North Coast Region Watershed Program Status

Total Page:16

File Type:pdf, Size:1020Kb

North Coast Region Watershed Program Status Shasta-Trinity National Forest North Coast Region Watershed Program Status Prepared for North Coast Water Board Per Requirements of USFS Waiver Order No R1-2010-0029 December 2010 Shasta-Trinity National Forest North Coast Region Watershed Program Status Contents Introduction Purpose and Forest Setting Shasta-Trinity National Forest within North Coast Water Region Section 1 Key Watersheds Section 2 Watershed Assessments Section 3 Watershed Condition Land Management Plan Watersheds of Concern Watershed Disturbance Levels Section 4 Forest Restoration Priorities Section 5 Sediment Source Inventory Status Section 6 Watershed Restoration Plans Legacy work Future Restoration Planning in Progress Appendix A Priority Watersheds Appendix B Showcase of Completed Restoration Projects 2 Introduction Purpose and Forest Setting The Forest’s watershed restoration program focuses on attaining the requirements of the Clean Water Act and Regional Board Basin Plans, but also emphasizes overall watershed health and resilience to possible future climatic extremes, floods and fires. Three focal areas make up the Forest’s restoration program: 1) reducing erosion and sedimentation associated with roads; 2 ) aquatic organism passage; and 3) restoring fire adapted ecosystems. The road improvement work consists of a combination of decommissioning and drainage improvement, making roads better adapted for large storm events. The aquatic organism passage portion of the program promotes organism accessibility to suitable habitats and more natural transport of fluvial ecosystem elements. The fire adapted ecosystem sustainability portion is addressed primarily through fuels and vegetation management programs. The monitoring and reporting requirements of the “Categorical Waiver of Waste Discharge… On Forest Service Lands Order No R1-2010-0029” (June 10, 2010) called for a summary of the key elements of the forests watershed restoration program; these are identification of Key Watersheds, a summary of watershed assessments, a summary of watershed conditions, identification of priority watersheds for restoration, an indication of the status of inventories and restoration implementation plans. Shasta-Trinity National Forest within North Coast Water Region The Shasta-Trinity National Forest is comprised of roughly 2 million acres that lie within two different Water Quality Control Board Regions; the North Coast Region and the Central Valley Regions (see Figure 1.1). There are three sub-basins (4th-field watersheds) that drain the Forest in the North Coast Region; these are Shasta, Trinity and South Fork Trinity River. The Shasta-Trinity National Forest administers roughly 30% of the 7.3 million acres within these subbasins. 3 Figure 1.0 Shasta-Trinity National Forest Watersheds within the North Coast Region 4 SECTION 1 – KEY WATERSHEDS Key Watersheds Key Watersheds provide watershed scale refugia specifically managed for maintaining or recovering habitat for anadromous and resident fish species. These watersheds comprise nearly 40% of USFS lands within the North Coast Water Board Region. There are four Key Watershed Areas on the Shasta- Trinity National Forest that are designated in the Northwest Forest Plan; these are New River, North Fork Trinity River, Canyon Creek and SF Trinity River. Each key area is equivalent to a 5th-field watershed with the exception of South Fork Trinity River which is comprised of two 5th-field watersheds, Upper SF Trinity River and Middle South Fork Trinity River. Management activities focus on restoration and minimizing impacts from roads, with no new roads to be constructed in roadless areas and an overall reduction in existing road mileage. Nonpoint source activities in Key Watersheds receive heightened attention, providing additional water quality protection and improvement. Figure 1.2 Key Watersheds Table 1.1 Shasta-Trinity National Forest Watersheds (& Key Watersheds) Within the North Coast Water Board Region Klamath Basin via Trinity Klamath Basin via Trinity River River Watersheds (HUC5) Watersheds (HUC5) on the on the % USFS Shasta-Trinity National % USFS Shasta-Trinity National Forest Acres Admin Forest Acres Admin Grass Valley-Weaver 567,674 25% Upper Shasta River 314,755 25% Browns Creek 188,503 25% Whitney-Sheep Rock 339,092 33% Canyon Creek 317,613 25% Parks Creek-Shasta River 228,110 25% North Fork Trinity River 389,612 25% Willow Creek 224,666 25% New River 448,094 33% Julien-Shasta River 42,214 0% Burnt Ranch 537,844 25% Little Shasta River 81,473 0% Lower Trinity River 387,873 50% Lower Shasta River 78,839 0% Upper South Fork Trinity River 301,675 33% Main Trinity River 350,985 33% Middle South Fork Trinity River 355,879 33% Coffee Creek 223,938 33% Upper Hayfork Creek 317,298 33% East Fork Trinity River 147,764 50% Lower Hayfork Creek 426,046 33% Stuart Fork 264,493 33% Lower South Fork Trinity River 387,550 33% Trinity Reservoir 317,572 33% Total Watershed Area Key Watersheds 1,812,874 25% Draining From NFS Lands 7,239,563 30% 5 SECTION 2 – WATERSHED ASSESSMENTS Watershed Assessments Watershed Analyses for 5th field watersheds that follow the Federal Guide for Watershed Analysis (Regional Interagency Executive Committee and the Intergovernmental Advisory Committee 1995) are complete over 77% of the watersheds on the forest; 80% of the watersheds in the Trinity River portion of the Klamath Basin is complete and 75% of the watersheds in the Sacramento River portion of the forest. Watershed Analyses are required in the Northwest Forest Plan to conduct activities proposed in Key Watersheds or Riparian Reserves. Copies of these assessments are available to the public online at www.fs.usda.gov/ Links to National Forests by state are available there; after selecting California, then Shasta-Trinity ,a search for “Watershed Assessments” will lead to the Watershed Assessment page (or follow the following hotlink Shasta-Trinity National Forest- Home.) Some of the Watershed Assessments include analyses for more than one watershed and are not necessarily named by watershed. Table 2.1 can be used to determine which documents describe which watersheds and which watersheds remain to be analyzed. Figure 2.1 below displays the status of Watershed Analyses on the forest. Table 2.1 Watershed Analysis Status and Cross walk from Watershed Name to corresponding Watershed Analysis Document ANALYSIS WATERSHED WA NAME ANALYSIS WATERSHED WA NAME BEEGUM CREEK COTTONWOOD CR MIDDLE HAYFORK CREEK M HAYFORK & SALT CR BROWNS CREEK (Incomplete) NORTH FORK TRINITY N. FORK TRINITY RIVER BURNT RANCH SOLDIER BURNT RANCH PLUMMER S. FORK TRINITY RIVER BUTTER CREEK BUTTER CR RAMSHORN U. TRINITY CANYON CREEK NF TRINITY, EFNF TRINITY & CANYON CR RATTLESNAKE CREEK S. FORK TRINITY RIVER CLEAR CREEK U CLEAR CR SALT CREEK M HAYFORK & SALT CR COFFEE CREEK U. TRINITY SHASTA SW (Incomplete) CORRAL CREEK (Incomplete) SHOTGUN-SLATE SHOTGUN-SLATE EAST FORK NEW RIVER NEW RIVER SMOKY S. FORK TRINITY RIVER EAST FORK NORTH FORK TRINITY N. FORK TRINITY RIVER SOLDIER SOLDIER BURNT RANCH EAST FORK SOUTH FORK TRINITY S. FORK TRINITY RIVER SOUTH FORK COTTONWOOD CREEK (Incomplete) EAST FORK TRINITY U. TRINITY STUART FORK U. TRINITY EAST TRINITY RES U. TRINITY SWIFT CREEK U. TRINITY ELTAPOM CREEK (Incomplete) UPPER HAYFORK CREEK U HAYFORK FRENCH FRENCH CREEK UPPER NEW RIVER NEW RIVER HAPPY CAMP S. FORK TRINITY RIVER UPPER PILGRIM (Incomplete) HEADWATERS HEADWATERS SACRAMENTO UPPER SACRAMENTO RIVER MCCLOUD FLATS HIDDEN VALLEY S. FORK TRINITY RIVER UPPER SOUTH FORK TRINITY S. FORK TRINITY RIVER HYAMPOM (Incomplete) UPPER TRINITY U. TRINITY LEWISTON U. TRINITY WEAVERVILLE WEAVERVILLE LOWER HAYFORK LOWER HAYFORK WEST TRINITY RES U. TRINITY LOWER NEW RIVER NEW RIVER WHITNEY (Incomplete) MIDDLE FORK COTTONWOOD COTTONWOOD CR WILLOW-PARKS (Incomplete) 6 Additional concurrent Watershed Assessment methods include the USFS Region 5, Fifth Field Watershed Condition Assessment (R5 USFS 2000) and a new National Watershed Condition Assessment (Oct 2010) that is designed to evaluate watersheds at a sub-watershed or 6th-field scale. The national assessment protocol was recently finalized and is expected to be iterative with initial assessments complete in late spring of 2011. These assessments are intended to evaluate all watersheds on Forest Service lands throughout the entire state and nationwide using a consistent process; by utilizing a consistent approach it is intended to enable better overall program management by improving the Forest Service’s ability to compare restoration priorities throughout the state and nationally. Watershed condition is also assessed routinely in environmental planning analyses that consider past, present and foreseeable future activities to evaluate the potential for off-site cumulative watershed effects. An equivalent roaded acre disturbance model is used for these evaluations; the results of these assessments are displayed in the following section in Figure 3.2 below. 7 Figure 2.1 Watershed Analyses Status, December 2010 8 SECTION 3 – WATERSHED CONDITION Land Management Plan Watersheds of Concern Watersheds of concern designated in the Forest Land and Resource Management Plan (LRMP)( USDA 1994) are Hyampom, Butter Creek, Plummer Creek, Rattlesnake Creek and East Fork South Fork Trinity River; all lie within the South Fork Trinity River Subbasin. Figure 3.1 Shasta-Trinity LRMP Watersheds of Concern Excessive sedimentation within the South Fork Trinity River is being addressed thru the TMDL for South Fork Trinity River and Hayfork Creek (EPA 1998) which
Recommended publications
  • Mainstem Klamath River Fall Chinook Salmon Redd Survey 2012
    1,839U.S. Fish & Wildlife Service Arcata Fisheries Data Series Report DS 2014-39 Mainstem Klamath River Fall Chinook Salmon Redd Survey 2012 Mark Magneson and Philip Colombano U.S. Fish and Wildlife Service Arcata Fish and Wildlife Office 1655 Heindon Road Arcata, CA 95521 (707) 882-7201 November 2014 Disclaimers Funding for this study was provided by the Klamath River Habitat Assessment Study administered by the Arcata Fish and Wildlife Office. Disclaimer: The mention of trade names or commercial products in this report does not constitute endorsement or recommendation for use by the Federal government. The Arcata Fish and Wildlife Office Fisheries Program reports its study findings through two publication series. The Arcata Fisheries Data Series was established to provide timely dissemination of data to local managers and for inclusion in agency databases. The Arcata Fisheries Technical Reports publishes scientific findings from single and multi-year studies that have undergone more extensive peer review and statistical testing. Additionally, some study results are published in a variety of professional fisheries journals. Key words: Chinook salmon, Klamath River, redd, escapement, spawning survey. The correct citation for this report is: Magneson, M.D., and P. Colombano. 2014. Mainstem Klamath River Fall Chinook Salmon Redd Survey 2012. U. S. Fish and Wildlife Service, Arcata Fish and Wildlife Office, Arcata Fisheries Data Series Report Number DS 2014-39, Arcata, California. ii Table of Contents page Introduction ........................................................................................................................
    [Show full text]
  • UKTR Chinook Biological Review Team
    Upper Klamath and Trinity River Chinook Salmon Biological Review Team Report Williams1, T. H., J. C. Garza1, N. Hetrick2, S. T. Lindley1, M. S. Mohr1, J. M. Myers3, M. R. O’Farrell1, R. M. Quiñones4, and D. J. Teel3 1 National Marine Fisheries Service, Southwest Fisheries Science Center, Santa Cruz, California. 2 U.S. Fish and Wildlife Service, Arcata Fish and Wildlife Office, Arcata, California. 3 National Marine Fisheries Service, Northwest Fisheries Science Center, Seattle, Washington. 4 U.S. Forest Service, Klamath National Forest, Yreka, California. December 2011 ii Table of Contents List of Figures.................................................................................................................... iv List of Tables ...................................................................................................................... v 1. Background..................................................................................................................... 1 2. ESU Configuration.......................................................................................................... 2 3. Biological Status of Upper Klamath and Trinity River Chinook Salmon ESU............ 11 4. Conclusions................................................................................................................... 25 5. References..................................................................................................................... 27 iii List of Figures Figure 1. Two generalized patterns of evolution of life-history
    [Show full text]
  • Estimation of Stream Conditions in Tributaries of the Klamath River, Northern California
    U.S. Fish & Wildlife Service Arcata Fisheries Technical Report TR 2018-32 Estimation of Stream Conditions in Tributaries of the Klamath River, Northern California Christopher V. Manhard, Nicholas A. Som, Edward C. Jones, Russell W. Perry U.S. Fish and Wildlife Service Arcata Fish and Wildlife Office 1655 Heindon Road Arcata, CA 95521 (707) 822-7201 January 2018 Funding for this study was provided by a variety of sources including the Klamath River Fish Habitat Assessment Program administered by the Arcata Fish and Wildlife Office, U.S. Fish and Wildlife Service and the Bureau of Reclamation, Klamath Falls Area Office. Disclaimer: The mention of trade names or commercial products in this report does not constitute endorsement or recommendation for use by the Federal Government. The findings and conclusions in this report are those of the authors and do not necessarily represent the views of the U.S. Fish and Wildlife Service. The Arcata Fish and Wildlife Office Fisheries Program reports its study findings through two publication series. The Arcata Fisheries Data Series was established to provide timely dissemination of data to local managers and for inclusion in agency databases. Arcata Fisheries Technical Reports publish scientific findings from single and multi- year studies that have undergone more extensive peer review and statistical testing. Additionally, some study results are published in a variety of professional fisheries aquatic habitat conservation journals. To ensure consistency with Service policy relating to its online peer-reviewed journals, Arcata Fisheries Data Series and Technical Reports are distributed electronically and made available in the public domain. Paper copies are no longer circulated.
    [Show full text]
  • Klamath River Hydroelectric Settlement Agreement Interim Measure 15
    Klamath River Hydroelectric Settlement Agreement Interim Measure 15: Final 2019 Water Quality Monitoring Study Plan Prepared: January 16, 2019 KHSA IM15 2019 STUDY PLAN Table of Contents 1. Introduction and Overview ............................................................................................. 1 2. Objectives ....................................................................................................................... 3 3. Monitoring Components ................................................................................................. 4 3.1 Public Health Monitoring of Cyanobacteria and Toxins .......................................... 4 3.2 Baseline Water Quality Monitoring of the Klamath River ....................................... 4 4. Quality Assurance, Data Management, and Dissemination ............................................ 5 4.1 KHSA Program Quality Assurance Strategy for 2019 ............................................. 5 5. Sampling Constituents and Frequency............................................................................ 7 5.1 Public Health Monitoring of Cyanobacteria and Toxins .......................................... 7 5.2 Comprehensive Baseline Water Quality Monitoring of the Klamath River ............. 9 6.0 References ................................................................................................................... 13 List of Figures Figure 1. 2019 KHSA IM 15 monitoring stations .............................................................. 2 List of Tables
    [Show full text]
  • Little Shasta River 2017-2019: Pre-Project Assessment of the Proposition 1 Ecosystem Restoration Grant Activities
    Little Shasta River 2017-2019: Pre-Project Assessment of the Proposition 1 Ecosystem Restoration Grant Activities Authors: Amber Lukk, Priscilla Vasquez-Housley, Robert Lusardi, Ann Willis Report prepared for: California Trout and California Wildlife Conservation Board December 2019 Contents Introduction ..................................................................................................................................... 1 Study Area ...................................................................................................................................... 1 Methods........................................................................................................................................... 4 Hydrologic Year Type ................................................................................................................. 4 Discharge ..................................................................................................................................... 4 Water Temperature ...................................................................................................................... 5 Water Quality .............................................................................................................................. 5 Aquatic Macroinvertebrates ........................................................................................................ 6 Fish Presence/Absence ...............................................................................................................
    [Show full text]
  • Klamath River Fall Chinook Salmon Age-Specific Escapement, River Harvest, and Run Size Estimates, 2020 Run
    1 Klamath River Fall Chinook Salmon Age-Specific Escapement, River Harvest, and Run Size Estimates, 2020 Run Klamath River Technical Team 15 February 2021 Summary The number of Klamath River fall Chinook Salmon returning to the Klamath River Basin (Basin) in 2020 was estimated to be: Run Size Age Number Proportion 2 9,077 0.17 3 37,820 0.69 4 7,579 0.14 5 8 0.00 Total 54,484 1.00 Preseason forecasts of the number of fall Chinook Salmon adults returning to the Basin and the corresponding post-season estimates are: Adults Preseason Postseason Sector Forecast Estimate Pre / Post Run Size 59,100 45,400 1.30 Fishery Mortality Tribal Harvest 8,600 5,200 1.65 Recreational Harvest 1,300 5,100 0.25 Drop-off Mortality 800 600 1.33 10,700 10,900 0.98 Escapement Hatchery Spawners 12,200 8,300 1.47 Natural Area Spawners 36,200 26,200 1.38 48,400 34,500 1.40 2 Introduction This report describes the data and methods used by the Klamath River Technical Team (KRTT) to estimate age-specific numbers of fall Chinook Salmon returning to the Basin in 2020. The estimates provided in this report are consistent with the Klamath Basin Megatable (CDFW 2021) and with the 2021 forecast of ocean stock abundance (KRTT 2021). Age-specific escapement estimates for 2020 and previous years, coupled with the coded-wire tag (CWT) recovery data from Basin hatchery stocks, allow for a cohort reconstruction of the hatchery and natural components of Klamath River fall Chinook Salmon (Goldwasser et al.
    [Show full text]
  • The Nelson Ranch Located Along the Shasta River Has Two Flow Gaging
    Baseline Assessment of Salmonid Habitat and Aquatic Ecology of the Nelson Ranch, Shasta River, California Water Year 2007 Jeffrey Mount, Peter Moyle, and Michael Deas, Principal Investigators Report prepared by: Carson Jeffres (Project lead), Evan Buckland, Bruce Hammock, Joseph Kiernan, Aaron King, Nickilou Krigbaum, Andrew Nichols, Sarah Null Report prepared for: United States Bureau of Reclamation Klamath Area Office Center for Watershed Sciences University of California, Davis • One Shields Avenue • Davis, CA 95616-8527 Table of Contents 1. EXECUTIVE SUMMARY..................................................................................................................................2 2. INTRODUCTION...............................................................................................................................................6 3. ACKNOWLEDGEMENTS .................................................................................................................................6 4. SITE DESCRIPTION.........................................................................................................................................7 5. HYDROLOGY.....................................................................................................................................................8 5.1. STAGE-DISCHARGE RATING CURVES .......................................................................................................9 5.2. PRECIPITATION........................................................................................................................................11
    [Show full text]
  • Yurok Final Brief
    Case 3:16-cv-06863-WHO Document 107 Filed 03/23/18 Page 1 of 22 JEFFREY H. WOOD, Acting Assistant Attorney General 1 Environment & Natural Resources Division 2 SETH M. BARSKY, Chief S. JAY GOVINDAN, Assistant Chief 3 ROBERT P. WILLIAMS, Sr. Trial Attorney KAITLYN POIRIER, Trial Attorney 4 U.S. Department of Justice 5 Environment & Natural Resources Division Wildlife & Marine Resources Section 6 Ben Franklin Station, P.O. Box 7611 7 Washington, D.C. 20044-7611 Tel: 202-307-6623; Fax: 202-305-0275 8 Email: [email protected] Email: [email protected] 9 10 Attorneys for Federal Defendants 11 UNITED STATES DISTRICT COURT 12 FOR THE NORTHERN DISTRICT OF CALIFORNIA 13 SAN FRANCISCO DIVISION 14 YUROK TRIBE, et al., ) 15 Case No. 3:16-cv-06863-WHO ) 16 Plaintiff, ) ) 17 FEDERAL DEFENDANTS’ RESPONSE v. ) TO DEFENDANT-INTERVENORS’ 18 ) MOTION FOR RELIEF FROM U.S. BUREAU OF RECLAMATION, et al., ) JUDGMENT AND/OR STAY OF 19 ) ENFORCEMENT (ECF No. 101) Defendants, ) 20 ) 21 and ) ) 22 KLAMATH WATER USERS ) ASSOCIATION, et al., ) 23 ) 24 Defendant-Intervenors. ) 25 26 27 28 1 Federal Defendants’ Response to Intervenors’ Motion for Relief 3:16-cv-6863-WHO Case 3:16-cv-06863-WHO Document 107 Filed 03/23/18 Page 2 of 22 1 TABLE OF CONTENTS 2 I. INTRODUCTION 3 3 II. FACTUAL BACKGROUND 5 4 A. Hydrologic Conditions In Water Year 2018 5 5 B. 2013 Biological Opinion Requirements for Suckers 5 6 III. DISCUSSION 7 7 A. Given Hydrologic Conditions, Guidance Measures 1 8 and 4 Cannot Both Be Implemented As They Were Designed Without Impermissibly Interfering With 9 Conditions Necessary to Protect Endangered Suckers 7 10 1.
    [Show full text]
  • SHASTA REPORT Final Cannon
    Removal of Dwinnell Dam and Alternatives Draft Concepts Report Prepared by Thomas Cannon Prepared for Karuk Tribe December 2011 1 Abstract Passage of salmon and steelhead to the upper Shasta River was blocked by the construction of Dwinnell Dam in 1928. Approximately 22 percent of the salmon and steelhead spawning and rearing habitat of the Shasta River was lost with the construction of the dam and reservoir. Spring run Chinook salmon that depended more on the upper watershed became extinct, while fall run Chinook salmon, coho salmon, and steelhead suffered severe declines in numbers from the loss of the upper watershed and long-term degradation of lower watershed habitats. Passage to the upper river could be restored by installing a fish ladder on the dam, trapping and hauling fish around the reservoir, dam removal, or providing a bypass route around the reservoir. These four alternatives are evaluated in this report. All four alternatives would require substantial habitat restoration including development of water supplies and improvements to spawning and rearing habitat and fish passage both above and below the Dam to achieve all the potential benefits. There are approximately 12 miles of accessible habitats to salmon and steelhead above Dwinnell Dam in the mainstem Shasta River, plus a similar amount in tributary creeks. There are approximately 16 miles of accessible habitat in Parks Creek. Dam removal would allow access to all of these habitats, including 4 miles in the reservoir reach, plus improve access and habitat to the six miles of Shasta River below the Dam. Ladder and Trap-and-Haul alternatives would allow access to only 8 additional miles of the upper Shasta River.
    [Show full text]
  • Shasta River Chinook and Coho Salmon Observations in 2013 Siskiyou County, CA
    California Department of Fish and Wildlife Final Report Klamath River Project August 14, 2014 Shasta River Chinook and Coho Salmon Observations in 2013 Siskiyou County, CA Prepared by: Diana Chesney and Morgan Knechtle California Department of Fish and Wildlife Klamath River Project 1625 S. Main Street Yreka, CA 96097 (530) 841-1176 1 California Department of Fish and Wildlife Final Report Klamath River Project August 14, 2014 Shasta River Fish Counting Facility, Chinook and Coho Salmon Observations in 2013 Siskiyou County, CA ABSTRACT A total of 8,021 fall run Chinook salmon (Chinook, Oncorhynchus tshawytscha) were estimated to have entered the Shasta River during the 2013 spawning season. An underwater video camera was operated in the flume of the Shasta River Fish Counting Facility (SRFCF) twenty four hours a day, seven days a week, from August 28, 2013 until December 9, 2013, when the weir sustained structural damage from ice build-up and was removed. The first Chinook was observed on September 9, 2013 and the last Chinook on December 3, 2013. KRP staff also processed a total of 512 Chinook carcasses during spawning ground surveys (of which 469 were used in fork length histograms), 65 Chinook carcasses as wash backs against the SRFCF weir (a systematic 1:10 sample), and 45 live Chinook in a trap immediately upstream of the video flume during the season. Chinook carcasses sampled in the spawning ground surveys ranged in fork length (FL) from 43 cm to 100 cm and grilse were determined to be < 59 cm in FL. Males ranged in FL from 43 to100 cm.
    [Show full text]
  • Schedule of Proposed Action (SOPA) 10/01/2020 to 12/31/2020 Klamath National Forest This Report Contains the Best Available Information at the Time of Publication
    Schedule of Proposed Action (SOPA) 10/01/2020 to 12/31/2020 Klamath National Forest This report contains the best available information at the time of publication. Questions may be directed to the Project Contact. Expected Project Name Project Purpose Planning Status Decision Implementation Project Contact Projects Occurring Nationwide Locatable Mining Rule - 36 CFR - Regulations, Directives, In Progress: Expected:12/2021 12/2021 Nancy Rusho 228, subpart A. Orders DEIS NOA in Federal Register 202-731-9196 EIS 09/13/2018 [email protected] Est. FEIS NOA in Federal Register 11/2021 Description: The U.S. Department of Agriculture proposes revisions to its regulations at 36 CFR 228, Subpart A governing locatable minerals operations on National Forest System lands.A draft EIS & proposed rule should be available for review/comment in late 2020 Web Link: http://www.fs.usda.gov/project/?project=57214 Location: UNIT - All Districts-level Units. STATE - All States. COUNTY - All Counties. LEGAL - Not Applicable. These regulations apply to all NFS lands open to mineral entry under the US mining laws. More Information is available at: https://www.fs.usda.gov/science-technology/geology/minerals/locatable-minerals/current-revisions. R5 - Pacific Southwest Region, Occurring in more than one Forest (excluding Regionwide) Six Rivers Hazardous Fuels and - Wildlife, Fish, Rare plants Developing Proposal Expected:06/2021 09/2021 Carol Spinos Fire Management Project - Vegetation management Est. Scoping Start 11/2020 707-441-3561 EA (other than forest products) [email protected] *UPDATED* - Fuels management Description: The Fuels & Fire Project would authorize a set of manual and mechanical land management tools to prepare our landscapes for up to 8,000 acres of prescribed burning every year.
    [Show full text]
  • Klamath River Fall Chinook Salmon Age-Specific Escapement, River Harvest, and Run Size Estimates, 2018 Run
    Klamath River Fall Chinook Salmon Age-Specific Escapement, River Harvest, and Run Size Estimates, 2018 Run Klamath River Technical Team 14 February 2019 Summary The number of Klamath River fall Chinook Salmon returning to the Klamath River Basin (Basin) in 2018 was estimated to be: Run Size Age Number Proportion 2 11,114 0.11 3 86,717 0.84 4 5,567 0.05 5 9 0.00 Total 103,407 1.00 Preseason forecasts of the number of fall Chinook Salmon adults returning to the Basin and the corresponding post-season estimates are: Adults Preseason Postseason Sector Forecast Estimate Pre / Post Run Size 91,900 92,300 1.00 Fishery Mortality Tribal Harvest 18,100 14,800 1.22 Recreational Harvest 3,500 4,100 0.85 Drop-off Mortality 1,600 1,300 1.23 23,200 20,200 1.15 Escapement Hatchery Spawners 27,900 18,600 1.50 Natural Area Spawners 40,700 53,600 0.76 68,600 72,200 0.95 Introduction This report describes the data and methods used by the Klamath River Technical Team (KRTT) to estimate age-specific numbers of fall Chinook Salmon returning to the Basin in 2018. The estimates provided in this report are consistent with the Klamath Basin Megatable (CDFW 2019) and with the 2019 forecast of ocean stock abundance (KRTT 2019). Age-specific escapement estimates for 2018 and previous years, coupled with the coded-wire tag (CWT) recovery data from Basin hatchery stocks, allow for a cohort reconstruction of the hatchery and natural components of Klamath River fall Chinook Salmon (Goldwasser et al.
    [Show full text]