WIND POWER IN MAINE: BALANCING CONSERVATION AND ENERGY PRODUCTION

 

Hannah Lafleur and Jordan Schoonover

ES212 Introduction to GIS and Remote Sensing

Colby College: Environmental Studies Program

 

Abstract

 

An expedited permitting area has been created to facilitate the development of wind power projects in Maine.  The purpose of this project was to investigate the impact of removing areas of conservation interest from the expedited permitting area.  We found that the removal of these areas impacts the total wind potential of the state, in an amount proportional to the size of the area removed.  The impact on the total wind potential ranged from 0.46-29.0 % decrease, depending on the calculation scenario used.  These findings may have implications for future policy decisions concerning wind power development.

 

Introduction

 

Recently, there has been increased interest in renewable sources of energy such as wind power.  In 2007 Maine governor John Baldacci established the Governor’s Task Force on Wind Power Development, which concluded that:  Maine can become a leader in wind power development, while protecting Maine’s quality of place and natural resources, and delivering meaningful benefits to our economy, environment, and Maine people” (Governor’s Task Force 2008).  The Task Force recommended that a portion of the state be designated as an expedited permitting area to streamline the permitting process for new wind projects.  The expedited area includes all organized townships, unorganized towns on the fringe of the Land Use Regulation Commission’s jurisdiction, and areas within six miles of certain public highways.  In all, the expedited area encompasses two-thirds of the state.

 

The purpose of this project was to investigate the impact of removing areas of conservation interest from the expedited permitting area.  Although large tracts of conservation land, such as Baxter State Park, are excluded from the expedited area, many smaller but significant conservation lands, such as Acadia National Park, are included.  We sought to measure the impacts on the total wind potential in the expedited area if conservation lands and the area immediately surrounding them were removed.  Conservation lands include federal and state-owned lands and non-profit easements (ME Office of GIS 2009).  Three scenarios were compared: 1km, 3km and 5km buffers around conservation lands. We also examined the impact of removing roadless areas.  Roadless areas are defined as: “areas where no roads have been built and where, as a result, no logging or other development has occurred” (NRDC 2009).

 

Methods

 

We compiled GIS data layers for the state of Maine including data for Conservation Lands, Roadless Areas, the Appalachian Trail, and Wind Resources (Figure 4). We created a layer for Expedited Areas based on the Governor’s Task Force Report. We used ArcGIS software, and our data were projected in NAD83, UTM Zone 19N.

 

We calculated the areas of wind power classes within the Expedited Area.  Next, we set up different scenarios to evaluate how the wind power potential of Maine changes with specific portions subtracted from the expedited permitting area. The Wind Resources layer defined seven wind potential classes.  The wind power density for each class was given as a range, calculated using the Weibull distribution with a k value of 2 (NREL 2002, DWIA 2003). We used minimum, mean, and maximum values of the wind power densities to account for possible variation (Table 1). To calculate the wind power potential of the state, we multiplied the areas of the polygons by the wind power density (Table 2).  We ran the minimum, mean, and maximum scenarios to establish a baseline for our analysis. Next, we created buffers of 1 km, 3 km, and 5 km around the conservation lands and subtracted them from the Wind Resources layer.  We calculated the total watts of wind power at minimum, mean, and maximum densities for the current expedited area and the expedited area with the conservation lands buffered at 1km, 3km, and 5km. We performed the same calculations with the removal of Roadless Areas.

 

Table 1. Minimum, mean and maximum wind power density for each of the seven wind power classes.

Wind Power Class

Minimum wind power density (W/m2)

Mean wind power density (W/m2)

Maximum wind power density (W/m2)

1

0

100

200

2

200

250

300

3

300

350

400

4

400

450

500

5

500

550

600

6

600

700

800

7

800

900

1000

 

Table 2. Attribute table of the Wind Resources layer with the minimum, mean and maximum wind densities and the corresponding wattage calculated by multiplying the wind density (W/m2) by the area (m2).

WPC

Area

Min

W/m2

Min

Watts

Mean

W/m2

Mean

Watts

Max

W/m2

Max

Watts

1

120000

0

0

100

12000010

200

24000020

3

2919999

300

875999970

350

1021999965

400

1167999960

2

2359999

200

471999960

250

589999950

300

707999940

3

360000

300

108000030

350

126000035

400

144000040

3

240000

300

72000030

350

84000035

400

96000040

2

24359999

200

4871999980

250

6089999975

300

7307999970

4

40000

400

16000000

450

18000000

500

20000000

 

Results

 

We found that removing the conservation land buffers decreased the total wind potential of the expedited area (Table 3).  The greatest reduction in wind potential occurred with the removal of conservation lands and a 5 km buffer around them.  Removing the roadless areas decreased the wind potential less than removing conservation lands with a 1km buffer.  The minimum, mean and maximum scenarios show a similar trend for the decreasing wind potential (Figure 3).


Table 3. Total power potential and percent change in power potential using minimum, mean and maximum wind power densities.  It is important to note that the values for total power potential were calculated for comparison purposes only.  They do not represent a realistic estimation of the total watts likely to be produced by wind power in Maine.

 

 

 

 

Minimum

 

Mean

 

Maximum

Area Removed

 

% change in area

 

Total watts

% change in wind potential

 

Total watts

% change in wind potential

 

Total watts

% change in wind potential

None

 

____

 

1.99x1012

____

 

6.89x1012

____

 

1.18x1013

____

 

Roadless area

 

-1.63

 

1.88x1012

-5.54

 

6.71x1012

-2.64

 

1.15x1013

-2.15

1 km buffer of conservation lands

 

-15.1

 

1.57 x1012

-21.0

 

5.76x1012

-16.5

 

9.94x1012

-15.7

3 km buffer of conservation lands

 

-39.3

 

1.02 x1012

-48.9

 

4.03x1012

-41.5

 

7.04x1012

-40.3

5 km buffer of conservation lands

 

-61.2

 

6.47 x1011

-67.6

 

2.57x1012

-62.7

 

4.50x1012

-61.9

 

Figure 3. Wind potential remaining after removal of conservation buffers.

 

Discussion

 

Depending on the wind density value used, removing buffers around conservation lands reduced the wind power potential in the expedited area by 1.0 – 29.0%.  Removing roadless areas did not have a significant impact on the state’s wind power potential.  The impact of removing conservation buffers increases as the size of the buffer increases.  Our results show that the objectives set forth by the Governor’s Task Force on Wind Power Development, including making Maine a leader in wind power development and protecting the state’s quality of place and natural resources, will require careful planning and consideration of scenarios similar to those presented in this poster.  Our data may be of importance to policy decisions regarding the balance between conservation and wind power development. 

 

Our analysis used buffer distances of 1, 3 and 5 km, but future analyses may be able to distinguish a more specific trend with buffer distances in smaller increments and over a wider range.  Although distance was the only variable considered in this analysis, conflict between conservation areas and wind development may result from a more complex interaction of factors.  Visibility of wind farms from conservation areas is a variable of interest that should be considered in future analyses.

 

Conclusion

 

Excluding areas of conservation interest from future wind power development decreases the total wind potential of Maine:

      The removal of a 1 km buffer reduced the wind power potential by 1.0 - 4.2%.

      The removal of a 3 km buffer reduced the wind power potential by 3.9 - 16.6%.

      The removal of a 5 km buffer reduced the wind power potential by 6.8 - 29.0%.

      The removal of the roadless areas reduced the wind power potential by 0.46 - 2.20%.

 

Acknowledgements

 

We would like to thank Philip Nyhus and Manny Gimond for their assistance with the planning and execution of this study.  We would also like to thank Emmie Theberge of the Natural Resources Council of Maine for providing us with ideas and data about wind power development in Maine.

 

Literature Cited

 

Appalachian Trail Conservancy. 2009. “Appalachian Trail GIS and GPS Data.” Accessed 7 April 2009. <http://www.appalachiantrail.org/site/c.mqLTIYOwGIF/b.4805623/k.438D/Appalachian_Trail_GIS_and_GPS_Data.htm>

Danish Wind Industry Association. 1 June 2003. “Weibull Distribution Plotter Programme.” Accessed 23 April 2009. <http://www.windpower.org/en/tour/wres/weibull/index.htm>

Governor’s Task Force on Wind Power Development. 14 February 2008. “Report of the Governor’s Task Force on Wind Power Development.” Accessed 1 April 2009. <http://www.maine.gov/doc/mfs/windpower/>

Maine Office of GIS. 2009. “GIS Data Catalogue.” Accessed 7 April 2009.  <http://megis.maine.gov/>

Natural Resources Council of Maine. 2009. “Wind Power.” Accessed 1 April 2009. <http://www.nrcm.org/issue_windpower.asp>

Natural Resources Defense Council. 2009. “The National Forest ‘Roadless Area’ Rule.” Accessed 7 April 2009. <http://www.nrdc.org/land/forests/qroadless.asp>

National Renewable Energy Laboratory. 2002. “Data and Analysis Tools.” Accessed 1 April 2009. <http://www.nrel.gov/wind/>

Roush, Wade. 10 January 2008. “Maine Wind Farm Gets Green Light, But Project Leader Says Cleantech Efforts Face Too Many Snarls.” Accessed 1 April 2007. <http://www.xconomy.com/boston/2008/01/10/main-wind-farm-gets-green-light-but-project-leader-says-cleantech-efforts-face-too-many-snarls/>

 

buffer5kmbuffer3kmbuffer1km

Figure 1. Expedited area of the Wind Resources layer with 1, 3, and 5 km conservation land buffers removed.

poster_map_4

Figure 2. Expedited area, wind power class, and areas of conservation interest in Maine.

Expedited_areacons_landsWind_potential

 

Figure 4. Expedited area map; conservation lands, roadless areas and Appalachian Trail map; and wind power class map.