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Abe's Run Wetland - Canaan Valley Institute

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Plant Communities of<br />

Abe’s <strong>Run</strong> <strong>Wetland</strong>,<br />

<strong>Canaan</strong> <strong>Valley</strong> State Park<br />

James Rentch<br />

Ronald Fortney<br />

James Anderson<br />

William Grafton


Abe’s <strong>Run</strong> <strong>Wetland</strong><br />

• 33 ha wetland<br />

• 148 ha watershed<br />

• Within <strong>Canaan</strong> <strong>Valley</strong> State Park<br />

• All major wetland vegetative-cover types<br />

present<br />

• Known location for several rare plants<br />

• Contact point for Greenbrier limestone


Study Objectives:<br />

• Vegetative sampling along 6 transects<br />

during July-August, 2002<br />

• Hydrologic sampling from 24 groundwater<br />

monitoring wells, April-August, 2002<br />

• Soil sampling along six vegetation<br />

transects<br />

• Overstory tree establishment trends<br />

• Changes in vegetation cover, 1945-2000


Transect Locations:<br />

To Lodge<br />

To WV<br />

Rt. 32


Vegetation Sampling Methods<br />

50 m<br />

5m<br />

20 m<br />

Herbs - Cover classes in 1 X 1 m subplots<br />

Shrubs - Stem counts in 5 X 5 m subplots<br />

Saplings [dbh1 m] - Complete tally by species<br />

Trees [dbh>10 cm] and small trees [2.5cm


Vegetation Data Analysis<br />

• Herbs IV = [Rel. Cov. + Rel. Freq.]/2<br />

• Shrubs/tall seedlings, Saplings = Stems ha -1<br />

• Small tree IV = [Rel. B.A. + Rel. Abund.]/2<br />

• Large tree IV = [Rel. B.A. + Rel. Abund.]/2


Changes in Post-logging Era<br />

Vegetation, 1945-2000<br />

• 1945 (BW, USDA) and 1997 (CIR, NAPP)<br />

aerial photographic coverages used<br />

• Watershed mapped by vegetative cover<br />

class [Cowardin et al. (1979), EPIC (1992)]<br />

• Evaluation of changes in vegetation cover<br />

class totals between 1945-2000, using<br />

Krushall-Wallis test [α=0.05]


Results: Vegetation Summary<br />

• 179 vascular plant species<br />

145 herbs [46 grasses and sedges]<br />

34 woody species [12 trees, 22 shrubs]<br />

23 exotic species<br />

5 species occurred in all 6 transects, 35<br />

species occurred once<br />

38 species at/near southernmost known<br />

station<br />

• 28 bryophytes<br />

24 mosses<br />

4 liverworts


8/1<br />

-10<br />

0<br />

10<br />

20<br />

30<br />

40<br />

Results: Depth to Groundwater<br />

4/11<br />

4/25<br />

5/9<br />

5/23<br />

6/6<br />

6/20<br />

7/4<br />

7/18<br />

T1 T2 T3<br />

T4 T5 T6<br />

Depth to water table (cm)


Results: Soil Horizon Depth<br />

Depth (cm)<br />

0<br />

20<br />

40<br />

60<br />

80<br />

100<br />

120<br />

Tran1 Tran2 Tran3 Tran4 Tran5 Tran6<br />

O A B C


Transect 1


Transect 1<br />

• Vegetation structure: PEM1<br />

• Dominant herbs: Carex atlantica, Leersia<br />

oryzoides, Scirpus tabernaemontani<br />

• Shrub: Rhododendron maximum<br />

– All: 800 stems ha -1<br />

• Small tree: Picea rubens<br />

– All: 306 trees ha -1 , 0.6 m 2 ha -1<br />

• Large tree: Betula allegheniensis, Tsuga<br />

canadensis<br />

– All: 285 trees ha -1 , 8.0 m 2 ha -1


Transect 2


Transect 2<br />

• Vegetation structure: PEM1<br />

• Dominant herbs: Euthamia graminifolia,<br />

Dennstaedtia punctilobula, Dryopteris intermedia,<br />

Osmunda cinnamomea<br />

• Shrub: Rubus allegheniensis<br />

– All: 371 stems ha -1<br />

• Small tree: Picea rubens<br />

– All: 139 trees ha -1 , 0.3 m 2 ha -1<br />

• Large tree: Betula allegheniensis, Tsuga.<br />

canadensis<br />

– All: 42 trees ha -1 , 3.0 m 2 ha - 1


Transect 3


Transect 4


Transect 6


Transects 3, 4, 6<br />

• Vegetation structure: PFO8<br />

• Dominant herbs: Caltha palustris, Senecio<br />

aureus, Glyceria striata [Geum rivale, Carex<br />

bromoides, Euphorbia purpurea, Polemonium<br />

van-bruntiae,Listera smallii, Equisetum<br />

sylvaticum, Saxifrage pensylvanica]<br />

• Shrub: Rhamnus alnifolia, Ilex verticillata,<br />

Alnus incana, Salix discolor, Viburnum<br />

lentago, [Viburnum opulus var. americana]<br />

– Average: 46,311 stems ha -1


Transects 3, 4, 6 -- continued<br />

• Small tree: Abies balsamea, Fraxinus nigra,<br />

Betula allegheniensis, Tsuga canadensis<br />

– Average: 267 trees ha -1 , 1.1 m 2 ha -1<br />

• Large trees: Betula allegheniensis, Fraxinus<br />

nigra, Tsuga canadensis, Abies balsamea<br />

– Average: 436 trees ha -1 , 11.0 m 2 ha -1


Transect 5


Transect 5<br />

• Vegetation structure: PFO8<br />

• Dominant herbs: Impatiens capensis, Carex<br />

bromoides, Carex gynandra, Glyceria striata<br />

[Geum rivale, Euphorbia purpurea, Polemonium<br />

van bruntiae]<br />

• Shrub: Ilex verticillata, Alnus incana<br />

– All: 12,880 stems ha -1<br />

• Small tree: A. balsamea, B. allegheniensis<br />

– All: 187 trees ha -1 , 0.9 m 2 ha -1<br />

• Large tree: F. nigra, A. balsamea, T. canadensis<br />

– All: 477 trees ha -1 , 11.0 m 2 ha -1


Establishment years for wetland<br />

overstory trees<br />

20<br />

balsam fir black ash hemlock red spruce<br />

15<br />

dbh (cm)<br />

10<br />

5<br />

0<br />

1750 1800 1850 1900 1950 2000<br />

establishment year (at dbh)


Changes in Vegetative Cover-Type<br />

1945-2000 [χ 2 = 1.06, p = 0.18]<br />

100<br />

16<br />

75<br />

1945<br />

12<br />

Area (ha)<br />

50<br />

2000<br />

8<br />

25<br />

4<br />

0<br />

UHU UFO1 UFO4 UFO8 USS1<br />

0<br />

PEM1 PFO4 PFO8 PSS1<br />

Uplands<br />

<strong>Wetland</strong>s


Changes in Vegetative Cover-Type in<br />

Watershed - 1945-2000<br />

• Watershed:<br />

– 30% decline in herbaceous cover<br />

– Increases in upland forested and scrubshrub<br />

areas<br />

• <strong>Wetland</strong>:<br />

– 50% decline in coniferous swamp forests<br />

– Increases in wet-graminoid and scrub-shrub<br />

• Impacts of beaver<br />

• Impacts of balsam wooly adelgid<br />

• Impacts of white-tailed deer


Summary: Abe’s <strong>Run</strong> wetland—an<br />

area of exceptional plant diversity<br />

• Characteristics common to <strong>Canaan</strong><br />

<strong>Valley</strong> as a whole<br />

• Non-continuous tree, small tree, and<br />

shrub vegetation structure<br />

• Variable hydrologic regime<br />

• Juxtaposition of acid and alkaline<br />

substrate<br />

• Relative degree of community stability<br />

and absence of destructive slash fires<br />

following logging

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