Trends in Sediment Delivery from Bay Area Watersheds determined from sediment budget analysis Peter W. Downs Stillwater Sciences, Berkeley, CA.

Slides:



Advertisements
Similar presentations
April 4, 2008 Variation in salmonid bed-habitat conditions with sediment yields in Lagunitas and San Geronimo Creeks Marin County, California Barry Hecht,
Advertisements

1 WATERSHED SPECIFIC AND REGIONAL SCALE SUSPENDED SEDIMENT LOAD ESTIMATES FOR BAY AREA SMALL TRIBUTARIES Mikołaj Lewicki and Lester McKee Sources Pathways.
Trends in Suspended Sediment Input to the San Francisco Bay from Local Tributaries Presented by Setenay Bozkurt Philip Williams &
Bankfull / Effective / Dominant
Geomorphic Context for Sediment Sources, Movement, and Deposition in the Bad River, Bad River Reservation, Wisconsin By Faith Fitzpatrick 1, Kirsten Cahow-Scholtes.
Process Geomorphology 9/20/2011. Pattern to Process, Process to Pattern.
WATERSHED – BAY INTERACTIONS: ANTHROPOGENIC INFLUENCES ON SEDIMENT SUPPLY, TRANSPORT, AND STORAGE Laurel Collins, Watershed Sciences, Berkeley, CA
Stream Geomorphology Leslie A. Morrissey UVM July 25, 2012.
Project Collaboration In 1999, as a result of several years of monitoring of neotropical migratory birds such as the willow flycatcher, Jim Steele from.
Gravel Mining Ryan Kindt Kristina Lowthian CIVE 717 April 9, 2012 Gualala River, California fly-over, Courtesy: Jamie Hall.
Section 3: Stream Deposition
Multi-scale Analysis of Sediment Yield in a Glaciated Environment Beverley C. Wemple 1 and Rebecca K. R. Ambers 2 1 Dept. of Geography, University of Vermont,
Towards a Rogue River Estuary Implementation Plan John Gardiner MBE, PhD, PE (Oregon)
1 Quantifying Hydromodification Impacts and Developing Mitigation Using a Four Factor Approach Judd Goodman CASQA Conference November.
Forest Hydrology Issue: Interaction of forests, fish, and climate One of the dominant pathways by which land cover change affects freshwater fish habitat.
S. Fork Nooksack River, WA. Reasons for Land Clearing Agriculture Lumber Mining Urban Development.
Hoover Dam – Colorado River. Reasons for Dams Flood Control 39,000 dams worldwide higher than 15 m (ICOLD, 1988)
ECOLOGICAL SERVICES RESTORATION PROJECT BLOSSOM WAY CREEK, ROGERS, ARKANSAS Morgan, R.A.; E. Cummings; S. Ekka; G. Goh; A. Ludwig; M. Matlock; A. McAllister;
Geomorphic Effects of Dams on Rivers Gordon Grant.
Lecture ERS 482/682 (Fall 2002) Erosion and sediment transport ERS 482/682 Small Watershed Hydrology.
Biological Objectives Tied to Physical Processes Dr. William Trush Scott McBain Arcata, CA.
Fundamentals of River Restoration and Salmonid Fisheries OWEB, 1999, Fundamentals of River Restoration and Salmonid Fisheries OWEB, 1999, Fundamentals.
Intro to Geomorphology (Geos 450/550) Lecture 5: watershed analyses field trip #3 – Walnut Gulch watersheds estimating flood discharges.
RIVER PROCESSES Introduction to Watershed Science Merritt College Marc Epstein, Instructor.
Temporal and spatial patterns of basin scale sediment dynamics and yield.
FLOODS A. Ramdial. INTRODUCTION Floods are a natural river process in response to changes in drainage basin inputs (precipitation / melt-water runoff)
Project Activity: Riparian Zone Restoration Scott Compton, Watershed Program Manager Valles Caldera National Preserve.
Flooding New Orleans, Aug Flooding –Varies with intensity and amount of rainfall –Perhaps the most universally experienced natural hazard Flood.
Icicle Creek Salmon Habitat Conditions* Land Development has affected stream channel movement, off channel habitat, and LWD recruitment. Barriers to migration.
Chapter 16: Running Water. Hydrologic cycle The hydrologic cycle is a summary of the circulation of Earth’s water supply Processes involved in the hydrologic.
Stream Processes and Habitat Ryan Johnson. Overview Watershed Processes – Factors and their effects on the watershed as a whole Stream Processes – Factors.
Oregon Case Studies Ryan Johnson. Studies  The response of impounded sediment to a culvert replacement project on Sutter Creek, a tributary of Honey.
Sediment Issues within Transboundary Basins Presented by Paul Bireta and Fernando Salas April 12, 2012.
How do humans affect watersheds and the hydrologic cycle ?
Soil Erosion TSM 352 Land and Water Management Systems.
San Pedro Creek: A Longitudinal Profile Study Andrew Georgeades Anne Jurek Mary Snow.
Streams (Rivers). Runoff: H 2 0 that does not sink into ground Most ends up in streams.
Streams (Rivers) Sci 6.1. Runoff: H 2 0 that does not sink into ground Most ends up in streams.
Chapter 11 – WATER ON THE GROUND
Watersheds Chapter 9. Watershed All land enclosed by a continuous hydrologic drainage divide and lying upslope from a specified point on a stream All.
River Systems Earth Space Science Mr. Coyle. The Hydrologic Cycle Infiltration = Groundwater System Runoff = Surface Water System Runoff = Precipitation.
Baird Claytor Hydroelectric Project Sedimentation Study.
Using GIS and the PSIAC Method to Predict Watershed Sediment Yield Rates Eric Berntsen.
Natural vs. Accelerated Soil Erosion Natural geologic erosion has occurred at a relatively slow rate since the earth was formed. Natural erosion produces.
Landform Geography Landforms of the Fluvial System.
© 2011 Pearson Education, Inc. Running Water Earth, 10e - Chapter 16.
How do humans affect watersheds and the hydrologic cycle ?
Erosion and Sedimentation Erosion – Detachment, movement and deposition of soil by water, wind, ice or gravity. Sediment – Particles derived from inorganic.
A Sediment Budget for Two Reaches of Alameda Creek (1900s through 2006) Paul Bigelow, Sarah Pearce, Lester McKee, and Alicia Gilbreath.
Christie Beeman and Jeff Haltiner Philip Williams & Associates Hydrograph Modification: An Introduction and.
Intro to Geomorphology (Geos 450/550) Lecture 7: channel geometry and sediment transport power laws in channel geometry bed load sediment transport Rouse.
Section 3: Stream Deposition
River Systems. Objective  Students will describe factors that affect the erosive ability of a river and the evolution of a river system.
Natural and artificial hydromorphological changes in Norway Agnès Moquet-Stenback – Section for erosion and sediment transport – Hydrology.
7. Hillslopes; surface erosion and mass movements
Completing the SF Bay Mercury TMDL Carrie Austin SF Bay Water Board.
Watersheds, Baylands and the Bay: Putting Landscapes Back Together or Rethinking Drainage around SF Bay Josh Collins, San Francisco Estuary Institute.
Fine sediment transport. Fines Till derived soils (e.g., Clarion) ~ 45-70% fines Alluvial soils (e.g., Coland) 65-80% fines Loess-derived soils ~ > 80%
SONOMA CREEK AND SEDIMENT: KNOWING WHAT WE DON’T KNOW MAY 2011.
Managing Natural Water Storage for Climate Change Adaptation.
Predicting the hydrologic implications of land use change in forested catchments Dennis P. Lettenmaier Department of Civil and Environmental Engineering.
Agricultural Soil and Water Conservation Stewardship
Estimating Annual Sediment Yield and a Sediment Delivery Ratio for Red Creek, Utah and Wyoming Paul Grams Department of Geography and Earth Resources.
Fundamentals of River Restoration and Salmonid Fisheries OWEB, 1999, Fundamentals of River Restoration and Salmonid Fisheries Dylan Castle.
Morphodynamic and Sediment Tracers in One-Dimension
Predicting the hydrologic and water quality implications of climate and land use change in forested catchments Dennis P. Lettenmaier Department of Civil.
Hydrology CIVL341.
Hydrology CIVL341 Introduction
State Water Board Order WR95-17: MMWD Compliance Reporting
River Systems Chapter 15.
Presentation transcript:

Trends in Sediment Delivery from Bay Area Watersheds determined from sediment budget analysis Peter W. Downs Stillwater Sciences, Berkeley, CA

Lagunitas Creek – sediment budget since 1983 Periods : European arrival & resource development : regulation and grazing : intensive damming 1983-present: raising of Peters Dam, planning, mitigation = 93.3 km 2 = 64.3 km 2 = 55.7 km 2 = 49.0 km 2 = 19.1 km 2 Total area = km 2

Data sources Establishing rates existing quantitative sediment source inventories analysis of sequential aerial photographs hillslope and in-channel reconnaissance digital terrain modeling of GLUs for extrapolation soil production / diffusion model application road sediment model application Corroborating rates literature review of nearby process rates estimates analysis of gauging records for sediment yields bathymetric surveys of Nicasio Reservoir Management scenarios sediment transport modeling Approach

Finite set of probably relevant processes Process category ProcessesMethod Hillslope mass wasting Creep / biogenic transport Shallow and deep landsliding Numerical modeling (UCB) Field surveys / air photos Overland Flow Sheetwash and Rill erosion Field surveys Channel production Head advance / knickpoint Gullying and incision Bank erosion Field surveys / air photos Structure / vegetation ages Field surveys Road-related Cut & fill failures Surface and crossing erosion Gully formation Numerical modeling (SEDMODL2), field surveys Agriculture Surface wash, accelerated runoff, shallow landsliding, bank destabilization Field surveys / air photos Urban Fine sediment release, accelerated runoff Field surveys / air photos Channel Management Destabilization: straightening, riparian veg removal Forced storage Field surveys / air photos Routing and Storage Sediment transport Channel & overbank storage Numerical modeling (TUGS) Field / x-section data

Discrete hillslope sources From air photo analysis From field surveys

Extrapolation via Geomorphic Landscape Units

Road-related erosion – SEDMODL2

Channel-related erosion Bank erosion Channel incision

Corroboration 1: Gauged sediment yields San Geronimo SPT PRS Gauge Location Average annual bedload (t a -1 ) Average annual suspended sediment load (t a -1 ) Average annual total sediment load (t a -1 ) Average annual unit total sediment load (t km -2 a -1 ) San Geronimo Creek at Lagunitas Rd. bridge (MMWD gauge) 1,6703,6685, Lagunitas Creek at Samuel P. Taylor State Park (USGS gauge ) 6413,6314, Lagunitas Creek at Pt. Reyes Station (USGS gauge ) 2,58414,64017,224276

Section 12B-12A Section 6A-6B Corroboration 2: Bathymetric yields

Study area Contributing drainage area (km 2 ) Sediment yield into reservoir study area (t a -1 ) MMWD estimate for the period of /6 Stillwater Sciences bathymetry survey estimate for the period of Stillwater Sciences GLU estimate for the period of Nicasio/Halleck Creek arm ,10025,47917,533 Entire Nicasio Reservoir (u/s of Seeger Dam) ,640N/A26,595 Bathymetric yields versus GLU

Watershed Area Sediment yield derived from sediment rating data Unit rate Bathymetry survey estimate Unit rate Sediment delivery estimated from extrapolated field survey Unit rate km 2 WY 1983–2008 t a -1 t km -2 a -1 WY 1961–2008 a WY 1961–1976 b t km -2 a -1 WY 1983–2008 t a -1 t km -2 a -1 San Geronimo Creek 23.15,340231n/a8, Lagunitas Creek at Samuel P. Taylor 32.74,270131n/a12, Lagunitas Creek at Pt. Reyes Station ,220276n/a19, Nicasio/Halleck Creek arm 54.9n/a25,500 a 46417, Whole Nicasio Reservoir 93.2n/a32,640 b 35026, Comparison of sediment delivery / yield results

Sediment Budget – sub- watershed Sediment Yields t a -1 M = mainstem T = tributary & hillslope

Sediment Budget – processes Sediment Yields t a -1 42% 26% 20% Unit Hillslope & tribs Main- stem Total Yield t km -2 a -1 SanGeron LagCr: SGC to DG Devils Gulch LagCr: DG to Nicasio Regulated Nicasio Cr LagCr: NC to PRS

Implications for the SF Bay…or “So What?” Lagunitas Creek (62.4 km 2 ) ~ 330 t km -2 a ~ 330 t km -2 a -1 –(Gauges = 131 – 276; bathymetry = 350 – 464; GLUs = 285 – 383) Southern Tomales bay sedimentation ( km 2 ): Rooney & Smith (1999) : 325 t km -2 a -1 (prograded primarily ) : 325 t km -2 a -1 (prograded primarily ) : 290 t km -2 a : 290 t km -2 a : 190 t km -2 a -1 (dry period; not efficient trapping) : 190 t km -2 a -1 (dry period; not efficient trapping) Redwood Creek (22.7 km 2 ) Pre 1840: 34 t km -2 a -1 Pre 1840: 34 t km -2 a : 304 t km -2 a -1 – Euro Arrival and Resource Development: : 304 t km -2 a -1 – Euro Arrival and Resource Development: : 324 t km -2 a -1 – Engineering as Management: : 324 t km -2 a -1 – Engineering as Management: : 198 t km -2 a -1 – Recovery & Restoration – reduces with incision : 198 t km -2 a -1 – Recovery & Restoration – reduces with incision Future: 154 t km -2 a -1 – because of legacy destabilization of tributaries Future: 154 t km -2 a -1 – because of legacy destabilization of tributaries

Redwood Creek ‘Wolman Curve’

Pre Redwood Creek

Estuarine Deposits Jon Warrick’s slides

Infilling: you bet! – Redwood Creek Big Lagoon Time period Measure Unit rate Pre Total Yield to Big Lagoon m 3 a Sedimentation rate (ave = 14%BL+50% susp intercepted) mma Morphological rate mma Sea-level rise mma

Thoughts…Sac/SJR vs. SF Bay Area Tribs? Pre-European – less “well-connected”: effective area smaller, overbank storage; Pre-European – less “well-connected”: effective area smaller, overbank storage; ~30 t km -2 a -1 ?~30 t km -2 a -1 ? Post-arrival, “resource development”, channel management, first flush: Post-arrival, “resource development”, channel management, first flush: > 350 t km -2 a -1 ; 500 t km -2 a -1 over decades?> 350 t km -2 a -1 ; 500 t km -2 a -1 over decades? Now, “normal” developed use = > 300 t km -2 a -1 Now, “normal” developed use = > 300 t km -2 a -1 Much from channelsMuch from channels Under “protective custody” = < 200 t km -2 a -1 in high relief watershed Under “protective custody” = < 200 t km -2 a -1 in high relief watershed Incision (loss of alluvial storage) is a very effective delivery mechanism Incision (loss of alluvial storage) is a very effective delivery mechanism 100% delivery; very little overbank storage100% delivery; very little overbank storage Not just volumes: changing sediment sources, and sediment caliber Not just volumes: changing sediment sources, and sediment caliber

Conceptual Model Yields proportional to: Relief Relief Relative erodibility (geology) Relative erodibility (geology) Frequency of large floods / high intensity precipitation events – ENSO Frequency of large floods / high intensity precipitation events – ENSO Fire / earthquakes triggering landslides Fire / earthquakes triggering landslides Effective contributing area – tributary disconnection Effective contributing area – tributary disconnection (Availability of marsh / lagoon / estuary habitat ) (Availability of marsh / lagoon / estuary habitat ) Land use history: agriculture vs. conservation management Land use history: agriculture vs. conservation management Road and rail Road and rail Channel management impacts on disconnecting floodplains: straightening (drainage or flood control) Channel management impacts on disconnecting floodplains: straightening (drainage or flood control) Dams: existing and former – supply reduction them increase Dams: existing and former – supply reduction them increase Urban development – supply increase then reduction then increase… Urban development – supply increase then reduction then increase… Aggregated mining – interception possibly, more likely narrowing and baseline related incision Aggregated mining – interception possibly, more likely narrowing and baseline related incision 1 / Area 1 / Area