Show new navigation
On
Columbia Basin Fish and Wildlife Program Columbia Basin Fish and Wildlife Program
SOW Report
Contract 58847: 1988-053-03 EXP PARKDALE U OF W COMPARATIVE HATCHERY STUDY
Project Number:
Title:
Hood River Production Program Monitoring and Evaluation (M&E)
BPA PM:
Stage:
Implementation
Area:
Province Subbasin %
Columbia Gorge Hood 100.00%
Contract Number:
58847
Contract Title:
1988-053-03 EXP PARKDALE U OF W COMPARATIVE HATCHERY STUDY
Contract Continuation:
Previous: Next:
n/a
  • 62859: 1988-053-03 EXP PARKDALE U OF W COMPARATIVE HATCHERY STUDY
Contract Status:
Closed
Contract Description:
Background - This project has two sibling contracts, 1 with NOAA Fisheries for project organization, implementation and the majority of data analysis and this one with the University of Washington for sample analysis and some data analysis.

Objective I. Hood River Spring Chinook Salmon Smolt Quality

The Hood River, Oregon Salmon Production Program is co-managed by the Warm Springs Tribe (WS) and the Oregon Department of Fish and Wildlife (ODFW) for supplementation of spring Chinook salmon in the Hood River system.  The current Master Plan for the Hood River Production Program (March 5, 2008 Draft) calls for a comparative hatchery release study designed to "provide co-managers with the best available information for determining a long term biologically sound and cost effective spring Chinook salmon production strategy for the Hood River Basin that balances harvest needs with ecological considerations".  Rearing faci... lities, both inside and outside the basin, are being evaluated for long-term use in the Hood River spring Chinook supplementation program.  The objective of this evaluation is to conduct a multi-year (2008-2018) comparative study of Hood River spring Chinook reared at three different hatchery facilities prior to being moved to the West Fork Hood River for final acclimation and release.  The facilities include, Round Butte Hatchery/Pelton Ladder (RBH) on the Deschutes River, OR; Columbia Gorge Hatchery (CGH) a.k.a. Carson National Hatchery on the Wind River, WA; Parkdale Fish Facility (PFF) on the Hood River, OR.  Each year, starting Fall 2008, returning adults will be collected in the Hood River, artificially spawned at the PFF, and gametes will be distributed to each of the respective hatchery facilities for long term-rearing to the parr-smolt stage.   Starting in Spring 2010 uniquely tagged juveniles from each facility will be moved to the Moving Falls Acclimation Pond on the West Fork Hood River for acclimation and forced release in April.  The Hood River Master Plan calls for monitoring fish health, size at release, specific growth rates, rates of precocious male maturation (age-2 minijacks, age-3 jacks) and ultimately smolt-to-adult returns (SAR's) for each brood year/release group.  SAR's for all adult year classes from all brood years will be available starting in 2013 with final returns in 2018.   These data will be used to evaluate which hatchery facility/regime is optimum for future long-term implementation in the Hood River Supplementation program.

As part of the broader Revised Hood River Production Master Plan we will conduct the following Hood River Smolt Quality Monitoring and Evaluation Study.  The overall goals will be:

A.  Monitor spring growth and smolt development at all rearing sites.

B.  Provide comparative metrics of smolt quality between rearing sites.

Specifically, we will determine if differences in growth, smolt development and early male maturation, exist between Hood River spring Chinook salmon reared at RBH, PFF and CGH and subsequently released into the West Fork Hood River for three consecutive brood years (BY) 2008-2010 released in years 2010-2012. In addition, we will monitor Deschutes stock spring Chinook reared at RBH and released into the Deschutes River and Carson stock spring Chinook reared at CGH and released into the Wind River.  These measures will allow us to:

C.  Assess the effects on growth and smolt development of transferring fish from out of basin rearing facilities (RBH and CGH) to the acclimation release site at Moving Falls on the West Fork Hood River.  

These physiological/life-history indices will provide early, predictable and replicated comparative data, before the acquisition of full SAR's from 2011-2015, for evaluating the three rearing regimes.  In addition, these metrics are independent of any potential alteration in ocean conditions that can produce variation in SAR's that are unrelated to freshwater rearing.  However, once SAR's are obtained we will be able to:

D.  Correlate physiological indices of growth and smolting to SAR to evaluate key factors responsible for potential differences in survival between release groups

This will allow us to:

E.  Evaluate rearing practices with regard to A, B and C to recommend "best" rearing practices and a long term rearing strategy for the HRPP. Results will be available for managers in late-2012 with the completion of our final comparative physiology report proposed in this SOW.  Final correlational analysis of physiological indicators with SAR's (D) will be conducted as adults return from 2012-2015.

NOTE for FY 13:

For the FY 2013 SOW under this Objective I we will conduct data analysis from all three brood years (2008-2010) and compile a summary report of these results for comanagers.
As of the writing of this SOW, the Hood River, Oregon Production Program co-managers have made some programmatic decisions based on results from this project to focus Hood River spring Chinook salmon rearing at Pelton Ladder, Parkdale Fish Facility with potential for longer term in basin rearing at the recently completed Moving Falls Acclimation Facilty on the West Fork fo the Hood River.  Rearing of Hood River spring Chinook at Carson hatchery was discontinued.  Rearing and release strategies for the BY 2011 fish are being finalized at this time.  During this contract period we will conduct spring (pre-release) physiological evaluation (adiposity, smolt, minijack)  of each separate rearing group produced (Pelton Ladder, Parkdale, Moving Falls) in the Hood Program to determine the best strategy or combination of strategies for future production.


Objective II.  Hood River Steelhead Trout Residualism Monitoring

          Like spring Chinook salmon, steelhead trout display significant phenotypic plasticity in both the age of smolting and age of maturation.  Hatchery-reared steelhead may adopt one of three life history pathways after release: 1) smolt and migrate to sea 2) sexually mature and remain in freshwater and attempt to spawn naturally (primarily males), or 3) "residualize" as a non-smolting and non-maturing parr and delay migration or maturation 'decisions' until the subsequent year(s).   The objective of this work is to use a series of recently developed physiological indices to quantify residualism rates of the steelhead trout population supplemented in to the Hood River by WS and ODFW.  These fish are from Hood River natural origin brood stock reared at Oak Springs Hatchery on the Deschutes River, OR and released in to the Hood River in May of each spring.  After transfer of the fish from Oak Springs to the Hood River we will collect 300 fish and sample them for length, weight, condition factor, pituitary glands for measurement of mRNA levels of reproductive hormones, plasma for measurement of 11-ketotestosterone and gonad tissue for mRNA measurement of reprodutive hormones and histological analysis.  Finally, we will collect gills for determination of Na+/K+-ATPase enzyme activity as an indicator of smoltification.  These indicese will be examined in a multifactorial analysis to catagorize fish into thier respective life-histories.  These data will be used to help determine rates of residualism in Hood River steelhead and to potentially help modify rearing regimes for these fish to minimize residualism rates.  This work will be conducted with S1 steelhead over three consecutive brood years for the reasons outlined above: BY 2011-2013 released in 2012-2014.
  
Account Type(s):
Expense
Contract Start Date:
12/01/2012
Contract End Date:
11/30/2013
Current Contract Value:
$99,757
Expenditures:
$99,757

* Expenditures data includes accruals and are based on data through 31-Mar-2025.

Env. Compliance Lead:
Contract Contractor:
Work Order Task(s):
Contract Type:
Contract (IGC)
Pricing Method:
Cost Reimbursement (CNF)
MarkerMarker
5 m
10 ft
Click the map to see this Contract's location details.

No photos have been uploaded yet for this Contract.

Full Name Organization Write Permission Contact Role Email Work Phone
Christopher Brun Confederated Tribes of Warm Springs Yes Interested Party cbrun@hrecn.net (541) 352-3548
Rossana Callejas Bonneville Power Administration No Interested Party rxcallejas@bpa.gov (503) 230-7558
Richard Golden Jr Bonneville Power Administration Yes COR rlgolden@bpa.gov (503) 230-5119
Donald Larsen National Oceanic and Atmospheric Administration Yes Technical Contact don.larsen@noaa.gov (206) 799-4476
Andre Punt University of Washington No Supervisor aepunt@u.washington.edu (206) 221-6319
Jessica Roshan University of Washington Yes Interested Party jroshan@uw.edu (206) 616-9521
John Skidmore Bonneville Power Administration Yes F&W Approver jtskidmore@bpa.gov (503) 230-5494
Kurt Unger Bonneville Power Administration Yes Env. Compliance Lead klunger@bpa.gov (503) 230-5885
Kristi Van Leuven Bonneville Power Administration Yes Contracting Officer kjvleuven@bpa.gov (503) 230-3605
Graham Young University of Washington Yes Contract Manager grahamy@u.washington.edu (206) 543-4291


Viewing 7 of 7 Work Statement Elements
Sort Order
WSEV ID
WE ID
Work Element Name
Title
Description
WSE Effective Budget
% of Total WSE Effective Budget
WSE Start
WSE End
A106935165Produce Environmental Compliance DocumentationEnvironmental ComplianceEnvironmental compliance with State (University of Washington) and Federal (NOAA laboratory) regulations and practices must be adhered to.$00.00%12/01/201211/30/2013
B106218185Produce CBFish Status ReportPeriodic Status Reports for BPAThe Contractor shall report on the status of milestones and deliverables in Pisces. Reports shall be completed either monthly or quarterly as determined by the BPA COTR. Additionally, when indicating a deliverable milestone as COMPLETE, the contractor shall provide metrics and the final location (latitude and longitude) prior to submitting the report to the BPA COTR.$5000.50%04/01/201311/30/2013
C106933119Manage and Administer ProjectsAdministration of BPA contractCoordinate logistical and financial details with BPA and NOAA Fisheries including progress reports, accrual estimates, and SOW's$1,0001.00%12/01/201211/30/2013
D106842157Collect/Generate/Validate Field and Lab DataAnalyze HRPP spring Chinook salmon smolt samplesBackground description provided for context. Work conducted under this contract is for laboratory analysis of collected samples. Fish Collections: Sampling for this project will take place in April 2013. 300 Hood River origin fish from each facility (RBH, PFF, MF) will be collected by dip-net, individually anesthetized in a buffered solution of 0.05% tricaine methanesulfonate (MS-222, Argent Chemical Laboratories, Redmond, WA), weighed to the nearest 0.1g and measured for fork length to the nearest 1.0 mm. Sex and state of maturation will be determined by visual observation. Under this UW contract: Carcasses from 50 fish from each population will be analyzed for whole body lipid via the method of Beckman et al. (unpublished) via the inverse of body moisture. Gill Na+/K+-ATPase activity: Gill tissue will be sampled from 50 fish from each population. Filaments from 3 gill arches will be placed in a solution of sucrose, EDTA, and imidazole according to methods described by Zaugg (1982) and then frozen on dry ice and stored at -80 C. Under this UW contract: Gill Na+/K+-ATPase activities will be measured using the method of McCormick (1993) and all values are reported in units of mmole PO4 x mg pro -1 x hr -1. Minijack screening Sex and state of maturational development will be visually assessed as follows: Immature female fish are identified by the gonad having an anterior thickening with a granular appearance. Immature male fish are identified by the gonad having a thin, clear, threadlike appearance with a diameter less than approximately 0.5 mm throughout the entire length. Precociously maturing males are identified by the gonad being opaque and having an anterior thickening of greater than approximately 1.0-1.5 mm (depending on date) and a smooth surface texture. It should be noted that these visual assessments provide preliminary estimates but, confirmation by 11-KT analysis at this early stage of development is required. Blood samples will be collected from the severed caudal vessel into heparinized Natelson tubes (VWR Scientific), centrifuged for 3 minutes at 3000 G, and stored frozen at -80C. Under this UW contract: Plasma 11-KT levels will determined in all male samples using an enzyme-linked immunosorbant assay (ELISA) according to the method of Cuisset et al. (1994). Approximately 150 males per population = 450 samples analyzed for 11-KT. References Cuisset, B., P. Pradelles, D.E. Kime, E.R. Kuhn, P. Babin, F. Le Menn. 1994. Enzyme immunoassay for 11-ketotestosterone using acetylcholinesterase as label. Application to the measurement of 11-ketotstosterone in plasma of Siberian sturgeon. Comparative Biochemistry and Physiology 108:229-241. Larsen, D.A., B. R. Beckman, K. A. Cooper, D. Barrett, M. Johnston, P. Swanson, and W. W. Dickhoff. 2004. Assessment of high rates of precocious male maturation in a spring Chinook salmon supplementation hatchery program. Transactions of the American Fisheries Society 133:98-120. McCormick, S. D. 1993. Methods for nonlethal gill biopsy and measurement of Na+/K+-ATPase activity. Canadian Journal of Fisheries and Aquatic Science 50:656-658. Zaugg, W. S. 1982. Some changes in smoltification and seawater adaptability of salmonids resulting from environmental and other factors. Aquaculture 28:143–151.$19,00019.00%12/01/201211/30/2013
E106844157Collect/Generate/Validate Field and Lab DataAnalyze HRPP steelhead samplesAll HRPP Steelhead samples will be collected under a sibling contract with NOAA fisheries and analyzed under this contract through the University of Washington Testis histology, plasma hormone, tissue mRNA and gill Na+/K+ATPase analyses Histological analysis of stage of spermatogenesis will performed on all testis samples collected in May to identify fish that had initiated puberty for the following spring. Fixed testis tissue will be dehydrated through a graded series of ethanol and embedded in paraffin. Sections will be cut at 4 microns on a standard rotary microtome and stained in hematoxylin and eosin. Stages of spermatogenesis will be determined according to the most advanced stage of germ cell present in the sections (Campbell et al. 2003, Schulz et al. 2011). Testes that contain only isolated Type A undifferentiated spermatogonia are classified as prespermatogenic or prepubertal. Stages of spermatogenesis are defined as follows: stage I, the presence of mitotic Type A differentiated spermatogonia; stage II, presence of late B spermatogonia and/or primary spermatocytes; stage III, presence of all meiotic stages of germ cells (primary and secondary spermatocytes and spermatids); stage IV, presence of all stages of germ cells and spermatozoa in tubules; stage V, mainly spermatozoa present in tubules. Plasma 11-ketotestosterone (11-KT) will be determined using a specific enzyme immunoassay (Cuissett et al. 1994). Prior to assay plasma samples were heat treated according to Schulz et al. (1994). Quantitative real time RT-PCR will be performed as described previously (Campbell et al. 2006). Total RNA will be isolated from frozen testes, whole pituitaries or gill tissue using using QiagenÕs RNeasy Plus spin column kit (Qiagen, Valencia, CA). Integrity of the RNA will be verified by an optical density (OD) absorption ratio OD 260 nm/ OD 280 nm >1.9 and quantified by spectrophotometry at 260 nm using a nanodrop ND-1000 (NanoDrop Technologies, Wilmington, DE). Total RNA will be diluted with nuclease free water to 10.0 ng/ml and transcribed (15 ml) using Superscript II RNase H- reverse transcriptase (Invitrogen, Carlsbad, CA). For pituitaries and testes the reverse transcription (RT) reaction conditions are as follows: 3.0 ml of 5x buffer, 1.5 ml of 0.1 M dTT, 0.75 ml of dNTPs (stock of 10 mM each dCTP, dGTP, dTTP and dATP; Promega, Madison WI), 0.225 ml random hexamer (500 ng/ml stock; Promega), 0.1875 ml Superscript II RNase H- (200 U/ml), 0.3 ml RNase inhibitor (20 U/ml; Promega), sterile distilled deionized (dd) H20 (6.0375 ml) and 3.0 ml of template. The temperature profile for both the RT reactions is: 25¡C for 10 min, 48¡C for 60 min and 95¡C for 10 min, followed by a 4¡C incubation. RT reactions were diluted with equal volumes of RNAse-free water for a final 1:2 dilution prior to measurement in real-time quantitative RT-PCR assays. Probes and primers for real-time quantitative RT-PCR assays were designed according to sequence data using Primer Express software from ABI. When possible intron/exon splice junctions were used in primer design to avoid potential signal from contaminating genomic DNA. Probe and primer sequence for FSH beta, LH beta, anti-Mullerian hormone (AMH) and a housekeeping gene, elongation factor alpha (ef1a) are presented in Table 1. Table 1. Probe and primer design for quantitative real time RT-PCR assays. Target Forward Primer 5'-3' Probe 5'-3' Reverse Primer 5'-3' FSH beta AGGACTGTCACGGAAGCATCA 6FAM-TCACCACCTGCGCCGGCC-BHQ1 GTTCAGGTCCGTTGTTTCGC LH beta GTCACCAAGGAGCCGGTTTT 6FAM-AGCCCATTTTCCACCGTGTACCAGC-BHQ1 GTCCCGGTAGGTGCACACA Elf1alpha GAGATGGGCAAGGGCTCTTT6FAM-TCAGCTTGTCCAGCACCCAGGCA-BHQ1 TGATACCACGCTCCCTCTCA AMH CATCTACAACTGCCAGGGAGTCT 6FAM-CAGCTTTCCCCTGACCAACGGGAA-BHQ1 CTGTTAAGCAGGATAGCATGGT BHQ1: 3' quencher (non-fluorescent) 6FAM: 5' fluorescent reporter dye For each transcript measured a total RNA sample will be analyzed without RT reaction to test for DNA contamination. All assays will be run on an ABI 7900 HT Fast Real-Time PCR System using 384 well plates and ABI's Universal PCR MasterMix Reagent. PCR efficiency for each transcript will be measured using a serial dilution of a testis or pituitary RNA sample from within the experiment as a reference. Standard curve dilutions are run in triplicate while samples are not replicated. Reaction conditions are as follows for 12 ml PCRs: 6.0 ml of Universal PCR MasterMix (ABI), 0.22 ml of forward primer (45 mM stock), 0.22 ml of reverse primer (45 mM stock), 0.24 ml of probe (10 mM stock), 2.32 ml dd H20 and 3.0 ml of diluted RT reaction. Cycling parameters were: 50 C for 2 min, 95 C for 10 min and 40-45 cycles of 95 C for 15 sec followed by 60 C for 1 min. Transcript levels are calculated using the serially diluted total RNA sample standard curve and efficiency corrected by housekeeper (ef1a) using the method from Pierce et al. (2004). Template RNA concentrations are quantified using a NanoDrop ND-1000 (NanoDrop Technologies, Wilmington, DE) and the samples will be diluted to the same concentration (10.0 ng/ml) prior to the RT reaction. All samples for each gene are contained within one plate. Gill Na+/K+-ATPase activities will be measured using the method of McCormick (1993) and all values are reported in units of mmole PO4 x mg pro -1 x hr -1. Campbell, B., J.T. Dickey, and P. Swanson. 2003. Endocrine changes during puberty onset in male spring Chinook salmon, Oncorhynchus tshawytscha. Biology of Reproduction 69: 2109-2117. Campbell, B., J.T. Dickey, B. Beckman, G. Young, A. Pierce, H. Fukada, and P. Swanson. 2006. Previtellogenic oocyte growth in salmon: relationships among body growth, plasma insulin-like growth factor-1, estradiol 17-beta, follicle-stimulating hormone and expression of ovarian genes of insulin-like growth factors, steroidogenic-acute regulatory protein and receptors for gonadotropins, growth hormone and somatolactin. Biology of Reproduction 75: 34-44. Cuisset, B., P. Pradelles, D.A. Kime, E.R. Kuhn, P. Babin, and F. LeMenn. 1994. Enzyme immunoassay for 11-ketotestosterone in plasma of Siberian sturgeon. Comparative Biochemistry and Physiology 108:229-241. McCormick, S. D. 1993. Methods for nonlethal gill biopsy and measurement of Na+/K+-ATPase activity. Canadian Journal of Fisheries and Aquatic Science. 50:656-658. Pierce, A.L., J.T. Dickey, D.A. Larsen, H. Fukada, P. Swanson, and W.W. Dickhoff. 2004. A quantitative real-time RT-PCR assay for salmon IGF-I mRNA, and its application in the study of GH regulation of IGF-I gene expression in primary culture of salmon hepatocytes. General and Comparative Endocrinology 135:401-411. Schulz, R.W., L.R. de Franca, J.-J. Lareyre, F. LeGac, H. Chiarini-Garcia, R. H. Nobrega, and T. Miura. 2010. Spermatogenesis in fish. General and Comparative Endocrinology 165:390-411. Schulz, R.W., L. van der Corput, J. Janssen-Dommerholt, and H. J. Th. Goos. 1994. Sexual steroids during puberty in male African catfish (Clarius gariepinus): serum levels and gonadotropin-stimulated testicular secretion in vitro. Comparative Biochemistry and Physiology B 164:195-205.$55,00055.00%12/01/201211/30/2013
F106932162Analyze/Interpret DataAssist with analysis of three year HRPP Spring Chinook comparative evaluationUnder this contract University of Washington personnel will assist NOAA personnel under sibling contract with conducting data preparation, graphics, statistical analysis of 3 year HRPP spring Chinook comparative evaluation study.$24,50024.50%12/01/201211/30/2013
G106934132Produce Progress (Annual) ReportFY 13 Progress Report data transferred to NOAAThe annual report requirement for this project will be fulfilled under sibling NOAA contract under project 1988-053-03. Relevant data will be transferred from University of Washington to NOAA.$00.00% 11/01/2013
      
$100,000
   

Deliverable Title WSE Sort Letter, Number, Title Start End Concluded
Environmental Compliance A: 165. Environmental Compliance 11/30/2013 11/30/2013
Fulfill all administrative tasks with quality products and in a timely manner. C: 119. Administration of BPA contract 11/30/2013 11/30/2013
Analyze BY 2011 HRPP Spring Chinook salmon samples D: 157. Analyze HRPP spring Chinook salmon smolt samples 08/31/2013 08/31/2013
Analyze HRPP Steelhead physiology samples E: 157. Analyze HRPP steelhead samples 08/31/2013 08/31/2013
Data analysis, graphics and interpretation-3 year HRPP spring Chinook Comparative Evaluation F: 162. Assist with analysis of three year HRPP Spring Chinook comparative evaluation 05/31/2013 05/31/2013
Data transfer to NOAA G: 132. FY 13 Progress Report data transferred to NOAA 11/01/2013 11/01/2013

Viewing of Implementation Metrics
Loading...
Sort Order
WE ID
Work Element Name
Title
Description
Metric ID
Metric
End Fiscal Year
Planned
Actual
Contractor Comments
All Measures
Annual Progress Report Measures
Populations
Viewing of Environmental Metrics Customize
Loading...
WSE ID
WSE Start
WSE End
WE ID
Title
WSE Progress
Study Plan
Protocol
Category
Subcategory
Focus 1
Focus 2
Specific Metric Title

Primary Focal Species Work Statement Elements
Chinook (O. tshawytscha) - Lower Columbia River ESU (Threatened)
  • 1 instance of WE 157 Collect/Generate/Validate Field and Lab Data
  • 1 instance of WE 162 Analyze/Interpret Data
Steelhead (O. mykiss) - Lower Columbia River DPS (Threatened)
  • 1 instance of WE 157 Collect/Generate/Validate Field and Lab Data

Sort WE ID WE Title NEPA NOAA USFWS NHPA Has Provisions Inadvertent Discovery Completed
A 165 Environmental Compliance 12/01/2012
B 185 Periodic Status Reports for BPA 12/01/2012
C 119 Administration of BPA contract 12/01/2012
D 157 Analyze HRPP spring Chinook salmon smolt samples 12/01/2012
E 157 Analyze HRPP steelhead samples 12/01/2012
F 162 Assist with analysis of three year HRPP Spring Chinook comparative evaluation 12/01/2012
G 132 FY 13 Progress Report data transferred to NOAA 12/01/2012