Iron Springs Bog SNA | |
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IUCN category V (protected landscape/seascape) [1] | |
Location | Clearwater County, Minnesota |
Nearest city | Shevlin, Minnesota |
Coordinates | 47°15′31″N95°14′25″W / 47.25859°N 95.24018°W Coordinates: 47°15′31″N95°14′25″W / 47.25859°N 95.24018°W |
Area | 231 acres (93 ha) |
Established | 1983 |
Governing body | Minnesota Department of Natural Resources |
Iron Springs Bog SNA is a scientific and natural area (SNA) of Minnesota, United States. [2] It is located in Clearwater County and spans 231 acres. [2] Iron springs bog is located in Minnesota's Chippewa Plains, two miles northeast of Lake Itasca, which is the headwaters of the Mississippi River and a popular tourist destination. [2] Contrary to its name, Iron Springs Bog does not actually contain a bog. [2] Rather, the wetland portion of the SNA is a fen fed by calcium-rich groundwater. [2] The SNA is composed of both wetland and forest habitats. [2] Iron Springs Bog hosts numerous rare plant species, notably orchids and carnivorous plants. [2] Due to Iron Springs' proximity to the University of Minnesota's Itasca Biological Station, it has been the subject of various research papers focusing primarily on nutrient cycling and chemistry. [3] [4] [5] [6] The land occupied by the SNA is the ancestral land of the Anishinaabe people.
Iron Springs Bog SNA is located within the Chippewa Plains section of Minnesota's Ecological Classification System. [2] Moraines are among the primary landforms in this region, and thus, Iron Springs Bog is situated on the slope of a gravel moraine. [2] [7] This physiography contrasts Iron Springs Bog with other fens since they typically occur in a depression. [2] Iron Springs Bog is considered a calcareous fen because its calcium-rich water is sourced from underground springs rather than precipitation. [6] [8] Along with calcium, Iron Springs Bog's water is also rich in magnesium and, as the name suggests, iron. [2] Throughout the wetland, pools of water appear orange due to the concentration of iron in the water. [2] The cool, calcium-rich groundwater fosters a unique vegetation community of plants that can tolerate low oxygen, low nutrient availability, and low temperatures. [8] The SNA is comprised of four main habitat classifications: mesic hardwood forest, forested rich peatland, wet meadow/carr, and acid peatland. [2]
Iron Springs Bog SNA is predominantly forested, with the higher elevation areas predominantly made up of red pine and jack pine. [2] Below this higher elevated area, the predominant tree cover switches towards trees more common in boreal forests including conifers such as balsam fir and white spruce, as well as deciduous trees more common in boreal forests such as paper birch and aspen. [2] Two creeks run through the lower elevation areas, forming a swamp along the riparian zone featuring black spruce as the predominant tree. [2] The understory features an array of plants including bryophytes, ferns, shrubs, grasses, and wildflowers including orchids. Some notable features of the understory are pitcher plants and sundew, both of which are carnivorous plants that are often found in nitrogen poor, calcium rich areas such as the Iron Springs Bog SNA. [2] [9] Other notable flora include species not commonly found in Minnesota such as winter bentgrass, bog adder's mouth, and ram's head orchid. [2]
Many birds call Iron Springs Bog SNA home, with 111 species having been recorded within the SNA. [10] Due to close proximity, the bird populations closely reflect the populations present at nearby Itasca State Park. The SNA provides a good location for birding with attractions including 21 species of warblers, Common Loon, Wilson's Snipe, and many raptors. [10] A complete list of the 111 species can be found at the SNA's Bird Checklist put together by the Minnesota DNR. Common mammals found in the area include white-tailed deer, black bears, and North American porcupines. [11] Deer hunting and trout fishing are permitted within the SNA. [2]
Professor David Biesboer, former director of the Itasca Biological Station, conducted research on nitrogen cycling at Iron Springs Bog. [6] [5] In 2000, Biesboer demonstrated that nitrogen fixation rates in Iron Springs Bog were very low, ranging from 0.43 μmol N fixed/m2/day to 1.20 μmol N fixed/m2/day. [6] Because the bog has very low rates of nitrification, it also had no detectable signs of denitrification occurring. [6] These low rates of nitrogen cycling processes in the bog likely stem from the low concentrations of nitrites and nitrates in the groundwater that feeds it and low rates of nitrification, mineralization, and ammonification. [6] In a follow-up study in 2002, Biesboer examined the fluxes of nitrogen in Iron Springs Bog. [5] This work determined that the primary source of nitrogen in the bog is from atmospheric deposition, accounting for 66% of nitrogen input. [5] Atmospheric deposition is followed by fixation (19%), mineralization (12%), and surface water (3%). [5] Biesboer hypothesized that most nitrogen fixation in the bog takes place in the Sphagnum layer since it dominates the understory. [5] The high proportion of nitrogen input from atmospheric deposition could prove problematic because it can lead to surface water acidification and disturbances in nitrogen cycling in the bog. [5] However, research has yet to determine the effects of high atmospheric nitrogen deposition in Iron Springs Bog. [5]
In 1953, Dr. Gilbert A. Leisman published work on organic matter accumulation in bogs surrounding Itasca State Park, including Iron Springs Bog. [4] By measuring the depth of the sedge mat layer, Leisman determined that the average rate of organic matter accumulation in Iron Springs Bog was 0.67 inches/year. [4] All of the bogs tested displayed relatively similar rates of organic matter accumulation, ranging from 0.54 inches/year to 0.79 inches/year. [4] In the top four inches of the sedge mat, Leisman found that 64% of the peat was in the form of Carex lasiocarpa , a sedge found in wetlands. [4]
The fen within Iron Springs Bog SNA is highly alkaline and contain high levels of calcium which is introduced into the water through upwelling processes through the glacial till present in the SNA. [3] As with many other fens rich in calcium, Iron Springs Bog SNA contains high levels of silicon. [3] There are many other metals found in higher than usual concentrations in the SNA including Mg, Ba, Al, Fe, and Mn. [3] The fens within Iron Springs Bog SNA also contain a lower than usual calcium/barium quotient (380) when compared to similar fens, with the quotient reflecting those found in poor fens. [3]
A fen is a type of peat-accumulating wetland fed by mineral-rich ground or surface water. It is one of the main types of wetlands along with marshes, swamps, and bogs. Bogs and fens, both peat-forming ecosystems, are also known as mires. The unique water chemistry of fens is a result of the ground or surface water input. Typically, this input results in higher mineral concentrations and a more basic pH than found in bogs. As peat accumulates in a fen, groundwater input can be reduced or cut off, making the fen ombrotrophic rather than minerotrophic. In this way, fens can become more acidic and transition to bogs over time.
A bog or bogland is a wetland that accumulates peat as a deposit of dead plant materials – often mosses, typically sphagnum moss. It is one of the four main types of wetlands. Other names for bogs include mire, mosses, quagmire, and muskeg; alkaline mires are called fens. A baygall is another type of bog found in the forest of the Gulf Coast states in the United States. They are often covered in heath or heather shrubs rooted in the sphagnum moss and peat. The gradual accumulation of decayed plant material in a bog functions as a carbon sink.
Askham Bog is small area of peat bog and Site of Special Scientific Interest situated within the Vale of York in North Yorkshire, England. It lies to the south-west of York, north of Copmanthorpe and near Askham Richard and Askham Bryan. It is regarded as one of the most ecologically diverse sites in Northern England.
A marsh is a wetland that is dominated by herbaceous rather than woody plant species. Marshes can often be found at the edges of lakes and streams, where they form a transition between the aquatic and terrestrial ecosystems. They are often dominated by grasses, rushes or reeds. If woody plants are present they tend to be low-growing shrubs, and the marsh is sometimes called a carr. This form of vegetation is what differentiates marshes from other types of wetland such as swamps, which are dominated by trees, and mires, which are wetlands that have accumulated deposits of acidic peat.
Itasca State Park is a state park of Minnesota, United States, and contains the headwaters of the Mississippi River. The park spans 32,690 acres (132.3 km2) of northern Minnesota, and is located about 21 miles (34 km) north of Park Rapids, Minnesota and 25 miles (40 km) from Bagley, Minnesota. The park is part of Minnesota's Pine Moraines and Outwash Plains Ecological Subsection and is contained within Clearwater, Hubbard, and Becker counties.
Plant nutrition is the study of the chemical elements and compounds necessary for plant growth and reproduction, plant metabolism and their external supply. In its absence the plant is unable to complete a normal life cycle, or that the element is part of some essential plant constituent or metabolite. This is in accordance with Justus von Liebig’s law of the minimum. The total essential plant nutrients include seventeen different elements: carbon, oxygen and hydrogen which are absorbed from the air, whereas other nutrients including nitrogen are typically obtained from the soil.
The pedosphere is the outermost layer of the Earth that is composed of soil and subject to soil formation processes. It exists at the interface of the lithosphere, atmosphere, hydrosphere and biosphere. The pedosphere is the skin of the Earth and only develops when there is a dynamic interaction between the atmosphere, biosphere, lithosphere and the hydrosphere. The pedosphere is the foundation of terrestrial life on Earth.
Aspen parkland refers to a very large area of transitional biome between prairie and boreal forest in two sections, namely the Peace River Country of northwestern Alberta crossing the border into British Columbia, and a much larger area stretching from central Alberta, all across central Saskatchewan to south central Manitoba and continuing into small parts of the US states of Minnesota and North Dakota. Aspen parkland consists of groves of aspen, poplar and spruce, interspersed with areas of prairie grasslands, also intersected by large stream and river valleys lined with aspen-spruce forests and dense shrubbery. This is the largest boreal-grassland transition zone in the world and is a zone of constant competition and tension as prairie and woodlands struggle to overtake each other within the parkland.
Serpentine soil is an uncommon soil type produced by weathered ultramafic rock such as peridotite and its metamorphic derivatives such as serpentinite. More precisely, serpentine soil contains minerals of the serpentine subgroup, especially antigorite, lizardite, and chrysotile or white asbestos, all of which are commonly found in ultramafic rocks. The term "serpentine" is commonly used to refer to both the soil type and the mineral group which forms its parent materials.
Big Bog State Recreation Area, a recent addition to the Minnesota state park system, is located on Minnesota State Highway 72, north of Waskish, Minnesota. It covers 9,459 acres (38.3 km2), primarily swamps, bogs, and upland "islands".
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A pocosin is a type of palustrine wetland with deep, acidic, sandy, peat soils. Groundwater saturates the soil except during brief seasonal dry spells and during prolonged droughts. Pocosin soils are nutrient-deficient (oligotrophic), especially in phosphorus.
Ķemeri National Park is a national park west of the city of Jūrmala, Latvia. Established in 1997, Ķemeri is the third largest national park in the country by area, covering an area of 381.65 km2. The territory of the park is mostly occupied by forests and mires, the most significant of them being The Great Ķemeri Bog. There are also several lakes, that are former lagoons of the Littorina Sea. Lake Kaņieris is a Ramsar site. The park also protects the famous natural mineral-springs and muds, used for centuries because of their therapeutic nature. The springs led to development of many resorts, spas, and sanitariums in the 19th century.
Human impact on the nitrogen cycle is diverse. Agricultural and industrial nitrogen (N) inputs to the environment currently exceed inputs from natural N fixation. As a consequence of anthropogenic inputs, the global nitrogen cycle (Fig. 1) has been significantly altered over the past century. Global atmospheric nitrous oxide (N2O) mole fractions have increased from a pre-industrial value of ~270 nmol/mol to ~319 nmol/mol in 2005. Human activities account for over one-third of N2O emissions, most of which are due to the agricultural sector. This article is intended to give a brief review of the history of anthropogenic N inputs, and reported impacts of nitrogen inputs on selected terrestrial and aquatic ecosystems.
Minerotrophic refers to environments that receive nutrients primarily through groundwater that flows through mineral-rich soils or rock, or surface water flowing over land. Minerotrophic, “minerogenous”, and “geogenous” are now often used interchangeably, although the latter two terms refer primarily to hydrological systems, while the former refers to nutrient dynamics. The hydrologic process behind minerotrophic wetlands results in water that has acquired dissolved chemicals which raise the nutrient levels and reduce the acidity. This in turn affects vegetation assemblages and diversity in the wetland in question. If dissolved chemicals include chemical bases such as calcium or magnesium ions, the water is referred to as base-rich and is neutral or alkaline. In contrast to minerotrophic environments, ombrotrophic environments get their water mainly from precipitation, and so are very low in nutrients and more acidic. Of the various wetland types, fens and rich fens are often minerotrophic while poor fens and bogs are often ombrotrophic. Marshes and swamps may also be fed through groundwater sources to a degree.
Aulacomnium palustre, the bog groove-moss or ribbed bog moss, is a moss that is nearly cosmopolitan in distribution. It occurs in North America, Hispaniola, Venezuela, Eurasia, and New Zealand. In North America, it occurs across southern arctic, subboreal, and boreal regions from Alaska and British Columbia to Greenland and Quebec. Documentation of ribbed bog moss's distribution in the contiguous United States is probably incomplete. It is reported sporadically south to Washington, Wyoming, Georgia, and Virginia.
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