changes in fragmentation of western washington forest land · land to nonforest land uses in...

1
Introduction FIA monitoring has detected very rapid conversion of forest land to nonforest land uses in western Washington in the last decade, with 5% of private timberland (270,000 acres) being converted between 1990-2000 (Fig. 1), following a similar rate of loss in the previous decade (Fig. 2). The human population in the state has almost doubled since 1970 (Figs 3a + 3b). It is likely, but unknown, whether increased fragmentation of forest land has also occurred. Fragmentation reduces patch size and increases edge environments, with important effects on fire risk, weedy species, timber management, and wildlife habitat. The objective of this project was to evaluate the extent and spatial pattern of forest fragmentation in western Washington and begin to assess its implications. Changes in fragmentation of western Washington forest land Andrew Gray 1 , Tyler Robinson 1 , and Beth Willhite 2 1) USDA Forest Service PNW Research Station FIA, Corvallis OR; 2) USDA Forest Service Region 6 FHP, Sandy OR Methods Imagery from three time periods was acquired—mid-1970s, early 1990s, and 2006—and land cover is being manually classified into GIS polygons of different land use zones for each time period: Wildland forest: area >=640 ac, <5 dispersed developments per 640 ac, and >80% forest land Intensive agriculture: area >=640 ac, <9 dispersed developments per 640 ac, and >80% agricultural land. Mixed forest/agriculture: area >=640 ac; <9 dispersed developments per 640 ac; and mixed forest, range, and agriculture with forest >= 50% of the non-agricultural land. Low-density residential: area any size with >=9 developments per 640 ac Urban: area >=40 ac; commercial, service, and residential uses with a city road pattern Non-vegetated: area >=640 ac covered with water, ice, rock, or sand. In addition, 44,500 systematically-placed points were identified outside federal lands across the state and man-made structures (e.g., single houses, or houses with barns) in an 80 ac circle around each point are being counted in non-urban land-use zones. Distance to the nearest contrasting land-use is calculated for each point. We are also assessing changes in tree cover in urban zones. To date we have completed all three time periods for southwest Washington (Fig. 4), and are about half-way through the work in northwest Washington. Conclusions Results to date suggest that forest fragmentation is increasing in southwest Washington; continuing work (e.g. Fig. 11) will quantify patterns across the state. Change in land use varied dramatically by county, with the greatest changes occurring in Clark County, near the Portland metro area (Figs 5a + 5b). Between 1976 and 2006, forest, agricultural, and mixed land in Clark county declined by 11, 32, and 25%, while low-density residential and urban land increased by 60 and 124%, respectively. In comparison, forestland loss in Pacific and Wahkiakum counties was 1%. For southwest Washington as a whole, most of the developing low-density residential areas between 1976 and 2006 came from forest land, while most of the developing urban areas came from agricultural and low-density residential land (Fig 6). Forest fragmentation increased in all ecoregions in southwest Washington, as indicated by decreases in area- to-perimeter ratios and mean patch size between 1976 and 2006 (Fig. 8). 13 9 New houses outside Sequim, Olympic Peninsula 1 WWA change in non-NFS timberland area 7,037 Timberland 2000 4.7% of private area -270 To non-forest Primarily DNR -60 To reserved Snoqualmie Pass, Gorge -30 Net to NFS 7,397 Timberland 1990 7,037 Timberland 2000 4.7% of private area -270 To non-forest Primarily DNR -60 To reserved Snoqualmie Pass, Gorge -30 Net to NFS 7,397 Timberland 1990 (thousand acres) Net private to public 148 (Gray et al. 2005. PNW-RB-246) Wildland forest and agriculture land uses, Cowlitz River valley, Lewis County WWA: loss of private timberland 0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 1935 1980 1990 2000 2010? Year Million acres 1.4 million acres lost 1935-2000, some to public, ~25,000 ac/yr to nonforest 2 Census: 1970 Population density Population density: People / 1,000 acres 2.5 - 25 26 - 50 51 - 100 101 - 500 501 - 1000 1001 - 1366 Population=3,413,000 3a Census: 2007 Population density Population density: People / 1,000 acres 2.5 - 25 26 - 50 51 - 100 101 - 500 501 - 1000 1001 - 1366 Population=6,468,000 3b 4 Loss of forestland 5b 5a 6 Forest Mixed Agriculture Low-density residential Urban Non- vegetated 1976 Area: 2,647,047 121,810 230,137 147,677 49,926 916 Change to/from: Forest 0 2,332 1,824 61,463 2,828 5,074 Mixed -2,332 0 -456 15,511 5,467 0 Agriculture -1,824 456 0 12,760 16,870 0 Low-density residential -61,463 -15,511 -12,760 0 15,624 482 Urban -2,828 -5,467 -16,870 -15,624 0 0 Nonvegetated -5,074 0 0 -482 0 0 Net Change -73,520 -18,192 -28,261 73,628 40,788 5,556 2006 Area: 2,573,526 103,618 201,876 221,306 90,714 6,472 Change in: Net changes in area by land use, nonfederal land, 1976 to 2006 (acres) The number of structures on forest land increased in all southwest counties, ranging from 14 to 72% increase by county, and 56% overall (Fig. 7). In Clark County, 29% of the points that were within ½ mile of low-density residential or urban in 1976 changed to low-density residential or urban by 2006 (only 3% of points outside ½ mile changed). Forest that is within ½ mile of low-density residential or urban also has significantly more structures, averaging 3.6 and 7.0 structures/square mile within ½ mile in 1976 and 2006 respectively. Outside ½ mile these averages were 1.8 and 2.6. Clark County 0 5 10 15 20 25 30 35 40 45 Wildland Forest Mixed Forest/Ag Intensive Agriculture Structures (#/mi2) 1976 1994 2006 Pacific County 0 5 10 15 20 25 30 35 40 Wildland Forest Mixed Forest/Ag Intensive Agriculture Structures (#/mi2) 1976 1994 2006 Southwest Washington 0 5 10 15 20 25 30 35 40 Wildland Forest Mixed Forest/Ag Intensive Agriculture Structures (#/ac) 1976 1994 2006 7 Houses in the woods Forest fragmentation Ecoregion Section Metric 1976 1994 2006 Cascades Total area (ha) 1,015,081 1,002,000 994,953 Cascades Total perimeter (km) 2,167 2,462 2,557 Cascades Area/Perimeter (ha/km) 468 407 389 Cascades Mean area (ha) 101,508 100,200 82,913 Coast Ranges Total area (ha) 430,001 427,090 425,522 Coast Ranges Total perimeter (km) 1,998 2,016 2,052 Coast Ranges Area/Perimeter (ha/km) 215 212 207 Coast Ranges Mean area (ha) 25,294 22,478 22,396 Puget + Willamette lowlands Total area (ha) 145,318 138,996 133,648 Puget + Willamette lowlands Total perimeter (km) 2,884 2,980 3,205 Puget + Willamette lowlands Area/Perimeter (ha/km) 50 47 42 Puget + Willamette lowlands Mean area (ha) 10,380 8,687 5,346 All SWWA Total area (ha) 1,590,400 1,568,087 1,554,124 All SWWA Total perimeter (km) 6,464 6,902 7,291 All SWWA Area/Perimeter (ha/km) 246 227 213 All SWWA Mean area (ha) 38,790 34,846 27,752 Year 8 Policy implications Similar amounts of development have occurred in both Oregon and Washington in the Portland area (Fig. 9). However, development is less dispersed in Oregon, indicating that land-use laws in place since the 1970s have been effective. Preliminary analysis of land value in King county indicates higher assessed value of land close to urban areas (Fig. 10), which may indicate pressure to develop those lands over other uses. 10 Market Value of Land Per Acre by Distance to Urban 0 1000 2000 3000 4000 5000 6000 7000 Urban <1/4 Mile 1/4 to 1/2 Mile 1/2 to 3/4 Mile 3/4 to 1 Mile >1 Mile * Parcel data provided by Luke Rogers, University of Washington 11 Funding for this project was provided by the Forest Health Monitoring program and the PNW Research Station

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Page 1: Changes in fragmentation of western Washington forest land · land to nonforest land uses in western Washington in the last decade, with 5% of private timberland (270,000 acres) being

IntroductionFIA monitoring has detected very rapid conversion of forest land to nonforest land uses in western Washington in the last decade, with 5% of private timberland (270,000 acres) being converted between 1990-2000 (Fig. 1), following a similar rate of loss in the previous decade (Fig. 2). The human population in the state has almost doubled since 1970 (Figs 3a + 3b). It is likely, but unknown, whether increased fragmentation of forest land has also occurred. Fragmentation reduces patch size and increases edge environments, with important effects on fire risk, weedy species, timber management, and wildlife habitat. The objective of this project was to evaluate the extent and spatial pattern of forest fragmentation in western Washington and begin to assess its implications.

Changes in fragmentation of western Washington forest landAndrew Gray1, Tyler Robinson1, and Beth Willhite2

1) USDA Forest Service PNW Research Station FIA, Corvallis OR; 2) USDA Forest Service Region 6 FHP, Sandy OR

MethodsImagery from three time periods was acquired—mid-1970s, early 1990s, and 2006—and land cover is being manually classified into GIS polygons of different land use zones for each time period:

Wildland forest: area >=640 ac, <5 dispersed developments per 640 ac, and >80% forest land

Intensive agriculture: area >=640 ac, <9 dispersed developments per 640 ac, and >80% agricultural land.

Mixed forest/agriculture: area >=640 ac; <9 dispersed developments per 640 ac; and mixed forest, range, and agriculture with forest >= 50% of the non-agricultural land.

Low-density residential: area any size with >=9 developments per 640 ac

Urban: area >=40 ac; commercial, service, and residential uses with a city road pattern

Non-vegetated: area >=640 ac covered with water, ice, rock, or sand.

In addition, 44,500 systematically-placed points were identified outside federal lands across the state and man-made structures (e.g., single houses, or houses with barns) in an 80 ac circle around each point are being counted in non-urban land-use zones. Distance to the nearest contrasting land-use is calculated for each point.

We are also assessing changes in tree cover in urban zones. To date we have completed all three time periods for southwest Washington (Fig. 4), and are about half-way through the work in northwest Washington.

ConclusionsResults to date suggest that forest fragmentation is increasing in southwest Washington; continuing work (e.g. Fig. 11) will quantify patterns across the state.

Change in land use varied dramatically by county, with the greatest changes occurring in Clark County, near the Portland metro area (Figs 5a + 5b). Between 1976 and 2006, forest, agricultural, and mixed land in Clark county declined by 11, 32, and 25%, while low-density residential and urban land increased by 60 and 124%, respectively. In comparison, forestland loss in Pacific and Wahkiakum counties was 1%. For southwest Washington as a whole, most of the developing low-density residential areas between 1976 and 2006 came from forest land, while most of the developing urban areas came from agricultural and low-density residential land (Fig 6).

Forest fragmentation increased in all ecoregions in southwest Washington, as indicated by decreases in area-to-perimeter ratios and mean patch size between 1976 and 2006 (Fig. 8).

13

9

New houses outside Sequim, Olympic Peninsula

1 WWA change in non-NFS timberland area

7,037Timberland 2000

4.7% of private area-270To non-forestPrimarily DNR-60To reservedSnoqualmie Pass, Gorge-30Net to NFS

7,397Timberland 1990

7,037Timberland 2000

4.7% of private area-270To non-forestPrimarily DNR-60To reservedSnoqualmie Pass, Gorge-30Net to NFS

7,397Timberland 1990

(thousand acres)

Net private to public 148

(Gray et al. 2005. PNW-RB-246)

Wildland forest and agriculture land uses, Cowlitz River valley, Lewis County

WWA: loss of private timberland

0.0

1.0

2.0

3.0

4.0

5.0

6.0

7.0

1935 1980 1990 2000 2010?

Year

Mill

ion

acre

s

1.4 million acres lost 1935-2000, some to public, ~25,000 ac/yr to nonforest2

Census: 1970 Population densityPopulation density:People / 1,000 acres

2.5 - 25

26 - 50

51 - 100

101 - 500

501 - 1000

1001 - 1366

Population=3,413,0003a

Census: 2007 Population densityPopulation density:People / 1,000 acres

2.5 - 25

26 - 50

51 - 100

101 - 500

501 - 1000

1001 - 1366

Population=6,468,0003b

4

Loss of forestland

5b

5a

6Forest Mixed Agriculture

Low-density residential Urban

Non-vegetated

1976 Area: 2,647,047 121,810 230,137 147,677 49,926 916Change to/from: Forest 0 2,332 1,824 61,463 2,828 5,074 Mixed -2,332 0 -456 15,511 5,467 0 Agriculture -1,824 456 0 12,760 16,870 0 Low-density residential -61,463 -15,511 -12,760 0 15,624 482 Urban -2,828 -5,467 -16,870 -15,624 0 0 Nonvegetated -5,074 0 0 -482 0 0Net Change -73,520 -18,192 -28,261 73,628 40,788 5,556

2006 Area: 2,573,526 103,618 201,876 221,306 90,714 6,472

Change in:Net changes in area by land use, nonfederal land, 1976 to 2006 (acres)

The number of structures on forest land increased in all southwest counties, ranging from 14 to 72% increase by county, and 56% overall (Fig. 7). In Clark County, 29% of the points that were within ½ mile of low-density residential or urban in 1976 changed to low-density residential or urban by 2006 (only 3% of points outside ½mile changed). Forest that is within ½ mile of low-density residential or urban also has significantly more structures, averaging 3.6 and 7.0 structures/square mile within ½mile in 1976 and 2006 respectively. Outside ½ mile these averages were 1.8 and 2.6.

Clark County

0

5

10

15

20

25

30

35

40

45

Wildland Forest Mixed Forest/Ag Intensive Agriculture

Stru

ctur

es (#

/mi2

)

197619942006

Pacific County

0

5

10

15

20

25

30

35

40

Wildland Forest Mixed Forest/Ag Intensive Agriculture

Stru

ctur

es (#

/mi2

)

197619942006

Southwest Washington

0

5

10

15

20

25

30

35

40

Wildland Forest Mixed Forest/Ag Intensive Agriculture

Stru

ctur

es (#

/ac)

197619942006

7Houses in the woods

Forest fragmentation

Ecoregion Section Metric 1976 1994 2006Cascades Total area (ha) 1,015,081 1,002,000 994,953Cascades Total perimeter (km) 2,167 2,462 2,557Cascades Area/Perimeter (ha/km) 468 407 389Cascades Mean area (ha) 101,508 100,200 82,913

Coast Ranges Total area (ha) 430,001 427,090 425,522Coast Ranges Total perimeter (km) 1,998 2,016 2,052Coast Ranges Area/Perimeter (ha/km) 215 212 207Coast Ranges Mean area (ha) 25,294 22,478 22,396

Puget + Willamette lowlands Total area (ha) 145,318 138,996 133,648Puget + Willamette lowlands Total perimeter (km) 2,884 2,980 3,205Puget + Willamette lowlands Area/Perimeter (ha/km) 50 47 42Puget + Willamette lowlands Mean area (ha) 10,380 8,687 5,346

All SWWA Total area (ha) 1,590,400 1,568,087 1,554,124All SWWA Total perimeter (km) 6,464 6,902 7,291All SWWA Area/Perimeter (ha/km) 246 227 213All SWWA Mean area (ha) 38,790 34,846 27,752

Year8

Policy implications

Similar amounts of development have occurred in both Oregon and Washington in the Portland area (Fig. 9). However, development is less dispersed in Oregon, indicating that land-use laws in place since the 1970s have been effective. Preliminary analysis of land value in King county indicates higher assessed value of land close to urban areas (Fig. 10), which may indicate pressure to develop those lands over other uses.

10 Market Value of Land Per Acre by Distance to Urban

01000200030004000500060007000

Urban <1/4 Mile 1/4 to 1/2Mile

1/2 to 3/4Mile

3/4 to 1Mile

>1 Mile

* Parcel data provided by Luke Rogers, University of Washington

11

Funding for this project was provided by the Forest Health Monitoring program and

the PNW Research Station