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ECOLOGICAL DEVELOPMENT
Forest Communities
The Black River Watershed supports four primary deciduous forest communities,
including beech-maple forests, mixed mesophytic forests, floodplain forests, and
Elm-Ash swamp forests. Deciduous forest communities contain trees that drop
their leaves in the late fall. Numerous shrubs and wildflowers grow below the
canopy of these forests, taking advantage of early spring sunlight before new
leaves emerge. The deciduous forests encountered throughout northern Ohio range
from northern New England to southern Florida and extend westward to the
prarielands in the middle of the country.
The forests encountered in the Black River Watershed result
from the adaptation of ecological communities to differing geological
conditions. As a result of glaciation, the watershed consists of lake plains to
the north (from Erie’s ancestral lakes) and till plains in the central part of
the watershed (where glacial till comprises the soils). The southern part of the
watershed, defined by glacial end moraine and the glaciated lower Appalachian
plateau, consists of more varied terrain. As the Black River carved its channels
through each of these geological zones, floodplain forest communities emerged
along its banks, remaining saturated for most of the year. The forests
encountered in the watershed reveal a great deal of information about the
varying geological conditions to which they have adapted.
Beech-maple forests dominate the old Lake Plains of Erie’s ancestral lakes and the flat
glacial till plains. These forests contain beech trees, with their smooth,
grayish bark. Unlike many deciduous trees, which completely shed their leaves,
beech trees often retain their brownish leaves throughout the winter. Sugar
maples, their leaves exploding into an intense spectrum of fiery yellow and
orange in the fall, also frequently grow in these forests. These maples produce
a sugary sap that can be boiled to make maple syrup. Other trees common to these
forests include red maple, black walnut, black cherry, and shagbark hickory.
Much of the northern part of the watershed consists of mixed mesophytic forests which
contain a diverse mixture of hardwood species. While beech and maple still grow
in these forests, they tend not to dominate. White and red oaks occur more
frequently in these northern woods. Although the American Chestnut tree
populated these forests as recently as 100 years ago, due to a deadly blight,
the Chestnut essentially disappeared from the Northern Ohio landscape during the
last century.
The trees occupying the floodplains that hug the banks of the Black River tend to
tolerate wetter conditions. Floodplain forest communities contain large numbers
of sycamore trees, easily identified by blotchy brown bark that falls off in
large flakes to reveal a bleached-white underbark. Cottonwoods, with their
quaking leaves and thickly-ridged, dark-gray bark, are also common. Other common
trees along these floodplains include silver and red maples, as well as Ohio
buckeye.
Elm-Ash swamp forests dominate wetland areas where standing
water submerges the land for at least a portion of the year. American Elm trees
once dominated the canopies of these forests. Today, due to Dutch Elm disease,
these trees usually die before reaching maturity. Black and white ashes grow in
abundance in these areas. Their wood is durable and has been used for everything
from furniture to early farm implements and baskets. Red and silver maples are
frequently encountered in these forests. Due to the drainage of wetlands, only
small remnants of these forests remain in the watershed.
[Back to the top]
Birds
Given its location in the upper portion of North America,
the Black River Watershed is host to over 200 species of birds. These birds have
adapted to the variety of habitats encountered in the watershed, including even
urban areas. Given the seasonal extremes of the area, many birds are here for
only a portion of the year and others are seen only during their fall or spring
migrations. The list below shows the seasons of habitation, including:
S= Summer
W= Winter
M= Migrant (parts of fall and spring)
The second column shows habitats to which these birds have
adapted, including:
F=Forest
W=Wetlands
M=Meadow, agricultural field, old field, shrubby areas
C= cities and urban areas
| Species |
Season |
Habitat |
| Pied-billed Grebe Podilymbus podiceps |
S |
W |
| Double-crested Cormorant Phalacrocorax auritus |
S |
W |
| Great Blue Heron Ardea herodias |
S |
W |
| Great Blue HeronArdea herodias |
SW |
W |
| Great EgretArdea alba |
S |
W |
Snowy Egret Egretta thula |
S |
W |
| Little Blue Heron Egretta caerulea |
S |
W |
| Cattle Egret Bubulcus ibis |
S |
W |
| Green Heron Butorides virescens |
S |
W |
| Black-crowned Night-Heron Nycticorax nycticorax |
S |
W |
| Yellow-crowned Night-Heron Nyctanassa violacea |
S |
W |
| Turkey Vulture Cathartes aura |
S |
WFMC |
| Snow Goose Chen caerulescens |
M |
|
| Canada Goose Branta canadensis |
SW |
W |
| Mute Swan Cygnus olor |
SW |
W |
| Tundra Swan Cygnus columbianus |
M |
|
| Wood Duck Aix sponsa |
S |
W |
| GadwallAnas strepera |
M |
|
| American Wigeon Anas americana |
M |
|
| American Black Duck Anas rubripes |
SW |
W |
| Mallard Anas platyrhynchos |
SW |
W |
| Blue-winged Teal Anas discors |
S |
W |
| Northern Shoveler Anas clypeata |
M |
|
| Northern Pintail Anas acuta |
M |
|
| Green-winged Teal Anas crecca |
M |
|
| Canvasback Aythya valisineria |
M |
|
| Redhead Aythya americana |
M |
|
| Ring-necked Duck Aythya collaris |
M |
|
| Greater Scaup Aythya marila |
M |
|
| Lesser Scaup Aythya affinis |
M |
|
| White-winged Scoter Melanitta fusca |
M |
|
| Oldsquaw Clangula hyemalis |
M |
|
| Bufflehead Bucephala albeola |
M |
|
| Common Goldeneye Bucephala clangula |
W |
W |
| Hooded Merganser Lophodytes cucullatus |
M |
|
| Common Merganser Mergus merganser |
W |
W |
| Red-breasted Merganser Mergus serrator |
W |
W |
| Ruddy Duck Oxyura jamaicensis |
M |
|
| Bald Eagle Haliaeetus leucocephalus |
SW |
W |
| Northern Harrier Circus cyaneus |
SW |
M |
| Sharp-shinned Hawk Accipiter striatus |
SW |
F |
| Cooper's Hawk Accipiter cooperii |
SW |
F |
| Northern Goshawk Accipiter gentilis |
M |
|
| Red-shouldered Hawk Buteo lineatus |
SW |
M |
| Broad-winged Hawk Buteo platypterus |
S |
F |
| Red-tailed Hawk Buteo jamaicensis |
SW |
FM |
| Rough-legged Hawk Buteo lagopus |
W |
M |
| American
Kestrel Falco sparverius |
SW |
M |
| Merlin
Falco columbarius |
M |
|
| Ring-necked
Pheasant Phasianus colchicus |
SW |
M |
| Wild
Turkey Meleagris gallopavo |
SW |
FM |
| Common
Moorhen Gallinula chloropus |
S |
W |
| American
Coot Fulica americana |
S |
W |
| Black-bellied
Plover Pluvialis squatarola |
M |
|
| Semipalmated
Plover Charadrius semipalmatus |
M |
|
| Piping
Plover Charadrius melodus |
M |
|
| Killdeer
Charadrius vociferus |
S |
MC |
| Greater
Yellowlegs Tringa melanoleuca |
M |
|
| Lesser
Yellowlegs Tringa flavipes |
M |
|
| Solitary
Sandpiper Tringa solitaria |
M |
|
| Spotted
Sandpiper Actitis macularia |
S |
W |
| Upland
Sandpiper Bartramia longicauda |
S |
M |
| Ruddy
Turnstone Arenaria interpres |
M |
|
| Red
Knot Calidris canutus |
M |
|
| Sanderling
Calidris alba |
M |
|
| Semipalmated
Sandpiper Calidris pusilla |
M |
|
| Least
Sandpiper Calidris minutilla |
M |
|
| White-rumped
Sandpiper Calidris fuscicollis |
M |
|
| Pectoral
Sandpiper Calidris melanotos |
M |
|
| Dunlin
Calidris alpina |
M |
|
| Short-billed
Dowitcher Limnodromus griseus |
M |
|
| Long-billed
Dowitcher Limnodromus scolopaceus |
M |
|
| Common
Snipe Gallinago gallinago |
M |
|
| American
Woodcock Scolopax minor |
S |
WFM |
| Bonaparte's
Gull Larus philadelphia |
MW |
|
| Ring-billed
Gull Larus delawarensis |
SW |
W |
| Herring
Gull Larus argentatus |
SW |
W |
| Glaucous
Gull Larus hyperboreus |
W |
W |
| Great
Black-backed Gull Larus marinus |
W |
W |
| Caspian
Tern Sterna caspia |
M |
|
| Common
Tern Sterna hirundo |
M |
|
| Forster's
Tern Sterna forsteri |
M |
|
| Rock
Dove Columba livia |
SW |
MC |
| Mourning
Dove Zenaida macroura |
SW |
FC |
| Black-billed
Cuckoo Coccyzus erythropthalmus |
S |
F |
| Yellow-billed
Cuckoo Coccyzus americanus |
S |
F |
| Barn
Owl Tyto alba |
SW |
M |
| Eastern
Screech-Owl Otus asio |
SW |
F |
| Great
Horned Owl Bubo virginianus |
SW |
F |
| Barred
Owl Strix varia |
SW |
F |
| Common
Nighthawk Chordeiles minor |
S |
C |
| Chimney
Swift Chaetura pelagica |
S |
FMC |
| Ruby-throated
Hummingbird Archilochus colubris |
S |
FM |
| Belted
Kingfisher Ceryle alcyon |
S |
W |
| Red-headed
Woodpecker Melanerpes erythrocephalus |
SW |
F |
| Red-bellied
Woodpecker Melanerpes carolinus |
SW |
F |
| Yellow-bellied
Sapsucker Sphyrapicus varius |
M |
|
| Downy
Woodpecker Picoides pubescens |
SW |
FM |
| Hairy
Woodpecker Picoides villosus |
SW |
F |
| Northern
Flicker Colaptes auratus |
SW |
F |
| Pileated
Woodpecker Dyrocopus pileatus |
SW |
F |
| Olive-sided
Flycatcher Contopus cooperi |
M |
|
| Eastern
Wood-Pewee Contopus virens |
S |
F |
| Yellow-bellied
Flycatcher Empidonax flaviventris |
M |
|
| Acadian
Flycatcher Empidonax virescens |
S |
F |
| Alder
Flycatcher Empidonax alnorum |
S |
WM |
| Willow
Flycatcher Empidonax trailii |
S |
WM |
| Least
Flycatcher Empidonax minimus |
S |
WFM |
| Eastern
Phoebe Sayornis phoebe |
S |
FM |
| Great
Crested Flycatcher Myiarchus crinitus |
S |
F |
| Eastern
Kingbird Tyrannus tyrannus |
S |
WFM |
| Loggerhead
Shrike Lanius ludovicianus |
S |
M |
| White-eyed
Vireo Vireo griseus |
S |
FM |
| Yellow-throated
Vireo Vireo flavifrons |
S |
F |
| Blue-headed
(formerly Solitary)Vireo Vireo solitarius |
S |
F |
| Warbling
Vireo Vireo gilvus |
S |
F |
| Red-eyed
Vireo Vireo olivaceus |
S |
F |
| Blue
Jay Cyanocitta cristata |
SW |
FMC |
| American
Crow Corvus brachyrhynchos |
SW |
FMC |
| Horned
Lark Eremophila alpestris |
SW |
WM |
| Purple
Martin Progne subis |
S |
WM |
| Tree
Swallow Tachycineta bicolor |
S |
WM |
| Northern
Rough-winged Swallow Stelgidopteryx serripennis |
S |
W |
| Bank
Swallow Riparia riparia |
S |
W |
| Cliff
Swallow Petrochelidon pyrrhonota |
S |
W |
| Barn
Swallow Hirundo rustica |
S |
MC |
| Black-capped
Chickadee Poecile atricapilla |
SW |
F |
| Tufted
Titmouse Baeolophus bicolor |
SW |
F |
| Red-breasted
Nuthatch Sitta canadensis |
SW |
F |
| White-breasted
Nuthatch Sitta carolinensis |
W |
F |
| Brown
Creeper Certhia americana |
M |
|
| Carolina
Wren Thryothorus ludovicianus |
SW |
FM |
| House
Wren Troglodytes aedon |
S |
WFMC |
| Winter
wren Troglodytes troglodytes |
M |
|
| Marsh
Wren Cistothorus palustris |
S |
W |
| Golden-crowned
Kinglet Regulus satrapa |
M |
|
| Ruby-crowned
Kinglet Regulus calendula |
M |
|
| Blue-gray
Gnatcatcher Polioptila caerulea |
M |
|
| Eastern
Bluebird Sialia sialis |
SW |
M |
| Veery
Catharus fuscescens |
S |
F |
| Gray-cheeked
Thrush Catharus minimus |
M |
|
| Swainson's
Thrush Catharus ustulatus |
M |
|
| Hermit
Thrush Catharus guttatus |
M |
|
| Wood
Thrush Hylocichla mustelina |
M |
|
| American
Robin Turdus migratorius |
SW |
WFMC |
| Gray
Catbird Dumatella carolinensis |
S |
WFM |
| Brown
Thrasher Toxostoma rufum |
S |
MF |
| European
Starling Sturnus vulgaris |
SW |
FMC |
| Cedar
Waxwing Bombycilla cedrorum |
SW |
FC |
| Blue-winged
Warbler Vermivora pinus |
S |
M |
| Golden-winged
Warbler Vermivora chrysoptera |
S |
M |
| Tennessee
Warbler Vermivora peregrina |
M |
|
| Orange-crowned
Warbler Vermivora celata |
M |
|
| Nashville
Warbler Vermivora ruficapilla |
M |
|
| Northern
Parula Parula americana |
M |
|
| Yellow
Warbler Dendroica petechia |
S |
WFM |
| Chestnut-sided
Warbler Dendroica pensylvanica |
M |
|
| Magnolia
Warbler Dendroica magnolia |
M |
|
| Cape
May Warbler Dendroica tigrina |
M |
|
| Black-throated
Blue Warbler Dendroica caerulescens |
M |
|
| Yellow-rumped
Warbler Dendroica coronata |
M |
|
| Black-throated
Green Warbler Dendroica virens |
M |
|
| Blackburnian
Warbler Dendroica fusca |
M |
|
| Yellow-throated
Warbler Dendroica dominica |
M |
|
| Pine
Warbler Dendroica pinus |
M |
|
| Prairie
Warbler Dendroica discolor |
M |
|
| Palm
Warbler Dendroica palmarum |
M |
|
| Bay-breasted
Warbler Dendroica castanea |
M |
|
| Blackpoll
Warbler Dendroica striata |
M |
|
| Cerulean
Warbler Dendroica cerulea |
M |
|
| Black-and-white
Warbler Mniotilta varia |
M |
|
| American
Redstart Setophaga ruticilla |
S |
F |
| Prothonotary
Warbler Protonotaria citrea |
S |
W |
| Ovenbird
Seirus aurocapillus |
S |
F |
| Northern
Waterthrush Seirus noveboracensis |
M |
|
| Louisiana
Waterthrush Seiurus motacilla |
S |
F |
| Connecticut
Warbler Oporornis agilis |
M |
|
| Mourning
Warbler Oporornis philadelphia |
M |
|
| Common
Yellowthroat Geothlypis trichas |
S |
M |
| Hooded Warbler Wilsonia citrina |
S |
F |
| Wilson's Warbler Wilsonia pusilla |
M |
|
| Canada Warbler Wilsonia canadensis |
M |
|
| Yellow-breasted Chat Icteria virens |
S |
M |
| Summer Tanager Piranga rubra |
S |
F |
| Scarlet Tanager Piranga olivacea |
S |
F |
| Eastern Towhee Pipilo erythropthalmus |
S |
MF |
| American Tree Sparrow Spizella arborea |
W |
MF |
| Chipping Sparrow Spizella passerina |
S |
MC |
| Field Sparrow Spizella pusilla |
S |
M |
| Vesper Sparrow Pooecetes gramineus |
S |
M |
| Savannah Sparrow Passerculus sandwichensis |
S |
M |
| Grasshopper Sparrow Ammodramus savannarum |
S |
M |
| Fox Sparrow Passerella iliaca |
M |
|
| Song Sparrow Melospiza melodia |
SW |
MW |
| Lincoln's Sparrow Melospiza lincolnii |
M |
|
| Swamp Sparrow Melospiza georgiana |
SW |
W |
| White-throated Sparrow Zonotrichia albicollis |
W |
MF |
| White-crowned Sparrow Zonotrichia leucophrys |
W |
MF |
| Dark-eyed Junco Junco hyemalis |
W |
MFC |
| Lapland Longspur Calcarius lapponicus |
W |
M |
| Snow Bunting Plectrophenax nivalis |
W |
M |
| Bobolink Dolichonyx oryzivorus |
S |
M |
| Red-winged Blackbird Agelaius phoeniceus |
S |
WM |
| Eastern Meadowlark Sturnella magna |
S |
M |
| Rusty Blackbird Euphagus carolinus |
M |
|
| Common Grackle Quiscalus quiscula |
SW |
FMC |
| Brown-headed Cowbird Molothrus ater |
SW |
M |
| Orchard Oriole Icterus spurius |
S |
FM |
| Baltimore Oriole Icterus galbula |
S |
F |
| Northern Cardinal Cardinalis cardinalis |
SW |
FMC |
| Rose-breasted Grosbeak Pheucticus ludovicianus |
S |
F |
| Indigo Bunting Passerina cyanea |
S |
FM |
| Dickcissel Spiza americana |
S |
M |
| Purple Finch Carpodacus purpureus |
M |
|
| House Finch Carpodacus mexicanus |
SW |
MC |
| American Goldfinch Carduelis tristis |
SW |
MC |
| House Sparrow Passer domesticus |
SW |
MC |
Season: S - Summer; W - Winter; M – Migrant (fall and
spring)
Habitat: F – Forest; W – wetland;
M – meadow, agricultural field, old field, shrubby areas; C – cities and urban areas
[Back to the top]
FISH, REPTILES, AMPHIBIANS
Amphibians are extremely sensitive to changes in their environment because they respire through their skin, which
is permeable to toxic pollutants. Amphibians are also sensitive to ultraviolet
radiation, temperature, and other environmental factors. They are in decline
both globally and locally due to a combination of factors, including widespread
habitat loss and possibly ozone depletion, acid rain, disease, and the
accumulation of toxic chemicals. Amphibians
are difficult to find, as they are secretive, highly camouflaged, and generally
subterranean. Yet, they play a crucial ecological role in the food web, as
agents of mosquito control, as well as vehicles for material and energy
transport in soil systems.
A variety of amphibious species
exist within the Black River Watershed. Frog and toad species inhabiting the watershed include:
American and Fowler’s toads, northern spring peeper, gray tree frog, western
chorus frog, bullfrog, green frog, pickerel frog, and wood frog. Salamander
species include: mudpuppy (which frequent large streams and rivers); eastern
spotted newt (which require permanent pools for breeding); the Ambystomids –
(Jefferson, smallmouth, spotted, silvery, tiger, and marbled salamanders); and
the Plethodontids – (dusky, two-lined, red-backed, slimy, and ravine
salamanders). All but the last three species require streams or wetlands for
feeding and breeding habitats.
At one time, the watershed
supported thousands of salamander populations that covered many square miles.
Today, they are reduced to a few populations. For example, only one population
each of Jefferson, silvery, and tiger salamanders is known to exist. A dozen
known populations exist of spotted salamanders and perhaps two dozen populations
of smallmouth salamanders. The single known marbled salamander population has
been decimated.
These salamander populations are
greatly dispersed and genetically isolated, as are local frog species. Instead
of breeding in swamp forest pools that once covered hundreds of acres, these
amphibians are now confined to isolated wet patches, called vernal pools, which
fill with fall and spring rains, but usually
dry out by July. These temporary wetlands are frequently not recognized as
protected lands by developers and regulators. Though seasonal, these vernal
pools are the most ecologically and biotically important wetlands in the area.
Without them, many salamanders and many species of frogs would quickly
disappear. The Ambystomid salamanders, for example, live in underground tunnels
and follow early spring rains, migrating to swamp forests or vernal pools to
breed.
Vernal pools range widely in size, some covering several
acres and others spanning just a dozen feet across. They form in depressions
left by uprooted trees or in other low spots in woods, streambeds, and swales
within floodplains and are characterized by the presence of such trees as the
swamp cottonwood, black willow, sycamore, pumpkin and green/red ash, black
willow, American elm, and silver maple. Vernal pools also contain fowl manna
grass, and a number of sedges such as Carex
crinita, C. intumescens, C. grayi, C. lupulina, C. seorsa, and C. bromoides.
Pools exposed to more sun will develop additional herbaceous species such as
buttonbush, moneywort, water purslane, swamp dock, and sensitive fern. In dry months, vernal pools are generally barren of herbaceous
vegetation, appearing as basins of blackened leaves with a scurfy fringe of
green sedges and fowl manna grass. While wet, they contain the eggs of countless
insects and crustaceans hatch. During the spring, vernal pools fizz with life:
fairy shrimp, protists, amphipods, water fleas and copepods lace and cloud the
water with their movements. Water striders, water boatmen, and other insects ply
the surface at their predatory trades. Dragonfly and damselfly nymphs, beetles
and their larvae, ostracods, fingernail clams, frog and toad tadpoles, and
isopods graze or hunt in the leaf litter at the pool’s bottom.
[Back to the top]
MAMMALS
Mammals once common to the area included black bears, river
otters, mountain lions, martens, muskrats, wolves, bobcats, gray foxes, white
tailed deer, elk, and raccoons. Mammal populations have been affected by the
recent growth in; human activity as
many species lack the ecological range and habitat needed to sustain healthy
populations. In some cases, as with the white tailed deer, animal populations
lack their natural predators due to human impacts.
As a result, these animal populations tend to proliferate and
overwhelm the food supplies in crowded forest communities.
[Back to the top]
EMERGENCE OF WETLANDS
Much of the biological diversity in
the Black River Watershed is concentrated in the fragmented wetland communities
throughout the area. As the predominant ecosystem type prior to European
settlement, the wetlands in the Black River Watershed reveal valuable
information about the species and communities that once proliferated throughout
the watershed. Ohio’s present wetlands date back to the end of the Ice Age,
about 12,000 years ago. When the glaciers retreated, they left behind altered
stream valleys and coated the landscape with a layer of glacial till. The biotic
community that colonized the landscape as it was released from the grip of the
ice consisted of a mixture of southern (“Carolinian”) species and northern
(“boreal”) organisms whose propagules (seeds, spores, and eggs) survived
physical transportation by the ice. For example, the watershed included larch
trees from northern climes as well as the Carolinian oaks and hickories. The
Black River Watershed also hosted about 90 (and likely more before European
settlement) of Ohio’s 150 species of sedges. Sedges are part of the Cyperaceae
family, resembling grasses but having solid rather than hollow stems.
The action of glaciers led to the
formation of bogs in the watershed. Bogs are rich ecosystems that formed in
areas where large chunks of ice broke off of melting glaciers and became
surrounded by the till that washed out as the glaciers receded. As the ice
chunks slowly melted, they left a depression called a kettle hole, in which
water collected. The ecology of bogs is characterized by acidic conditions and
the presence of water with few or no inlets or outlets. Bogs are ombrotrophic,
meaning that their water levels vary according to rates of evaporation and
rainfall. The remains of incompletely decayed vegetation accumulate in bogs. The
chemical by-products of this slow decomposition include acids. This acidic
environment becomes toxic, limiting the presence of bacteria and fungi essential
to the decaying process. The bog’s decaying plant material slowly forms a
floating mat that supports a living biotic community, giving rise to the term
“quaking bog.” Sphagnum moss species compete well in such environments and
tend to further acidify the system.
Although physically wet, the low pH of bogs makes it difficult for many plant
species to extract water with their roots, allowing such species as blueberries,
which are typically adapted to dry conditions, to flourish. Another
characteristic of bogs is the low nutrient content of the organic soils that
exerts selective pressures, favoring carnivorous species.
These carnivorous plants, such as sundew and pitcher plant, supplement
their nitrogen diet by trapping and digesting insects.
While many bogs have been drained for agriculture, the
finest remaining example of a bog in Lorain County is Camden Bog. Acquired by
Oberlin College in 1991, Camden Bog is located in the Vermilion River watershed,
which lies to the west of the Black River. The historical existence of bogs in
the area is apparent from the presence of organic bog soils, called Carlisle
Muck (abbreviated with the code “Cg”on soil maps). Most Cg soils in Lorain
County are in Camden, Henrietta, and Columbia Townships, outside of the Black
River Watershed. A few areas with Cg soils exist within the watershed, mostly in
Russia, Brighton, Wellington, and Pittsfield Townships.
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EXOTIC INVASIVE PLANTS
The introduction of exotic and invasive plants presents a significant ecological
threat in the Black River Watershed. These are plants that originate from
another part of the world (exotic) and proliferate by outcompeting local plants
(invasive). Substantial populations of exotic herbaceous and woody species,
mostly of European or Asian origin, are now firmly established throughout the
Black River Watershed. Most
pervasive is a collection of early successional species dominated by summer
annuals and herbaceous perennials that regularly compete with local row crops
(such as corn and soybeans). These species often dominate disturbed habitats
such as roadsides and construction sites. They occur less frequently in
naturally disturbed communities, particularly in areas such as regularly scoured
sandbars along waterways. Invasive species commonly encountered in upland
forests include Amaranthus
spp., Chenopodium alba, Cirsium arvense, certain Polygonum spp., the foxtail grasses
(Setaria spp.) and Xanthium
stramarium (cocklebur). Tussilago
farfara (colt’s foot), Phragmites
communes (flag grass), and Typha
angustifolia, among others, colonize wet sites and floodplains, sometimes
crowding out native flora. Local
forest understory habitats remain relatively free of invaders, with the notable
exception of Allaria petiolata, the garlic mustard.
Naturalized woody exotics constitute the greatest threat to
the watershed’s remaining natural communities. Multiflora rose (Rosa multiflora) is
especially invasive. Over the last
several decades, it has become a conspicuous and troublesome component of the
understory in many local forests. Its
bird-dispersed seeds facilitate rapid colonization of fallow farm fields,
sometimes rendering these sites unusable (along with Cretaegus spp.for grazing within a few years. Additional woody species invading from adjacent managed plantings include
members of Berberis, Euonymous, Ligustrum(privet), and Rhamnus (buckthorn). Uncontrolled, these aggressive exotic species can transform natural
landscapes, reducing biodiversity and physical access with dense, sometimes
thorny, low-growing canopies. The
density of alien woody species is increasing so rapidly that controlling it will
be difficult to nearly impossible within the next two decades.
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HUMAN MODIFICATIONS
The Black River Watershed contains several fragments of once abundant forest and
wetland communities. Human activity, particularly over the last 100 years, has
drastically altered the composition of forests and habitat in the area. By the
early 1900’s, most forests were cleared and burned by settlers and farmers.
Wetlands were drained to create fields for agriculture and support the
establishment of new settlements for recent immigrants. The composition of
forests changed as they adapted to conditions altered by human activity. The
introduction of exotic European and Asian plants has altered the mix of species
encountered in the woods and wetland areas.
Fortunately, the emerging field of restoration ecology has
the potential to reclaim biologically impoverished sites. Restoration ecology
involves the re-introduction of native forest and wetland habitats through
hydrological modifications, the introduction of native seed varieties, and the
control of invasive, exotic species. Wetland banks have led to the establishment
or expansion of wetland communities throughout the watershed (unfortunately,
these banks are often established as a result of wetland destruction elsewhere).
Many residents and businesses are now utilizing natural landscaping techniques
that incorporate native species and help to repair the fragmented ecological
fabric of the Black River Watershed. While the original ecological integrity of
the Black River Watershed will never be fully restored, an increasing number of
tools and techniques are becoming available to land-owners or residents
interested in restoring native ecological conditions.
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