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Advanced stand age Diversity of tree sizes from sapling to large sawtimber Presence of very old and large trees Presence of large standing dead trees Increased amounts of dead stumps and coarse woody debris An estimation of “old growth” acres in Wisconsin Old growth” compared to “old standsOld growth forests are natural stands that have developed over a period of time, generally at least 120 years, without experiencing a stand-replacing disturbance. Typical traits of old growth in Wisconsin include: Advanced stand age Diversity of tree sizes from saplings to large sawtimber Presence of very old and large trees Presence of large, standing dead trees Increased amounts of dead stumps and coarse woody debris Pit and mound topography and presence of canopy gaps Several of these characteristics are measured in the Forest Inventory and Analysis database and can be used to identify forests with old growth characteristics. In this report, we present one methodology for estimating old growth acreage across several inventories. Division of Forestry WI Dept of Natural Resources 8/2014

Old Growth Characteristics in Wisconsin's Forests · Forested acres meeting old growth criteria White / red / jack pine Oak / hickory Maple / beech / birch Elm / ash / cottonwood

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Advanced stand age

Diversity of tree sizes from sapling to large sawtimber

Presence of very old and large trees

Presence of large standing dead trees

Increased amounts of dead stumps and coarse woody debris

An estimation of “old growth” acres in Wisconsin

“Old growth” compared to “old stands”

Old growth forests are natural stands that have developed over a period of time, generally at

least 120 years, without experiencing a stand-replacing disturbance. Typical traits of old

growth in Wisconsin include:

Advanced stand age

Diversity of tree sizes from saplings to large sawtimber

Presence of very old and large trees

Presence of large, standing dead trees

Increased amounts of dead stumps and coarse woody debris

Pit and mound topography and presence of canopy gaps

Several of these characteristics are measured in the Forest Inventory and Analysis database

and can be used to identify forests with old growth characteristics. In this report, we present

one methodology for estimating old growth acreage across several inventories.

Division of Forestry WI Dept of Natural Resources 8/2014

Advanced Stand Age

Wisconsin’s forests are aging as almost half of all

timberland is over 60 years of age (Figure 1). The

amount of very old forest (over 120 years) is far less than

what it was in 1983, but has increased 60% in the last

decade.

In 1983, over 4% of timberland was at least 120 years of

age, and 80% of this was in the oak / hickory or maple /

beech / birch forest types (Figure 2). Thirty years later, in

2013, only 1.2% of timberland is this old and less than

50% is in either oak / hickory or maple / beech / birch

type.

Forest Inventory and Analysis (FIA) approximates stand

age by weighting the cored age of several canopy trees of

differing sizes by the proportion of that size class in the

canopy. This procedure may underestimate the age of

very old stands that have trees in many size classes.

In this analysis, we will see that many stands with old

growth characteristics do not have an advanced stand

age in the FIA inventory and many stands with advanced

ages do not have typical features of old growth.

Figure 1. Area of timberland by stand age class (Forest Inventory and Analysis).

Figure 2. Acreage of timberland over 120 years old by forest type group (forest Inventory and Analysis).

-

1

2

3

4

5

0-20 21-40 41-60 61-80 81-100 101-120 121+

Mill

ion

acr

es

Stand age class (yrs)

Area of timberland by stand age class 1983 1996 2004 2013

0

50

100

150

200

250

300

350

Oak / hickory White / red /jack pine

Maple / beech /birch

Spruce / fir Elm / ash /cottonwood

Tho

usa

nd

acr

es

Area in timberland over 120 yrs of age 1983 1996 2004 2013

As a forest ages, large trees die and fall over. They

open canopy gaps for saplings and poles to fill in and

the stand becomes a mix of trees of various sizes and

ages creating a layered canopy.

In the FIA database, tree ages are not measured but

tree diameters are and in general correlate well with

tree age. One measure of the evenness of distribution

of tree diameters is the Shannon’s index of diversity*.

The index increases when the number of trees in each

diameter class up to 21+ inches is more evenly

distributed. As stands age, the distribution becomes

flatter and the value of the diversity index increases

(Figure 3).

As mentioned, the diversity index increases with age

(Figure 4). Between 1996 and 2013, however, the

average value of the index decreased in all age classes.

The forest types with the highest average diversity

index are maple/beech/birch, oak/hickory and white

/red/jack pine. These types have higher numbers of

large diameter trees in old stands.

*For an explanation see: http://en.wikipedia.org/wiki/Diversity_index

0

50

100

150

200

5-6.9 7-8.9 9-10.9 11-12.9 13-14.9 15-16.9 17-18.9 19-20.9 21.0+

tre

es

pe

r a

cre

Daimeter class (in)

Diameter distribution and diversity index: pine forest type

0-40 yrs (Index: 1.23)

41-80 yrs (Index: 1.85)

81-120 yrs (Index: 2.05)

>120 yr (Index: 2.11)

Figure 3. The relationship between diameter distribution and diversity index (Forest Inventory and Analysis, 2013).

Figure 4. Average value of Shannon’s index of diversity by stand age, 1996 and 2013 (Forest Inventory and Analysis).

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0.3

0.5

0.8

1.0

1.3

1.5

0-20 yrs 21-40 yrs 41-60 yrs 61-80 yrs 81-100 yrs >100 yrs

Average diversity of canopy

1996

2013

Diversity of tree sizes from sapling to large sawtimber

Large and very old trees not only provide structural

diversity and a layered canopy but also genetic

diversity. Trees that have survived challenges from

abiotic forces, disease and insects over decades may

harbor important genes for survival.

The number of large sawtimber trees has increased

steadily since 1996, 50% for trees 17 to 20.9 inches

in diameter and 23% for trees 21 inches and greater

(Figure 5).

The density of trees (trees per acre) over 21 inches

in diameter increases significantly with stand age

(Figure 6).

The density of these large trees in stands younger

than 80 years is very low. Over 50% of all large

trees are in younger stands (<80 yrs) but at a very

low density. The density of large trees is 8 times

higher in stands over 120 years of age compared to

forests younger than 80 years old.

Presence of very old and large trees

sawtimber

0

10

20

30

40

50

White / red /jack pine

Oak /hickory

Maple /beech /birch

Elm / ash /cottonwood

Aspen /birch

Spruce / fir All types

Density of trees over 21 inches dbh by stand age

0-80 yrs 81-100 yrs 101-120 yrs >120 yrs

23 27 32 35

12 14

16 19 18

16

20 22

0

10

20

30

40

50

60

70

80

1996 2004 2009 2013

Mill

ion

tre

es

Number of large trees by diameter class

21.0+ inches

19.0-20.9 inches

17.0-18.9 inches

Figure 5. Trends in the number of trees greater than 17 inches (Forest Inventory and Analysis).

Figure 6. The density of large trees (over 21 inches dbh) by forest type group (Forest Inventory and Analysis).

Presence of large standing dead trees

Large standing dead trees or snags provide

vital nesting, foraging and denning sites for

many species of forest birds and mammals.

The density of large standing dead trees (over

17 inches dbh) increases dramatically after a

stand age of 100 years (Figure 7). Snag

density decreased between 1996 and 2013 for

stands less than 120 years of age.

The highest density of large standing dead

trees occurs on the white / red / jack pine

types which also has the highest density of

large living trees.

The major species of large snags in the

database were red oaks and eastern white

pine.

0.0

1.0

2.0

3.0

4.0

Maple / beech /birch group

Oak / hickorygroup

White / red /jack pine group

All types

0.4

1.7 2.7

1.6 0.4

0.7

0.7

0.6

Tre

es p

er a

cre

Density of standing dead trees in stands over 120 yrs old

21+ inches

17-21 inches

Figure 7. The density of large standing dead trees (Forest Inventory and Analysis, 2013).

Figure 8. The density of large standing dead trees in stands over 120 yrs old by forest type group (Forest Inventory and

Analysis, 2013).

0.7

1.0

1.7 1.9

0.5 0.8

1.0

2.0

0.00

0.50

1.00

1.50

2.00

2.50

0-20 21-40 41-60 61-80 81-100 101-120 >120

Tre

es p

er a

cre

Stand age (yrs)

Density of standing dead trees over 17 inches

1996

2013

.

Without intervention as stands become older they

accumulate greater amounts of carbon in non-living

material such as coarse woody debris (CWD),

standing dead trees, stumps and litter. These

components are a major contributor to old growth

ecosystems not only serving as a reservoir of stored

carbon but also supporting a diversity of species.

Carbon in dead material accumulates steadily with

age and then levels off after about stand age 140

due to a decrease in litter density in older stands

(Figure 9). Carbon, however, continues to

accumulate in stumps, coarse woody debris and

standing dead trees past 180 years (sampling error

is extremely high as there are only five stands in the

database older than 180 years).

The forest type group which has the greatest

density of carbon is spruce / fir due to the large

amount of litter (Figure 10). The white / red / jack

pine type has the highest density of carbon in

coarse woody debris and stumps.

Increased amounts of dead stumps and coarse woody debris

0

5

10

15

20

25

30

Spruce / fir Maple /beech /birch

White / red /jack pine

Oak /hickory

Elm / ash /cottonwood

All foresttypes

Sho

rt t

on

s p

er a

cre

Carbon by component in stands over 120 yrs

Litter

Standing dead

CWD

0

5

10

15

20

0 - 20 21 -40

41 -60

61 -80

81 -100

101 -120

121 -140

141 -160

161 -180

181+

sho

rt t

on

s p

er

acre

Stand age class (yrs)

Carbon density in dead wood and litter

Litter

Standing dead trees

Stumps & CWD

Figure 10. The density of carbon by forest type in stands over 120 years of age (Forest Inventory and Analysis, 2013).

Figure 9. The density of carbon in coarse woody debris, stumps and litter (Forest Inventory and Analysis, 2013).

An estimation of “old growth” acres in Wisconsin

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10

20

30

40

50

60

70

80

90

1996 2004 2013

Tho

usa

nd

acr

es

Forested acres meeting old growth criteria

White / red / jack pine

Oak / hickory

Maple / beech / birch

Elm / ash / cottonwood

* Frelich, Lee and Reich, Peter. 1996. Eastern Old Growth Forests: Prospects for Rediscovery and Recovery. Island Press. Chapter 11 pg 24.

Figure 11. An estimation of forested acreage meeting old growth criteria.

is not solely a function of stand age. A given stand must meet several criteria such as the presence of many large trees (at least 21 inches

dbh) plus a few very large trees (at least 30 inches dbh), the presence of large standing dead trees (at least 17 inches dbh), a diversity of

canopy tree sizes ranging from sapling to large sawtimber (high diversity index) and a large amount of coarse woody debris.

In order to approximate the acreage of forest having these old growth characteristics, in this analysis we used the average value from the FIA

database for all stands over 120 years of age as a

minimum criterion for these five features. By summing

the acreage of stands which met four of the five

criteria, we were able to estimate the acreage in old

growth as follows: 60,330 acres in 1996, 60,811 in 2004

and 77,205 acres in 2013 (Figure 11). Interestingly, 40%

of old growth acreage is located in southern Wisconsin.

Whereas only 2% of all forest in the state is on Native

American land, 15% of old growth acreage is in

Menominee County, presumably on reservation land.

This is only an estimate based on undocumented

criteria but the estimate for 1996, 60,330 acres, is very

close to the approximation of 57,000 acres by Frelich

and Reich (1996*). Based on this analysis, old growth

forests, as opposed to old forests may actually have

increased since 1996. One of the reasons is the large

increase in trees over 17 inches (Figure 5).

In order to define old growth forests, stand age alone is not very helpful since many very old

stands have been harvested or disturbed multiple times. For this reason “old growth” status

6.6

4.4

0

3

6

9

Maple / beech / birch Oak / hickory White / red / jackpine

All types

Sho

rt t

on

s p

er a

cre

Carbon in stumps and coarse woody debris Old Growth Stands >120 yrs

5.5

1.9

0.0

2.0

4.0

6.0

8.0

Maple / beech / birch Oak / hickory White / red / jackpine

All types

Snag

s p

er a

cre

Dead standing trees over 17 inches Old Growth Stands >120 yrs

The charts on this page (Figure 12) show the difference between old stands (at least 120 years old in the FIA inventory) and “old growth”

as estimated in this analysis. The number of large trees is 2 ½ times higher on old growth. The number of very large trees is over five

times higher and the number of large snags is almost three times higher on old growth stands compared to stands which are over 120

years old. Many of these old growth stands are not listed as having an advanced stand age in the FIA inventory: almost 50% of “old

growth” stands have a designated stand age of less than 100 years.

1.5

1.2

0.0

0.3

0.6

0.9

1.2

1.5

1.8

Maple / beech /birch

Oak / hickory White / red / jackpine

All types

Canopy diversity

Old Growth Stands >120 yrs

-

10

20

30

40

50

9-12.9 13-16.9 17-20.9 21-24.9 25-29.9 >30 in

Tree

s p

er a

cre

Diameter class (in)

Number of trees per acre by diameter class Old Growth Stands >120 yrs

Old growth compared to old stands

Figure 12. Diameter distribution (top left), canopy diversity (top right), density of standing dead trees (bottom left) and carbon density in CWD (bottom right) on estimated old growth vs. stands which

are over 120 years of age in the FIA database.