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GIS Modeling Approach to Forest Habitat Mapping

GIS Modeling Approach to Forest Habitat Mapping









I. History/Background



II. Methodology



III. Results



IV. Future Considerations

What is a Forest Habitat Type?







• Alexander Von Humboldt



• Braun-Blanquet system in Europe



• Minnesota DNR Native Plant Communities



• Dr John Kotar at University of Wisconsin Madison

John Kotar’s Forest Habitat Type

Classification for North Central Minnesota





• Simplified classification for forest managers



• Based on late-successional plant communities



• Aids in management decisions – Ecologically Based

Forest Management

Goals and Objectives







• Creation of an automated method for producing ecosystem

(habitat type) maps



• Demonstrate the use of Visual Basic and ArcGIS as a tool

for habitat type mapping



• Quantify the accuracy of two different methods of habitat

type mapping: the raster and the vector method

Why Create a Forest Habitat Model?







• 17,000 total cover type polygons



• 3-5 days for each township, with over 30 townships total

Study Area

Forest Habitat Type Model Requirements







• Soils – SSURGO



• Cover Type



• Habitat type sample points – stratified systematic

random sample based on cover type



• Digital Elevation Model – Raster



• First Law of Geography

Vector Habitat Typing Model





• Pivot tables showing probability of each habitat type

occurring on which soil type and cover type









*Courtesy of Cheryl Adams Blandin Forestry

Cover Type by Habitat Type Pivot Table



Habitat Type AAbAa AbArAo AbArV AbArV-Ly AbFnAu AbFnThAn



Red Pine 2 0 0 0 0 0



Jack Pine 0 1 0 0 0 0



Balsam Fir 5 9 9 14 10 0



White Spruce 25 3 2 3 10 0



Upland Black Spruce 12 6 1 2 6 0



Black Spruce 0 3 4 2 1 2



Tamarack 0 2 0 0 0 1



N White Cedar 0 0 1 1 3 12



N Hardwoods 52 20 1 1 10 0

Cover Type

Lowland Hdwds 0 3 0 0 40 35



Balm O' Gilead 3 2 3 0 23 2



Aspen 194 262 41 38 177 2



Birch 10 26 5 3 8 0



Lowland Grass 0 0 0 0 0 0



Lowland Brush 0 0 0 0 0 1



Marsh 0 0 0 0 1 0



Stagnant Spruce 0 0 0 0 0 0

Grand Total 303 337 67 64 289 55





• Use the top two

Vector Model

Four Step Process





1. Join the habitat type points layer with the cover

type layer



2. Assign the “easy” ones



3. Add based on adjacency, soil type, and cover

type



4. Add based on only soil type, and cover type

Step One – Spatial Join

Step Two – Add Known Types





• Add all of the Marsh, Muskeg, Lowland Grass, Lowland

Brush, etc.

Step Three – Adjacency





• Query soil type layer to select one particular soil

type

• Query habitat type layer to select the polygons

that have already been habitat typed

• Select all the polygons that touch the edge of the

already habitat typed polygons

• From that group select all the polygons with a

certain cover type

• From that group select all the polygons that have

their centers in the selected soil types

• Assign the appropriate habitat type

Step Three – Adjacency

Step Four – Only Soil and Cover Type





• Query the soil type layer to select a certain soil

type

• Query the habitat type layer to find all of the

polygons that have their centers within the certain

soil type

• Select FROM THE SELECTED the polygons that

have the cover type being looked for

• DESELECT all of the polygons that have already

been habitat typed

• Add the habitat type

Step Four – Only Soil and Cover Type

Sample and Verification Points









• Three sampling schemes: 30, 40, and 50%

stratified random sample based on PLS section







Percentage # of Points for Model Creation # of Points for Verification



30 61 138



40 80 119



50 109 90

Results





Fifty Percent Sampling Rate





• Classification based on 109 samples

• Overall assigned habitat types percentage: 81%

• 26 samples classified correctly, 64 classified

incorrectly, 90 total samples

• 26/90 = 29% correct, 64/90 = 71% incorrect, Khat =

0.1676

Results

Results





Forty Percent Sampling Rate



• Classification based on 79 samples

• Overall assigned habitat types percentage: 79%

• 31 samples classified correctly, 88 classified

incorrectly, 119 total samples

• 31/119 = 26% correct, 88/119 = 74% incorrect,

Khat = 0.1485

Results

Results





Thirty Percent Sampling Rate





• Classification based on 61 samples

• Overall assigned habitat types percentage: 79%

• 35 samples classified correctly, 84 classified

incorrectly, 138 total samples

• 35/138 = 25% correct, 84/138 = 75% incorrect,

Khat = 0.1362

Results

Accuracy Measure by Sampling Percent





Accuracy Measures 50% 40% 30%





Percentage of Polygons Assigned a Habitat Type 81% 79% 79%





Overall Accuracy 29% 26% 26%





Number of Plots Classified Correctly 26 31 35





Number of Plots Classified Incorrectly 63 87 101





Percentage Classified Correctly 29% 26% 26%





Percentage Classified Incorrectly 71% 73% 73%



Khat 0.1676 0.1484 0.1362



Percentage Omission 71% 74% 74%





Percentage Commission 6% 5% 5%

Raster Model

Raster Modeling Technique



1. Convert cover type and soil type to raster

2. Reclassify the cover type layer to discard all of

the areas that won’t be considered for forest

management

3. Add together the cover type and soil type.

Separate out cover type/soil type combinations

that could be classified into more than one

habitat type – reclassify the slope to a 1-10

scale

4. Add together slope and cover type/soil type

combinations – reclass to meaningful scale

5. Add all of the multi habitat type combinations

with the single habitat type codes

6. Reclassify to meaningful scale and apply

majority filter

Step One – Cover Type Reclassify

Possible Soil Type Cover Type Combinations



Possible Values V1 V2 V3 V4 V5 V6 V7 V8 V9 V10



AAbAa 46 47 66 67 71 72 73 74 76 77



AbArAo 66 68



AbArV



AbArV-Ly 26 62



AbFnAu



AbFnThAn 29 35 46 52



AbFnThAn-Moss 29 35 46 52



AbPiG



AbPiPl 11 12



AbPiV 30 66



AbThLe 27 28 29 33 34 35



AbThSp 33 35



ATiCa 38 46 58 66 65 73 76 68



ATiPo 46 47 66 67 73 74



FnLa 45 49 52 56



FnTiAt 46 66



PmCh 27 28 33 34



PmPl 27 28 33 34

Step Two – Reclass Slope and

Add to Individual Cover/Soil Combinations

Step Two

Step 3 – Add Together All Output from Step 2

Along With Output from Step 3

Step 5 – Reclass to Meaningful Output and

Apply Majority Filter

Raster Results

Accuracy Measures 50% 40%



Unfiltered 4 Filter 8 Filter Unfiltered 4 Filter 8 Filter



Overall Accuracy 21% 21% 21% 18% 19% 20%

Number of Plots Classified Correctly 15 15 15 18 18 19

Number of Plots Classified Incorrectly 56 56 56 79 78 77

Percentage Classifed Correctly 21% 21% 21% 18% 19% 20%

Percentage Classifed Incorrectly 79% 79% 79% 92% 81% 80%

Khat 0.07856 0.07792 0.07792 0.0753 0.07521 0.0874

Percentage Omission 79% 79% 79% 81% 81% 80%

Percentage Comission 7% 7% 7% 7% 7% 7%



Accuracy Measures 30% All

Unfiltered 4 Filter 8 Filter Unfiltered 4 Filter 8 Filter

Overall Accuracy 23% 23% 24% 22% 23% 23%

Number of Plots Classified Correctly 25 25 26 36 36 37

Number of Plots Classified Incorrectly 83 82 81 125 124 123

Percentage Classifed Correctly 23% 23% 24% 22% 23% 23%

Percentage Classifed Incorrectly 77% 77% 76% 78% 77% 77%

Khat 0.11632 0.11677 0.12754 0.10144 0.10149 0.10853

Percentage Omission 77% 77% 76% 78% 78% 77%

Percentage Comission 6% 6% 6% 6% 6% 6%

Comparison of the Accuracy Measures Between

the Raster and Vector Model





Accuracy Measures 50% 40% 30%





Vector Raster Vector Raster Vector Raster







Overall Accuracy 29% 17% 26% 16% 25% 19%







Number of Plots Classified Correctly 26 15 31 19 35 26









• Excludes verification points that fell on 'NoData'

pixel values

• Dark areas (Not the Same) are most commonly lowland areas that

were removed from the raster model

Future Considerations





• Increased sampling points

• Vector model order dependency

• Geographic extent of study area

– Soil types 619 and 622B missing

– Occur with: AbArV, AbArV-Ly, AbFnAu, AbPiV,

AbPiG, and FnTiAt

• Polygons with multiple sample points

Thanks and Questions?



Thank you to Cheryl Adams of UPM Blandin Forestry

for all of the data used in this study. I would also like

to thank Misha Blinnikov, Jorge Arriagada, and Benjamin

Richason III for all of their guidance, suggestions, and

motivation.



Jesse Adams

JSA GIServices

5406 Oneida Street

Duluth, MN 55804

Phone: 218.525.1172

Fax: 218.525.1382

Mobile: 608.215.8464



Email: jesse@jsagiservices.com

Website: www.jsagiservices.com


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