muskegon watershed research partnership the vision: collaborative,integrated, relevant science for a...
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Muskegon Watershed Muskegon Watershed ResearchResearch
PartnershipPartnership
The vision:The vision:
Collaborative,Collaborative,Integrated,Integrated,
Relevant Science Relevant Science for a better futurefor a better future
http://www.mwrp.net
A Collaborative Approach to Understanding the Dynamics of the Muskegon Watershed: A Comprehensive Model, Risk Assessment, and Tools for Use in Management
Principle InvestigatorsMike Wiley, University of Michigan (Lead Institution)
Bryan C. Pijanowski, Purdue UniversityJohn Koches, Grand Valley State University
Paul Seelbach, Michigan Department of Natural ResourcesCo-investigators: Ed Rutherford (UM),Paul Richards (UM),David Jude (UM),James Diana (UM)Rich O'Neil (MDNR),Doran Mason (NOAA)Brian Eadie (NOAA)R. Jan Stevenson (MSU),David W. Hyndman (MSU),Robert Walker (MSU),Stuart Gage (MSU),Rick Rediske (GVSU),Paul Thorsnes (GVSU),Gary Dawson (Consumers Energy),Dale Black (Brooks TWP, Supervisor).
Affiliated MRP Stake-holder groups:Muskegon Watershed Assembly; MDNR,MDEQ,Consumers Energy Inc.,Trout Unlimited,Brooks Township,Land Conservancy of West Michigan, Timberland RC&D,Lake Michigan FederationMichigan Stream and Lake Association
Integrated Modeling of the Muskegon River: A New Approach to Ecological Risk Assessment for Great Lakes
WatershedsMichael Wiley1, R. Jan Stevenson4, Bryan Pijanowski2, Paul Richards2, Catherine Riseng1,
David Hynman4, Ed Rutherford3, and, John Koches5
Funded by the Great Lakes Fisheries TrustA product of the Muskegon Watershed Research Partnership
1School of Natural Resources and Environment, University of Michigan2 Department of Forestry and Natural Resources, Purdue University,
3 Institute for Fisheries Res., Michigan Department of Natural Resources4 Departments of Zoology and Geology, Michigan State University,
5Annis Center, Water Research Institute, Grand Valley State University, 6 Dept. of Geology, Brocksport-SUNY
Talk Overview
Context: a work in progress1. Time Line: where we are now…2. Highlighted updates on the Mega-Modeling3. Next steps4. Impacts5. Issues
Objective: Comprehensive forecasting tool for Ecosystem Management in Great Lakes Tributaries
Watershed Stakeholders’
Questions
Managementscenario
evaluations
EcologicalInventory &Assessment
MREMSIntegrated modeling
Muskegon River Ecological Modeling System
2001
2002
2003
2004
2005
2006
2007
MODELINGProject
ASSESSMENTProject
Basin wide Modeling Framework
FisheriesModel
Development
Model integration and risk assessment
Watershed Estuary/ Lake Michigan
Muskegon WatershedResearch Partnership
Talk Overview
Context: a work in progress1. Time Line: where we are now…2. Highlighted updates on the MREMS-Modeling3. Next steps4. Impacts5. Issues
Objective: Developing forecasting tools for Ecosystem Management in Great Lakes Tributaries
Watershed Stakeholders’
Questions
Managementscenario
evaluations
EcologicalInventory &Assessment
MREMSIntegrated modeling
Muskegon River Ecological Modeling System
2000,2002
2001-2003
2006
2007Stakeholders’Conference
2001-2005
Model Predicts TypeLTM 2 Land Use change Neural net
MODFLOW Groundwater flow Simulation
MRI_DARCY Groundwater upwelling GIS
HEC-HMS Surface water flows Simulation
MRI_FDUR Surface water flow frequencies RegressionSystem
HEC-RAS Surface water hydraulics Simulation
GWLF Surface dissolved loads Simulation
MRI_LOADS Surface dissolved loads Regression
Regional Assessment Models
All taxa Sensitive taxa EPT Index Algal Index
Fish/insect diversityFish/insect diversityEPT taxa/ Sensitive fishAlgal Index
Regression/Reg TreeRegressionRegressionRegression
Bioenergetic IB Models Steelhead Salmon Walleye
Growth rateandsurvivorship
Simulation Simulation Simulation
Standing Stock ModelsSport fishesTotal fishesSensitive fishesTotal AlgaeFilter-feedersGrazing inverts
Kg/hec total massKg/hec total massKg/hec total massg/m2
g/m2
g/m2
RegressionSEM1
SEM1
SEM1
SEM1
SEM1
MREMS Components
•More is better (some times)
Climate
Reach Hydrology
Reach Hydraulics
Local hydraulics and substratum
Individual Fish growth & mortality
Hec_HMSCoupled to MODFLOW
Hec_RAS
Steelhead IBMTyler and Rutherford 2002
hours ~x00 km2
decades ~ x00 km2
weeks ~x000 km2
days ~x km2
days ~x m2
days x cm2
Landscape
HistoricalDaily/Hourly 1985-2005
LTM2 Neural Net
Example: comprehensive mechanistic modeling across scales
t = 1 day
t = 0=fixed per run
Surfacet = 1 hr GW t = 1 day
t = .1 day
t = 1 day
t = 1 day
UPDATE Highlights UPDATE Highlights
• Now using improved climate data (Now using improved climate data (NEXRAD & Leaf area NEXRAD & Leaf area
index modeling for ETindex modeling for ET))• Improved LTM2 for future Improved LTM2 for future and backcastsand backcasts• Multiple Versions of coupled hydro modelsMultiple Versions of coupled hydro models
running running (including hi-res Cedar,Brooks,Bigelow)(including hi-res Cedar,Brooks,Bigelow)
• Hi-Res Hec-RAS Channel Hydraulics Model: Hi-Res Hec-RAS Channel Hydraulics Model: Croton to Croton to below Newagobelow Newago
• Lower River Fish and Productivity studies wrapping Lower River Fish and Productivity studies wrapping upup
• Dynamic Fish habitat models for L RiverDynamic Fish habitat models for L River(includes new Temperature and Prey Models)(includes new Temperature and Prey Models)
• Hi-RES Steelhead IBMHi-RES Steelhead IBM
NEXRAD for Expanded NEXRAD for Expanded MuskegonMuskegon
Mukegon Expanded watershed boundary with NEXRAD gridcells used for extracting spatially variable precipitation overlaied
• NEXRAD data NEXRAD data becomes available becomes available in 1996in 1996
• 4 km grid cells4 km grid cells• Available for liquid Available for liquid
precipitation onlyprecipitation only• June-September June-September
20032003• Significant Significant
variation even variation even over very short over very short distancesdistances
Baldwin
Stanton
Kent City
Houghton Lake
Gladwin
Grayling
Hesperia
Wellston Tippy
Muskegon
Traverse City
Grand Haven
Glennie Alcona Dam
Cedar Creek Watershed
Thiessen polygons with NCDC weather station names used for determining precipitation across the expanded Muskegon model area and the Cedar Creek watershed
Expanded Muskegon watershed boundary
•Standard Climate Run• synthetic record •1985- 2005
Dynamic Seasonal Vegetation Density Dynamic Seasonal Vegetation Density based on MODIS imagery for Expanded based on MODIS imagery for Expanded MuskegonMuskegon
1km resolution MODIS LAI grids showing vegetation density over the expanded Muskegon and Cedar Creek watersheds
Leaf Area Index (LAI)
<1
1-2
2-3
3-4
4-5
5-6
6-7
Cedar Creek watershed
Expanded Muskegon watershed
Increasing the hidden layers from 1 to 2 increased model performance significantly.On average, one hidden layer correctly predicted around 50% of the cells to transition;the best 2 hidden layer model predicted 79% correctly. (which reflects a 50% increase in model performance!)
Future (Past) Landuse change in MREMSis handled by an enhanced version (LTM2)
of Pijanowski et al.’s Land Transformation Model
Pijanowski, B.C., D. G. Brown, G. Manik and B. Shellito (2002a) Using Artificial Neural Networks and GIS to Forecast Land Use Changes:
A Land Transformation Model. Computers, Environment and Urban Systems. 26, 6:553-575.
Historicalreconstruction
Air Photointerpretation
1830 1978 2020 2040
Neural Netprojection
Neural Netprojection
Historical data sets augmented by neural net predictions provide a temporal framework
•Present {1998}
1978
Urban to AgForest to Ag
•1998
1977
Urban to AgForest to Ag
1976
Urban to AgForest to Ag
1975
Urban to AgForest to Ag
1974
Urban to AgForest to Ag
1973
Urban to AgForest to Ag
1972
Urban to AgForest to Ag
1971
Urban to AgForest to Ag
1970
Urban to AgForest to Ag
1969
Urban to AgForest to Ag
1968
Urban to AgForest to Ag
1967
Urban to AgForest to Ag
1966
Urban to AgForest to Ag
1965
Urban to AgForest to Ag
1964
Urban to AgForest to Ag
1963
Urban to AgForest to Ag
1962
Urban to AgForest to Ag
1961
Urban to AgForest to Ag
1960
Urban to AgForest to Ag
1959
Urban to AgForest to Ag
1958
Urban to AgForest to Ag
1957
Urban to AgForest to Ag
1956
Urban to AgForest to Ag
1955
Urban to AgForest to Ag
1954
Urban to AgForest to Ag
1953
Urban to AgForest to Ag
1952
Urban to AgForest to Ag
1951
Urban to AgForest to Ag
1950
Urban to AgForest to Ag
1949
Urban to AgForest to Ag
1948
Urban to AgForest to Ag
1947
Urban to AgForest to Ag
1946
Urban to AgForest to Ag
1945
Urban to AgForest to Ag
1944
Urban to AgForest to Ag
1943
Urban to AgForest to Ag
1942
Urban to AgForest to Ag
1941
Urban to AgForest to Ag
1940
Urban to AgForest to Ag
1939
Urban to AgForest to Ag
1938
Urban to AgForest to Ag
1937
Urban to AgForest to Ag
1936
Urban to AgForest to Ag
1935
Urban to AgForest to Ag
1934
Urban to AgForest to Ag
1933
Urban to AgForest to Ag
1932
Urban to AgForest to Ag
1931
Urban to AgForest to Ag
1930
Urban to AgForest to Ag
1929
Urban to AgForest to Ag
1928
Urban to AgForest to Ag
1927
Urban to AgForest to Ag
1926
Urban to AgForest to Ag
1925
Urban to AgForest to Ag
1924
Urban to AgForest to Ag
1923
Urban to AgForest to Ag
1922
Urban to AgForest to Ag
1921
Urban to AgForest to Ag
1920
Urban to AgForest to Ag
1919
Urban to AgForest to Ag
1918
Urban to AgForest to Ag
1917
Urban to AgForest to Ag
1916
Urban to AgForest to Ag
1915
Urban to AgForest to Ag
1914
Urban to AgForest to Ag
1913
Urban to AgForest to Ag
1912
Urban to AgForest to Ag
1911
Urban to AgForest to Ag
1910
Urban to AgForest to Ag
1909
Urban to AgForest to Ag
1908
Urban to AgForest to Ag
1907
Urban to AgForest to Ag
1906
Urban to AgForest to Ag
1905
Urban to AgForest to Ag
1904
Urban to AgForest to Ag
1903
Urban to AgForest to Ag
1902
Urban to AgForest to Ag
1901
Urban to AgForest to Ag
1900
Urban to AgForest to Ag
•Circa 1900
SCHEMATIC MODEL OF MREMS-HEC SCHEMATIC MODEL OF MREMS-HEC COUPLED WITH COUPLED WITH MODFLOWMODFLOW
strestreamam
INTERNALLY-DRAINEDINTERNALLY-DRAINED AREASAREAS TOPOGRAPHICALYTOPOGRAPHICALYCONNECTEDCONNECTED
RoadRoadHousesHouses
EVAPEVAP
RECHARGERECHARGE
EVAPEVAP
RUNOFFRUNOFF
IMP RUNOFFIMP RUNOFF
PRECIPPRECIP
STREAMSTREAM
RECHARGERECHARGE
PRECIPPRECIP
SNOWPACKSNOWPACK
MODFLOWMODFLOW22
HEC-HMSrouting
Custom SMAModule 1,2
1. P. Richards, SUNY:Brockport based on GWLF hydrology code2. Custom implementation by D. Hyndman and A. Kendall, Michigan State University
MODFLOWMODFLOW takes the recharge data and iterates takes the recharge data and iteratesa steady state solution to Darcy’s law for each Daya steady state solution to Darcy’s law for each DayOf the simulation period.Of the simulation period.
Figure 6 - Modeled hydrographs for Cedar Creek using observed 1998 and LTM projected 2040 landcover scenarios. Precipitation and temperature patterns, and all other variables held constant. Days are arbitrary simulation dates.
MREMS can be used to evaluate effects of alternate land use patterns
1978
2040
1830
Cedar Creek
Historical climate > Obs and forcast Land cover >HEC_HMS*
Example of multiple ecological responses predicted by MREMS in preliminary runs for a “Fast Growth” scenario. Change rates for a 1998 to 2040 time frame comparison. Site hydro
% DD 1 Channel2
Response % SedLoad
3 %TDS4 Fish
spp. loss
Cedar Creek -13 % aggrade +26 % +32% 3-4 Brooks Creek -22 % aggrade +72 % +20% 1-2 Main River @ Evart 0 % No change +1% +20% 2-3 Main River @ Reedsburg 0 % No change +6 % +3% 0-1
1 %DD: Percent change in Dominant Discharge (determines the size of the equilibrium channel); product of HEC_HMS run and empirical load model. 2 Channel response: expected response based on %DD 3 %SL: Percent increase in average daily sediment load [tonnes/day] 4 %TDS: Percent change in median Total Dissolved Solids concentration (ppm)
MREMS scenario runs target the entire watershed and provide a time-dependent context for understanding ourCurrent conditions, identifying risks that lie ahead, and a testing ground for alternate Management Scenarios.
MRW Outline
Modeled Depth to Water
in meters
High : 177.8
Low : 0
At the end of each time step………At the end of each time step………
B = A* K/T * (head – stream elev*)B = A* K/T * (head – stream elev*)B = baseflow average for monthB = baseflow average for monthA = Cell areaA = Cell areaK = conductivityK = conductivityT = 1 T = 1
Coupled Modflow MREMS modelGroundwater flux per river km
0
10
20
30
40
0 50 100 150 200 250 300 350
River length (km)
GW
flux
(cfs
/km
)
Evart
/CROTON//FLOW/01JAN1999/1DAY/OBS/
1999 2000 2001 2002 2003 2004
1999 2000 2001 2002 2003 2004
0
50
100
150
200
250
GIS used to assemble reach-scale channel models from multiple data GIS used to assemble reach-scale channel models from multiple data sources sources
Air Photos (1998)Field survey reconnaissanceAcoustic Doppler profiling
Cross-section profiles were then extracted (using GeoRAS) for HEC_RAS
182 12979.97
12844.5112726.27
12655.3*12584.38
12221.5412160.0*
12098.49
12034.6*
11970.7711812.1*
11656.3*
11496.3*
11344.8*11208.1*11070.65
10917.5*10700.9*
10532.5*10434.*
10335.49
9722.78*9645.68*
9568.5949122.06*
8886.17*8811.5118623.773
8451.5907952.06*
7723.46*7420.68*
7266.48*7188.16*7109.840
7022.23*
6934.6206550.720
6475.64*6400.55*
6325.4786028.507
5888.78*
5730.18*5641.44*5552.707
5410.12*
5253.43*
5168.03*
5082.642
4839.1454541.97*4202.10*
3789.26*3618.385
3518.43*
3418.475
3255.86*
3093.2493001.66*2910.08*2818.500
2663.1461943.01*
1328.43*1186.3501117.94*1049.53*981.133
795.253*
535.085*
451.471183.230*
LMR
Area0Area1
Area2
HEC_RAS Simulations run for 1 year
167 transects20-50 cells per transect (Q dependent)Typically ~4000-5000 cellsDepth, Velocity, SubstratePrey density inferred from cell substrate
Valley segment Hydraulic model 12.91 km for 18.2
0 2000 4000 6000 8000 10000 12000 14000190192194196198200202204206208
test Plan: Plan 2001 5/11/2005
Main Channel Distance (m)
Ele
vatio
n (m
)
Legend
WS 31DEC2001 2400
Ground
12.75
12.49 12.13
12.00 11.88
11.64 11.49
11.32 11.18 10.98
10.75 10.54 10.39*
10.24 9.59*
9.47 9.20 8.94
8.83* 8.72 8.53
8.36 7.78
7.4*
7.135* 7.02
6.84
6.345* 6.23 5.93
5.73 5.595* 5.46
5.25 5.12*
4.99 4.75 4.54 4.27 3.905* 3.65* 3.52
3.32 3.00 2.86* 2.72
2.57 1.75
1.31 1.09 .99* 0.89
0.61 .485*
0.36
musk_18_2 Plan: Plan 02 2/10/2005 Legend
WS PF 1Ground
Bank Sta
Levee
Ground
Example cross-sectionunsteady (continuous) run for: VSEC unit 18.2: yr=2001Cross section ID= 6742.67 (meters up from downstrean end of 18.2)
Flows can be driven by hydrographs from gage records or MREMS hydrologic models
Dynamic Fish Habitat Dynamic Fish Habitat ModelingModeling
•Adult Walleye habitat•2001 by month• VSEC 18.2•HSI-based
Steelhead IBM operating inSteelhead IBM operating inMuskegon River VSEC 18.1-4Muskegon River VSEC 18.1-4
Day of Year
100 150 200 250 300 350
YO
Y D
ensi
ty (
num
ber
* m
-2)
0.01
0.1
1
10
Data20012003
First split:
Groundwater vs. Runoff
GradientDrainage Area
Second split:
Classification Tree
Presence/Absence location
Model development
Chinook present
•Ed Rutherford and Crew
Results
Total Smolts: 1,025,902
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
River
Sm
olt
s
Chinook smolt estimateSmolt per river system
•Ed Rutherford and Crew
Lower River Productivity Lower River Productivity GVSU,MSU,UMGVSU,MSU,UM
Mosaic of aerial photos from the lower Muskegon River watershed, showing habitat maps of a wetland area (left) and stream segment (right), as well as preliminary data collected on algal biomass in wetland, stream and lake sites in spring 2004. Larger circles indicate more productivity.
What’s next on the MREMS What’s next on the MREMS agenda?agenda?
• Model integration completed June 2006Model integration completed June 2006
• Landscape and Hydrology Scenario runs Landscape and Hydrology Scenario runs completed by Sept 2006completed by Sept 2006
• Stake-holder scenario modeling completed Stake-holder scenario modeling completed by Dec 2006by Dec 2006
• Final report out to Stakeholders Summer Final report out to Stakeholders Summer 20072007
GLFT-MWRP Technology Transfer and DiffusionSpin-off or Linked /Leveraged Funded Research•EPA-STAR ILWIMI Lake Michigan Assessment•EPA-STAR Multi-stressor dynamics•UM/NOAA Isotopic analysis of lower river foodwebs•USGS Great Lakes Aquatic-GAP analysis•GLFT/GLFC Big River Habitat Methodology•GLFC Modeling Lamprey Habitats•NOAA (pending) Integrated Assessment with MDNR•GLFT (pending) Hires IBM modeling expansion
•13 papers published & In Press in peer-reviewed outlets•15 more currently in review and submission•>60 talks/posters at National/International Scientific Meetings
•Regional/ National/ International impacts•Collaborative studies: Muskegon Watershed Assembly, MDNR, MDEQ•Collaborative educational presentations: Michigan Lakes and Streams Assosciation•MDEQ nutrient criteria legislation•MDNR Ecoregional planning and groundwater protection programing•National Nutrient Criteria Working Group•Western States EMAP•Poyang Lake Watershed Partnership (China)•Ganges River Modeling and assessment (India)•Landuse change/planning (E.Africa)
Issues:Data & Topic Volumes! :ComplexityCoordination & Communication2007 and Disposition
Objective: Developing forecasting tools for Ecosystem Management in Great Lakes Tributaries
Watershed Stakeholders’
Questions
Managementscenario
evaluations
EcologicalInventory &Assessment
MREMSIntegrated modeling
Muskegon River Ecological Modeling System
2000,2002
2001-2003
2006
2007
2001-2005
How might variations in hydrology affect How might variations in hydrology affect habitat and fish recruitment in the Lower habitat and fish recruitment in the Lower River?River?
/CROTON//FLOW/01JAN1999/1DAY/OBS/
1999 2000 2001 2002 2003 2004
1999 2000 2001 2002 2003 2004
0
50
100
150
200
250