GREATER FUNDY ECOSYSTEM RESEARCH PROJECT

UNB Faculty of Forestry and Environmental Management

State of the Greater Fundy Ecosystem


Effects of Forestry Practices on Species Composition and Taxonomic and Structural Diversity

Mark R. Roberts and Ian R. Methven
Faculty of Forestry and Environmental Management
University of New Brunswick
Fredericton, N.B. E3B 6C2


This study was initiated in 1992 with the goal of determining the effects of forest harvesting on plant species composition, species diversity and stand structural diversity. This summary reports on the species composition and taxonomic diversity portion of the study.

METHODS

A chronosequence of artificially regenerated clearcuts (plantations) and naturally regenerated clearcuts were compared to mature natural stands which have been affected by past Spruce Budworm outbreaks. Three plantations in each of three age classes (5-7, 10-12 and 14-16 years; 9 plantations total) and two naturally regenerated clearcuts (7 and 38 years) were selected in the Fundy Model Forest adjacent to Fundy National Park. Three natural stands with maximum tree ages of approximately 90 years were selected within the Park. All stands were dominated by Spruce and Fir on imperfectly to moderately-well drained sites with vegetation type (VT) 2, 3, 6, or 7 (Note: 2&3=low fertility sites, 6&7=moderate fertility sites). Species composition and diversity of all vascular plants and many common bryophytes in the herbaceous layer (<1 m tall) were assessed in all stands based on percent cover of each species.

RESULTS

Plant composition rather than diversity was affected most by disturbances. Fifty-five species occurred in the plantations that were not found in the mature natural stands; many of these were invader species which take advantage of disturbances (Table 1; Figure 1). Only six of the species found in mature natural stands were absent from the plantations, suggesting that species richness tends to increase in artificially regenerated stands compared to mature natural stands. However, species percent cover fluctuated widely between the natural stands and the plantations. A total of 20 species had lower abundance in the plantations (Figure 1). Along with the species that disappeared, these species should be the focus of biodiversity management efforts (Table 1).

Table 1. Species listed by type of response in plantations from local study

Species that decreased in plantations: (most abundant in natural stands)

Balsam Fir (Abies balsamea)
Wild Sarsaparilla (Aralia nudicaulis)
Liverwort sp. (Bazzania trilobata)
Smaller Enchanter's Nightshade (Circaea alpina)
Yellow Clintonia (Clintonia borealis )
Broom Moss (Dicranum scoparium )
Wood Fern (Dryopteris austriaca )
Fern (Dryopteris campyloptera)
Stair-step Moss (Hylocomium splendens)
Cinnamon Fern (Osmunda cinnamomea)
Interrupted Fern (Osmunda claytoniana)
Common Wood Sorrel (Oxalis montana)
Sphagnum spp.
Northern Beech Fern (Thelypteris phegopteris)
Starflower (Trientalis borealis)

Species not found in plantations:
(present in natural stands)

Striped Maple (Acer pensylvanicum)*
Aster sp. (Aster lanceolatus)
Yellow Birch (Betula alleghaniensis)*
Three-way Sedge (Dulichium arundinaceum)*
Indian Cucumber-root (Medeola virginiana)*
Raspberry sp. (Rubus alleghaniensis)*


* Found in only one stand.

Species that increased in
plantations:

(abundant in natural stands)

Three-fruited Sedge (Carex trisperma)
Bunchberry (Cornus canadensis)
Lichen spp.
Twinflower (Linnaea borealis)
Hair Cap Mosses (Polytrichum spp.)
Dwarf Raspberry (Rubus pubescens)
Wild Red Raspberry (Rubus strigosus)
Rough-stemmed Goldenrod (Solidago rugosa)

Table 1. (Continued)

Species that were found only in plantations:

Pearly Everlasting (Anaphalis margaritacea)
Bristly Sarsaparilla (Aralia hispida)
Swamp Aster (Aster puniceus)*
Aster (Aster x blakei)
Lady Fern (Athyrium filix-femina)*
Brome Grass (Bromus ciliatus)*
Sedge (Carex deflexa)*
Sedge (Carex scoparia)*
Sedge (Carex stipata)*
Leatherleaf (Chamaedaphne calyculata)
Red Osier (Cornus stolonifera)*
False Violet (Dalibarda repens)*
Northern Bush Honeysuckle (Diervilla lonicera)
Trailing Arbutus (Epigaea repens)*
Fireweed (Epilobium angustifolium)
Horsetail (Equisetum spp.)*
Spotted Joe-Pye Weed (Eupatorium maculatum)*
Rough Bedstraw (Galium asprellum)*
Rattlesnake Grass (Glyceria canadensis)

 


Hawkweed sp. (Hieracium caespitosum)
Canada St. Johnswort (Hypericum canadensis)*
Rush (Juncus brevicaudatus)
Soft Rush (Juncus effusus)
Path Rush (Juncus tenius)*
Sheep Laurel (Kalmia angustifolia)
Blue Lettuce (Lactuca biennis)
Wild Lettuce (Lactuca canadensis)*
Labrador-tea (Ledum groenlandicum)
Rush (Luzula parviflora)*
Running Clubmoss (Lycopodium clavatum)
Ground Pine (Lycopodium obscurum)
Water Horehound (Lycopus uniflorus)*
Naked Miterwort (Mitella nuda)*
Mnium spp.*
Sensitive Fern (Onoclea sensibilis)*
Fowl Meadow-grass (Poa palustris)
Fringed Black Bindweed (Polygonum cilinode)

 


Quaking Aspen (Populus tremuloides)
Rough Cinquefoil (Potentilla norvegica)*
Gall-of-the-Earth (Prenanthes trifoliata)*

Moss (Ptilium pulcherrimum)

Wild Gooseberry (Ribes hirtellum)*
Sheep Sorrel (Rumex acetosella)
Bebb Willow (Salix bebbiana)
Pussy Willow (Salix discolor)*
Balsam Willow (Salix pyrifolia)
Red-berried Elder (Sambucus racemosa)
Golden Ragwort (Senecio aureus)*
Swamp Ragwort (Senecio schweinitzianus)*
Tall Goldenrod (Solidago altissima)
Bog Goldenrod (Solidago uliginosa)
Meadowsweet (Spiraea latifolia)
King-of-the-Meadow (Thalictrum pubescens)*
Purple Trillium (Trillium erectum)*

* Species found only in one vegetation type 6 stand.

 

Figure 1.

 

There were no significant differences among the three age classes of plantations nor between the old plantations (14-16 years) and the natural stands in any species diversity index, including species richness, Simpson's index, Shannon-Wiener index, Shannon evenness, and Margalef's index (Table 2).

Site conditions had a greater effect on species richness and diversity than stand management. Plantations on slightly richer sites (VT 6, 7) had significantly higher species richness, Shannon and Margalef diversity indices than stands on poorer sites (VT 2, 3; Table 2). Therefore, site conditions should be carefully assessed in any diversity study. Also, harvesting may have different effects on species diversity depending on site conditions.

IMPLICATIONS FOR MANAGEMENT

Additional studies are currently under way to determine the life-history characteristics of species that control their response to harvesting disturbances. This information is needed to meet land management and conservation objectives that call for maintenance of species diversity.

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Information provided by:
Dr. Graham Forbes
Faculty of Forestry and Environmental Management at UNB
Last Update: May 7, 1998
This document: http://www.unb.ca/web/forestry/centers/cwru/soe/forpract.htm