation:
Snake River FCS are listed as an Evolutionary Significant Unit (ESU) and considered to be part of a single genetically similar aggregate and are managed as a single population. The NPTH program is integrated with production at Lyons Ferry Hatchery (WDFW), the Fall Chinook Acclimation Program (project 1998-010-05), and the Idaho Power Company (IPC) mitigation program. Currently broodstock are obtained from two primary sources: volunteers to the ladder at NPTH and adults collected at Lower Granite Dam (LGR). Broodstock collection protocols at LGR are determined annually by the comanagers. Typically, 30% of the trapped adults are transported to NPTH and 70% to LFH, targeting even distribution of females for spawning. Fish hauling schedules to meet this ratio (along with sex and origin ratios) are coordinated between WDFW and NPT to ensure mutual success, and adjustments are made by both programs as needed. Coordination of all activities by these parties related to Snake River fall Chinook is agreed to each year through the Lyons Ferry Annual Operation Plan. A weekly webinar is conducted by the co-managers during FCS adult returns to manage fisheries, maximize the resource, and communicate status/trends.
Baseline FCS data collection for adult spawner abundance, spawn timing, and habitat evaluations has been occurring in the Clearwater River and major tributaries including the South Fork Clearwater River, Main Fork Clearwater River and lower Selway River since 1988. M&E of fish produced in NPTHC facilities began in 2003. Standardized performance measures quantified and utilized in program performance evaluations are described in Appendix A, Table A.2 of the 2010 Nez Perce Tribal Hatchery Complex Annual Operation Plan. Some small scale production experiments may also occur as part of the M&E program.
SCS in the Clearwater River Subbasin were essentially extirpated by Lewiston Dam (Schoen et al. 1999; USFWS 1999; Murphy and Metsker 1962). However, naturalized populations have been re-established in Lolo Creek and mainstem/tributary reaches of the Lochsa, Selway and South Fork (S.F.) Clearwater rivers (Larson and Mobrand 1992). Founding hatchery stocks used to re-colonize SCS were primarily obtained from the Rapid River Hatchery. Genetic analysis has confirmed that existing natural SCS in the Clearwater River Subbasin are derived from reintroduced Snake River stocks. Some small scale production experiments may also occur as part of the M&E program.
NPTHC works with Dworshak National Fish Hatchery (USFWS), Kooskia Tribal Hatchery (NPT), and Clearwater Anadromous Hatchery (IDFG) in a coordinated approach to SCS supplementation in the Clearwater Basin. All actions and plans are developed and agreed to by these parties in the Clearwater Annual Operation Plan. Fish transport and outplant, broodstock capture, surplus distribution, spawning and other work is done cooperatively. These programs frequently assist each other through equipment or staff sharing to meet common work objectives. A weekly webinar is conducted by the co-managers during SCS adult returns to manage fisheries, maximize the resource, and communicate status/trends.
Baseline SCS data collection for adult spawner abundance and spawn timing has been occurring in Lolo and Newsome creeks since 1987 and in Meadow Creek since 1993. Juvenile production and survival data collection has been occurring in Lolo and Meadow creeks since 1993 and in Newsome Creek since 1995. Various habitat evaluations have occurred in the three creeks since 1991. Monitoring and evaluation (M&E) of SCS produced in NPTHC facilities began in 2003. Standardized performance measures quantified and utilized in program performance evaluations are described in Appendix A, Table A.2 of the 2010 Nez Perce Tribal Hatchery Complex Annual Operation Plan. Some small scale production experiments may also occur as part of the M&E program.
All monitoring and evaluation for this project (both FCS and SCS) is conducted by BPA project 1983-350-03. Data is collected and shared between the two projects to meet reporting requirements, and to facilitate decision-making by resource managers. A detailed monitoring and evaluation plan for the NPTHC has been developed and is available on request (Monitoring and Evaluation Plan for The NPTH: Action Plan, Hesse and Cramer 2000). All aspects of ongoing or proposed M&E are discussed in detail in that document and subsequent M&E annual reports.
Results for all project M&E studies can be found on the Bonneville Power Administration’s (BPA) report website at https://efw.bpa.gov/IntegratedFWP/reportcenter.aspx.
All NPTHC fish health monitoring is conducted through the USFWS Idaho Fish Health Center, which provides this service for both DNFH and Kooskia Hatchery as well. A multi-year contract covers this work, and specifics are addressed during the Clearwater Annual Operation Plan process.
An additional collaborative effort is being conducted between the NPT's Lamprey Restoration Initiative and NPTHC. Although BPA does not fund any portion of this initiative, beginning in 2006 they agreed to let lampreys be held at NPTH after collection at Columbia River dams in the fall/winter and prior to outplanting the following spring. They agreed to this as long as no work was conducted by NPTHC employees or dollars spent from the project on this activity, and as long as fish health risks were absolutely minimized since lampreys are known carriers of frunculosis. NPTHC has submitted a lamprey risk assesment to BPA via Pisces analyzing the risk, and NPT Department of Fisheries Resource Management employees that work on the initiative submit a lamprey activities document each year to BPA, also through Pisces.
Related project list:
BPA 198335003 Nez Perce Tribal Hatchery M&E This project provides a comprehensive monitoring and evaluation of NPTH Phase I production of fall and spring Chinook salmon.
BPA 199901700 Rehabilitate Lapwai Creek This project involves channel revegetation, riparian fencing and culvert assessment/replacement. Improvement in water quality will benefit the operation of the North Lapwai Valley Acclimation Facility
Other: LSRCP 200101 Idaho Fish Health Center This project provides subcontract fish health monitoring services for fall and spring Chinook salmon within NPTHC.
Other: LSRCP 200112 Lyons Ferry Hatchery/WDFW. NPTH production is closely coordinate with Snake River fall Chinook at Lyons Ferry. Both facilities share broodstock collected at Lower Granite Dam. An annual operation plan provides coordination specifics between projects.
BPA 200203200 Fall Chin Passage Lower Granite Dam. This project provides fall Chinook broodstock (goal: 30% of fish trapped are transported to NPTH for broodstock)
Other: LSRCP USFWS Dworshak Hatchery This project provides NPTH with spring Chinook broodstock that is surplus to LSRCP production needs. An annual operation plan provides coordination specifics between projects.
Other: LSRCP USFWS Clearwater Hatchery/IDFG. This project provides NPTH with spring Chinook broodstock that is surplus to LSRCP production needs. An annual operation plan provides coordination specifics between projects.
LSRCP # 200112 - Lyons Ferry Hatchery ------ Production of yearling and sub-yearling fall Chinook salmon for on-station releases and outplants above Lower Granite Dam.
LSRCP #200118 - LSRCP Fall Chinook Production & Evaluation Prog. ----- Evaluate yearling and sub-yearling fall Chinook salmon released on-station from LFH. Run reconstruction of adult fall Chinook returns to Lower Granite Dam.
Idaho Power Corporation - ICP Fall Chinook Program ----- Spawning ground surveys in the Snake River. Production of fall Chinook salmon for release below Hells Canyon Dam. Habitat quality in Snake River above and below Hells Canyon Dam Complex.
200301700 - Integrated Status Effectiveness Monitoring Project. Provide (i) subbasin-scale pilot status and trend monitoring efforts for anadromous salmonids and their habitat in the South Fork Salmon River basin, and (ii) effectiveness monitoring for suites of habitat restoration projects in selected watersheds within the three target subbasins.
BPA 198909802 – Salmon Supplementation Studies in Idaho Rivers. Evaluate various supplementation strategies for maintaining and rebuilding spring/summer Chinook populations in Idaho.
BPA 199403300 - Fish Passage Center’s Smolt Monitoring Project. Juvenile and natural salmon produced in relation to these facilities will provide release and migration data for in-river information on migration timing and survival.
BPA 199600800 - PATH (Plan for Analyzing and Testing Hypotheses). Naturally produced juveniles from targeted streams will provide data for life cycle model
BPA 199703800 - Listed Stock Chinook Salmon Gamete Preservation (Cryopreservation).
pNOB | pHOS | PNI | |
Target | <div class="userEnteredValue">0.30</div> | <div class="userEnteredValue">0.70</div> | 0.30 |
Realized | <div class="userEnteredValue">0.14</div> | <div class="userEnteredValue">0.77</div> | 0.15 |
pNOB | pHOS | PNI | |
Target | <div class="userEnteredValue">0.75</div> | <div class="userEnteredValue">0.75</div> | 0.50 |
Realized | <div class="userEnteredValue">0.10</div> | <div class="userEnteredValue">0.32</div> | 0.24 |
pNOB | pHOS | PNI | |
Target | <div class="userEnteredValue">0.75</div> | <div class="userEnteredValue">0.75</div> | 0.50 |
Realized | <div class="userEnteredValue">0.10</div> | <div class="userEnteredValue">0.32</div> | 0.24 |
pNOB | pHOS | PNI | |
Target | <div class="userEnteredValue">0.75</div> | <div class="userEnteredValue">0.75</div> | 0.50 |
Realized | <div class="userEnteredValue">0.10</div> | <div class="userEnteredValue">0.32</div> | 0.24 |
pNOB | pHOS | PNI | |
Target | <div class="userEnteredValue">0.75</div> | <div class="userEnteredValue">0.75</div> | 0.50 |
Realized | <div class="userEnteredValue">0.10</div> | <div class="userEnteredValue">0.32</div> | 0.24 |
Name (Identifier) | Area Type | Source for Limiting Factor Information | |
---|---|---|---|
Type of Location | Count | ||
Gedney Creek-Selway River (1706030204) | HUC 5 | Expert Panel Assessment Unit | 2 |
Upper South Fork Clearwater River (1706030505) | HUC 5 | Expert Panel Assessment Unit | 3 |
Middle South Fork Clearwater River (1706030507) | HUC 5 | Expert Panel Assessment Unit | 3 |
Cottonwood Creek (1706030607) | HUC 5 | Expert Panel Assessment Unit | 1 |
Lower Clearwater River (1706030613) | HUC 5 | Expert Panel Assessment Unit | 1 |
Glade Creek-Lochsa River (170603030708) | HUC 6 | Expert Panel Assessment Unit | 3 |
Big Smith Creek-Middle Fork Clearwater River (170603040201) | HUC 6 | Expert Panel Assessment Unit | 1 |
Maggie Creek (170603040202) | HUC 6 | Expert Panel Assessment Unit | 1 |
Suttler Creek-Middle Fork Clearwater River (170603040203) | HUC 6 | Expert Panel Assessment Unit | 1 |
Lower Newsome Creek (170603050402) | HUC 6 | Expert Panel Assessment Unit | 1 |
Threemile Creek (170603050902) | HUC 6 | Expert Panel Assessment Unit | 1 |
Suzie Creek-Lawyer Creek (170603060107) | HUC 6 | Expert Panel Assessment Unit | 1 |
Upper Lolo Creek (170603060201) | HUC 6 | Expert Panel Assessment Unit | 1 |
Musselshell Creek (170603060202) | HUC 6 | Expert Panel Assessment Unit | 2 |
Middle Lolo Creek (170603060204) | HUC 6 | Expert Panel Assessment Unit | 1 |
Lower Lolo Creek (170603060205) | HUC 6 | Expert Panel Assessment Unit | 1 |
Upper Jim Ford Creek (170603060301) | HUC 6 | Expert Panel Assessment Unit | 1 |
Tom Taha Creek-Clearwater River (170603060501) | HUC 6 | Expert Panel Assessment Unit | 2 |
Fivemile Creek-Clearwater River (170603060503) | HUC 6 | Expert Panel Assessment Unit | 2 |
Big Creek-Clearwater River (170603060504) | HUC 6 | Expert Panel Assessment Unit | 1 |
Howard Gulch-Potlatch River (170603061103) | HUC 6 | Expert Panel Assessment Unit | 1 |
Sweetwater Creek (170603061205) | HUC 6 | Expert Panel Assessment Unit | 1 |
Lower Lapwai Creek (170603061206) | HUC 6 | Expert Panel Assessment Unit | 1 |
Wheeler Canyon-Clearwater River (170603061302) | HUC 6 | Expert Panel Assessment Unit | 1 |
Rattlesnake Canyon-Clearwater River (170603061305) | HUC 6 | Expert Panel Assessment Unit | 1 |
Hatwai Creek (170603061306) | HUC 6 | Expert Panel Assessment Unit | 1 |
Lindsay Creek (170603061307) | HUC 6 | Expert Panel Assessment Unit | 1 |
Catholic Creek-Clearwater River (170603061308) | HUC 6 | Expert Panel Assessment Unit | 1 |
Freeman Creek-North Fork Clearwater River (170603080804) | HUC 6 | None | |
Headwaters Meadow Creek (170603020301) | HUC 6 | Expert Panel Assessment Unit | 1 |
Middle Meadow Creek (170603020304) | HUC 6 | Expert Panel Assessment Unit | 1 |
Lower Meadow Creek (170603020307) | HUC 6 | Expert Panel Assessment Unit | 1 |
Gedney Creek (170603020401) | HUC 6 | Expert Panel Assessment Unit | 1 |
Redbird Creek-Snake River (170601030305) | HUC 6 | EDT (Ecosystem Diagnosis and Treatment) | 1 |
Tammany Creek (170601030306) | HUC 6 | None | |
The Dalles Dam to John Day Dam | Mainstem | None | |
John Day Dam | Mainstem | None | |
The Dalles Dam | Mainstem | None | |
Confluence of Snake and Columbia River to Priest Rapids Dam | Mainstem | None | |
Ice Harbor Dam to Lower Monumental Dam | Mainstem | None | |
Confluence of Snake and Columbia River to Ice Harbor Dam | Mainstem | None | |
McNary Dam to Confluence of Snake and Columbia River | Mainstem | None | |
John Day Dam to McNary Dam | Mainstem | None | |
Priest Rapids Dam to Wanapum Dam | Mainstem | None | |
McNary Dam | Mainstem | None | |
Ice Harbor Dam | Mainstem | None | |
Priest Rapids Dam | Mainstem | None | |
Lower Monumental Dam | Mainstem | None | |
Little Goose Dam | Mainstem | None | |
Little Goose Dam to Lower Granite Dam | Mainstem | None | |
Lower Monumental Dam to Little Goose Dam | Mainstem | None | |
Lower Granite Dam | Mainstem | None | |
Lower Granite Dam to Hells Canyon Dam | Mainstem | None | |
Wanapum Dam | Mainstem | None | |
Dworshak Dam | Mainstem | None | |
Chief Joseph Dam to Grand Coulee Dam | Mainstem | None | |
Wells Dam to Chief Joseph Dam | Mainstem | None | |
Chief Joseph Dam | Mainstem | None | |
Grand Coulee Dam to Keenleyside Dam | Mainstem | None | |
Wells Dam | Mainstem | None | |
Rocky Reach Dam to Wells Dam | Mainstem | None | |
Rocky Reach Dam | Mainstem | None | |
Rock Island Dam to Rocky Reach Dam | Mainstem | None | |
Wanapum Dam to Rock Island Dam | Mainstem | None | |
Rock Island Dam | Mainstem | None | |
Grand Coulee Dam | Mainstem | None | |
Bonneville Dam to The Dalles Dam | Mainstem | None | |
Bonneville Dam - Powerhouse 1 | Mainstem | None | |
Bonneville Dam - Spillway | Mainstem | None | |
Bonneville Dam - Powerhouse 2 | Mainstem | None | |
Dworshak Reservoir | Mainstem | None | |
Hells Canyon Dam | Mainstem | None | |
Hungry Horse Dam beginning of Hungry Horse Reservoir | Mainstem | None | |
Kerr Dam | Mainstem | None | |
Kerr Dam to Hungry Horse Dam | Mainstem | None | |
Hungry Horse Dam | Mainstem | None | |
Libby Dam to end of Mainstem Kootenay River | Mainstem | None | |
Corra Linn Dam to Libby Dam | Mainstem | None | |
Libby Dam | Mainstem | None | |
Albeni Falls Dam into Lake Pend Oreille | Mainstem | None | |
Box Canyon Dam to Albeni Falls Dam | Mainstem | None | |
Albeni Falls Dam | Mainstem | None | |
Confluence of Snake and Clearwater River to Dworshak Dam | Mainstem | None | |
Confluence of MF and CF Willamette River to Confluence of MF Willamette River and Fall Creek | Mainstem | None | |
Detroit Reservoir | Mainstem | None | |
Detroit Dam | Mainstem | None | |
Big Cliff Dam to Detroit Dam | Mainstem | None | |
Green Peter Reservoir | Mainstem | None | |
Foster Dam to Green Peter Dam | Mainstem | None | |
Confluence of North and South Santiam River to Foster Dam | Mainstem | None | |
Confluence of North and South Santiam River to Big Cliff Dam | Mainstem | None | |
Confluence of Willamette and Santiam River to Confluence of North and South Santiam River | Mainstem | None | |
Big Cliff Dam | Mainstem | None | |
Foster Dam | Mainstem | None | |
Green Peter Dam | Mainstem | None | |
Fern Ridge Reservoir | Mainstem | None | |
Confluence of Willamette and Long Tom River to Fern Ridge Dam | Mainstem | None | |
Fern Ridge Dam | Mainstem | None | |
Dexter Dam to Lookout Point Dam | Mainstem | None | |
Lookout Point Dam to Hills Creek Dam | Mainstem | None | |
Fall Creek Reservoir | Mainstem | None | |
Blue River Lake | Mainstem | None | |
Cougar Reservoir | Mainstem | None | |
Leaburg Dam to Confluence of McKenzie and Blue River | Mainstem | None | |
Confluence of Willamette and McKenzie River to Leaburg Dam | Mainstem | None | |
Leaburg Dam | Mainstem | None | |
Confluence of McKenzie and Blue River to Blue River Dam | Mainstem | None | |
Blue River Dam | Mainstem | None | |
Confluence of McKenzie and South Fork McKenzie River to Cougar Dam | Mainstem | None | |
Cougar Dam | Mainstem | None | |
Confluence of McKenzie and Blue River to Confluence of McKenzie and South Fork McKenzie River | Mainstem | None | |
Confluence of Willamette and Columbia River to Confluence of MF Willamette and CF Willamette River | Mainstem | None | |
Confluence of MF Willamette River and Fall Creek to Fall Creek Dam | Mainstem | None | |
Confluence of MF Willamette River and Fall Creek to Dexter Dam | Mainstem | None | |
Fall Creek Dam | Mainstem | None | |
Lookout Point Dam | Mainstem | None | |
Dexter Dam | Mainstem | None | |
Hills Creek Reservoir | Mainstem | None | |
Hills Creek Dam | Mainstem | None | |
Cottage Grove Lake | Mainstem | None | |
Dorena Lake | Mainstem | None | |
Confluence of MF and CF Willamette River to Confluence of CF Willamette and Row River | Mainstem | None | |
Dorena Dam | Mainstem | None | |
Confluence of CF Willamette River and Row River to Cottage Grove Dam | Mainstem | None | |
Cottage Grove Dam | Mainstem | None | |
Confluence of CF Willamette River and Row River to Dorena Dam | Mainstem | None |
Work Class | Work Elements | ||||
Hatchery |
|
||||
Planning and Coordination |
|
||||
Research, Monitoring, and Evaluation + Data Management |
|
Work Class | Work Elements | ||||
Hatchery |
|
||||
Planning and Coordination |
|
||||
Research, Monitoring, and Evaluation + Data Management |
|
Work Class | Work Elements | ||||||||||||||
Planning and Coordination |
|
||||||||||||||
Research, Monitoring, and Evaluation + Data Management |
|
Work Class | Work Elements | ||||||
Hatchery |
|
||||||
Planning and Coordination |
|
Work Class | Work Elements | ||||||||
Planning and Coordination |
|
||||||||
Research, Monitoring, and Evaluation + Data Management |
|
Project Deliverables | How the project deliverables help meet this objective* |
---|---|
Salmon Production - Fall Chinook (DELV-1) | |
|
Project Deliverables | How the project deliverables help meet this objective* |
---|---|
Salmon Production - Spring Chinook (DELV-2) | |
|
Project Deliverables | How the project deliverables help meet this objective* |
---|---|
Project Management and Regional Coordination (DELV-3) | |
|
|
Provide Timely Exchange of Science-Based Information (DELV-5) | |
|
Project Deliverables | How the project deliverables help meet this objective* |
---|---|
Facility and Equipment Maintenance/Capital Improvements (DELV-4) | |
|
Project Deliverables | How the project deliverables help meet this objective* |
---|---|
Provide Timely Exchange of Science-Based Information (DELV-5) | |
|
Project Deliverable | Start | End | Budget |
---|---|---|---|
Salmon Production - Fall Chinook (DELV-1) | 2012 | 2016 | $5,218,346 |
Salmon Production - Spring Chinook (DELV-2) | 2012 | 2016 | $5,306,835 |
Project Management and Regional Coordination (DELV-3) | 2012 | 2016 | $489,697 |
Facility and Equipment Maintenance/Capital Improvements (DELV-4) | 2012 | 2016 | $689,962 |
Provide Timely Exchange of Science-Based Information (DELV-5) | 2012 | 2016 | $47,756 |
Total | $11,752,596 |
Fiscal Year | Proposal Budget Limit | Actual Request | Explanation of amount above FY2010 |
---|---|---|---|
2012 | $2,213,655 | Includes 3% annual increase from FY10 funding, and .083 FTE ($8,985) for a new DFRM Data Steward (new cost). | |
2013 | $2,280,065 | Includes 3% annual increase from FY10 funding, and .083 FTE ($8,985) for a new DFRM Data Steward (new cost). | |
2014 | $2,348,467 | Includes 3% annual increase from FY10 funding, and .083 FTE ($8,985) for a new DFRM Data Steward (new cost). | |
2015 | $2,418,921 | Includes 3% annual increase from FY10 funding, and .083 FTE ($8,985) for a new DFRM Data Steward (new cost). | |
2016 | $2,491,488 | Includes 3% annual increase from FY10 funding, and .083 FTE ($8,985) for a new DFRM Data Steward (new cost). | |
Total | $0 | $11,752,596 |
Item | Notes | FY 2012 | FY 2013 | FY 2014 | FY 2015 | FY 2016 |
---|---|---|---|---|---|---|
Personnel | Salaries, benefits, OT, holiday pay, etc. | $1,283,920 | $1,322,438 | $1,362,111 | $1,402,974 | $1,445,063 |
Travel | Includes per diem for remote site standby. | $14,389 | $14,820 | $15,256 | $15,723 | $16,195 |
Prof. Meetings & Training | Registration and other training fees. | $2,915 | $3,002 | $3,093 | $3,185 | $3,281 |
Vehicles | GSA and Tribally-owned vehicle costs. | $66,410 | $68,402 | $70,454 | $72,568 | $74,745 |
Facilities/Equipment | (See explanation below) | $205,870 | $212,046 | $218,407 | $224,960 | $231,708 |
Rent/Utilities | Standard utilities and includes computer costs, toilet rental, etc. | $154,956 | $159,605 | $164,393 | $169,324 | $174,404 |
Capital Equipment | Indirect-exempt costs. Helicopter outplant, chiller maint., other annual contracts. NO capital equip | $42,059 | $43,321 | $44,621 | $45,959 | $47,338 |
Overhead/Indirect | Calculated at 22.5% | $398,863 | $410,829 | $423,154 | $435,848 | $448,924 |
Other | BPA required insurance policy for NPTHC assets. | $44,273 | $45,602 | $46,978 | $48,380 | $49,830 |
PIT Tags | $0 | $0 | $0 | $0 | $0 | |
Total | $2,213,655 | $2,280,065 | $2,348,467 | $2,418,921 | $2,491,488 |
Assessment Number: | 1983-350-00-ISRP-20101015 |
---|---|
Project: | 1983-350-00 - Nez Perce Tribal Hatchery Operations and Maintenance (O&M) |
Review: | RME / AP Category Review |
Proposal Number: | RMECAT-1983-350-00 |
Completed Date: | 12/17/2010 |
Final Round ISRP Date: | 12/17/2010 |
Final Round ISRP Rating: | Meets Scientific Review Criteria |
Final Round ISRP Comment: | |
This meets criteria but also see comments on the M&E proposal 198335003.
Now that the program has shown that it can produce fall and spring Chinook that return to the Clearwater River as adults, perhaps it is time to begin to consider whether (and to what extent) the effort will yield self-sustaining runs of natural origin. The next iteration of the project needs to begin to address whether and how self-sustaining Clearwater River salmon runs will be achieved. Thus, while the NPT has done a good job in guiding the NPTH to this point, the ISRP’s longstanding concerns about the viability of the supplementation approach to rebuild self-sustaining natural reproduction in Idaho rives and streams remains unanswered. 1. Purpose, Significance to Regional Programs, Technical Background, and Objectives The proponents do a good job of describing the history of the project and how it fits into regional Fish and Wildlife Program and AP planning. Technical background, along with the growth and evolution of the NPTH program is well described. 2. History: Accomplishments, Results, and Adaptive Management Past ISRP concerns that project results were not being adequately described have been effectively dealt with by the very commendable January 2009 Orofino symposium. The current proposal summarizes material presented at the symposium but often provides inadequate narrative for those who did not have the opportunity to attend the symposium. The proponents do a very good job of describing the project’s history and evolution, as well as to a lesser degree, how they went about solving unforeseen problems, mostly associated with low return of adults or with limited water supply. It is evident that the hatchery was built at a site having unsuitable water supply. The hatchery is reported to be operating better than in its first few years, however. Within the last year or so, production has increased to the point that objectives are being met or nearly so in terms of numbers of released fish. One of the four or so apparent current “issues” with the project is whether the basic requirements for fish production are adequate at the NPTH facility. From the proposal it appears that ongoing improvements (of a wide variety) are adequate for the near future and that issue no longer exists. Another issue is survival of juveniles immediately after release. It was mentioned at the symposium that results from tagging juveniles at Newsome Creek showed very high mortality by Lower Granite dam. It is important to understand relationships among fish size at release, time of movement from acclimation site, whether release is volitional or forced, and the habitat used by those fish as they overwinter. Granted, such monitoring should be (is?) done by another project (NPT M&E) but results need to be closely linked to this project so the best release strategies can be developed. Currently it does not appear that is receiving adequate attention. Production goals for both spring and fall Chinook, in terms of numbers of juveniles leaving the various acclimation facilities, now seem close to being met. The obvious question now is whether those are the most appropriate production goals. Because the ultimate goal must be natural production, and the project duration is “until natural production in target streams can support exclusively the fishery management principles, goals and objectives listed above,” the key issue is whether the project is indeed moving toward that goal. Objectives are not being met in terms of proportion of natural influence (PNI). The proportions of natural-origin adults in hatchery broodstocks (pNOB) are too low, and the proportions of hatchery-origin adults among naturally spawning fish (pHOS) are too high, therefore the PNI values are too low. For the ISRP to evaluate progress toward meeting PNI objectives, it would help for the proponents to provide the pNOB, pHOS, and PNI results for each year of hatchery operation. SARs for the FCS and SCS components are roughly 0.1% and 0.3%, respectively. For natural production to be self-sustaining, SARs will have to increase by an order of magnitude. How can this be achieved? The next iteration of the project should start to address these issues and describe a plan for achieving them, otherwise, there will never be a termination date for the artificial production efforts on this project and the ultimate goals will never be achieved. 3. Project Relationships, Emerging Limiting Factors, and Tailored Questions for Type of Work (Hatchery, RME, Tagging) Adequately described. 4. Deliverables, Work Elements, Metrics, and Methods Adequately described. |
|
First Round ISRP Date: | 10/18/2010 |
First Round ISRP Rating: | Meets Scientific Review Criteria |
First Round ISRP Comment: | |
This meets criteria but also see comments on the M&E proposal 198335003. Now that the program has shown that it can produce fall and spring Chinook that return to the Clearwater River as adults, perhaps it is time to begin to consider whether (and to what extent) the effort will yield self-sustaining runs of natural origin. The next iteration of the project needs to begin to address whether and how self-sustaining Clearwater River salmon runs will be achieved. Thus, while the NPT has done a good job in guiding the NPTH to this point, the ISRP’s longstanding concerns about the viability of the supplementation approach to rebuild self-sustaining natural reproduction in Idaho rives and streams remains unanswered. 1. Purpose, Significance to Regional Programs, Technical Background, and Objectives The proponents do a good job of describing the history of the project and how it fits into regional Fish and Wildlife Program and AP planning. Technical background, along with the growth and evolution of the NPTH program is well described. 2. History: Accomplishments, Results, and Adaptive Management Past ISRP concerns that project results were not being adequately described have been effectively dealt with by the very commendable January 2009 Orofino symposium. The current proposal summarizes material presented at the symposium but often provides inadequate narrative for those who did not have the opportunity to attend the symposium. The proponents do a very good job of describing the project’s history and evolution, as well as to a lesser degree, how they went about solving unforeseen problems, mostly associated with low return of adults or with limited water supply. It is evident that the hatchery was built at a site having unsuitable water supply. The hatchery is reported to be operating better than in its first few years, however. Within the last year or so, production has increased to the point that objectives are being met or nearly so in terms of numbers of released fish. One of the four or so apparent current “issues” with the project is whether the basic requirements for fish production are adequate at the NPTH facility. From the proposal it appears that ongoing improvements (of a wide variety) are adequate for the near future and that issue no longer exists. Another issue is survival of juveniles immediately after release. It was mentioned at the symposium that results from tagging juveniles at Newsome Creek showed very high mortality by Lower Granite dam. It is important to understand relationships among fish size at release, time of movement from acclimation site, whether release is volitional or forced, and the habitat used by those fish as they overwinter. Granted, such monitoring should be (is?) done by another project (NPT M&E) but results need to be closely linked to this project so the best release strategies can be developed. Currently it does not appear that is receiving adequate attention. Production goals for both spring and fall Chinook, in terms of numbers of juveniles leaving the various acclimation facilities, now seem close to being met. The obvious question now is whether those are the most appropriate production goals. Because the ultimate goal must be natural production, and the project duration is “until natural production in target streams can support exclusively the fishery management principles, goals and objectives listed above,” the key issue is whether the project is indeed moving toward that goal. Objectives are not being met in terms of proportion of natural influence (PNI). The proportions of natural-origin adults in hatchery broodstocks (pNOB) are too low, and the proportions of hatchery-origin adults among naturally spawning fish (pHOS) are too high, therefore the PNI values are too low. For the ISRP to evaluate progress toward meeting PNI objectives, it would help for the proponents to provide the pNOB, pHOS, and PNI results for each year of hatchery operation. SARs for the FCS and SCS components are roughly 0.1% and 0.3%, respectively. For natural production to be self-sustaining, SARs will have to increase by an order of magnitude. How can this be achieved? The next iteration of the project should start to address these issues and describe a plan for achieving them, otherwise, there will never be a termination date for the artificial production efforts on this project and the ultimate goals will never be achieved. 3. Project Relationships, Emerging Limiting Factors, and Tailored Questions for Type of Work (Hatchery, RME, Tagging) Adequately described. 4. Deliverables, Work Elements, Metrics, and Methods Adequately described. |
|
Documentation Links: |
|
Proponent Response: | |
|