EPA Region 5 Assessing Ecosystem Condition in Region 5 by Mary L. White & Charles G. Maurice 1.

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EPA Region 5 Assessing Ecosystem Condition in Region 5 by Mary L. White & Charles G. Maurice 1

Transcript of EPA Region 5 Assessing Ecosystem Condition in Region 5 by Mary L. White & Charles G. Maurice 1.

Page 1: EPA Region 5 Assessing Ecosystem Condition in Region 5 by Mary L. White & Charles G. Maurice 1.

EPA Region 5

Assessing Ecosystem Condition in Region 5

byMary L. White & Charles G. Maurice

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HEALTHY COMMUNITIES AND ECOSYSTEMS

Protect, sustain or restore the health of people, communities, and ecosystemsusing integrated and comprehensive approaches and partnerships.

Goal 4

Objective 4.3 Restore and protect critical ecosystems

But how do we Prioritize issues?

Measure success?

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Partner Identified Ecosystems

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Three Criteria –DiversitySustainabilityRarity

Indicator data sets to populate these criteriaDiversity – four data setsSustainability – twelve data setsRarity – four data sets

Critical Ecosystem Assessment Model

CrEAM

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Base Map – National Land Cover Data Base 1992

30m x 30m pixel size

only undeveloped land coverclasses were used

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Ecoregion Legend

Omernik Ecoregions for Region 5

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Diversity SustainabilityRarity

4 data layers 4 data layers

12 data layers

final composite ecosystem score 7

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"Diversity" Layers

land cover diversity calculation by ecoregion

temp. and precipitation maxima by ecoregion

appropriateness of land cover

contiguous sizes of undeveloped areas

higher diversity(better)

lower diversity(worse)100 0

higher Shannon index lower Shannon index

higher temperature and precip lower temperature and precip

(Kuchler) appropriate land cover (Kuchler) inappropriate land cover

larger contiguous area smaller contiguous area

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area / perimeter calculation

waterbody created by impoundments

road density

contiguous sizes by land cover type

more contiguous(better)

more fragmented(worse)100 0

larger area/perimeter smaller area/perimeter

fewer impoundments more impoundments

lower road density higher road density

larger contiguous area smaller contiguous area

"Fragmentation" Layers

appropriateness of land cover(Kuchler) appropriate land cover (Kuchler) inappropriate land cover

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"Stress" Layers

airport noise

hazardous waste cleanup sites

water quality summary from BASINS model

air quality from OPPT air risk model

less stressed(better)

more stressed(worse)100 0

land outside of airport buffer zone land within airport buffer zone

land outside RCRA site zone land inside RCRA site zone

low N, sediment, high O2 high N, sediment, low O2

fewer exceedances of thresholds more exceedances of thresholds

Superfund NPL sites

waterway obstructions

land outside NPL sites land within NPL sites

fewer dams per HUC more dams per HUC

urban disturbanceland further from developed area land closer to developed area

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land cover rarity by ecoregion

species rarity per 7.5 minute quad

number of rare species per 7.5 minute quad

number of rare taxa per 7.5 minute quad

more rare species and features(better)

fewer rare species and features(worse)100 0

land cover type is very rare land cover type is ubiquitous

G1 Heritage rating G5 Heritage rating

more species observed fewer species observed

more taxa observed fewer taxa observed

"Rarity" Layers

* Raw rare species data used to generate these 3 layers were provided by the Natural Heritage Programs of Illinois, Indiana, Michigan, Minnesota, Ohio, and Wisconsin in cooperation with The Nature Conservancy. These data are confidential business information and cannot be provided or reproduced without written consent of the corresponding Natural Heritage Program. 11

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CrEAM / Essential Ecological Attributes Crosswalk

Diversity Sustainability Rarity

Biotic Condition 1 2 3

Landscape Condition 2 5 1

Chem. & Phys. Characteristics 7

Hydrology & Geomorphology 4

Natural Disturbance Regimes 1

Ecological Processes

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Airports13

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Water Quality14

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Air Toxics

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Composite layer for acriteria is the sum of all

normalized indicator layers

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Diversity compositescores 0 - 397

Sustainability compositescores 464 - 1157

Rarity compositescores 0 - 331

Criteria scores were normalizedbetween 0 – 100 and addedfor a final ecosystem score.

range = 23-253 mean = 139

Results

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Final Composite ofEcological Condition

Final CompositeScores

0-2021-4041-6061-8081-100no data

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low = 23high = 253

mean = 139

Distribution of composite ecosystem scores

Results

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Top 1 %

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Results

Composite score

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Top 10%Top 1%

Top .1%

AC BDF E

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of p

ixel

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MeanTop 10 %

first derivative

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A > 210 (top 0.1%)

B 209 - 190 (top 1.0%)

C 189 - 165 (top 10%)

D 164 - 122

E 121 - 76

F < 76

legendcategory score

Ecological Significance Ratings

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Ecological Significance Ratings

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Critical Ecosystem Assessment Model

To validate and evaluate model:

1. Best Professional Judgment2. Statistical Analysis3. SAB review4. Field validation (RARE grant)5. Peer review in journals

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Validation1. Best Professional Judgment

Areas in red havecomposite scores in the top 1% of all cells

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400 km N

1 St. Croix State Park, MN2 Wisconsin Dells, Baraboo, WI3 Sleeping Bear Dunes National Lakeshore, MI4 Indiana Dunes National Lakeshore, IN5 Shawnee National Forest, IL6 Hoosier National Forest, IN7 Wayne National Forest, OH

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Within criterion correlation of data layers:

Diversity 0.41 between land cover diversity and contiguous area of undeveloped land

Sustainability 0.45 between weighted road density and development buffer

Rarity 0.52 between rare species abundance and rare taxa abundance

Thus we conclude that the individual data layers within a criterion do not duplicate each other.

2. Sensitivity Analysis

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Correlations between individual criteria and their relationship with the total composite score. All correlations aresignificant at p < .0001; N = 3,634,183.

Total CompositeScore

C1 Composite Score

C2 CompositeScore

C3 Composite Score

TotalCompositeScore

1.00 .59 .51 .34

C1 CompositeScore

.59 1.00 .40 -0.02

C2 CompositeScore

.51 .40 1.00 -0.08

C3 CompositeScore

.34 -0.02 -0.08 1.00

Correlations between individual criteria and their relationship with the total composite score. All correlations are

Thus we conclude that the criteria do not duplicate each other

Sensitivity Analysis

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http://www.epa.gov/sab/panels/epec_crmpesls.html

Evaluation of Model 3. SAB Review June 2004

5. Peer Review journal article

The Critical Ecosystem Assessment Model (CrEAM)Identifying healthy ecosystems for environmental protection planning

Mary L. White, Charles G. Maurice, Amy Mysz, Thomas BrodyIn

Campbell, J.C., K. B. Jones, J. H. Smith and M. T. KoppeNorth American Land Cover Summit

Association of American Geographers, 2008

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Develop quick* assessment protocols for forests non-forest terrestrial wetlands lakes

Validation of Model 4. RARE Grant 2003-2005

*quick meansassessment of a 300 x 300 m parcelby four people in four hours.

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Proposed Uses of the CrEAM

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1. Quantify and Track Ecosystem Quality

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1992 results

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AB

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2. Prioritize

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3. NEPA Reviews

Location of airport32

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4. Targeting

low diversitylow sustainabililty

high diversitylow sustainability

high diversityhigh sustainability

low diversityhigh sustainability

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Texas Environmental Resource Stewards

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Primary Collaborators

Charles Maurice & Mary WhiteCritical Ecosystems Team

Amy Mysz Robert Beltran & John SchneiderPesticides Program Gt. Lakes Nat. Program Office

Mike Gentleman Lawrence Lehrman Water Division Office of Information Services

Brenda Jones Dan MazurSuperfund Division Waste Management Program

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