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Superior Coastal Plain Ecological Landscape
Download the Superior Coastal Plain chapter [PDF] of the Ecological Landscapes of Wisconsin. This chapter provides a detailed assessment of the ecological and socioeconomic conditions for the Superior Coastal Plain. It also identifies important planning and management considerations and suggests management opportunities that are compatible with the ecology of the landscape. The tabs below provide additional information.
Landscape at a Glance
Please note that each of these topics is covered in much more detail in the Superior Coastal Plain chapter [PDF].
Physical & Biotic Environment | Socioeconomic Conditions | Considerations for Planning & Management
| Physical & Biotic Environment | |
|---|---|
|
Size |
1,416 square miles (905,929 acres), representing 2.5% of the area of the state. |
|
Climate |
Typical of northern Wisconsin, though conditions are somewhat moderated by the proximity to Lake Superior; mean growing season of 122 days, mean annual temperature is 40.2 deg. F, mean annual precipitation is 32 inches, and mean annual snowfall is 87.4 inches. Cool summers, deep snows (including lake effect snows), high humidity, fog, mist, wave spray, currents, ice, and strong winds (e.g., along exposed coastlines, where blow-down events are frequent) affect parts of the Ecological Landscape, especially near Lake Superior. Some areas near Lake Superior support grass-based agriculture (18.5% of the Ecological Landscape). Portions of the northern Bayfield Peninsula have a climate and soils favorable for growing apples and other fruits. Areas away from Lake Superior have a shorter growing season and forests become more important than agriculture. Learn more from the chapter [PDF] |
|
Bedrock |
Late Precambrian sandstones are exposed and form cliffs and ledges along the northern edge of the Bayfield Peninsula and on the shores of the Apostle Islands. Igneous rocks (e.g., basalts) form the underpinnings of several waterfalls. Learn more from the chapter [PDF] |
|
Geology & Landforms |
The Bayfield Peninsula is hilly, as are some of the Apostle Islands. Both are covered by glacial tills. The level plains on either side of the Bayfield Peninsula slope gently toward Lake Superior. They are dissected by many deeply incised streams and several large rivers that generally flow from south to north toward Lake Superior. Sandspits, often enclosing lagoons and wetlands, are well-developed in the Apostle Islands archipelago and at river mouths; some of the larger spits are several miles long. Learn more from the chapter [PDF] |
|
Soils |
Important soils include deep, poorly-drained reddish lacustrine clays on either side of the Bayfield Peninsula. The clay deposits include lenses of sand or coarse-textured till; these areas are especially erosion-prone when they are cut by streams. The tills covering the Bayfield Peninsula and Apostle Islands are variable in composition, but include clays, silts, loams and sands. Organic soils are limited in extent, occurring mostly in association with the peatlands on the margins of the coastal lagoons and to a lesser extent in basins underlain by impermeable tills. Learn more from the chapter [PDF] |
|
Hydrology |
Lake Superior has had an enormous influence on the climate, landforms, soils, vegetation, and economy of the Superior Coastal Plain. Freshwater estuaries are present along the coast. Inland lakes are rare, but lagoons, some of them quite large, occur behind the coastal sandspits. Important rivers include the St. Louis, Nemadji, Bad, White, Amnicon, and Bois Brule. Coldwater streams originate in the aquifers at the northern edge of the Northwest Sands in Bayfield County and flow north across the Superior Coastal Plain before emptying into Lake Superior. Many of the streams flowing across the clay plain suffered severe damage to their banks and beds during the era of heavy logging in the late 19th and early 20th centuries. Some of them have not yet recovered and their slumping banks continue to dump sediments into the main channels, and ultimately, into Lake Superior. Water (and soil) management can be challenging in this Ecological Landscape. Learn more from the chapter [PDF] |
|
Current Landcover |
Aspen-dominated boreal forests are abundant on the clay plains to the west and east of the Bayfield Peninsula. In some areas white spruce, balsam fir, and white pine (these were the dominant canopy trees prior to the Cutover) are now common understory species, or are even colonizing abandoned pastures. Older stands of boreal conifers still occur in a few places, such as the City of Superior Municipal Forest. Forest fragmentation is significant on the clay plain owing to the interspersion of forests with fields and pastures. Northern hardwood and hemlock-hardwood forests occur on the Apostle Islands and include old-growth remnants. Dry forests of pine and oak are scarce in this Ecological Landscape but they do occur on some of the sandspits associated with coastal estuaries. The largest coastal wetlands cover thousands of acres, and these are composed of complex vegetation mosaics that include coniferous and deciduous forests, shrublands, wet meadows and marsh. Large wetlands in the interior of the Superior Coastal Plain include the Bibon Swamp, a huge wetland of almost 10,000 acres along the White River on the southern edge of the Ecological Landscape, and Sultz Swamp, a peatland perched high on the northern Bayfield Peninsula. An extensive complex of wetlands of variable structure occurs on poorly drained red clays in and around the City of Superior. Learn more from the chapter [PDF] |
|
Socioeconomic Conditions
(based on data from Douglas, Bayfield, and Ashland counties) |
|
|---|---|
|
Population |
75,056, 1.3% of the state total |
|
Population Density |
20 persons/ sq. mile |
|
Per Capita Income |
$26,597 |
|
Important Economic Sectors |
Government, tourism-related, health care and social services, and retail trade sectors employed the most people in 2007, reflecting high government service and recreation dependence. Some agriculture, including the growing of specialty crops such as apples and cherries, occurs here. Forestry, agriculture, and commercial fishing have the largest effects on the natural resources of the Superior Coastal Plain. |
|
Public Ownership |
Federal lands include Apostle Islands National Lakeshore (NPS); Whittlesey Creek National Wildlife Refuge; several USCG light stations; and a very small portion of the Chequamegon-Nicolet National Forest. Important state-owned properties include the Brule River State Forest, and several state parks, wildlife areas, fishery areas, and natural areas. Most county-owned land is county forest (which includes several "special use" areas that are not managed primarily for wood products). The City of Superior owns a Municipal Forest of over 4,000 acres along the St. Louis River, and a large part of Wisconsin Point (part of a coastal barrier spit separating St. Louis and Allouez bays from the waters of Lake Superior at Duluth-Superior). A map showing public land ownership (county, state, and federal) and private lands enrolled in the Forest Tax Programs in this Ecological Landscape can be found at the end of this chapter. |
|
Other Notable Ownerships |
Other lands of high conservation value include the reservations of the Bad River and Red Cliff Bands of Lake Superior Ojibwa, projects under the direction of NGOs (e.g., local land trusts), and industrial forests. The Wisconsin Chapter of The Nature Conservancy has developed conservation easements with landowners along the Brule River and has also worked with many of the governmental units in this Ecological Landscape (including tribal governments) on conservation projects of mutual interest and benefit. Local land trusts have been active on Madeline Island (Ashland County) and in Douglas County. |
| Considerations for Planning & Management | |
|---|---|
Major planning and management considerations in the Superior Coastal Plain include climate change; impacts of water level changes on the coastal wetlands and associated biota (including attempts to stabilize the water level of Lake Superior); the continued appearance and spread of invasive species; population trends in certain native species; managing water on the clay soils; and increasing the acreage of conifer-dominated boreal forest. Other important issues are shoreline development along rivers and Lake Superior and protection of areas used by migratory birds and spawning fish. Management of lands in the red clay country to lessen erosion and improve water quality and habitat for aquatic life, and reduce negative edge impacts (construction, agriculture, forestry - including reforestation), are issues deserving major consideration. The occurrences of many rare and geographically limited natural communities of exceptional quality have been documented here recently, along with numerous associated rare species. The coastal estuaries are regionally significant repositories for intact natural communities, such as conifer swamp, sedge meadow, fen, and marsh. Many rare plants and animals have been documented in the estuaries, which are also important nursery areas for fish. Use of some of these coastal wetlands, lagoons and associated sandspit habitats by migratory birds is very high, and some of the rare species use these habitats to the exclusion of most or any others. Learn more about management opportunities from the chapter [PDF] |
Species
Species of Greatest Conservation Need
The following species are listed according to their probability of occurring in the Superior Coastal Plain Ecological Landscape, based on the findings in Wisconsin's 2015 Wildlife Action Plan.
See the key to association scores [PDF] for complete definitions.
(Please see also the Significant Flora [PDF] and the Significant Wildlife [PDF] sections in the Superior Coastal Plain chapter).
| Amphibians | Score | |
|---|---|---|
| Four-toed Salamander | Hemidactylium scutatum | 3 |
| Pickerel Frog | Lithobates palustris | 1 |
| Mink Frog | Lithobates septentrionalis | 3 |
| Ants, wasps, and bees | Score | |
|---|---|---|
| Yellow Bumble Bee | Bombus fervidus | 1 |
| Confusing Bumble Bee | Bombus perplexus | 1 |
| Yellowbanded Bumble Bee | Bombus terricola | 1 |
| Sanderson's Bumble Bee | Bombus sandersoni | 1 |
| Indiscriminate Cuckoo Bumble Bee | Bombus insularis | 3 |
| Aquatic and terrestrial snails | Score | |
|---|---|---|
| Boreal Top | Zoogenetes harpa | 2 |
| Beetles | Score | |
|---|---|---|
| Hairy-necked Tiger Beetle | Cicindela hirticollis rhodensis | 3 |
| Northern Barrens Tiger Beetle | Cicindela patruela patruela | 3 |
| A Predaceous Diving Beetle | Hygrotus falli | 2 |
| A Hydroporus Diving Beetle | Heterosternuta pulchra | 3 |
| A Predaceous Diving Beetle | Hydrocolus persimilis | 3 |
| A Predaceous Diving Beetle | Hydrocolus rubyae | 3 |
| A Predaceous Diving Beetle | Hydroporus morio | 3 |
| Robust Dubiraphian Riffle Beetle | Dubiraphia robusta | 1 |
| A Crawling Water Beetle | Haliplus apostolicus | 3 |
| A Minute Moss Beetle | Hydraena angulicollis | 3 |
| A Minute Moss Beetle | Ochthebius lineatus | 3 |
| A Predaceous Diving Beetle | Ilybius subaeneus | 3 |
| A Predaceous Diving Beetle | Ilybius confusus | 3 |
| A Predaceous Diving Beetle | Oreodytes scitulus | 3 |
| A Predaceous Diving Beetle | Rhantus sericans | 3 |
| A Water Scavenger Beetle | Agabetes acuductus | 1 |
| A Water Scavenger Beetle | Helophorus latipenis | 3 |
| A Predaceous Diving Beetle | Ilybius angustior | 3 |
| Birds | Score | |
|---|---|---|
| American Bittern | Botaurus lentiginosus | 3 |
| Least Bittern | Ixobrychus exilis | 1 |
| American Black Duck | Anas rubripes | 1 |
| Northern Goshawk | Accipiter gentilis | 1 |
| Red-shouldered Hawk | Buteo lineatus | 1 |
| Peregrine Falcon | Falco peregrinus | 3 |
| Sharp-tailed Grouse | Tympanuchus phasianellus | 2 |
| Yellow Rail | Coturnicops noveboracensis | 2 |
| Piping Plover | Charadrius melodus | 3 |
| Upland Sandpiper | Bartramia longicauda | 3 |
| Rufa Red Knot | Calidris canutus rufa | 1 |
| American Woodcock | Scolopax minor | 3 |
| Caspian Tern | Hydroprogne caspia | 1 |
| Common Tern | Sterna hirundo | 3 |
| Black Tern | Chlidonias niger | 3 |
| Long-eared Owl | Asio otus | 2 |
| Common Nighthawk | Chordeiles minor | 1 |
| Eastern Whip-poor-will | Antrostomus vociferus | 1 |
| Red-headed Woodpecker | Melanerpes erythrocephalus | 1 |
| Black-backed Woodpecker | Picoides arcticus | 2 |
| Olive-sided Flycatcher | Contopus cooperi | 2 |
| Least Flycatcher | Empidonax minimus | 3 |
| Purple Martin | Progne subis | 1 |
| Gray Jay | Perisoreus canadensis | 1 |
| Ruby-crowned Kinglet | Regulus calendula | 2 |
| Swainson's Thrush | Catharus ustulatus | 3 |
| Loggerhead Shrike | Lanius ludovicianus | 1 |
| Golden-winged Warbler | Vermivora chrysoptera | 3 |
| Connecticut Warbler | Oporornis agilis | 1 |
| Dickcissel | Spiza americana | 1 |
| Vesper Sparrow | Pooecetes gramineus | 1 |
| Grasshopper Sparrow | Ammodramus savannarum | 1 |
| Le Conte's Sparrow | Ammodramus leconteii | 3 |
| Bobolink | Dolichonyx oryzivorus | 3 |
| Eastern Meadowlark | Sturnella magna | 3 |
| Western Meadowlark | Sturnella neglecta | 1 |
| Yellow-headed Blackbird | Xanthocephalus xanthocephalus | 1 |
| Rusty Blackbird | Euphagus carolinus | 2 |
| Brewer's Blackbird | Euphagus cyanocephalus | 3 |
| Evening Grosbeak | Coccothraustes vespertinus | 2 |
| Butterflies and moths | Score | |
|---|---|---|
| West Virginia White | Pieris virginiensis | 2 |
| Gray Copper | Lycaena dione | 1 |
| Semirelict Underwing Moth | Catocala semirelicta | 2 |
| Caddisflies | Score | |
|---|---|---|
| A Humpless Casemaker Caddisfly | Brachycentrus lateralis | 3 |
| A Fingernet Caddisfly | Wormaldia moesta | 3 |
| Dragonflies and damselflies | Score | |
|---|---|---|
| Pronghorn Clubtail | Gomphus graslinellus | 1 |
| Mottled Darner | Aeshna clepsydra | 1 |
| Spatterdock Darner | Rhionaeschna mutata | 1 |
| Zigzag Darner | Aeshna sitchensis | 3 |
| Subarctic Darner | Aeshna subarctica | 1 |
| Lake Emerald | Somatochlora cingulata | 1 |
| Plains Emerald | Somatochlora ensigera | 1 |
| Forcipate Emerald | Somatochlora forcipata | 3 |
| Incurvate Emerald | Somatochlora incurvata | 3 |
| Ringed Boghaunter | Williamsonia lintneri | 1 |
| Alkali Bluet | Enallagma clausum | 3 |
| Sphagnum Sprite | Nehalennia gracilis | 1 |
| Fishes | Score | |
|---|---|---|
| Lake Sturgeon | Acipenser fulvescens | 3 |
| American Eel | Anguilla rostrata | 1 |
| Shortjaw Cisco | Coregonus zenithicus | 3 |
| Flies | Score | |
|---|---|---|
| A Non-biting Midge | Pseudodiamesa pertinax | 3 |
| Grasshoppers and allies | Score | |
|---|---|---|
| Blue-legged Grasshopper | Melanoplus flavidus | 1 |
| Stone's Locust | Melanoplus stonei | 1 |
| Bruner's Spur-throat Grasshopper | Melanoplus bruneri | 3 |
| Huckleberry Spur-throat Grasshopper | Melanoplus fasciatus | 2 |
| Forest Locust | Melanoplus islandicus | 3 |
| A Spur-throat Grasshopper | Melanoplus foedus | 2 |
| Gladston's Spur-throat Grasshopper | Melanoplus gladstoni | 1 |
| Rocky Mountain Sprinkled Locust | Chloealtis abdominalis | 3 |
| Lake Huron Locust | Trimerotropis huroniana | 1 |
| Crackling Forest Grasshopper | Trimerotropis verruculata | 2 |
| Seaside Grasshopper | Trimerotropis maritima | 1 |
| Spotted-winged Grasshopper | Orphulella pelidna | 2 |
| Delicate Meadow Katydid | Orchelimum delicatum | 1 |
| Speckled Rangeland Grasshopper | Arphia conspersa | 3 |
| Clear-winged Grasshopper | Camnula pellucida | 3 |
| Ash-brown Grasshopper | Trachyrhachys kiowa | 1 |
| Club-horned Grasshopper | Aeropedellus clavatus | 1 |
| Leafhoppers and true bugs | Score | |
|---|---|---|
| A Backswimmer | Notonecta borealis | 3 |
| Mammals | Score | |
|---|---|---|
| Water Shrew | Sorex palustris | 1 |
| Little Brown Bat | Myotis lucifugus | 2 |
| Northern Long-eared Bat | Myotis septentrionalis | 2 |
| Silver-haired Bat | Lasionycteris noctivagans | 2 |
| Big Brown Bat | Eptesicus fuscus | 2 |
| Franklin's Ground Squirrel | Poliocitellus franklinii | 2 |
| Northern Flying Squirrel | Glaucomys sabrinus | 2 |
| Woodland Jumping Mouse | Napaeozapus insignis | 1 |
| American Marten | Martes americana | 2 |
| Mayflies | Score | |
|---|---|---|
| American Sand Burrowing Mayfly | Dolania americana | 1 |
| A Small Minnow Mayfly | Paracloeodes minutus | 2 |
| A Spiny Crawler Mayfly | Eurylophella aestiva | 1 |
| A Flat-headed Mayfly | Rhithrogena undulata | 3 |
| A Flat-headed Mayfly | Maccaffertium pulchellum | 2 |
| A Spiny Crawler Mayfly | Drunella cornuta | 3 |
| A Large Square-gilled Mayfly | Neoephemera bicolor | 3 |
| A Small Minnow Mayfly | Plauditus cestus | 3 |
| Mussels and clams | Score | |
|---|---|---|
| Elktoe | Alasmidonta marginata | 1 |
| Eastern Elliptio | Elliptio complanata | 3 |
| Reptiles | Score | |
|---|---|---|
| Wood Turtle | Glyptemys insculpta | 3 |
| Blanding's Turtle | Emydoidea blandingii | 1 |
| Stoneflies | Score | |
|---|---|---|
| A Perlodid Stonefly | Isogenoides frontalis | 3 |
Community opportunities
Natural community management opportunities
The Superior Coastal Plain Ecological Landscape contains opportunities to manage for the following natural communities, based on the findings in the 2015 Wildlife Action Plan (originally presented by the Ecosystem Management Team).
See the key to association scores [PDF] for complete definitions.
General opportunities
General management opportunities 1
Lake Superior, the largest freshwater lake in the world, affects virtually all natural features and many economic aspects of the Superior Coastal Plain. Continued cooperation and coordination across county, state and international boundaries will be needed to manage this globally important resource sustainably over time.
The freshwater estuaries in this landscape are exceptional and offer opportunities to protect or restore many high quality wetland habitats. The National Oceanic and Atmospheric Administration (NOAA) recently designated the St. Louis River Estuary as part of a nation-wide system of "National Estuarine Research Reserves." This designation will present opportunities for coastal wetland-related research, stewardship and education through private, state and federal partnerships. The Bad River-Kakagon Sloughs was designated a "wetland of international significance" in 2012 through the Ramsar Convention.
The Superior Coastal Plain offers excellent opportunities to maintain high-quality examples of many natural community types. The "sandscapes," with their beach, dune, barrens and dry forest communities, are among the best examples known from the western Great Lakes region. Bedrock features include cliffs, glades and ledges, and these provide habitat for a number rare plants, some of them at their extreme range limits. The extensive red clay wetlands in and around the city of Superior host exceptional concentrations of rare plants.
Boreal Forest once covered much of the Superior Coastal Plain, and the landscape presents the state's best opportunities to protect, restore and maintain this natural community. Returning conifers to these forests now largely dominated by aspen is a major opportunity. Collectively, these forests also provide opportunities to increase large trees, cavity trees, coarse woody debris, patches of old-growth forest, large forest patches and a reduction of the hard edge that is now prevalent throughout much of this region. Old-growth hemlock-hardwood forests, now extremely rare anywhere in Wisconsin, occur on several of the Apostle Islands. Browse-sensitive conifers (hemlock, white cedar, Canada yew) are common and reproducing well in these forests.
Several of the major river corridors, such as the Bad and Nemadji, contain stands of floristically rich mesic hardwood forests and the state's northernmost occurrences of floodplain forest. Streams coming out of the deep sand aquifers on the northern Bayfield Peninsula support coldwater assemblages, which include native brook trout and numerous other species.
Significant opportunities to maintain breeding and migratory habitats in both natural and human caused or "surrogate" communities are found in this landscape. For example, colonial bird rookeries are significant and include the only breeding sites on Lake Superior for the WI Endangered Common Tern. Some of the grass-dominated cleared lands in the lacustrine clay plain are extensive for this part of the state and are inhabited by rare and declining grassland birds. These grassland areas offer opportunities for careful assessment to determine which are best to maintain for their habitat value versus increasing the size of forest blocks to increase forest area, reduce forest edge, retain snow cover and water for longer periods and provide habitat for forest interior species that are now relatively scarce in many parts of the Superior Coastal Plain.
1. The text presented here is a summarized version of a longer section developed for the Ecological Landscapes of Wisconsin.
Maps
Superior Coastal Plain printable maps
- Finley's Vegetation of the Mid-1800s [PDF]
- Land Cover of the Mid-1800's [PDF]
- Landtype Associations (LTAs) [PDF]
- Public Land Ownership, Easements and Private Land Enrolled in Forest Tax Programs [PDF]
- Ecologically Significant Places [PDF]
- Exceptional and Outstanding Resource Waters and 303(d) Degraded Waters (2010 Update) [PDF]
- Dams [PDF]
- WISCLAND Land Cover (1992) [PDF]
- Soil Regions [PDF]
- Relative Tree Density in the Mid-1800s [PDF]
- Population Density, Cities, and Transportation [PDF]
Also see the statewide maps.
LTAs
Superior Coastal Plain Landtype Associations
Landtype Associations (LTAs) are units of the National Hierarchical Framework of Ecological Units (NHFEU), a hierarchical ecological land classification system. LTAs are much smaller than Ecological Landscapes, ranging in size from 10,000 and 300,000 acres. In Wisconsin, they are usually based on glacial features like individual moraines or outwash plains. LTAs can be very useful for planning at finer scales within an Ecological Landscape.
The following are the LTAs associated with the Superior Coastal Plain Ecological Landscape. The Superior Coastal Plain LTA map [PDF] can be used to locate these LTAs. Clicking on an LTA in the list below will open a data table for that LTA in PDF format. Descriptions are included, where available.
