Opportunity Information: Apply for FWS R8 YFWO 2010 FISHERIES FP 05
Apply for FWS R8 YFWO 2010 FISHERIES FP 05
- The Fish and Wildlife Service in the science and technology and other research and development sector is offering a public funding opportunity titled "Blue Creek Chinook Coho Life Cycle Monitoring Project" and is now available to receive applicants.
- Interested and eligible applicants and submit their applications by referencing the CFDA number(s): 15.608 Fish and Wildlife Management Assistance.
- This funding opportunity was created on Jul 14, 2010 and posted on Jul 14, 2010.
- Applicants must submit their applications by This is Notice of Intent. This opportunity has been awarded to the Yurok Tribe. No other applications will be reviewed.. (Agency may still review applications by suitable applicants for the remaining/unused allocated funding in 2026.)
- Each selected applicant is eligible to receive up to $29,980.00 in funding.
- Eligible applicants include: Others (see text field entitled Additional Information on Eligibility for clarification).
- This opportunity is a Notice of Intent.
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Opportunity Summary:
The Blue Creek Chinook Coho Life Cycle Monitoring Project is a U.S. Fish and Wildlife Service (USFWS) discretionary grant opportunity focused on tracking the status and trends of adult salmon populations in Blue Creek, a major tributary in the Lower Klamath Sub-basin. Blue Creek is described as the largest and most pristine tributary in this part of the basin and is repeatedly highlighted as one of the most important remaining strongholds for anadromous fish in the region. Historical and scientific references cited in the announcement emphasize that Blue Creek has unusually high potential for supporting anadromous fish compared to nearby tributaries, and that its Chinook and coho stocks may be especially important because other lower Klamath tributaries have seen very low or even nonexistent late-fall Chinook and coho presence over past decades. In other words, the project is framed as essential baseline monitoring for a rare, high-value refuge population, rather than routine sampling in a system with many alternative data sources.
A central reason the project matters is that Blue Creek supports a distinct late-fall Chinook run (typically peaking in November and December) that has been characterized as a unique stock adapted to the lower Klamath system. The opportunity description notes research suggesting these fish may be genetically and physically more similar to Smith River or southern Oregon stocks than to other Klamath groups, and that their distinctive run timing, body characteristics, and coloration have been recognized for a long time. Blue Creek also supports one of the largest remaining coho runs in the Lower Klamath Sub-basin, with the Crescent City Fork called out as particularly important habitat that can be heavily used by coho in the upper reaches. Because Blue Creek is relatively pristine and somewhat isolated from other wild coho refugia, the coho stock is presented as a potentially critical genetic refuge for the Klamath Basin, increasing the stakes for consistent, long-term monitoring.
The project itself began in fiscal year 1989 and is designed primarily to collect adult Chinook escapement data and related life-cycle information across the Blue Creek drainage. That information is used to assess population trends over time, understand distribution and movement (including immigration/emigration timing), and document habitat use during the spawning season. The announcement underscores that Chinook trend data from Blue Creek is an “integral component” of the broader Klamath Basin “Mega Table,” a multi-source compilation used to improve estimates of wild salmonid abundance basinwide and to strengthen forecasts of future run sizes. Coho data are collected to the extent feasible, but the announcement is candid that budget constraints and winter high-flow conditions often limit survey duration into late December and January, which can mean surveys conclude before peak coho spawning in some years.
For the 2010-2011 field season specifically, the stated objectives and tasks emphasize generating both an escapement estimate and a spawner index for fall Chinook, while also documenting the timing and extent of Chinook immigration and spawning across the basin. Two complementary population metrics are central to the work. First, the project aims to produce a fall 2010 adult Chinook escapement estimate using an “area under the curve” (AUC) method, which combines fish marking with repeated snorkel counts to estimate abundance while accounting for how long fish remain in the system (residence time) and how reliably observers detect fish (observer efficiency). Second, it aims to produce a fall 2010 Chinook spawner index count using peak weekly snorkel survey counts. A major longer-term goal is to run the AUC estimate and the index count side-by-side for enough years to quantify the relationship between the two. If that relationship is strong, it could allow managers to translate older index-count datasets (collected since the early 1990s) into estimated population abundances, and it could also allow future abundance estimates in years when full AUC work is not possible due to stream conditions or funding.
Methodologically, the project relies on targeted adult capture and marking in the lower reaches of Blue Creek as fish enter the system. Capture uses a 3.5-inch mesh tooth tangle net that can be fished passively or drifted, depending on conditions, with staff continuously attending the net and moving captured fish into holding tubes. Captured salmonids are measured, sexed when possible using external traits, and sampled for scales. Marking is done with a visible streamer tag (batch-marked by event using the same color behind the dorsal fin) and a secondary fin clip; fish are then allowed to recover and released upstream. The project incorporates explicit tests of observer efficiency by allowing a known number of marked fish to disperse and then having divers count them within a block-netted section, while recording physical parameters that could influence detection (for example, visibility and flow-related conditions). Residence time is estimated by tracking the decline of marked fish detections over time (a mark depletion curve), calculating area-under-curve values for marked fish, and using those results to convert weekly snorkel counts into weekly abundance estimates that are then summed to generate the annual escapement estimate.
In addition to marking and snorkel-based abundance work, the project conducts weekly spawning surveys from October through mid-December to document immigration and spawning activity not only for late-fall Chinook and coho, but also for steelhead and coastal cutthroat trout encountered during the same period. Surveys use direct observation via snorkeling across established reaches in the anadromous portion of the drainage. Crews record detailed information on live fish (species, counts, exact locations, size/condition/sex when feasible, and any marks or scars), redds (location, species association when possible, habitat type, and redd dimensions, with redds flagged to avoid recounting), and carcasses (location, species, fork length, sex, percent spawned, scale collection, mark/clip documentation, carcass condition, and flagging to avoid duplicate counts; heads are collected if adipose-clipped). Collectively, these data provide a picture of run timing, spatial distribution, spawning intensity, and post-spawn mortality patterns, which are directly relevant to both local restoration decisions and broader population assessments.
On the management side, the opportunity explicitly ties the project to harvest management and regulatory decision-making. The data support the Pacific Fishery Management Council, the California Fish and Game Commission, and Tribal governments by helping track population trends and estimate key indicators such as fall Chinook ocean stock abundance, age composition, and spawning run size. Those estimates feed into determinations about whether conservation goals for Klamath River fall Chinook are met in a given year and help produce projections of fishable stock used to set fishing regulations along the southern Oregon coast. The project also has a workforce development component aimed at improving the skills and knowledge of Yurok Tribal Fisheries Program staff and Yurok Tribal members through hands-on involvement in multiple fisheries monitoring activities, strengthening long-term local capacity to conduct technically demanding field assessments.
Administratively, this listing is a Notice of Intent rather than an open competition. It states that the opportunity has already been awarded to the Yurok Tribe and that no other applications will be reviewed. The funding opportunity number is FWS R8 YFWO 2010 FISHERIES FP 05 under CFDA 15.608 (Fish and Wildlife Management Assistance). The award amount is fixed, with an award ceiling and floor of $29,980, and there is no cost-sharing or matching requirement. The opportunity was posted on July 14, 2010, and the agency is the U.S. Fish and Wildlife Service.
Frequently Asked Questions (FAQs): Blue Creek Chinook Coho Life Cycle Monitoring Project (USFWS)
What is the Blue Creek Chinook Coho Life Cycle Monitoring Project?
It is a U.S. Fish and Wildlife Service (USFWS) discretionary grant-supported project focused on tracking the status and trends of adult salmon populations in Blue Creek, a major tributary in the Lower Klamath Sub-basin. The work centers on adult Chinook (especially a distinct late-fall run) and collects coho information to the extent feasible.
Which agency is offering (and administering) this grant opportunity?
The agency is the U.S. Fish and Wildlife Service (USFWS).
Is this an open grant competition?
No. This listing is a Notice of Intent rather than an open competition. It states the opportunity has already been awarded and that no other applications will be reviewed.
Who has already been selected for the award?
The Notice of Intent states that the opportunity has already been awarded to the Yurok Tribe.
Will USFWS review additional applications for this opportunity?
No. The announcement explicitly states that no other applications will be reviewed.
What is the funding opportunity number?
FWS R8 YFWO 2010 FISHERIES FP 05.
What CFDA program is associated with this award?
CFDA 15.608, Fish and Wildlife Management Assistance.
When was the opportunity posted?
It was posted on July 14, 2010.
What is the award amount (ceiling and floor)?
The award amount is fixed, with both the award ceiling and the award floor listed as $29,980.
Is cost sharing or matching required?
No. The listing states there is no cost-sharing or matching requirement.
Where does the project take place?
The project takes place in Blue Creek, described as a major tributary in the Lower Klamath Sub-basin.
Why is Blue Creek a priority location for monitoring?
Blue Creek is described as the largest and most pristine tributary in this part of the basin and repeatedly highlighted as one of the most important remaining strongholds for anadromous fish in the region. The opportunity frames the work as essential baseline monitoring for a rare, high-value refuge population.
Which fish populations are the main focus of the monitoring?
The primary focus is adult Chinook salmon escapement and related life-cycle information across the Blue Creek drainage. Coho salmon data are also collected to the extent feasible, and surveys document steelhead and coastal cutthroat trout encountered during the same period.
What is notable about the Blue Creek Chinook run mentioned in the announcement?
The opportunity emphasizes a distinct late-fall Chinook run that typically peaks in November and December and has been characterized as a unique stock adapted to the lower Klamath system, with research cited suggesting genetic and physical similarities to Smith River or southern Oregon stocks.
What is notable about the Blue Creek coho population mentioned in the announcement?
Blue Creek is described as supporting one of the largest remaining coho runs in the Lower Klamath Sub-basin, and the Crescent City Fork is called out as particularly important habitat that can be heavily used by coho in the upper reaches. Because Blue Creek is relatively pristine and somewhat isolated from other wild coho refugia, the coho stock is presented as a potentially important genetic refuge for the Klamath Basin.
When did this monitoring project begin?
The project began in fiscal year 1989.
What are the core purposes of the project?
The project is designed to collect adult Chinook escapement data and related information used to assess population trends over time, understand distribution and movement (including immigration/emigration timing), and document habitat use during the spawning season.
How are Blue Creek data used beyond the creek itself?
The announcement states that Chinook trend data from Blue Creek are an integral component of the Klamath Basin "Mega Table," a multi-source compilation used to improve estimates of wild salmonid abundance basinwide and strengthen forecasts of future run sizes.
What field season is specifically described in the announcement?
The opportunity description highlights objectives and tasks for the 2010-2011 field season, including producing a fall 2010 adult Chinook escapement estimate and a fall 2010 Chinook spawner index count.
What two population metrics are central to the 2010 fall Chinook work?
(1) An adult Chinook escapement estimate using an area under the curve (AUC) method, and (2) a Chinook spawner index count using peak weekly snorkel survey counts.
What is the AUC method in the context of this project?
As described, the AUC approach combines fish marking with repeated snorkel counts to estimate abundance while accounting for how long fish remain in the system (residence time) and how reliably observers detect fish (observer efficiency).
Why does the project run the AUC estimate and index count side-by-side?
A longer-term goal is to operate both methods for enough years to quantify the relationship between them. If the relationship is strong, managers could translate older index-count datasets (collected since the early 1990s) into estimated population abundances and produce future abundance estimates in years when full AUC work is not possible due to stream conditions or funding.
How are adult salmon captured for marking?
Adult capture and marking occurs in the lower reaches of Blue Creek as fish enter the system. Capture uses a 3.5-inch mesh tooth tangle net that can be fished passively or drifted depending on conditions, with staff continuously attending the net and moving captured fish into holding tubes.
What data are collected from captured fish?
Captured salmonids are measured, sexed when possible using external traits, and sampled for scales.
How are fish marked in this project?
Marking uses a visible streamer tag placed behind the dorsal fin (batch-marked by event using the same color) plus a secondary fin clip. Fish are allowed to recover and then released upstream.
How does the project measure observer efficiency for snorkel counts?
The project uses explicit observer efficiency tests by allowing a known number of marked fish to disperse and then having divers count them within a block-netted section, while recording physical parameters that could influence detection (such as visibility and flow-related conditions).
How is residence time estimated for the AUC approach?
Residence time is estimated by tracking the decline of marked fish detections over time (a mark depletion curve), calculating area-under-curve values for marked fish, and using those results to convert weekly snorkel counts into weekly abundance estimates that are summed to generate the annual escapement estimate.
What is the Chinook spawner index count described here?
It is based on peak weekly snorkel survey counts, providing an index of spawner abundance that can be compared against AUC-derived escapement estimates.
When do spawning surveys occur?
Weekly spawning surveys are conducted from October through mid-December.
Which species are included in the weekly spawning surveys?
The surveys document immigration and spawning activity for late-fall Chinook and coho, and also record steelhead and coastal cutthroat trout encountered during the same period.
How are the surveys conducted?
Surveys rely on direct observation via snorkeling across established reaches in the anadromous portion of the drainage.
What information is recorded for live fish observations?
Crews record species, counts, exact locations, size/condition/sex when feasible, and any marks or scars.
What information is recorded for redds?
Redd data include location, species association when possible, habitat type, and redd dimensions. Redds are flagged to avoid recounting.
What information is recorded for carcasses?
Carcass data include location, species, fork length, sex, percent spawned, scale collection, mark/clip documentation, carcass condition, and flagging to avoid duplicate counts. Heads are collected if the fish is adipose-clipped.
Why might coho monitoring be less complete than Chinook monitoring in some years?
The announcement notes that budget constraints and winter high-flow conditions often limit survey duration into late December and January, which can mean surveys conclude before peak coho spawning in some years.
How do the project results support fisheries management decisions?
The opportunity explicitly ties the work to harvest management and regulatory decision-making. The data support the Pacific Fishery Management Council, the California Fish and Game Commission, and Tribal governments by helping track trends and estimate indicators such as fall Chinook ocean stock abundance, age composition, and spawning run size, which inform conservation goal evaluations and projections used to set fishing regulations along the southern Oregon coast.
Does the project include a workforce or training component?
Yes. The listing describes a workforce development component aimed at improving skills and knowledge of Yurok Tribal Fisheries Program staff and Yurok Tribal members through hands-on involvement in multiple fisheries monitoring activities to strengthen long-term local capacity.
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