APn81. Northern Poor Conifer Swamp

Similar documents
Draft North Lake Muskeg ERA Plan

Patterned Peatland. Summary. Protection Not listed in New York State, not listed federally. Rarity G3G4, S1

Carp River Complex ERA Plan

Prison Camp Muskeg ERA Plan

Figure 2. Key to the forested vegetation types of Nova Scotia

Sage Lake Cedar Swamp Ecological Reference Area (ERA)

Shingleton Patterned Fen ERA Plan

Cedar Forest Group. Eastern white cedar Balsam fir / Stair-step moss

Ecosystem Unit Analysis

Iron County Land and Water Conservation Department

Appendix 2: Individual RoW Descriptions

A Natural Features Assessment for the Shingleton Forest Management Unit

Transitioning black ash wetlands to an EAB infested future

Red Pine Management Guide A handbook to red pine management in the North Central Region

Review of Natural Environment Existing Conditions, Johnston Road Study Area

PROJECT 4 ALL-SEASON ROAD ENVIRONMENTAL IMPACT STATEMENT. Appendix 9-3 Botanical and Vegetation Resource Survey Field Report

North Black Reroute Habitat Assessment for Cardamine pratensis

d. Estimated potential indirect impacts to ombrotrophic bog communities due to proposed mine dewatering should not be rated as no effect.

Vegetation Condition and Water Quality in Great Lakes Coastal Wetlands

TESTS FOR HYDROPHYTIC VEGETATION 1. RAPID TEST 2. 50:20 DOMINANCE TEST 3. PREVALENCE TEST

Wet Coniferous Forest Group

ERA Management Plan-Walton Marsh Pine Barrens

Shrubs & Trees for Wildlife

Appendix F. Botanical Survey Report

Wet Forest System PPA/TAP-WF1. photo by R.P. Dana, MN DNR. Skull Lake Wildlife Management Area, Kittson County, MN

Characterization of vegetation growth after harvest in forested catchments to support coupled SWAT/ALMANAC modelling.

Using Ecological Site Concepts to Assess Restoration Success: A Case Study on MLRA 98 Mucky Depressions

Headwaters Site. An Evaluation of the Ecological Significance of the

Forest Growth after Fire and Clearing for Seismic Lines in the Upland Habitats of the Gwich in Settlement Area

Bin Xu NSERC Industrial Research Chair for Colleges, Peatland Restoration NAIT

A guide to translate northwestern Ontario ecosites into Ecosites of Ontario

Climate Change Vulnerability Assessment for Bog Relict in Wisconsin

Each point here will be imaged with airborne LiDAR and visited by crews to measure trees and their condition.

Mesic Hardwood Forest System

Squaw Bay Wooded Dune and Swale Complex

LANDFIRE Biophysical Setting Model

HABITATS AT CEDAR CREEK NATURAL HISTORY AREA

Open File Report Ext

Dwarf Shrub Bog. Summary. Protection Not listed in New York State, not listed federally. Rarity G4, S3

Old Field Forest Group

8) Which of the following species is best adapted to poorly drained sites? a) Bur oak b) Eastern red cedar c) Black ash d) Yellow birch

Initial results of leather-leaf (Chamaedaphne calyculata) and speckled alder (Alnus rugosa) cutting regime on plant biodiversity on Cranberry Bog

Please see the pages below for full description of each tree!

Update on the National Wetland Plant List

Spruce Pine Forest Group

Balsam Willow. Summary. Protection Rare in New York State, not listed federally.

MANAGED FOREST LANDS STEWARDSHIP FORESTRY PLAN

38. VEGETATION Introduction. Vegetation Cook Inlet Drainages

6.0 ASSESSMENT OF POTENTIAL EFFECTS ON VEGETATION AND WETLANDS

The Crandon Mine Experience

NorthMet Project Baseline Wetland Type Evaluation

Soil Nutrient Regime. Soil Moisture Regime. BWBSwk EDATOPIC GRID. Poor B. Rich D. Medium C. Xeric 1. Subxeric 2. Submesic 3. Mesic 4.

2015 Wisconsin Envirothon KEY Forestry Exam

Silviculture Art & science of establishing & tending trees & forests

Pitch Pine-Blueberry Peat Swamp

Mixedwood Forest Group

Restoring The North Shore Forest. Welcome!

Appendix B: Site Index Curves for Selected Tree Species. Interpreting Site Index Curves

THERMOKARST VEGETATION IN LOWLAND BIRCH FORESTS ON THE TANANA FLATS, INTERIOR ALASKA, U.S.A.

RATES OF TREE GROWTH AND FOREST SUCCESSION IN THE ANCHORAGE-MATANUSKA VALLEY AREA, ALASKA*

Temperature of upland and peatland soils in a north central Minnesota forest

FOREST COMPOSITION AND STRUCTURE

Coastal Forest Group

Background: Environmental Context: Exposure and Effects: Risk Management Implications:

Ecological Information

G3.Db Picea mire woodland

Overall Category & Criteria. Red List Category Red List Criteria Red List Category Red List Criteria

Hunting Club, Lake County, and Wolf Land Parcels Fall 2010 Wildlife and Wetland Assessment Final Report

Tables and Figures for Silvicultural Interpretation: MHn44

environmental excellence and sustainability C reating Biodiversity in the Oil Sands A Case Study Chris Fordham December 5, 2012

Highland Forest Group

Vermont Department of Forest, Parks and Recreation And UVM Extension

Understory plant diversity and composition in boreal mixedwood forests

Spruce Hemlock Forest Group

Upstream Oil and Gas Spills to Boreal Wetland Environments Best Practices and Evolving Tools

Appendix A. Wetland Determination Forms and Site Photography

Heron Glen Wetland Buffer Enhancement Project. Progress Report. November 15, 2005

Biol 697, Laboratory 1. Relevé sampling in the Bicycle Bumps forest, 2017

The management priority in this area is to continue to provide these multiple benefits while minimizing user conflicts.

2008 NorthMet Mine/Forest Service Additional Parcel Summer Wildlife and Wetland Assessment Final Report

Climate Change Vulnerability Assessment for Poor Fen in Wisconsin

New Forest Genetic Resource Management and Conservation Standards: How they Apply to the Reclamation Business

Appendix 1: List of TRCA Vegetation Communities (2014 scores)

OTTER PONDS DEMONSTRATION FOREST FOREST ECOSYSTEM CLASSIFICATION. Forestry Division, Truro

RIPARIAN FOREST BUFFER

Trace Elements: 2011 Agency Meeting

Determining the Average Width of the Riparian Zone in the Cassels-Rabbit Lakes Area of Temagami, Ontario using Understory Indicator Species

esota Department ttural Resources Vegetation Analysis of the Red Lake Peatlands by Remote Sensing Methods QK 9 :38.M3 H 3 3><

2.0 Plant /Tree Processes in the Boreal Forest

Forest Technical Note

Tables and Figures for Silvicultural Interpretation: FDn43

Assessment of Contaminated Soil in the Canadian Boreal Forest using Standardized Toxicity tests. Mary Moody, SRC Rick Scroggins, Environment Canada

Avian Habitat Considerations in Northern Hardwoods Silviculture

Great Lakes-St. Lawrence Ecosite Fact sheets (third draft)

Case Study of Bog Change on Long Lake in Aitkin County, Minnesota USA

Pine Oak Hemlock in the Northeast

Potentially Trackable Small Patch Communities of the Maybelle Dunes, Richardson River Dunes and Marguerite Crag and Tail Wildland Parks

Lab 8. Photointerpretation of (Ontario Boreal) Tree Species

Intolerant Hardwood Forest Group

Vegetation Communities of Maybelle River Wildland Provincial Park

Transcription:

Northern Poor Conifer Swamp Conifer-dominated peatlands with sparse canopy of stunted trees. Understory is depauperate and dominated by ericaceous shrubs, fine-leaved graminoids, and low Sphagnum hummocks. Minerotrophic plant species are present. Vegetation Structure & Composition Description is based on summary of vascular plant data from 60 plots (relevés) and bryophyte data from 5 plots. Moss layer is dominated mostly by Sphagnum species, which form nearly continuous carpets consisting of low hummocks of S. magellanicum and extensive lawns of S. angustifolium. Hollows are dominated by brown mosses such as Calliergon cordifolium. Forb cover is sparse (< 25%) and typically includes three-leaved false Solomon s seal (Smilacina trifolia), with stemless lady s slipper (Cypripedium acaule), Indian pipe (Monotropa uniflora), and pitcher plant (Sarracenia purpurea) sometimes present. Graminoid cover is variable. Fine-leaved graminoids such as three-fruited bog sedge (Carex trisperma) are important; cottongrasses, particularly tussock cottongrass (Eriophorum vaginatum), are commonly present. Low-shrub layer is dominated by ericaceous shrubs, typically with 5 25% cover; Labrador tea (Ledum groenlandicum) and leatherleaf (Chamaedaphne calyculata) are abundant. Small cranberry (Vaccinium oxycoccos) is frequent but less abundant. Tall-shrub layer is sparse (< 25% cover), with minerotrophic indicators such as bog birch (Betula pumila) and speckled alder (Alnus incana) occasionally present. Understory trees typically include scattered black spruce with tamarack frequent. Canopy is patchy (25 50% cover) and dominated by stunted (< 33ft [10m] tall) black spruce or tamarack. Notes: Species diversity is relatively low, but minerotrophic indicators are typical, including the moss Calliergon stramineum, which is present among Sphagnum species on hummocks (see Appendix D for an explanation of minerotrophic versus nonminerotrophic species). Landscape Setting & Soils APn81 occurs in peat-filled basins on nutrient-poor outwash plains, on bedrockdominated terrain, on noncalcareous till, and on other landforms in basins with small watersheds where surface water inputs are minimal. In these basins, APn81 is often adjacent to open poor fens or rich swamps at the margins of bogs. APn81 also occurs in large peatlands on glacial lake plains in areas adjacent to rich fen water tracks or between forested bogs and uplands. In most settings soils are moderately deep to very deep peat (> 20in [50cm]), although they can be shallower in bedrock-dominated landscapes or on nutrient-poor sand plains. The upper layer of soil is poorly decomposed (fibric) peat formed from Sphagnum and may be underlain by more decomposed peat of variable origin. The surface water is acidic (ph = 4.2 5.5) and low in minerals, particularly Ca ++. Water-table fluctuations are less variable than in forested bogs (i.e., APn80) but more variable than in poor fens (i.e., APn91). Natural History APn81 occurs primarily in the Laurentian Mixed Forest Province, where climate and poor soil drainage result in active peat accumulation. The most extensive examples are in the Glacial Lake Agassiz basin in the MOP and in the basins of Glacial Lakes Aitkin 225 ACID PEATLAND SYSTEM Northern Floristic Region

and Upham in the MDL. The distribution of APn81 is similar to that of Northern Spruce Bogs (APn80), but because it can develop in conditions that are less continuously saturated and less nutrient poor, its range extends farther west into the Tallgrass Aspen Parklands Province and south beyond the acid till of the Superior and Koochiching glacial lobes into the MIM. In general, APn81 develops in peatlands where the peat surface is becoming isolated from mineral-rich groundwater because of buildup of peat and invasion by Sphagnum, which leads to increasingly acidic conditions with the water table typically below the peat surface. APn81 is transitional in water chemistry between bogs and rich black spruce swamps. The community may develop from rich black spruce swamps in settings where buildup of Sphagnum-dominated substrates creates conditions increasingly unfavorable to minerotrophic species. APn81 may also develop from poor fens where the formation of Sphagnum hummocks creates sufficiently aerated conditions for the establishment and growth of black spruce and tamarack. Although catastrophic fires can occur in poor conifer swamps, they are not common, because the community is present in wet landscapes or in areas where the upland forests are mostly hardwoods rather than fire-prone conifers. An analysis of Public Land Survey (PLS) records indicates that the historic rotation of catastrophic fires in APn81 was about 570 years. If fires are particularly intense, they can release sufficient quantities of nutrients from peat and vegetation to convert APn81 to a rich swamp community. Moderate surface fires and light windthrow were somewhat more common disturbances in APn81, occurring about every 90 years. The ability of black spruce and tamarack to send up new stems, or layer, from branches buried by peat has been interpreted as an adaptive trait for surviving windthrow. There is, however, little direct evidence that windthrow has a significant impact on poor swamp forests. The PLS records suggest the historic rotation of catastrophic windthrow in APn81 was about 500 years. Trees in APn81 are somewhat susceptible to windthrow because of structurally weak peat soils and shallow root systems, but this seems to be offset by short height (< 30ft [10m]), sparse crowns, root grafting, and branch layering. Similar Native Plant Community Classes APn80 Northern Spruce Bog APn80 is a Sphagnum-dominated peatland community with stunted black spruce trees and can appear similar to APn81. APn80 differs from APn81 by being isolated from mineral-rich groundwater, with surface water ph usually < 4.2. As a result, the vegetation in APn80 is composed mainly of bog species; minerotrophic species are absent, and most hollows are covered by Sphagnum angustifolium carpets. In APn81, surface water ph is usually > 4.2, minerotrophic species such as bog birch, speckled alder, creeping sedge (Carex chordorrhiza), and bluejoint (Calamagrostis canadensis) are present, and Sphagnum carpets are restricted to low hummocks and areas around tree bases. Brown mosses, such as Calliergon cordifolium, are abundant in hollows. APn81 APn80 Speckled alder (Alnus incana) 27 - Bluejoint (Calamagrostis canadensis) 23 - Spinulose shield fern (Dryopteris carthusiana) 17 - Buckbean (Menyanthes trifoliata) 16 - Lake sedge (Carex lacustris) 16 - Bog birch (Betula pumila) 44 - Creeping sedge (Carex chordorrhiza) 33 - Balsam fir (U) 17 - APn91 Northern Poor Fen APn91 often has a sparse canopy of stunted black spruce or tamarack and can appear similar to APn81. APn91 differs from APn81 by usually having tree canopy cover < 25%, by the presence of light-requiring species such as bog wiregrass sedge (Carex oligosperma), and by having hollows dominated by semiaquatic Sphagnum species, such as S. subsecundum, S. papillosum, or S. majus. APn81 usually has tree canopy cover of 25 50% and is more likely to have shade-tolerant species such as creeping snowberry (Gaultheria hispidula), stemless lady s slipper, and three-fruited bog sedge 226 APn80 Indicator Species There are no species restricted to APn80 relative to APn81. Instead, APn80 is distinguished by being composed of a restricted set of 25 vascular plant species tolerant of ombrotrophic conditions (see Appendix D). Significant presence of species other than these 25 species usually indicates the plant community is not a bog. If minerotrophic species are present but are limited to just a few individuals that are unlikely to persist at the site, the community would still be classified as APn80 rather than APn81.

(Carex trisperma). APn81 is also more likely to have hollows dominated by semiaquatic brown mosses such as Calliergon cordifolium. FPn62 Northern Rich Spruce Swamp (Basin) FPn62 is similar to APn81 but is richer in minerals and has denser canopy cover with taller trees. FPn62 has higher species diversity (usually 23 species/400m 2 ) and is more likely to have rich forest indicators such as white cedar, twinflower (Linnaea borealis), and bluebead lily (Clintonia borealis). APn81 has lower species diversity (usually < 23 species/400m 2 ) and is more likely to have shade-intolerant species, including bog rosemary (Andromeda glaucophylla), pitcher plant, and tussock cottongrass (Eriophorum vaginatum). APn81 APn91 Indian pipe (Monotropa uniflora) 33 - Lingonberry (Vaccinium vitis-idaea) 11 - Stemless lady s slipper (Cypripedium acaule) 39 1 Northern red oak (U) 27 1 Spinulose shield fern (Dryopteris carthusiana) 17 1 Creeping snowberry (Gaultheria hispidula) 38 2 Three-fruited bog sedge (Carex trisperma) 80 7 Velvet-leaved or lowbush blueberry* 47 4 *Velvet-leaved or lowbush blueberry (Vaccinium myrtilloides or V. angustifolium) APn81 FPn62 Creeping sedge (Carex chordorrhiza) 33 - Pitcher plant (Sarracenia purpurea) 31 - Tawny cottongrass (Eriophorum virginicum) 20 - Buckbean (Menyanthes trifoliata) 16 - Bog wiregrass sedge (Carex oligosperma) 14 - Bog rosemary (Andromeda glaucophylla) 50 3 Tussock cottongrass (Eriophorum vaginatum) 34 3 Round-leaved sundew (Drosera rotundifolia) 19 3 APn91 Indicator Species FPn62 Indicator Species APn81 APn91 White beak rush (Rhynchospora alba) - 32 Beaked sedge (Carex utriculata) - 17 Spatulate-leaved sundew (Drosera intermedia) - 14 Scheuchzeria (Scheuchzeria palustris) 6 51 Fen wiregrass sedge (Carex lasiocarpa) 8 49 Candle-lantern sedge (Carex limosa) 9 44 Bog wiregrass sedge (Carex oligosperma) 14 42 Round-leaved sundew (Drosera rotundifolia) 19 52 APn81 FPn62 Bluebead lily (Clintonia borealis) - 48 Fly honeysuckle (Lonicera canadensis) - 23 Mountain ashes (U) 2 61 Dwarf raspberry (Rubus pubescens) 2 55 Twinflower (Linnaea borealis) 2 52 Red raspberry (Rubus idaeus) 2 32 White cedar (U) 2 26 Goldthread (Coptis trifolia) 5 55 FPn71 Northern Rich Spruce Swamp (Water Track) FPn71 is similar to APn81 but is richer in minerals and has denser canopy cover with taller trees. As a result, FPn71 has higher species diversity (usually > 23 species/400m 2 ) and is more likely to have rich forest indicators such as white cedar, red-osier dogwood (Cornus sericea), sweet-scented bedstraw (Galium triflorum), and naked miterwort (Mitella nuda). APn81 has lower species diversity (usually < 23 species/400m 2 ) and is more likely to have shade-intolerant species such as tussock cottongrass and creeping sedge (Carex chordorrhiza). APn81 FPn71 Tussock cottongrass (Eriophorum vaginatum) 34 - Northern red oak (U) 27 - Bog wiregrass sedge (Carex oligosperma) 14 - Few-fruited sedge (Carex pauciflora) 14 - Creeping sedge (Carex chordorrhiza) 33 7 Paper birch (U) 30 7 Bluejoint (Calamagrostis canadensis) 23 7 Three-fruited bog sedge (Carex trisperma) 80 29 ACID PEATLAND SYSTEM Northern Floristic Region FPn71 Indicator Species APn81 FPn71 Dwarf alder (Rhamnus alnifolia) - 79 Red-osier dogwood (Cornus sericea) - 71 Sweet-scented bedstraw (Galium triflorum) - 64 Naked miterwort (Mitella nuda) - 57 Marsh bellflower (Campanula aparinoides) - 50 Labrador bedstraw (Galium labradoricum) - 43 Touch-me-not (Impatiens spp.) - 36 White cedar (C,U) 2 50 Native Plant Community Types in Class APn81a Poor Black Spruce Swamp Tree canopy has > 50% cover, typically dominated by black spruce, occasionally with tamarack (which rarely may be codominant). Paper birch is also occasionally present in the canopy. Tall shrubs are usually absent or infrequent. APn81a occurs in slightly drier areas than APn81b and as a result has a denser tree canopy and greater presence of shade-tolerant species in the understory, including Indian pipe, creeping snowberry, ferns (especially Dryopteris spp.), lingonberry (Vaccinium vitis-idaea), soft-leaved sedge (Carex disperma), clubmosses and groundpines (Lycopodium spp.), bunchberry (Cornus canadensis), juneberries (Amelanchier spp.), and balsam fir. Description is based on summary of vegetation data from 21 plots. 227

APn81b Poor Tamarack - Black Spruce Swamp Tree canopy has 25 50% cover and is dominated by black spruce with occasional tamarack, or by tamarack with black spruce. APn81b develops in slightly wetter areas than APn81a. Because of this, APn81b has a more open canopy and more light-demanding species in the understory, including bog rosemary, creeping sedge (Carex chordorrhiza), bog birch, bog wiregrass sedge (C. oligosperma), lake sedge (C. lacustris), few-fruited sedge (C. pauciflora), bog willow (Salix pedicellaris), buckbean (Menyanthes trifoliata), and bog laurel (Kalmia polifolia). APn81b is divided into two subtypes, based on differences in the abundance of black spruce and tamarack in the tree canopy. APn81b1 Black Spruce Subtype Tree canopy is dominated by black spruce, occasionally with some tamarack. Understory species that help to differentiate APn81b1 from APn81b2 are round-leaved sundew (Drosera rotundifolia), few-fruited sedge (Carex pauciflora), and buckbean. Description is based on summary of vegetation data from 13 plots. APn81b2 Tamarack Subtype Tree canopy is dominated by tamarack, typically with black spruce, and is slightly more open than the canopy of APn81b1. As a result, bog rosemary and leatherleaf are more abundant in the understory of APn81b2. The presence of lowbush blueberry (Vaccinium angustifolium) in the understory also helps to distinguish APn81b2. Description is based on summary of vegetation data from 16 plots. Hubbard County, MN photo by T.J. Whitfeld MN DNR 228

APn81 Northern Poor Conifer Swamp Species Frequency & Cover Forbs, Ferns & Fern Allies Three-leaved false Solomon s seal (Smilacina trifolia) 85 Stemless lady s slipper (Cypripedium acaule) 40 Indian pipe (Monotropa uniflora) 35 Pitcher plant (Sarracenia purpurea) 32 Round-leaved sundew (Drosera rotundifolia) 20 Spinulose shield fern (Dryopteris carthusiana) 18 Buckbean (Menyanthes trifoliata) 17 Northern blue flag (Iris versicolor) 13 Tufted loosestrife (Lysimachia thyrsiflora) 13 Bunchberry (Cornus canadensis) 10 Bristly clubmoss (Lycopodium annotinum) 10 Marsh cinquefoil (Potentilla palustris) 10 Grasses & Sedges Three-fruited bog sedge (Carex trisperma) 83 Poor sedge (Carex paupercula) 37 Tussock cottongrass (Eriophorum vaginatum) 37 Creeping sedge (Carex chordorrhiza) 33 Bluejoint (Calamagrostis canadensis) 25 Tawny cottongrass (Eriophorum virginicum) 22 Lake sedge (Carex lacustris) 17 Bog wiregrass sedge (Carex oligosperma) 15 Few-fruited sedge (Carex pauciflora) 13 Soft-leaved sedge (Carex disperma) 10 freq% cover freq% cover Low shrubs Labrador tea (Ledum groenlandicum) 93 Leatherleaf (Chamaedaphne calyculata) 83 Small cranberry (Vaccinium oxycoccos) 80 Bog laurel (Kalmia polifolia) 60 Bog rosemary (Andromeda glaucophylla) 53 Velvet-leaved blueberry (Vaccinium myrtilloides) 48 Creeping snowberry (Gaultheria hispidula) 38 Lowbush blueberry (Vaccinium angustifolium) 38 Lingonberry (Vaccinium vitis-idaea) 12 Tall Shrubs Bog birch (Betula pumila) 47 Speckled alder (Alnus incana) 27 Bog willow (Salix pedicellaris) 13 Balsam willow (Salix pyrifolia) 10 Trees Canopy Understory freq% cover freq% cover Black spruce 93 92 Tamarack 73 65 Paper birch 15 32 White pine 8 22 Northern red oak - - 27 Red maple - - 23 Balsam fir - - 18 229