Great Lakes Water Levels and Coastal Systems Coastal Resiliency and Climate Change Scudder D. Mackey, Ph.D. Ohio Department of Natural Resources Lake Erie.

Slides:



Advertisements
Similar presentations
Ecosystem Flows Hydrology and Connectivity Joe Trungale October 2, 2006.
Advertisements

River Regulation / Dam Construction – Effects on Rivers and Streams.
Group 1: Tonle Sap Location: Roberto 1.Mr. Carl Middleton 2.Mr. Chea Chan Tou 3.Mr. Eric Guerin 4.Mr. Ganesh Pangare 5.Mr. Hiek Sopheap 6.Mr. Hourt Khieu.
1 Floodplain Management Session 13 Biology Management and restoration of floodplain ecology Prepared by Susan Bolton, PhD, PE.
Lake Status Indicator Selection and Use in SLICE David F. Staples.
AIACC Regional Study AS07 Southeast Asia Regional Vulnerability to Changing Water Resources and Extreme Hydrological due to Climate Change.
Lake Status Indicator Selection David F. Staples Ray Valley.
Aquatic Ecosystems Monday, August 22nd Reminder: HW3 Part II due Wednesday! Midterm Thursday.
Translating climate science into urban conservation action Abigail Derby Lewis The Field Museum, Science Action Center Chicago Wilderness, Climate Action.
Yellow Perch & Climate Change How will a changing climate affect Lake Erie yellow perch? OHSU-TS
Dave Sauchyn, Ph.D., P.Geo. C-CIARN Prairies Prairie Adaptation Research Collaborative Senate Committee on Agriculture and Forestry Ottawa, December, 2002.
WP12. Hindcast and scenario studies on coastal-shelf climate and ecosystem variability and change Why? (in addition to the call text) Need to relate “today’s”
An Investigation on the Effects of Climate Change On Algal Blooms in Lake Champlain Patricia Brousseau, Lauren Chicote, John Keyes, Jenna Mandelbaum, Christopher.
Consequences of Global climate Change. Impact of Global Warming Sea level rising Altered precipitation pattern Change in soil moisture content Increase.
April 22, 2003 IERM Overall Objectives 1.Quantify relationship between hydrologic and hydraulic attributes and effects on selected ecological performance.
1 Issue: Society Depends on Ecosystem Modeling to Predict Threats and Minimize Risk.
State Partnerships: Coastal & Environmental Issues Facing the MACOORA States November 17, 2009 MACOORA Kate Zultner Coastal States Organization
Future Research NeedsWorld Heritage and Climate Change World Heritage and Climate Change - Future Research Needs Bastian Bomhard World Heritage Officer.
Presentation to the Workshop Climate Change and Great Lakes Water Levels March 30, 2001 Chicago, Illinois Gerald E. Galloway, Jr., P.E., Ph.D. International.
Integrated Ecosystem Assessment for the Gulf of Mexico Becky Allee Gulf Coast Services Center.
History of the Great Lakes. Summary Formation About the Great Lakes The Individual Lakes The Great Lakes Restoration Act Restoration Goals.
Climate Change Adaptation : Case Studies U.S. Fish and Wildlife Service May 14, 2008.
Ganga Basin Hydrologic Regime – Environmental Flow Perspective World Bank and INRM Consultants New Delhi February, 2015.
Estuaries Payton Collins December 1 st, The Basics and Terminology  An estuary is the area in which rivers meet the sea.  One of the most productive.
U.S. Department of the Interior U.S. Geological Survey USGS Great Lakes Science Center Great Lakes Research.
IPCC WGII Third Assessment Report – Regional Issues with Emphasis on Developing Countries of Africa Paul V. Desanker (Malawi) Coordinating Lead Author.
Climate Change: SEAFWA Thoughts? Ken Haddad, Executive Director Florida Fish and Wildlife Conservation Commission September 2007.
Ecosystem Forecasting Testbed David J. Schwab NOAA Great Lakes Environmental Research Laboratory.
 Impacts on the Environment.  Crops o Moderate warming and more carbon dioxide in the atmosphere may help plants to grow faster. However, more severe.
Lake Huron Initiative: A Work in Process Presented by: Jim Bredin - Michigan Office of the Great Lakes.
Background:Project Background * Work Statement * Relevance Study Area Methodology:Past Studies Data Preparation *? Actual Data Adjustments * Modeling Procedure.
KATLYND REESE AQUATIC ECOLOGY 9 NOVEMBER 2011 Hypoxia or “Dead Zones” in Aquatic Systems.
By Geoff, Grant, and Brendan. Lakes Increase air temps/ decrease winter ice cover increases lake water evaporation. Inland lake management and associated.
1 Floodplain Management Session 10 Biology Biological Landscape Prepared by Susan Bolton, PhD, PE.
Development of a Linked Hydrodynamic – Sediment Transport – Water Quality Model for the Lower Maumee River and Western Lake Erie Basin Joseph DePinto,
NYS Department of Environmental Conservation Climate Change Adaptation Challenges: Maintaining Ecosystem Services in Shoreline Management.
Coastal development impacts on biological communities in the Chesapeake Bay Examples from the Atlantic Slope Consortium R
Stream Processes and Habitat Ryan Johnson. Overview Watershed Processes – Factors and their effects on the watershed as a whole Stream Processes – Factors.
Climate: Outlook and Operational Planning Jayantha Obeysekera (’Obey’), Ph.D.,P.E.,D.WRE Department Director Hydrologic & Environmental Systems Modeling.
1 Restoring Water Levels on Lakes Michigan-Huron: Impact Analysis IUGLS Study Board Meeting Windsor, ON Nov 30, 2010 Bryan Tolson 1 Masoud Asadzadeh Saman.
EPA and Flood Risk – Programs and Perspectives Rob Wood Acting Deputy Office Director Office of Wetlands, Oceans and Watersheds U.S. Environmental Protection.
Impacts of climate change on the Chicago River system.
St. Johns River Water Management District Special Publication SJ97-SP8 Water Management Alternatives: Effects on Lake Levels and Wetlands in the Orange.
Looking at Impacts of Climate Change on Seattle City Light Lynn Best, Director Environmental Affairs.
Managing Western Water as Climate Changes Denver, CO February 20-21, 2008.
1 State of San Lorenzo River Symposium Nicole Beck, PhD 2NDNATURE April San Lorenzo Lagoon A Decade of Dry Season WQ Monitoring.
Engineering Hydrology (ECIV 4323)
I. Alaska, Yukon and Coastal British Columbia Lightly settled/ water abundant region. Increased spring flood risks Glacial retreat/disappearance in south;
Climate Limnos / Ocean Biota Global –> Regional Climate Models (e.g. CGCM -> Great Lakes down-scaled projections) Air Temperature, Humidity, Precipitation,
Great Lakes Environmental Research Laboratory Review – Ann Arbor, MI November 15-18, Click to edit Master text styles –Second level Third level.
A Pivotal Moment for Leaders Across the Gulf Coast States and Connected Communities Throughout the Country.
January 27, 2011 Summary Background on Delta Flow and Habitat Relationships Delta Stewardship Council Presentation by the Independent Consultant.
Population - 44,301 18% - Aged 65+ Household Median Income- $29,530 Jan.-March 2004 unemployment 14 % Demographics.
Natural and artificial hydromorphological changes in Norway Agnès Moquet-Stenback – Section for erosion and sediment transport – Hydrology.
Sustaining Lakes in a Changing Environment - SLICE.
Restoration Ecology. CB Carbon cycle Fig
Environmental Flow Instream Flow “Environmental flow” is the term for the amount of water needed in a watercourse to maintain healthy, natural ecosystems.
MRERP Missouri River Ecosystem Restoration Plan and Environmental Impact Statement One River ▪ One Vision A Component of the Missouri River Recovery Program.
DELAWARE NATIONAL ESTUARINE RESEARCH RESERVE Promoting stewardship of the nation’s coastal areas through science and education …
57th Annual Meeting of the GLFC Buffalo, NY June 6-7, 2012 Water Level Regulation in the LO/SLR System Environmental Considerations and Plan BV7.
Adapting to Climate Change: Using the Green to Beat the Blues Roberta Clowater Executive Director Canadian Parks and Wilderness Society - New Brunswick.
Developing recommendations for sustainable flows in the Great Lakes Basin of New York and Pennsylvania Sustainable Flows: The flow of water in a natural.
ENVIRONMENTAL SCIENCE TEACHERS’ CONFERENCE ENVIRONMENTAL SCIENCE TEACHERS’ CONFERENCE, Borki Molo, Poland, 7-10 February 2007 Projection of future climate.
River Regulation / Dam Construction – Effects on Rivers and Streams.
The Science of Environmental Sustainability
Puget Sound Coastal Geomorphology
Bahram Khazaei, Hector Bravo, and Harvey Bootsma
The Great Lakes.
Lake Erie Fisheries Community Status: 2013
Watersheds as Integrators of Climate: The Hydrogeomorphic Template as
Presentation transcript:

Great Lakes Water Levels and Coastal Systems Coastal Resiliency and Climate Change Scudder D. Mackey, Ph.D. Ohio Department of Natural Resources Lake Erie Millennium Conference October 30, 2013

What Drives Water Level Change?  Climate Precipitation + Runoff – Evaporation = NBS Precipitation + Runoff – Evaporation = NBS  Seasonal changes in climate (annual)  Inflows and Outflows Connecting Channel Flows between Lakes Connecting Channel Flows between Lakes Water-Level Regulation Water-Level Regulation  Diversions (into and out of basin)  Consumptive Uses  Wind and Storm Events (short term)

Basinwide Drop in GL Water Levels

August 2013 Forecast

Climate Variability and Water Levels  According to the most recent climate models, climate change in the Great Lakes basin during the next years is likely to be characterized by: Increase in storm severity - an increase in precipitation and more frequent and intense storms (weather variability); Increase in storm severity - an increase in precipitation and more frequent and intense storms (weather variability); Increase in evaporation - an increase in lake evaporation resulting from higher surface water temperatures, increased wind speed, lack of winter ice; Increase in evaporation - an increase in lake evaporation resulting from higher surface water temperatures, increased wind speed, lack of winter ice; Change in seasonal timing - increased water supply during winter/spring months (increased precipitation) accompanied by larger decreases in supply during summer/fall months (increased evaporation) resulting in slight overall annual declines in Great Lakes water levels. Change in seasonal timing - increased water supply during winter/spring months (increased precipitation) accompanied by larger decreases in supply during summer/fall months (increased evaporation) resulting in slight overall annual declines in Great Lakes water levels.

Future Lake Erie Water Levels  Lake Erie water levels are anticipated to remain below long-term historic mean water levels, but generally within the range of historic water levels. Anticipate more extreme and variable water level events, i.e. anticipate water level regimes that may exceed historic thresholds, both low and high. Anticipate more extreme and variable water level events, i.e. anticipate water level regimes that may exceed historic thresholds, both low and high.  How might these changes impact the Lake Erie coast and shorelines? How vulnerable is our coast to these stressors? What can we do to adapt to minimize the impact of environmental and socio-economic climate stressors?

Changes in Water Level Regime  Major shifts in shoreline position/location  Loss of hydraulic connectivity Wetlands Wetlands Small tributaries Small tributaries Loss of wetlands and fish spawning/nursery habitat Loss of wetlands and fish spawning/nursery habitat  Changes in seasonal magnitude, timing and duration Seasonal highs and lows Seasonal highs and lows Intermittently exposed Western Basin reefs (Lake Erie)? Intermittently exposed Western Basin reefs (Lake Erie)?  Altered tributary flows and Lake circulation patterns Connectivity between spawning and nursery habitats Connectivity between spawning and nursery habitats Nutrient and contaminant loadings Nutrient and contaminant loadings  Altered littoral sediment transport rates (nearshore habitat)

Coastal Habitat Enhancement Initiative Collaborative effort between the Ohio Division of Wildlife, University of Toledo, Ohio EPA, and ODNR Office of Coastal Management  Shoreline alteration affects fish species diversity and abundance  Armoring alters diversity but response is variable based on underlying substrate/habitat types  Shoreline/terrestrial vegetation positive effect  Develop habitat use index and develop model to simulate future shoreline conditions  Stratify management goals based on shoreline types

Coastal Habitat Outreach, Education, Implementation and Research  Habitat Enhancement Flyer Background Background Results Results Suggested Actions Suggested Actions Fish Photos/Community Groupings Fish Photos/Community Groupings Importance (GL Fishery, Benefits) Importance (GL Fishery, Benefits)  Develop Habitat Enhancement Guidance Distribution at pre-application site visits (OCM) Distribution at pre-application site visits (OCM) Incorporation into reach-based LESEMP (OCM) Incorporation into reach-based LESEMP (OCM) Incorporation into Coastal Design Manual (OCM) Incorporation into Coastal Design Manual (OCM)

Sand Resource Management Collaborative effort between the Ohio Division of Geological Survey and ODNR Office of Coastal Management  Calculate volume of coarse-grained sediment contributed to the littoral zone by bluff erosion.  Volume is annualized and expressed as cubic yards/year. Surrogate for net sediment transport rate.  Can be used to quantify cumulative impacts of shore protection on sand resources and nearshore habitat.

Superstorm Sandy (1-year Anniversary)  Impacts of Superstorm Sandy included sand transport landward. Increase in beach widths Increase in beach widths Navigation channels blocked by sand Navigation channels blocked by sand  Massive dredging effort spring 2013 a result of low Lake Erie water levels and littoral sand transport by Sandy.  Nearshore habitat impacts are unknown. Limited baseline data. Change detection not possible.

Vulnerability Assessment and Thresholds for Restoration Projects  Objective is to identify water-level ranges and thresholds that minimize adverse impacts to restoration projects and provide a mechanism to anticipate potential impacts due to changing water level regimes.  What parameters are required for your restoration project function successfully? What are the thresholds beyond which your project will be severely compromised and eventually fail? What are the thresholds beyond which your project will be severely compromised and eventually fail? Is it plausible that those thresholds will be reached or surpassed? Is it plausible that those thresholds will be reached or surpassed? If so, can you modify the design such that functionality is maintained or enhanced? If so, can you modify the design such that functionality is maintained or enhanced? If not, are there alternative functional benefits that would accrue under a different set of conditions? (e.g. fish habitat converts to wetland habitat) If not, are there alternative functional benefits that would accrue under a different set of conditions? (e.g. fish habitat converts to wetland habitat)

How High is “High” and how Low is “Low”? (1934) (1986) ft ft (mean)

Summary  Lake Erie water levels are anticipated to remain below long-term historic mean water levels, but generally within the range of historic water levels. Anticipate more extreme and variable water level events, i.e. anticipate water level regimes that may exceed historic thresholds, both low and high. Anticipate more extreme and variable water level events, i.e. anticipate water level regimes that may exceed historic thresholds, both low and high.  Areas for future research/data needs: Future water level regimes (maximum and minimum values, duration) Future water level regimes (maximum and minimum values, duration) Nearshore habitat enhancements (biotic and abiotic linkages) Nearshore habitat enhancements (biotic and abiotic linkages) Bathymetry, substrate, shoreline condition assessmentsBathymetry, substrate, shoreline condition assessments Nearshore aquatic communities, habitat linkagesNearshore aquatic communities, habitat linkages Sand resource management (environmental and economic impacts) Sand resource management (environmental and economic impacts) Distribution, source areas, littoral sediment transport rates and directionDistribution, source areas, littoral sediment transport rates and direction Low and High Water Thresholds (magnitude and duration) Low and High Water Thresholds (magnitude and duration) Ecological impacts, design criteria for restoration and enhancement projectsEcological impacts, design criteria for restoration and enhancement projects Nearshore and Coastal Vulnerability Assessments Nearshore and Coastal Vulnerability Assessments Climate change and water level regime scenarios Climate change and water level regime scenarios

Lake Erie Bathymetry Central Basin Eastern Basin Western Basin Lake St. Clair

Hydrological Components Lake Superior Hydrologic Values Courtesy IUGLS Long Lac/ Ogoki 154 m 3 /s (5400 cfs). Chicago Diversion 91 m 3 /s (3,200 cfs) Lake Michigan- Huron Lake Erie 56% precipitation 40% runoff 4% diversions % evaporation 57% outflow 39% precipitation 34% runoff 27% inflow % evaporation 68% outflow 1% Chicago diversion 79% inflow 11% precipitation 10% runoff % outflow 11% evaporation Lake Superior Lake Ontario 79% inflow 15% runoff 6% precipitation % outflow 7% evaporation St. Marys River 2110 m 3 /s St. Clair/Detroit River 5360 m 3 /s (190,000 cfs) Niagara River 5780 m 3 /s (204,000cfs) St. Lawrence 7060 m 3 /s

Diversions and Impacts Lake Superior Great Lakes Courtesy IUGLS Long Lac/ Ogoki 154 m 3 /s (5,400 cfs). Chicago Diversion 91 m 3 /s (3,200 cfs) Welland Canal 244 m 3 /s (8620 cfs) +9 cm (+3.5”) 0 Net +9 cm (+3.5”) +7 cm (+2.8”) -4 cm (-1.6”) -12 cm (-4.7”) Net -9 cm (-3.5”) +11 cm (+4.3”) -6 cm (-2.4”) -4 cm (-1.6”) Net +1 cm (+0.4”) Lake Michigan- Huron Lake Erie Connecting Channel Diversion in Diversion out Diversion within St. Clair River Sault St. Marie Control Structures Cornwall Massena Control Structures

August 2013 Forecast

Great Lakes Nearshore and Coastal Systems Climate change impacts will directly affect the physical integrity of the Great Lakes coastal and nearshore systems, which will in turn affect the Great Lakes habitats and the ecosystem  Seasonal Changes in Water Level Regimes and Storm Frequency: Slightly lower mean average water levels and increased water level variability – Increased potential for coastal and riverine flooding, altered coastal wetland biodiversity, loss of connectivity or inundation of coastal and riparian spawning/nursery habitats, altered marina/harbor/port access (increase dredging activity). A – high, C - >66% Slightly lower mean average water levels and increased water level variability – Increased potential for coastal and riverine flooding, altered coastal wetland biodiversity, loss of connectivity or inundation of coastal and riparian spawning/nursery habitats, altered marina/harbor/port access (increase dredging activity). A – high, C - >66% Increased Storm magnitude and Frequency - Altered littoral sediment transport processes, increased shore erosion, reduced nearshore water quality, reduced marina/harbor/port access (increase dredging activity), declining open-lake spawning fish recruitment. A – high, C – >95% (medium low and 33-66% for fish recruitment) Increased Storm magnitude and Frequency - Altered littoral sediment transport processes, increased shore erosion, reduced nearshore water quality, reduced marina/harbor/port access (increase dredging activity), declining open-lake spawning fish recruitment. A – high, C – >95% (medium low and 33-66% for fish recruitment)  Seasonal Changes in Precipitation Increased spring-summer flows and runoff – Increased flows/nutrient loading promotes nearshore algal blooms, changes in seasonal flood-pulse driven spawning activity (recent Lake Erie example) A – high, C – >95% (for shallow lakes, but scale and timing issues for deep lakes 95% (for shallow lakes, but scale and timing issues for deep lakes <33%)  Altered Thermal Regimes: Higher surface water temperatures - Increased primary productivity (eutrophication) and changes in seasonal timing (spawning initiated earlier/later due to thermal triggers) A - high, C - >66% Higher surface water temperatures - Increased primary productivity (eutrophication) and changes in seasonal timing (spawning initiated earlier/later due to thermal triggers) A - high, C - >66% Deeper and stronger thermocline - Reduced Lake Erie hypolimnion volume and expansion of central basin hypoxia (bottom waters) A – medium high, C – 33-66% (linked to productivity, water levels) Deeper and stronger thermocline - Reduced Lake Erie hypolimnion volume and expansion of central basin hypoxia (bottom waters) A – medium high, C – 33-66% (linked to productivity, water levels) Change in species distributions - Boundaries for up to 19 fish species would shift northward (both cold and warmwater species) A – medium high, C – 33-66% Change in species distributions - Boundaries for up to 19 fish species would shift northward (both cold and warmwater species) A – medium high, C – 33-66% Lower thermal constraints – Expansion of invasive species (both wetland and aquatic) A- medium low, C - >66% Lower thermal constraints – Expansion of invasive species (both wetland and aquatic) A- medium low, C - >66%