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41 41

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1993). 1993).

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31 31

1996) 1996) be be

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1993). 1993).

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1995), 1995),

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1995). 1995).

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a a

the the

the the

techniques techniques

and and

random random

classification classification

our our

matrix matrix

We We

the the

Producer's Producer's

Lowland Lowland Landsat Landsat

Farmland Farmland

Upland Upland

Water Water

Column Column Urban Urban

Sparse Sparse

was was

Shrub Shrub

assignment assignment

river river

study study

10, 10,

in in

the the

produce produce

technique technique

random random

capture. capture.

study study

types types

types types

analysis analysis

for for

categories. categories.

using using

Silvicultural Silvicultural

dry dry

completed completed

beds, beds,

a a

recorded recorded

category, category,

patch patch

using using

this this

used used

I.-Error I.-Error

the the

July July

supervt:~ed supervt:~ed

I I

6 6

5 5

3 3

7 7

4 4

2 2

1994). 1994).

and and

agreement agreement

statistic statistic

random random

between between

the the

egory egory

would would

determined determined point point

information. information.

and and

values values

sampling sampling

stratified stratified

Lillesand Lillesand accuracy, accuracy,

patch patch

analyses. analyses. these these

for for

one one

ha) ha)

within within

fication. fication. river river patch patch

illumination illumination 8.2). 8.2).

image image

nents nents

cation cation

in in

7; 7;

were were

We We

'Includes 'Includes

Category Category Table Table /~ • l¥[(Q)JFJEIP

D U/NV

D S/EF

D F/G w

~ UF

II LF

D SF

N

0 Skm 10km I I I

Figure 2.- Patch types within the MOFEP study region: Urban and Non-vegetated (U/NV}, Shrub and Early Successional Forest (S/EF}, Fannland and Grasslands (FIG), Water (W), Upland Forest (UF), Lowland Forest and Wetlands {LF), Sparse Forest and Partial Cuts (SF).

44 Table 3.-Aspect categories and codes used for intersec­ overall stream and road densities of 1. 7 km/ 2 2 tion with patch types in Arc/Info GIS. km and 1.4 km/km , respectively. Land area within stream and road buffers increased Aspect range Category linearly with increasing buffer width (fig. 3), though at a slower rate for road buffers than Degrees stream buffers. Area in road and stream buff­ flat 1 flat ers was 1, 711 ha (2.8 percent of landscape) and

0.0- ~22.5 N 2,061 ha (3.4 percent of landscape), respec­

>22.5 - ~67.5 NE tively, for a buffer width of 10 m, and 15,884 ha

>67.5- ~112.5 E (26.1 percent oflandscape) and 19,115 ha (31.4

> 112.5- ~157.5 SE percent of landscape), respectively, for a buffer

> 157.5- ~202.5 s width of 100 m. > 202.5- ~247.5 sw > 24 7.5 - ~292.5 w

> 292.5- ~337.5 NW

> 337.5- ~360.0 N

1slope <1 percent whole. We calculated the area of each patch type within all stream buffers, road buffers, the nine MOFEP study sites, and within the entire landscape. We also examined the distribution 0 20 40 60 80 100 of patch types by classes of aspect, slope, and Buffer Width (m) elevation. For each patch type, we determined mean patch area, maximum patch area, mean Figure 3.-Change in buffer area around roads fractal dimension, mean core area index (using and streams with increasing buffer width. a buffer of 40 m), total edge length, and edge density. Patch metrics and distributions were compared between the MOFEP study sites and Total road length in stream buffer zones was the regional landscape. All manipulations of 21.8 km in 10-m buffers and 36.0 km in 100-m final coverages and statistical summaries were buffers (fig. 4A) corresponding to densities of 2 2 done in Arc/Info GIS Unix version 7.0.4 and 1.1 km/km and 1.9 km/km , respectively (fig. SAS Unix version. All patch metrics were 4B). Road density reached a maximum of 2.0 calculated using FRAGSTATS version 2.0 km/km 2 in 40-m buffers, as compared to 1.4 (McGarigal and Marks 1995). km/km 2 in the study region as a whole.

RESULTS The overall classification accuracy for the landscape was 87 percent (table 1). The KHAT Total land area within the boundary designated statistic was 79 percent, indicating that the for this study was 60,727 ha (607.3 km 2). Total classification was 79 percent better than a stream length within this region was 1,036.9 random assignment of pixels to patch types. km and road length totaled 861.3 km, giving The majority of the landscape was covered with upland forest (UF; 73 percent). Sparse or partially cut forest (SF) and shrub or early Table 4.-Elevation categories and codes used for successional forest (S/EF) covered about 10 intersection with cover types in Arc/Info GIS. percent of the landscape each. Lowland forest and wetlands (LF) covered 5 percent and farm­ Elevation range Category land or grassland (F /G) covered 2 percent. All other patch types each represented ~2 percent Meters of the land area (fig. 5). MOFEP study sites, :::::o-~150 except for site 7, were also dominated by upland >150- ~200 2 forest. Shrub and early successional forest was >200- ~250 3 underrepresented in the MOFEP sites (average = >250- ~300 4 3 percent) relative to the landscape (9 percent). >300- ~350 5 Farmland, urban/non-vegetated areas, and >350 6 water were not detected in any MOFEP study 45

Land Land

than than

among among

became became

farmland farmland

dominated dominated

found found

percent) percent)

amount amount on on

cent. cent.

categories categories

about about

Most Most >40 >40

area area

cent cent

and and

>100 >100

<40 <40

Figure Figure

as as study study

sites sites

46 46

-g -g

6 6

_J _J

a: a:

E E

.r:: .r::

0, 0,

~ ~

; ;

"0 "0

~ ~

~ ~

D D "iii "iii

C\J C\J

0 0

~ ~

ell ell

c c

CD CD

E E

a a

flat flat

OO@W~W------

400·~------, 400·~------, 200 200

300 300

100 100

eastern eastern

roads roads

widths widths

0.5 0.5

2.5 2.5

1.5 1.5

percent; percent;

percent. percent.

25 25

whole. whole.

of of

was was

at at

other other

0 0

2 2

of of

area area

percent percent

o+-~~----~----r---~----

Patch Patch

sites sites

on on

1 1

ground ground

4.-Totallength 4.-Totallength

+-----,_----~----~-----+----~ +-----,_----~----~-----+----~

aspect aspect

.------, .------,

lowland lowland

0 0

0 0

percent percent

this this

the the

more more

percent percent

(16 (16

were were

<10 <10

slopes slopes

(83 (83

within. within.

B) B)

was was

and and

A) A)

in in

categories categories

within. within.

were were

land land

Missouri. Missouri.

percent) percent)

scale scale

types types

about about

percent) percent)

all all

Upland Upland

common. common.

(table (table

percent percent

also also

categories, categories,

20 20

20 20

where where

was was

relatively relatively

forest forest

slope, slope,

of of

< <

less less

stream stream

area area

aspect aspect

10 10

of of

the the

were were

located located

the the

the the

Stream Stream

50 50

Stream Stream

5, 5,

analysis. analysis.

percent. percent.

of of

diverse diverse

shrub shrub

study study

forest forest

(table (table

(99.1 (99.1

and and

slope slope

40 40

and and

and and

40 40

fig. fig.

landscape landscape

percent percent

(A) (A)

flat flat

only only

more more

categories categories

buffers buffers

evenly evenly

with with

Buffer Buffer

6A). 6A).

Buffer Buffer

on on

and and

sparse sparse

37 37 urban urban

land land

percent) percent)

landscape, landscape,

(table (table

6). 6).

dominated dominated

and and

patch patch

than than

evenly evenly

slopes slopes

60 60

percent percent

60 60

The The

In In

a a

was was

density density

About About

of of

distributed distributed

(m) (m)

Upland Upland

(m) (m)

(no (no

slightly slightly

farmland farmland

general, general,

was was

areas areas

forest forest

different different

5). 5).

the the

type type

(table (table

majority majority

between between

aspect) aspect)

distributed distributed

had had

<10 <10

80 80

80 80

Only Only

on on

landscape landscape of of

48 48

{B) {B)

south­

all all

in in

(86 (86

forest forest

was was

larger larger

the the

6, 6,

a a

per­

slopes slopes

per­

the the

slopes slopes

of of

slope slope

slope slope

fig. fig.

of of

10 10

100 100

100 100

widths, widths,

buffers buffers

types types

in in

road road

roads. roads.

and and

lent lent

similar similar scale scale

partially partially

more more

less less Only Only

fig. fig.

the the

farmland farmland a a

scape. scape.

except except

ated ated

slightly slightly

sparse sparse

slightly slightly Patch Patch

on on stream stream

between between

The The

farmland farmland

m. m. categories categories

shrub shrub

became became

96 96

(compare (compare Eighty-six Eighty-six

forest forest

elevations elevations

The The

areas areas

erly erly

area area common common

elevation elevation

Farmland Farmland

other other

categories. categories.

occurred occurred

aspect, aspect,

6B). 6B).

patches patches

mon mon

random random

10-m 10-m

land land

percent percent

5). 5).

landscape. landscape.

Larger Larger

in in

farmland farmland

common common

slopes. slopes.

majority majority

area area

with with

between between

buffers buffers

four four

in in

in in

Lowland Lowland

common common

were were

patch patch

<150m <150m

types types

dominated dominated

or or

urban urban

stream stream

forest forest

The The

Shrub Shrub

among among

Shrub Shrub

buffers buffers

between between

less less

except except

more more

flat flat

though though

the the

>350 >350

relatively relatively

buffers buffers

was was

cut cut

200 200

early early

on on

of of

was was

on on

(92 (92

fig. fig.

was was

sparse sparse

patch patch

road road

and and

<250 <250

(fig. (fig.

percent percent

proportions proportions

similarly similarly

of of

distribution distribution

areas areas

MOFEP MOFEP

sparse sparse

Shrub Shrub

had had

common common

types types

flat flat

areas areas

flat flat

than than

evenly evenly

and and

and and

of of

percent), percent),

7A 7A

common common

in in

water water areas areas

m m

250 250

than than

more more

located located

where where

and and

areas areas

buffers buffers

forest forest

in in

stream stream

for for

successional successional

6C). 6C).

urban urban

and and

distribution distribution

the the

Roads Roads

the the

road road

than than

types types

m, m,

ground ground

20 20

than than

ground ground

a a

to to

forest forest

narrower narrower

all all

250 250

farmland farmland

and and

more more

in in

water, water,

on on

and and

similar similar

appeared appeared

early early

of of

area area

forest forest

fig. fig.

would would

with with

majority majority

and and

the the landscape landscape

(and (and was was

common. common.

distributed distributed

sites. sites.

distributed distributed

were were

elevation elevation

stream stream

was was

water water

buffers buffers

urban urban

in in

in in

slopes slopes

within within

areas areas

at at

were were

than than

m. m.

buffers buffers on on

were were

in in

with with

300m 300m

5). 5).

of of

and and

landscape landscape

common common

was was

wider wider

stream stream

and and

of of

100 100

successional successional

found found

and and

about about

water), water),

elevations elevations

which which

the the

relatively relatively

west-facing west-facing slopes.

and and

sparse sparse

relatively relatively

be be

prevalence prevalence

Ninety-nine Ninety-nine

All All

patch patch

Upland Upland

stream stream

and and

detected detected

were were

road road

partially partially

were were

40 40

(compare (compare more more

forest forest

areas areas

with with

buffers. buffers.

of of

m m

more more

north north

more more

other other

west-facing west-facing slopes.

than than

expected expected

stream stream

(table (table

partially partially

four four

buffers buffers

of of

categories categories

was was

Sparse Sparse

shrub shrub

at at

60 60

wide. wide.

percent percent

was was

buffers buffers

urban urban among among

within within

which which

different different

buffers buffers

forest forest

more more

(fig. (fig.

types types

relatively relatively

an an

closely closely

elevation elevation

were were

percent percent

common common

as as

in in

common common

were were

elevation elevation

buffers. buffers.

had had forest forest

to to

<300 <300

more more

<300 <300

more more

7). 7).

relatively relatively

easterly easterly

at at

cut cut

buffers buffers

the the

a a

6C). 6C).

Patch Patch

within within

northeast­

area area fig. fig.

However, However,

forest forest

forest forest

along along

percent percent

based based

land land

common common

was was

were were

cut cut

whole, whole,

road road

aspect aspect

this this

and and

of of

Upland Upland

similar similar

than than

at at

found found

where where

m m

areas areas

com­

land­

except except

associ­

was was

m m

preva­

7B 7B

the the

more more

in in

<200 <200

than than

in in

and and

was was

and and

in in

to to

on on of of

47 47

types types

patch patch

MOFEP MOFEP

for for

1 1

patch patch

and and

of of

table table

See See

landscape landscape

the the

sites. sites.

5.-Distribution 5.-Distribution

types. types.

within within

study study

Figure Figure

8 8

9 9

6 6

7 7

Sites Sites

Site Site

Site Site

Site Site

Site Site

All All

UF UF

94% 94%

UF UF

81% 81%

65% 65%

LF LF

12% 12%

10% 10%

S/EF S/EF

S/EF S/EF

SF SF

1% 1%

2% 2%

3% 3%

S/EF S/EF

S/EF S/EF

LF LF

3% 3%

Landscape Landscape

LF LF

5% 5%

(S/EF) (S/EF)

SF SF

SF SF

u90% u90%

~UF ~UF

C)UF C)UF

SF SF

w w

1% 1%

18% 18%

UF UF

73% 73%

0 0

.~~en,~~ .~~en,~~

(SF) (SF)

2Yo 2Yo

F/G F/G

Forest Forest

(LF) (LF)

(U/NV) (U/NV)

Cuts Cuts

S/EF S/EF

(FIG) (FIG)

0.4% 0.4%

(UF) (UF)

UINV UINV

Successional Successional

SF SF

5 5

10% 10%

3 3

1 1

2 2

Forest/Wetlands Forest/Wetlands

ForesUPartial ForesUPartial

Forest Forest

(W) (W)

Site Site

Site Site

Site Site

Site Site

Site4 Site4

Farm/Grassland Farm/Grassland

Urban/Non-vegetated Urban/Non-vegetated

Shrub/Early Shrub/Early

93% 93%

• • 1111 1111 DSparse DSparse

DUpland DUpland Elllowland Elllowland

DWater DWater

Ill Ill

, ,

/0 /0

% %

50

0 0

3

% %

S/EF S/EF

0.4% 0.4%

S/EF S/EF

S/EF S/EF

/0 /0

1

0/ 0/

S/EF S/EF

SFS/EF SFS/EF

5

SF SF

7% 7%

3% 3%

SF SF

SF SF

SF SF

6% 6%

0.5% 0.5%

~UF ~UF

085% 085%

LF LF

u99.1 u99.1

5% 5%

rT'\, rT'\,

u86% u86%

~UF ~UF

LF LF

C!)UF C!)UF

LF LF

~.~~ ~.~~

4% 4%

LF LF 5% 5% Table 5.-Area ofeach patch type within slope categories for the study landscape, southeastern Missouri. *"'CXl +~ @ Patch type Slope (percent) ~ >0- ~10 >10- ~5 >25- ~0 >40-~5 >55- <70 >70 - ~5 >85- 100 Total Percent ,toll - Hectares ------

Urban and non-vegetated 185 28 3 <1 0 0 0 0 215 0.4 Shrub and early successional forest 3,348 1,885 295 34 4 2 <1 0 5,566 9.2 Farmland and grasslands 1,037 207 8 3 0 0 0 0 1,254 2.1 Water 320 85 42 16 2

Total 22,665 30,562 7,014 432 43 9 2 2 60,728 Percent 37.3 50.3 11.5 0.7 0.1 <0.1 <0.1 <0.1 100

Table 6.-Area ofeach patch type within aspect categories for the study landscape, southeastern Missouri.

Patch type Aspect (degrees) Flat N NE E SE s SW w NW Total Percent - Hectares ------

Urban and non-vegetated 130 14 12 8 8 7 11 8 17 215 0.4 Shrub and early successional forest 1,555 416 628 745 748 467 333 294 380 5,566 9.2 Farmland and grasslands 544 87 129 116 106 79 49 59 86 1,254 2.1 Water 170 22 62 48 44 26 24 28 42 465 0.8 Upland forest 4,745 4,821 5,183 5,211 5,529 4,858 4,504 4,127 5,084 44,062 72.6 Lowland forest and wetlands 813 121 95 106 163 267 525 595 314 2,999 4.9 Sparse forest and partial cuts 1,501 443 434 470 644 752 804 585 533 6,166 10.2

Total 9,458 5,924 6,544 6,702 7,242 6,456 6,248 5,696 6,457 60,726 Percent 15.6 9.8 10.8 11.0 11.9 10.6 10.3 9.4 10.6 100

and and wetlands; wetlands; SF--sparse SF--sparse forest forest and and cuts. cuts. partial c.o c.o

.p. .p.

U!NV--urban U!NV--urban

and and non-vegetated; non-vegetated;

SIEF--shrub SIEF--shrub and and early early successional successional E:ij E:ij

forest; forest; FIG-farmland FIG-farmland and and grasslands; grasslands; W-water; W-water; UF--upland UF--upland forest; forest; LF-lowland LF-lowland forest forest 1 1 w w s s

= =

~ ~ SF SF 1068 1068

1.36 1.36 5.8 5.8

178.5 178.5 11.5 11.5 1,614.1 1,614.1 26.1 26.1

~ ~

LF LF 870 870 ~ ~ 1.37 1.37 3.5 3.5 136.4 136.4

6.2 6.2 1,011.8 1,011.8 33.7 33.7

a a

"'" "'"

UF UF

332 332 1.35 1.35 132.8 132.8 20,876.2 20,876.2 17.7 17.7 @ @ 2,435.8 2,435.8 5.5 5.5

w w

Landscape Landscape 838 838 1.38 1.38 ~ ~ 12.2 12.2 63.2 63.2 8.1 8.1 130.7 130.7 28.1 28.1

FIG FIG 159 159 1.35 1.35 ~ ~ 7.9 7.9 81.7 81.7 17.2 17.2

283.9 283.9 22.6 22.6

l2'.l l2'.l

SIEF SIEF 849 849 1.36 1.36 6.6 6.6

214.9 214.9 12.0 12.0 1,409.7 1,409.7 25.3 25.3 l".l l".l

U/NV U/NV 60 60 1.37 1.37 3.6 3.6 21.2 21.2 § § 5.5 5.5 74.6 74.6

34.7 34.7

~ ~

SF SF 58 58 1.35 1.35 6.6 6.6 48.4 48.4 14.6 14.6 91.7 91.7 24.1 24.1

Study Study sites sites LF LF 86 86 1.36 1.36 2.5 2.5 12.4 12.4 5.8 5.8 83.0 83.0 38.2 38.2

MOFEP MOFEP UF UF 38 38 1.33 1.33 80.8 80.8 479.1 479.1 30.7 30.7 196.9 196.9 6.4 6.4

SIEF SIEF 31 31 1.37 1.37 3.7 3.7 23.8 23.8 9.0 9.0 36.4 36.4 31.9 31.9

lla lla lla lla Percent Percent Km Km Km/km

2 2

tl:J.!e

dimension dimension size size size size

area area index index length length 1 1

Patch Patch N N Mean Mean fractal fractal Mean Mean patch patch Max Max patch patch Mean Mean core core Total Total edge edge Edge Edge density density

Table Table 8.-Landscape 8.-Landscape metrics metrics by by cover cover type type for for MOFEP MOFEP sites sites and and the the entire entire landscape, landscape, southeastern southeastern Missouri. Missouri.

Percent Percent 0.4 0.4 14.6 14.6 37.0 37.0 40.3 40.3 6.9 6.9 0.7 0.7 100 100

Total Total 268 268 8,872 8,872 22,491 22,491 24,450 24,450 4,189 4,189 428 428 60,698 60,698

Sparse Sparse forest forest and and partial partial cuts cuts 37 37 1,417 1,417 2,252 2,252 2,017 2,017 337 337 106 106 6,167 6,167 10.2 10.2

Lowland Lowland forest forest and and wetlands wetlands 15 15 409 409 744 744 1,536 1,536 271 271 26 26 3,001 3,001 4.9 4.9

Upland Upland forest forest 107 107 4,977 4,977 16,125 16,125 19,358 19,358 3,287 3,287 207 207 44,062 44,062 72.6 72.6

Water Water 55 55 394 394 11 11 6 6 0 0 0 0 465 465 0.8 0.8

Farmland Farmland and and grasslands grasslands 7 7 293 293 776 776 145 145 7 7 0 0 1,228 1,228 2.0 2.0

Shrub Shrub and and early early successional successional forest forest 30 30 1343 1343 2,454 2,454 1,366 1,366 278 278 89 89 5,561 5,561 9.2 9.2

Urban Urban and and non-vegetated non-vegetated 17 17 39 39 128 128 22 22 8 8 0 0 215 215 0.4 0.4

- llectares llectares ------

>0- >150- >200- ~150 ~150 ~00 ~00 >250- 900 900 ~50 ~50 >300- >350 >350 950 950 Total Total Percent Percent

Patch Patch type type Elevation Elevation {meters} {meters}

Table Table 7.- Area Area of of each each patch patch type type within within elevation elevation categories categories for for the the study study landscape, landscape, southeastern southeastern Missouri. Missouri.

~00~~~~------

50 50

B) B)

A) A)

Figure Figure

r., r.,

~20% ~20%

() ()

(3 (3

() ()

~20% ~20%

(3 (3

c40% c40%

Q) Q)

t1l t1l

> >

(D60% (D60%

0 0

t1l t1l

~80% ~80%

<{20% <{20%

> >

c40% c40% (D60% (D60%

Q) Q)

(3 (3

0 0 t1l t1l

() ()

t1l t1l

~80% ~80%

.. ..

> >

(D60% (D60%

0 0

~ ~

c40% c40%

t1l t1l

t1l t1l

~80% ~80%

100% 100%

100% 100%

scape, scape,

aspect aspect

1 1

0% 0%

0% 0%

0% 0%

u1Nv u1Nv

6.-Distribution 6.-Distribution

>0-1 >0-1

flat flat

>0-150 >0-150

categories, categories,

southeastern southeastern

• •

0 0

s/EF s/EF

> > 1

N N

0-25 0-25

> >

150-200 150-200

and and

• •

of of

NE NE

Missouri. Missouri.

>25-40 >25-40

patch patch

{C} {C}

F/G F/G

>200-250 >200-250

elevation elevation

Aspect Aspect

E E

types types

>40-55 >40-55

Elevation Elevation

~ ~

See See

Slope(%) Slope(%)

SE SE

among: among:

(degrees) (degrees)

w w

table table

categories categories

>55-70 >55-70

>250-300 >250-300

(m) (m)

1 1

s s

for for

{A) {A)

> >

70-85 70-85

slope slope

patch patch

for for

>300-350 >300-350

sw sw

the the

categories, categories,

>85-1 >85-1

types. types.

study study

w w

00 00

LF LF

>350 >350

land­

> > 1

NW NW

00 00

{B) {B) .SF .SF

51 51

in in

CAl CAl

than than

the the

7 7

types. types.

a a

other other

the the

densi­

in in

CAl's CAl's

the the

forest forest

forest forest

percent) percent)

in in

all all

(33. (33.

MOFEP MOFEP

lowest lowest

had had

on on

sparse sparse

whole whole

Maximum Maximum

percent, percent,

in in

patch patch

Edge Edge

a a

(31 (31

large large

landscape landscape

the the

whereas whereas

the the

for for

similar similar

index index

all all

type type as as

sparse sparse

as as

in in

upland upland

17.7 17.7

the the

than than

which which

density density

sites. sites.

sites sites

had had

for for

for for

had had

sites, sites,

area area

the the

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and and

ence ence

be be More More

effect effect

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elimination elimination

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tures tures

species species

1990). 1990).

road road

the the

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play play

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and and

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already already tially tially

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structure structure

recorded recorded

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ing. ing.

buffers buffers

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support support

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ecotones ecotones

tion tion

landscape landscape

ian ian

et et

considered considered

100m 100m

aL aL

press). press).

lMr@lFJEIP lMr@lFJEIP

to to

forests forests

small small

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importance importance

cut cut

Best Best

relatively relatively

a a

to to

communities communities

of of

density density

Machtans Machtans

and and

than than

cut cut

associated associated

may may

of of

corridors. corridors.

1993) 1993)

31 31

could could

relatively relatively

to to

suggesting suggesting

DISCUSSION DISCUSSION

In In

this this

support support

populations, populations,

evaluated. evaluated.

(Bennett (Bennett

on on

as as

dominated dominated

habitat habitat

also also

areas, areas,

100m, 100m,

in in

diverse diverse

us) us)

of of

of of

1991, 1991,

remote remote for for

percent percent

stands stands

within within

and and

Bailey Bailey

percentage percentage

within within

1980). 1980).

forests forests

region region

indicates indicates

growth, growth,

provide provide

Previous Previous

Allowing Allowing

one-quarter one-quarter

habitat habitat

these these

than than

may may

road road

of of

1.4 1.4 riparian riparian

network network

1.6 1.6

and and

be be

to to

density density

undisturbed undisturbed

is is

represents represents

activity. activity.

forest forest have have

road-influenced, road-influenced,

widespread widespread

it it

fragmentation fragmentation

a a

km/km

Lyon Lyon

km/km

a a

et et

be be

suggesting suggesting

movement movement

for for

greater greater

wildlife wildlife

of of

do do

density, density,

boreal, boreal,

microclimate microclimate with with

1979). 1979).

and and

of of

residual residual Individuals Individuals

this this areas areas

1991) 1991)

is is

critical critical

Avian Avian

of of

concem concem

of of

aL aL

habitat habitat

(Gregory (Gregory

dispersal dispersal

for for

roads roads

microclimatic microclimatic

contained contained

by by

Roads Roads

likely likely

New New

large large

distinct distinct

cutting cutting

the the

studies studies

that that

for for

the the

interior interior

zone. zone.

decreased decreased

on on

especially especially

AND AND

farmland. farmland.

1983). 1983).

(1996) (1996)

of of

landscape landscape

patch patch

territories territories

humans, humans,

In In

by by

2 2

2 2

but but

of of

an an

Rocky Rocky

species species

habitat habitat

landscape landscape the the

role role

York, York,

We We

mixed-wood mixed-wood

communities communities

a a

within within

reduced reduced

variable variable

a a

ungulates ungulates

in in

due due

that that

this this

habitats habitats

areas. areas. the the

significant significant

in in hunters hunters

here. here.

loss loss

distrtbution distrtbution

large large

edge edge

CONCLUSIONS CONCLUSIONS

These These

rates rates

widespread widespread

or or

can can

region region and and

creating creating

et et

detected detected

have have

types types

found found

corridors corridors

in in

(Reed (Reed

These These

this this

may may

within within

to to

Adirondack Adirondack

of of

other other

black black

road road

al. al.

landscape landscape

(Brosofske (Brosofske

Mountains, Mountains,

for for

fragmentation fragmentation

of of

rapidly rapidly

given given

the the

use use

contrtbute contrtbute

availability, availability,

effect effect

such such

increased increased

portion portion

diverse diverse

should should

habitat habitat

However, However,

This This

and and

that that

environment, environment,

impacting impacting shown shown

landscape landscape

the the

1991, 1991,

regions

large large

rely rely

that that

large large

in in

could could

after after et et

that that

(Brocke (Brocke

linear linear

networks networks

Ozark Ozark

by by

riparian riparian

human human

bear bear

these these

additional additional

forest forest

similar similar

as as

amount amount

dispersal dispersal

aL aL

farmland farmland

an an

had had

as as

road road

of of

(Stauffer (Stauffer

for for

more more

one-half one-half

with with are are

of of

animals animals

influ­

buffers buffers

verte­

Naiman Naiman

be be

vegeta­

harvest­

move­

of of

and and

par­ that that

100m, 100m,

1996). 1996).

edge edge

be be

could could

(Ursus (Ursus

ripar­

also also

some some

et et

fea­

been been

given given

road road

were were

et et

aL, aL,

are are

aL aL

of of

of of

low low

upland upland

type type

patch's patch's

interrelationships interrelationships

This This

of of

ture ture and and

dyn.amics dyn.amics

Characterization Characterization

tion tion

practices practices

consider consider

respect respect roles roles from from

assessment assessment

patch patch

types. types.

results results categories, categories,

coverage coverage

ture, ture,

variation variation

Slope, Slope,

through through diversity diversity

(Swanson (Swanson

treatments. treatments.

study study

level level

have have

treatments treatments should should

temporal temporal

considered considered

the the

larger larger

pattem pattem

to to

(Larsen (Larsen

scape scape within within Forested Forested

degree degree

reptiles reptiles

We We

threat. threat.

turtles turtles extreme extreme

barrier barrier

our our

(e.g., (e.g.,

40 40

expand expand

amount amount

obsetved obsetved

MOFEP MOFEP

function. function.

of of

within within

within within

study study

may may

sources sources

structure structure

in in

m, m,

moisture, moisture,

long-term long-term

high high

distrtbution. distrtbution.

sites sites

as as

landscapes, landscapes,

aspect, aspect,

community community

Note Note

stream stream

in in forest) forest)

area area

suggest suggest

further further

to to

and and

for for

determining determining

of of

et et

are are

Road Road

we we

their their

the the

microclimatic microclimatic

and and

of of

a a may may

in in

areas areas

introduce introduce

distrtbutions distrtbutions

of of

MOFEP MOFEP

et et

these these

patch patch

al. al.

the the

areas areas

surface surface

slope slope

whole. whole.

herpetofauna herpetofauna

when when

landscapes landscapes

MOFEP MOFEP

within within

at at

patch patch

found found

of of

of of

landscape landscape

most most

snakes) snakes)

that that

sites sites

was was

landscape landscape

al. al.

spatial spatial

with with

regional regional

that that

1997). 1997).

effects effects

the the

densities densities

or or

differentially differentially

and and

topographical topographical core core

On On

applicability applicability

buffers buffers

(Wallin (Wallin

consider consider

and and

are are

that, that,

consequences consequences

1988, 1988,

variables, variables,

during during

types types

the the

in in

and and

of of

our our

must must comparing comparing

likely likely

types types

landscape landscape

between between

average, average,

numerous numerous

study study

that that

different different

the the

types types

temperature) temperature)

elevation elevation

If If

the the

area area

represented represented

the the

core core

study study

However, However,

additional additional

nutrtent nutrtent

distrtbution distrtbution

were were

distrtbutions distrtbutions

regional regional

MOFEP MOFEP

on on

although although

elevation elevation

Effects Effects

elevation elevation

vegetation vegetation

Zobel Zobel

where where

study study

et et

in in

cover cover

higher higher

less less

of of

environment environment

structure. structure.

should should

heterogeneity heterogeneity

also also

reached reached

to to

is is

the the

insulation, insulation,

within within

the the

habitat habitat

sites sites

and and

al. al.

(e.g., (e.g.,

the the

hatvested hatvested

killed killed

sites sites

similar similar

be be

because because

landscape landscape

using using

of of

influence influence

than than

contour contour

be be

summer, summer,

impact impact et et

1994). 1994).

influence influence

results results

among among

sites sites

scale. scale.

influences influences

gradients gradients of of

the the

animals animals

researchers researchers

affected. affected.

amphibians amphibians

areas areas

landscape. landscape.

managers managers

than than

their their

diversity diversity

for for

error error

data data

van van

the the

al. al.

elucidate elucidate

considered considered play play

silvicultural silvicultural

(except (except

patches patches

by by

to to

for for

1.9 1.9

also also

of of

distrtbutions distrtbutions

long-term long-term 20 20

an an

landscape­

across across

1976). 1976).

must must

of of

relative relative

a a

vehicles vehicles

in in

Gelder Gelder

hatvest hatvest

management management

studies studies

surrounding surrounding

tempera­ were were

any any

Spatial Spatial

of of

Managers Managers

important important

km/km

intetvals. intetvals.

areas areas

the the percent percent

into into

of of

greater greater

edge edge

of of

patch patch

poses poses

regenera­

of of

and and

the the

structure structure

(e.g., (e.g.,

the the

plant plant

study study

for for roads roads

and and

on on

of of also also

struc­

MOFEP MOFEP

should should

patch patch

the the

the the

aspect aspect

derived derived

Our Our

want want

The The

width width

land­

and and

the the

may may

bare bare

1973). 1973).

with with

to to

in in

and and

a a

2 2

of of

be be a a

53 53

of of

a a

1-

on on

5: 5:

the the

21-

Gen. Gen.

R., R.,

an an

A.W., A.W.,

De­

Gen. Gen.

re­

effect effect

Dou­

mitigat­

1997. 1997.

Ecologi­

streams streams

Cam­

K.A. K.A.

Press. Press.

Service, Service,

and and

In: In:

resources. resources.

MO. MO.

Saunders, Saunders,

U.S. U.S.

Missouri Missouri

Station: Station:

Norton, Norton,

ecosystem. ecosystem.

the the

Ozark Ozark

Station: Station:

1995. 1995.

Press: Press:

U.S. U.S.

R.J.; R.J.;

sensitive sensitive

Service, Service,

gradients gradients

D.C. D.C.

In: In:

harvesting harvesting

applications applications

conservation conservation

mosaics: mosaics:

Haney, Haney,

Stephen Stephen

small small

The The

MN: MN:

Conservation. Conservation.

management: management:

on on

PA: PA:

of of

scheme scheme

fragmentation fragmentation

T.A. T.A.

Forest Forest

Louis, Louis,

Ecosystem Ecosystem

future. future.

regions. regions.

forest forest

wildlife wildlife

of of

Applications. Applications.

landscape landscape

symposium: symposium:

Dey, Dey,

northeast? northeast?

99-117. 99-117.

old-growth old-growth

Project: Project:

Forest Forest

from from

St. St.

University University

M.S.; M.S.;

to to

Paul, Paul,

roadsides, roadsides,

Gustafson, Gustafson,

Missouri Missouri

1993. 1993.

Chipping Chipping

review. review.

Naiman, Naiman,

Nature Nature

the the

Washington. Washington.

and and

and and

R.; R.;

and and

the the

forest forest

Shifley, Shifley,

University University

Experiment Experiment

a a

Spies, Spies,

Effects Effects

Experiment Experiment

into into

C. C.

Forest Forest

St. St.

press. press.

Radnor, Radnor,

J.; J.;

on on

the the

3-5; 3-5;

Is Is

in in

Landscape Landscape

networks networks

L.; L.;

J.P.; J.P.;

eds. eds.

Project Project

Beatty: Beatty:

In In

Ecosystem Ecosystem

of of

microclimatic microclimatic

Yale Yale

Boyce, Boyce,

management: management:

Roads, Roads,

J.F.; J.F.;

In: In:

forest forest

Ecological Ecological

Agriculture, Agriculture,

1997. 1997.

Forest Forest

management management

edges edges

gradients gradients

Department Department

western western

Jensen, Jensen,

present, present,

Ozark Ozark

approach approach

June June Forest Forest

road road

Ecosystem Ecosystem In: In:

issue issue

Chen, Chen,

R.J., R.J., corridors. corridors.

CT: CT:

of of

1995. 1995.

Cambridge Cambridge

Brian Brian

Agriculture, Agriculture,

Hauser, Hauser,

in in

NC-193. NC-193.

1997. 1997.

of of

NE-140. NE-140.

landscapes landscapes

of of

Surrey Surrey

O'Pezio, O'Pezio,

1991. 1991.

J.F. J.F.

of of

B.L.; B.L.;

B.; B.;

1997 1997

of of

forest forest

past, past,

.F. .F.

MA: MA:

forests. forests.

K.D.; K.D.;

species. species.

conservation: conservation:

Ecosystem Ecosystem

Forest Forest

J J

Central Central

Franklin, Franklin,

Rep. Rep.

management management

role role

A A

Rep. Rep.

R.T.T. R.T.T.

clearcut clearcut

Hobbs, Hobbs,

Haven, Haven,

Ecosystem Ecosystem

A.F. A.F.

p. p.

Missouri Missouri

Proceedings Proceedings

R.H.; R.H.;

Missouri Missouri

sustainable sustainable

Applications, Applications,

overview. overview.

impact impact

p. p.

J.; J.;

uplands uplands

the the

53. 53.

New New

for for

eds. eds.

an an

74-86. 74-86.

632 632

ecology ecology

bridge, bridge,

from from

Growing-season Growing-season

glas-fir glas-fir cal cal

Franklin, Franklin,

19 19

to to

25. 25. microclimatic microclimatic

North North

13-17. 13-17.

search; search; experimental experimental

Department Department

Forest Forest

Brookshire, Brookshire,

eds. eds.

Project: Project:

1990. 1990.

Tech. Tech.

Ozark Ozark

MO: MO:

forest forest

Northeastern Northeastern

The The

management management

partment partment

ing ing

2: 2:

wildlife wildlife

D.A.; D.A.;

Tech. Tech.

Australia: :

wildlife wildlife

Franklin, Franklin,

Forman, Forman,

Chen, Chen,

Brosofske, Brosofske,

Brookshire, Brookshire,

Brookshire, Brookshire,

Brocke, Brocke,

Bennett, Bennett,

of of

on on

or or

et et

m. m.

to to

on on

of of

of of

with with

we we

of of

GIS GIS

on on

a a

25: 25:

other other

if if

mind. mind.

about about

Steve Steve

40 40

and and

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fluctu­

non­

edge edge

refer­

in in

often often

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image image

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length length

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(Chen (Chen

or or

extreme extreme

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interior interior

analysis analysis

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suggestions suggestions

landscape. landscape.

only only

are are

9.9 9.9

lowland, lowland,

of of

between between

patches patches

although although

patches patches

of of

Characteriz­

with with

this this

estimate estimate

time. time.

drawn drawn

high high

Glenn Glenn

and and

low low

provided provided

were were

of of

landscapes. landscapes.

result result

study. study.

Brian Brian

versus versus

between between

studies. studies.

edge edge

about about dependent dependent

conducted conducted

and and

scales, scales,

Research. Research.

and and

in in

and and

that that

be be

species species

available available

Therefore, Therefore,

these these

by by

provide provide

within within

the the

areas areas

exhibit exhibit

1981) 1981)

be be

this this are are

structure structure and and

forested forested

boundary boundary

1995. 1995.

(e.g., (e.g.,

of of

measurements measurements

or or

CITED CITED

in in

MDC MDC

than than

study study

forest forest

width width

forested forested

future future

forest forest

would would

forest forest

types types

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al. al.

point point

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not not

manuscript. manuscript.

Forest Forest

of of

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of of

generous generous

Although Although

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upland upland

total total

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Department Department limited limited

this this

neighboring neighboring

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results results

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of of

do do

this this

however however

edge edge

should should

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occur occur

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softer softer

largest largest

Shifley Shifley

forested forested

currently currently

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comments comments

habitat habitat

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by by

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area area

from from

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compare compare

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our our

classification, classification,

that, that,

ha ha

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benefit benefit

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Evaluation Evaluation

Maclean Maclean

to to

sites, sites,

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species species

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and and This This

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structure structure

Jordan, Jordan, core core

minimize minimize

this this

Journal Journal

Missouri Missouri

GIS GIS

and and

For For

LITERATURE LITERATURE

draft draft

landscape landscape

2) 2)

Whitcomb Whitcomb

that that variables variables

interior interior

Stephen Stephen

may may

sparsely sparsely

ACKNOWLEDGMENTS ACKNOWLEDGMENTS

that that

from from

>lOOm >lOOm

types types

Ann Ann

on on

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E.Z.; E.Z.;

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average average

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1995). 1995).

Baskent, Baskent,

processing. processing.

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databases. databases.

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within within the the

microclimate microclimate ground ground

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McGartgal, McGartgal,

Larsen, Larsen,

Lyon, Lyon,

Lillesand, Lillesand,

Machtans, Machtans,

Russin, Russin,

Hunsaker, Hunsaker,

54 54

Futuyma, Futuyma, Gustafson, Gustafson,

Glenn, Glenn,

Gregocy, Gregocy,

Gott, Gott,

Agriculture, Agriculture,

west west

fying fying

PNW-351. PNW-351.

John John

ing ing

Timmins, Timmins,

Forestry. Forestry.

Biology. Biology.

ecosystem ecosystem

ment ment spatial spatial

E.W.; E.W.;

Brookshire, Brookshire,

431. 431.

95:4-9. 95:4-9.

Journal Journal backscatter. backscatter.

sensing sensing

pattem. pattem.

Estimating Estimating

Kummins, Kummins,

science science

raphy raphy

of of

landscape landscape

ture, ture,

ties). ties). spective spective

National National

Carter, Carter,

540-551. 540-551.

Sunderland, Sunderland,

1996. 1996.

1994. 1994.

J. J.

patch patch

L.J. L.J.

habitat habitat

S.M.; S.M.;

D.R.; D.R.;

Y.A.; Y.A.;

1975. 1975.

Research Research

landscape landscape

Forest Forest

Rolla, Rolla,

S.V.; S.V.;

Wiley Wiley

corridors corridors

England, England,

Use Use

Sampling Sampling

T.M.; T.M.;

of of

D.J. D.J.

1983. 1983.

pattem pattem

C.T.; C.T.;

C.S.; C.S.;

Oregon, Oregon,

K.; K.;

and and

E.; E.;

and and

of of

Landscape Landscape

10: 10:

of of

colonization. colonization.

mammals mammals

Forest Forest

81: 81:

Nudds, Nudds,

Reich, Reich,

Shifley, Shifley,

S.P.; S.P.;

Portland, Portland,

of of

heterogeneity heterogeneity

researchers. researchers.

Swanson, Swanson,

Soil Soil

Biogeography. Biogeography.

K.W. K.W. riparian riparian

Karks, Karks,

Gardner, Gardner,

effectiveness effectiveness

slash slash

and and

MO: MO:

1986. 1986.

B.L.; B.L.;

Kiefer, Kiefer,

Forest Forest

Remote Remote

1366-1379. 1366-1379.

image image

Villard, Villard,

O'Neill, O'Neill,

IEEE IEEE

riparian riparian

Service. Service.

MA: MA:

Road Road

592-595. 592-595.

Station. Station.

Levine, Levine,

by by

analysis analysis

survey survey

K. K.

Area, Area,

structure. structure.

Sons, Sons,

Ripley Ripley

to to

1991. 1991.

U.S. U.S.

R.M.; R.M.;

T.D. T.D.

pine pine

Dey, Dey,

Sinauer Sinauer

Evolutionary Evolutionary

S.R.; S.R.;

B.J. B.J.

forest forest

Transactions Transactions

1997. 1997.

characterize characterize

density density

interpretation. interpretation.

R.W. R.W.

Service, Service,

in in

zones. zones.

Ecology. Ecology.

OR: OR:

Sensing. Sensing.

R.V.; R.V.;

M-A.; M-A.;

R.H. R.H.

F.J.; F.J.;

56 56

Department Department

buffer buffer

Missouri Missouri

Ecology. Ecology.

Canadian Canadian

Inc. Inc.

biomass biomass

1989. 1989.

An An

of of

D.C.; D.C.;

Hoffer, Hoffer,

D.A.; D.A.;

and and

1995. 1995.

Thompson, Thompson,

122 122

Journal Journal

program program

birds. birds.

for for

1994. 1994.

p. p.

U.S. U.S.

on on

10 10

the the

Jackson, Jackson,

16: 16:

Associates. Associates.

1996. 1996.

ecosystem ecosystem

McKee, McKee,

Bioscience. Bioscience.

Gen. Gen.

749 749

Hannon, Hannon,

models models

Shannon Shannon

Pacific Pacific

p. p.

Guidelines Guidelines

the the

elk. elk.

strips strips

Kurzejeski, Kurzejeski,

Norton, Norton,

Insular Insular

Mark Mark

9: 9:

FRAGSTATS: FRAGSTATS:

Department Department

29 29

261-268. 261-268.

R.M. R.M.

Remote Remote

Conservation Conservation

77: 77:

p. p.

using using

(parts (parts

biology. biology.

207-226. 207-226.

probability probability

landscape landscape

Tech. Tech.

The The

Joumal Joumal

on on

of of

parks. parks.

(3): (3):

for for

W.A; W.A;

of of

New New

1\vain 1\vain

describ­

Forestry. Forestry.

as as

North­

94-107. 94-107.

F.R., F.R.,

Geo­

B.L.; B.L.;

1991. 1991.

S.J. S.J.

biogeog­

Agricul­

quanti­

427-

effect effect

D.J. D.J.

per­

coun­

radar radar

move­

of of

Rep. Rep.

41: 41:

York: York:

for for

III; III;

of of

of of

of of

a a

Stauffer, Stauffer,

Swanson, Swanson,

Spencer, Spencer,

Schumaker, Schumaker,

Rost, Rost,

Reed, Reed,

Pickett, Pickett,

Missouri Missouri

Naiman, Naiman,

Meinert, Meinert,

Agriculture, Agriculture,

Wildlife Wildlife

Woodmansee, Woodmansee,

by by

Bioscience. Bioscience.

Journal Journal

vation vation

to to on on

Forest Forest

effects effects Massengale, Massengale,

resource, resource,

NC-139. NC-139.

mule mule

The The

641. 641.

mentation mentation

tions. tions.

regional regional scape scape

ecological ecological

Department Department

Stephen Stephen

an an

Department Department

succession succession

North North research; research;

56-68. 56-68. forms, forms,

Gen. Gen. 1210-1225. 1210-1225.

study study Ozark Ozark

1996. 1996.

G.R.; G.R.;

R.A.; R.A.;

predict predict

birds birds

ecosystem ecosystem

experimental experimental

role role

S.T.A.; S.T.A.;

Tech. Tech. J.S., J.S.,

D.F.; D.F.;

D.; D.;

R.J.; R.J.;

deer deer

Geological Geological

3: 3:

ecology: ecology:

Contribution Contribution

area. area.

Central Central

F.J.; F.J.;

Forest Forest

Biology. Biology.

Experiment Experiment

of of

geology, geology,

Bailey, Bailey,

Johnson-Bamard, Johnson-Bamard,

Management. Management.

ofWildlife ofWildlife

biodiversity. biodiversity.

of of

of of

St. St.

N.H. N.H.

209-212. 209-212.

R., R.,

Nigh, Nigh,

habitat habitat

1989: 1989:

habitat habitat

1997 1997

systems. systems.

and and

Jr.; Jr.;

Decamps, Decamps,

in in

Best, Best,

riparian riparian

riparian riparian

Rep. Rep.

in in

Kratz, Kratz,

38: 38:

Cadenasso, Cadenasso,

In: In:

Paul, Paul,

Forest Forest

eds. eds.

of of

of of

R.A. R.A.

the the

Ecosystem Ecosystem

pattems pattems

R.G. R.G.

Missouri. Missouri.

1996. 1996.

Forest Forest

Roussopoulos, Roussopoulos,

T.; T.;

spatial spatial

elk elk

Agriculture, Agriculture,

J.A. J.A.

Natural Natural

Brookshire, Brookshire,

10: 10:

92-98. 92-98.

June June

and and

an an

Survey. Survey.

L.B. L.B.

NC-193. NC-193.

approach approach

Proceedings Proceedings

alterations. alterations.

Rocky Rocky

1992. 1992.

connectivity. connectivity.

MN: MN:

T.K.; T.K.;

Kabrick, Kabrick,

in in

Management. Management.

Station. Station.

Service, Service,

1098-1106. 1098-1106.

analysis. analysis.

1988. 1988.

Science. Science.

communities: communities:

of of

corridors corridors

1979. 1979.

soils soils

Using Using

relation relation

H.; H.;

Experiment Experiment

3-5; 3-5;

1980. 1980. Ecological Ecological

44: 44:

heterogeneity heterogeneity

roads roads

U.S. U.S.

and and

Resources. Resources.

Caine, Caine,

M.L. M.L.

Missouri's Missouri's

Mountains. Mountains.

Rolla, Rolla,

Pollock, Pollock,

1979. 1979.

Project Project

of of

St. St.

Landform Landform

1-15. 1-15.

Distribution Distribution

St. St.

landscape landscape

J.; J.;

to to

J. J.

processes. processes.

84 84

Habitat Habitat

Department Department

Forest Forest

Brian Brian

North North

the the

269: 269:

to to

Resour. Resour.

Joumal Joumal

Paul, Paul,

1995. 1995.

to to

in in

landscape landscape

Louis, Louis,

of of

S.M.; S.M.;

1997. 1997.

Baker, Baker,

MO: MO:

N.; N.;

p. p.

forest forest Stratigraphic Stratigraphic

Ecology. Ecology.

MOFEP MOFEP

Applica­

roads. roads.

maintaining maintaining

the the

symposium: symposium:

43: 43:

M. M.

331-334. 331-334.

Station: Station:

L.; L.;

evaluating evaluating

Central Central

Service, Service,

forest forest

MN: MN:

185 185

Land­

Missouri Missouri

selection selection

Missouri Missouri effects effects

Land­

Conser­

in in

MO. MO.

1993. 1993.

634-

Bull. Bull.

Shifley, Shifley,

W.L. W.L.

frag­

indices indices

of of

of of

p. p.

U.S. U.S.

77: 77: of of

55 55

In: In:

to to

93-

in in

on on

Ims, Ims,

a a

of of

13: 13:

in in

B.; B.;

569-

Review Review

land­

the the

125-206. 125-206.

Bystrak, Bystrak,

1994. 1994.

J.F.; J.F.;

and and

legacies legacies

forest. forest.

Forest Forest

4: 4:

western western

approach approach

Dyrness, Dyrness,

B. B.

171-197. 171-197.

Monographs. Monographs.

changes changes

traffic traffic

369-380. 369-380.

K.M.; K.M.;

eds. eds.

Horne, Horne,

to to

diversity diversity

20: 20:

Annual Annual

Lynch, Lynch,

environment environment

ecology: ecology:

G.M.; G.M.;

66: 66:

Oecologia. Oecologia.

central central

from from

land-use land-use

fragmentation fragmentation

of of

Marks, Marks,

Van Van

and and

L. L.

deciduous deciduous

B.M., B.M.,

C.S.; C.S.;

the the

mechanisms mechanisms

Ecological Ecological

quantitative quantitative

Hawk, Hawk,

Applications. Applications.

F.J.; F.J.;

of of

man-dominated man-dominated

process. process.

Oikos. Oikos.

response response

forest forest

rules: rules:

N.C.; N.C.;

bujo bujo

A A

Springer-Verlag: Springer-Verlag:

in in

of of

Klimkiewicz, Klimkiewicz,

A.; A.;

on on

Landscape Landscape

resulting resulting

eastern eastern

Systematics. Systematics.

Sharpe, Sharpe,

Bujo Bujo

structure, structure,

Robbins, Robbins,

1973. 1973.

York: York:

Oregon. Oregon.

B.L.; B.L.;

Ecological Ecological

of of

pattern pattern

Relationships Relationships

ecology. ecology.

and and

of of

1989. 1989.

Swanson, Swanson,

Ecological Ecological

R.L.; R.L.;

Effects Effects

ofthe ofthe

Stenseth, Stenseth,

McKee, McKee,

pattern pattern

New New

J.J. J.J.

generation generation

R.F.; R.F.;

dynamics dynamics

communities communities

mortality mortality

of of

1993. 1993.

1976. 1976.

M.G. M.G.

135-156. 135-156.

D.O.; D.O.;

J.A.; J.A.;

1981. 1981.

D.B.; D.B.;

forest. forest.

the the

Ecology Ecology

Gelder, Gelder,

Cascades Cascades

46: 46:

forest forest

composition, composition,

C.T. C.T.

R.A. R.A.

landscape landscape

scapes. scapes.

island island

580. 580. Burgess, Burgess,

D. D.

avifauna avifauna

in in

pattern pattern

Landscape Landscape

to to

95. 95.

of of

population population

effect effect

Whitcomb, Whitcomb,

Zobel, Zobel,

Wiens, Wiens,

Whitcomb, Whitcomb,

Wallin, Wallin,

van van Turner, Turner,