G. Bryan
Iowa State University Extension Publication Pm-1351f
Copyright 1993
Introduction
Fens are the rarest of Iowa's wetland communities and of great
scientific interest. While their geology varies, they all are the
products of the seepage of groundwater to the surface. Because the
water is rich in calcium and other minerals, only a select group of
plants is able to grow there. As a result, fens contain many plant
species considered endangered or threatened in Iowa.
A few of the oldest fens contain plant remains that date back 10,000 years, though most Iowa fens are less than 5,000 years old. A few of these younger fens may have existed 10,000 years ago, but because of dramatic climate changes, they may have dried up and lost the plant remains (by burning or erosion) that could prove their age. When the climate grew wetter again about 5,000 years ago, these fens may have reappeared. Most Iowa fens, however, are thought to be of rather recent origin, geologically speaking. It is likely they were formed in the last 5,000 years and are related to the changes in geology brought by the receding of the last glaciers from Iowa.
Why should I be concerned?
Fens are an important and unique wetland type. Not only are the fens
themselves rare, but they shelter over 200 plant species, 20 of which
are Iowa endangered and threatened species. Many of the plant species
have been in these areas for thousands of years. The fen's
vegetation, in turn, shelters wildlife by providing valuable
habitat.
Fens are valuable to humans as well. They are important as sites
of groundwater discharge good indicators of shallow aquifers.
Vegetation in all wetlands plays an important role in recycling
nutrients, trapping eroding soil, and filtering out polluting
chemicals such as nitrates. However, the rarity of fens and their
relatively small size makes it important to protect them from
overloading by these materials. Too many nutrients
or other chemicals can irreparably damage fens. As miners watched
their canaries for signs of poisoned air, it is
wise for humans to watch closely the health of plant and animal life
in ecosystems such as fens, which are good indicators of
environmental quality. The condition of plants and animals in fens
can help us mon- itor the quality of groundwater resources.
What are fen wetlands?
The name fen is not as commonly used in the United States as in
Europe where these wetlands are not as rare. In Iowa, fens have been
called marshes, seeps, side-hill seeps, mound springs, wet prairies,
sedge meadows, and sloughs. They also have been mistakenly called
bogs, hanging bogs, and hillside bogs. Fens are typically found on
hillsides, though occasionally in low areas between hills.
There are many different kinds of wetlands. Certain characteristics make fens unique. Typically, the water in fens is neutral to alkaline (the pH is 7 or greater) and rich in nutrients. The water comes from groundwater that saturates the fens' organic soils layers of partially decomposed plant material called peat. In certain areas this peat is so saturated with water it sometimes is called "quaking soil" because the ground trembles when walked on. Sometimes the water that saturatesthis soil carries enough dissolved calcium carbonate to form a grayish-white, lime-rich substance called marl or tufa when it comes to the surface. Because of this calcium deposit, these wetlands are sometimes referred to as calcareous.
Because of the dissolved calcium and other minerals in the water, fen plants are very distinctive. The most common plants in the fen are sedges that often hide some rare and beautiful wild flowers. Other plants that live in the fen include grasses, forbs (broad-leaved plants), and a few shrubs and trees.
Fens differ substantially from other wetlands. Some of these
differences cannot be directly observed because they are deep below
the soil surface.
Geological settings - underground structure
Fens can form where a groundwater source rich in minerals is
exposed to the surface. Depending on a fen's location in the state,
its foundation was laid either during a glacial period hundreds of
thousands of years ago (and since eroded), or during the most recent
glacial period about 10,000 years ago. In either case, the geology
provided an ideal setting for the development of a fen. There are
basically two settings:
These geological settings of fens are important because they relate to the likelihood of contamination by chemicals and other pollutants. Fens with groundwater sources near the surface (second setting) can be contaminated by surface-derived pollutants much more easily than fens whose source of groundwater is buried (first setting). However, the glacial deposits surrounding the buried groundwater sources of eastern Iowa fens are old and weathered. This makes them more fractured, allowing pollutants moving through the ground to enter the fen easily and rapidly. Thus eastern Iowa fens are more likely to be contaminated by surface pollutants that move into and through the fractures than similar western Iowa fens, whose geologic setting is younger and not as weathered.
Soils
Fen soil contains a large quantity of decomposing plant and animal
material called humus. Soils with a high humus content are called
organic soils. Fen organic soil is saturated with water, and the
humus is so rotted that it is difficult to discern any bits of plant
or animal material. Such organic soil is called muck. In contrast,
the true peat soils of bogs show recognizable bits of plant stems and
other material. Two soil series are typical of Iowa fens: Palms muck
and Houghton muck. However, some exceptions exist; these soil series
do not always have fens, and some fens are found on other soil
series.
Water pH
A particular water chemistry also characterizes a fen. For example,
its pH is alkaline, neutral, or only slightly acidic, whereas a bog
is very acidic. Fen soils are saturated with water coming directly
from groundwater sources. This groundwater supplies most of the
nutrients needed by fen plants. Classification of Iowa fens is based
on the quantity of available nutrients and the water pH. There are
three distinct types:
Only two nutrient-poor fens are known to exist in Iowa. One of these
is located in Pilot Knob State Park. Nutrient-rich fens are located
chiefly in the types of geological settings typical of eastern Iowa.
Most of the very nutrient-rich fens are found in northwestern Iowa.
Very nutrient-rich fens also may be characterized by calcium
carbonate (lime- stone) deposits of marl or tufa.
Water hardness
The hardness of water is largely defined by the quantity of dissolved
calcium and magnesium ions in the water. The more dissolved ions
present, the harder the water. Hard water tends to be more alkaline.
As a result, slightly alkaline, very nutrient-rich fen have higher
concentrations of dissolved calcium carbonate, sulfate and silica
than neutral, nutrient-rich fens. The different water chemistry among
fens was first thought to reflect an east-west gradient across the
state. Currently, researchers feel it is more likely due to
differences in the
nature of the geology of the sites. Water-response to rainfall. A
fens's response to rainfall is related to its geological setting.
Moisture levels in eastern Iowa fens tend to reflect the current
quantity of rainfall. Most eastern fens are drier during drought
periods and recover quickly
after wet periods because the geological materials around the
groundwater sources allow water to move rapidly through to the fens
after a rainfall. At the same time, these materials do not hold
water
well enough and the groundwater storage volume is not large enough to
maintain moisture levels during droughts.
Some western Iowa fens have geological materials surrounding them that cause water to move through more slowly. These materials hold water better and the groundwater sources can store more water. These conditions can help maintain a more constant moisture level and cause a more delayed response to changes in rainfall patterns.
Plant life
Certain species of plants, such as beak-rush, Grass of Parnassus, and
brook lobelia, can be used as indicators of fens. (click
for scientific names of plants) Of those plant species peculiar
to fens, 80 percent occur in both eastern Iowa and western Iowa fens.
These include upright sedge, inland sedge, bull sedge, purple-stemmed
aster, flat-topped white aster, Muhly, and Grass of Parnassus. Most
fens in Iowa are dominated by upright sedge.
However, some well-developed western fens contain a variety of dominant sedges that include water and beaked sedge. Beak-rush also is frequent in western fens, but not in eastern fens. There are a number of forbs found in eastern fens that are rare or absent in western fens. These include marsh-marigold or cowslip, swamp saxifrage, sensitive fern, and marsh fern. Eastern fens have twenty-two species of trees and shrubs while western fens contain only two.
It is likely that the differences in plant populations found in
eastern and western fens are due chiefly to differences in climate
and moisture, though variations in geology and water chemistry may
also play a part. In some individual cases, plant population
characteristics may reflect land use, such as loss of plant species
due to grazing.
Iowa fens shelter more than 200 species of wildflowers, some of which
only live in fens. This encompasses approximately 13 percent of the
state's native wildflowers. Recent searches of fens have discovered
over 20 species of plants that are considered rare in Iowa. Three of
the species had previously been listed as extirpated (gone from the
state completely). State endangered plants (species in danger of
being extirpated) found in fens include bog bedstraw and bogbean. The
seven state threatened plants (species becoming very rare in the
state) found in fens are bog birch, yellow monkey flower, beak-rush,
narrow-leaved fringed gentian, bog willow, small arrow grass, and
large arrow grass. State special concern plant species found in fens
are valerian, brook lobelia, tall cottongrass, and sage or hoary
willow. These plants are listed so that they will be more closely
studied and monitored in the state.
Zonation of plants is an unusual phenomenon found in fen plant communities. Plants in fens can be grouped into three distinct zones: the discharge zone, the sedge mat zone, and the border zone (see Figure 2). Much like the concentric growth rings in a tree trunk, the first zone forms around the groundwater seepage area, the second zone forms around the first, and the third around the second. Actual presence af all three zones, as well as how distinctly they are defined, varies among fens. In Iowa, only a few large, well-developed fens such as Silver Lake and Excelsior fens in the northwest, fully demonstrate this phenomenon. Some other western Iowa fens have three zones, but the sedge mat zone is narrow and not as well defined. Zonation becomes less distinct in fens from west to east across the state. Eastern Iowa fens are primarily made up of border zone with small discharge zones, if any. Most do not have sedge mat zones.
Animal Life
All wetland types are important habitat for a large number of
wildlife species. Many birds, such as the sora rail, yellow-headed
blackbird, marsh wren, and common snipe depend on fens and other
wetlands. Fens have been found to shelter a great variety of
butterflies. This includes the rare Baltimore checkerspot butterfly.
Unique communities of microscopic border zone plants and animals,
such as diatoms, also have been found in fens.
Formerly, fens were thought to occur only in northwest Iowa. However, fens in Iowa include some peaty wetlands found in the northeastern part of the state. A statewide fen inventory found 200 fens in 37 Iowa counties. The search identified many other possible fen sites that had been destroyed by cultivation, grazing, mining, or impoundments.
Of the 200 existing fens, about 25 are considered high quality--those that have suffered little or no damage, and exhibit a large number and wide variety of plant species characteristic of fens. Ranging in size from less than 1/2 acre to 25 acres, most of these fens are located in privately owned pastures surrounded by cropland.
This location has been detrimental to fens. Most have been altered in some way through grazing or drainage for farming. Damage to fens from direct use as a water source for livestock, mining for peat or gravel, or from runoff and drift of pesticides and fertilizers from surrounding fields. These are major threats to Iowa's remaining fens unless something is done soon. The future of this rare wetland type is entrusted to your hands--the landowner."
Financial assistance
Some landowners are in a financial position that allows them to set
this land aside or sell the fen property. And there are various
programs that provide cost assistance for doing so.
Acquisition of property such as fens is a high priority for some agencies and organizations. The Iowa Department of Natural Resources is active in acquiring fens for the state from willing sellers. Private organizations such as The Nature Conservancy, the Iowa Natural Heritage Foundation, and Pheasants Forever also work toward buying fens. Rather than managing the fens themselves, these organizations sometimes turn them over to the local County Conservation Board.
However, the landowner may not wish to sell. When a fen is located, for example, in the middle of pasture or cropland, it is not convenient to sell a small parcel. When the landowner does not wish to sell, but does want to maintain the fen in its native state, there are options that provide tax credits for the landowner. These include conservation easements that allow the landowner to retain ownership and the right to use the property in ways agreed upon with the agency providing the easement payment. The landowner may use the land for recreation such as bird watching, but may not farm, drain, or fill the fen. In return, the landowner benefits by retaining ownership of the property, gaining tax benefits, and controlling access. The easement is usually permanent to ensure that the land is maintained as a natural area.
Reserved life estates are another way of setting aside property. The landowner gives the deed to the land to a qualifying organization, but reserves lifetime use of the property. Again this use must not destroy the natural state of the property. Reserved life estates also provide the landowner with tax benefits. For more options, see the booklet: The LandownerÕs Options: a guide to the voluntary protection of land in Iowa, available from the Iowa Natural Heritage Foundation, Des Moines, Iowa 50319, (515) 288-1846.
Technical assistance
For help in managing fens or in identifying plants, there is a wide
range of assistance available. The primary source is the Bureau of
Preserves and Ecological Services, Iowa Department of Natural
Resources, Wallace State Office Building, Des Moines, IA 50319, (515)
281-3891 (technical assistance, fen inventory, initial management
plans). Other sources include:
Tne of the primary techniques in fen management is avoiding land-use practices that are damaging to fens, such as grazing, draining, or tilling the fen. Also avoid farming practices outside the fen that allow excessive soil and chemical runoff and pesticide drift.
Attempts at draining fens for farming can cause irreversible damage, as well as often being illegal. The real tragedy is that after spending a large quantity of money tiling a fen to drain it, the land often remains wet. The land is still untillable and the fen is lost. Therefore, it is important to avoid trying to crop these areas.
Livestock grazing and watering also can damage fens. Many fens are located in pastures that are grazed by cattle. Some landowners allow cattle access to fens. In wet years, cattle do not venture far into the fen because of the wet, unstable ground. However, during dry years, cattle trampling can cause uneven surfaces and trails that allow undesirable exotic weeds to invade the fen. It is best to fence off the fen and devise an alternative water source.
Protect water quality
In a recent study of 20 Iowa fens, it was found that some of the most
important techniques in managing fens were those that managed the
land around the fen. In particular, land management practices that
safeguard water quality help maintain quality fens. Because many fens
have row crops upslope from them, it is critical to protect fens from
the runoff or drift of agricultural chemicals. Of 20 fens studied, 10
contained pesticides and 14 exhibited high levels of nitrates. These
chemicals can be harmful to the wildlife and plants of the fen.
Excess nitrogen and herbicide runoff, with resultant changes in pH,
can weaken and kill sensitive plant species, making room for the
invasion of less desirable species. Pesticides can affect wildlife in
many ways. For more information see the ISU Extension brochure:
Agricultural Pesticides and Wildlife: A Balancing Act .
Buffer strips of grass at least 20 feet wide (preferably 66-99 feet wide), can help reduce the quantity of chemicals carried into fens from nearby farming areas. Buffer strips are most effective when used in conjunction with other farming practices that help reduce runoff. These practices include conservation tillage, strip cropping, and terracing. Because fens get their water directly from the groundwater, farming practices that reduce the quantity of fertilizer and pesticides entering groundwater sources will reduce the quantity that enters fens. Crop rotations and use of Integrated Pest Management (IPM) are among these practices.
Control weeds and woody vegetation
We are still learning about the best way to maintain fen plant
communities. Researchers are experimenting with careful burning once
every four or five years to remove invading woody vegetation. Burning
must be done only during wet periods so that the organic soils (the
peat) is not burned. Effects of burning on rare insect populations is
a concern that needs further study.
Burning for weed control is not always the best option. Each fen must be considered on an individual basis. Some fens seem to benefit most from careful spot spraying or the mowing of undesirable plants. Woody vegetation can sometimes be controlled by cutting or girdling. Herbicides should only be used when burning, mowing, cutting, and girdling are not effective options.
The timing of control attempts is important to combat certain weed
species effectively. For example, Canada thistle is best controlled
by late spring burns-between May and June. Early spring burns can
actually increase sprouting and reproduction. Annual burns may be
necessary during the first three years of control efforts.
Hand-cutting of individual plants can be an effective control if done
at least three times each year-in June, August, and September.
Careful spot-spraying of the amine formulation of 2,4-D can be used
in heavy infestations. Use all herbicides according to label
directions.
There is wide agreement that maintaining steady water levels, fencing
out livestock, and protecting the fen from runoff and contaminated
groundwater are all critical to maintaining high quality fens. With
your help, Iowans will have this important resource for many
generations to come.
Wetland Plants and Plant Communities of Minnesota and
Wisconsin is a guide to fen plants, including those in Iowa fens.
It can be obtained for $6.50 from Dept. of the Army, St. Paul
District, Corps of Engineers, ATTN: CENCS-LM/SALES AGENT, U.S. Post
Office and Custom House, St. Paul, MN 55101-1479
Vegetation Management Manual and Guidelines for 25 aggressive woody and herbaceous species can be obtained from the Illinois Nature Preserves Commission, 524 So. Second St., Lincoln Tower Plaza, Springfield, IL 62701-1787, (217) 785-8686.
* Nomenclature follows: Reed, Jr., P. J. 1988. National list of
plant
species that occur in wetlands: Iowa. U. S. Fish and Wildlife
Service
Biological Report NERC-88/18. 15. A copy can be viewed at your
local
U.S. Soil Conservation Service office.
To Plant Life
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beak-rush |
Rhynchospora capillacea |
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beaked sedge |
Carex rostrata |
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bog bedstraw |
Galium labradoricum |
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bog birch |
Betula pumila |
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bog willow |
Salix pedicellaris |
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bogbean |
Menyanthes trifoliata |
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brook lobelia |
Lobelia kalmii |
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bull sedge |
Carex lanuginosa |
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bulrush |
Scirpus spp. |
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cattails |
Typha spp. |
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common boneset |
Eupatorim perfoliatum |
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flat-topped white aster |
Aster umbellatus |
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fringed gentian |
Gentianopsis crinata |
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Grass of Parnassus |
Parnassia glauca |
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inland sedge |
Carex interior |
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large arrow grass |
Triglochin maritimum |
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marsh fern |
Thelypteris thelypteroides |
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marsh-marigold or cowslip |
Caltha palustris |
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Muhly or barnyard grass |
Muhlenbergia glomerata |
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narrow-leaved fringed gentian |
Gentianopsis procera |
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northern bog violet |
Viola nephrophylla |
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Olney's bulrush |
Scirpus americanus |
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purple-stemmed aster |
Aster puniceus |
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reedgrass (common reed) |
Phragmites australis |
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sage or hoary willow |
Salix candida |
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sensitive fern |
Onoclea sensibilis |
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small arrow grass |
Triglochin palustre |
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spotted Joe-Pye-Weed |
Eupatoriadelphus maculatus |
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swamp saxifrage |
Saxifraga pensylvanica |
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tall cottongrass |
Eriophorum angustifolium |
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upright sedge |
Carex stricta |
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valerian |
Valeriana edulis |
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water sedge |
Carex aquatilis |
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yellow monkey flower |
Mimulus glabratus |
rohrberg@iastate.edu