This post discusses a number of prairie plant species that "should" be at Black Earth Rettenmund Prairie but are not. This discussion is based on a review of the various floras that
have been done at Black Earth Rettenmund Prairie over the past 65 years, and on observations
that Kathie and I have made during the past 15 years.
See the table at the end of this post for a complete list of the prairie species known to be present.
See the table at the end of this post for a complete list of the prairie species known to be present.
This outstanding Wisconsin prairie remnant is one of the
jewels of southern Wisconsin, whose study goes back to the work in the early
1950s by John Curtis and students. Kathie and I have been managing this prairie
since 2001, and I have done historical research on the site (Brock, 2014). This
prairie is characterized by its diverse prairie flora and absence from
disturbance. For the past 30 years it has been extensively managed, involving major
and continuous brush and invasive tree control, weed control, and prescribed
burns.
Typical prairie grasses at Rettenmund are big bluestem, side
oats grama, little bluestem, Indian grass, prairie dropseed, and needle grass.
However, the present discussion is restricted to forbs, which are much more
diverse.
Rettenmund Prairie is part of the original southern
Wisconsin prairie along and near Black Earth Creek which was first delineated
by the Federal land surveyors in presettlement 1832 (Section 27 of Town 8N
Range 6E). All except the present 16 acres have now been converted to
agriculture or urban settlement. (This 16 acres is considerably larger than the
4 acre size that Curtis and Greene (1949) decided was the minimum size a prairie
could be and still be reasonably studied floristically.)
In their study of southern Wisconsin prairies, Curtis and
Greene (1949) and Curtis (1959) classified prairie species, based on their
natural distribution, into five categories: dry, dry-mesic, mesic, wet-mesic,
and wet. Henderson (1998), using the Curtis data, followed these same
categories. It should be noted that although most prairie species have an
optimum habitat in one or two of the prairie types, most species are often
found in the other prairie types, generally in reduced amounts. This is
reflected in the Henderson data which give the percentage of prairie stands
across the state in which a given species is found. Henderson’s data are
derived from a computerized analysis of the Curtis data that was carried out by
Umbanhowar (1992). (Computers were not available when Curtis did his analysis.)
Fortunately, all of the Curtis original field data were still available to
Umbanhowar.
Rettenmund Prairie is a typical dry to dry-mesic prairie
with a small amount of mesic habitat. It is mostly a high knoll that sits
between crop fields, but lower areas along the northern edge, and the
north-facing unit itself, are more mesic in character. Only a small area in one
corner has ever been cropped, and cropping ceased about 30 years ago. The
former crop field was planted to prairie about 10 years ago and now has a
diverse species flora, with emphasis on species the grow well in dry-mesic to
mesic sites.
Although the prairie flora at Rettenmund is extensive and
diverse, there are a number of species that are missing. The purpose of this
post is to discuss these missing species.
It should be emphasized that no new species have ever been
knowingly introduced here. Seeds have been collected here primarily for
planting back at formerly brushy sites, or in other parts of Rettenmund where
species enhancement was needed. Thus, as far as can be told, we have here the
original native flora
The complete Rettenmund Prairie species list is given at the
end of this post, with their prairie types. The following table lists species
that are missing but, based on their classifications, “should” be there. Each of these species is discussed
separately below.
Species missing from Rettenmund Prairie
|
Curtis/Henderson classification
|
Aster novae-angliae
|
M-WM
|
Astragalus
canadensis
|
M-WM
|
Baptisia alba
|
D-DM-M-WM
|
Baptisia bracteata
|
D-DM-M-WM
|
Ceanothus americanus
|
D-DM-M-WM
|
Desmodium canadense
|
DM-M-WM
|
Desmodium illinoense
|
D-DM-M-WM
|
Echincacea pallida
|
DM-M-WM
|
Heliopsis
helianthoides
|
D-DM-M-WM
|
Lespedeza capitata
|
D-DM-M-WM
|
Liatris pycnostachya
|
DM-M-WM
|
Oxalis violacea
|
DM-M-WM
|
Parthenium
integrifolium
|
DM-M-WM
|
Zizia aptera
|
DM-M-WM
|
Zizia aureus
|
DM-M-WM
|
Astragalus Canadensis
is common in southern Wisconsin and is found in borders, clearings, trails,
roadsides, dry to mesic prairies, and other similar habitats.
Baptisia alba is a
widespread prairie species which, although primarily a mesic species, is often
found on drier prairies. Although found only in southern Wisconsin, it is
widespread here. Also, it is widely planted in prairie restorations, where it
does extremely well. There are habitats at Rettenmund where this species could
thrive, but it seems not to be here.
Baptisia bracteata
is also a widespread prairie species, found from dry to mesic prairies, dry
lime sites, sandy and gravelly sites. A species of the prairies, it “should” be
at Rettenmund, but isn’t.
Although Ceanothus
americanus is often considered a savanna species, it also thrives in dry to
mesic prairies, roadsides, hillsides and banks, and other similar habitats.
This relative of buckthorn is actually a shrub, but where prescribed fire is
frequent it never gets very large. Extensive populations of Ceanothus are present a few miles from
Rettenmund at Pleasant Valley Conservancy, including some thriving native
populations along County Highway F. For some reason, seeds have been unable to
manage the three mile distance along Highway F.
Echinacea pallida
is present as a native in a few southern Wisconsin counties but is widely
distributed in other states south of here, including a wide sweep of states
along the Mississippi River. Also, it is widely used in prairie plantings where
it grows extremely well. Native populations are known within 20 miles of
Rettenmund, yet it has not worked its way here.
Desmodium illinoiense
and Desmodium canadense are prairie
species that do well in dry-mesic to mesic habitats, and are widespread in
Wisconsin. They both are found along roadsides and railroads. According to
Cochrane and Iltis (2000) D. illinoense
“…sometimes persist[s] along grassy, unshaded roadsides and railroads with mixtures
of weeds and prairie or upland-thicket species.” D. canadense, being showy, is widely used in prairie restorations,
where it thrives. Neither species has ever been reported from Rettenmund.
Heliopsis
helianthoides (false or ox-eye sunflower) is common throughout southern and
western Wisconsin, on wet to dry-mesic prairies. Because it flowers early, it
is also widely used in prairie plantings, where it thrives.
Although Lespedeza
capitata has never been reported at Rettenmund, it is widespread in
Wisconsin and the Midwest. According to Cochrane and Iltis (2000) it is
“Wisconsin’s most abundant native legume, common in dry to mesic prairies…”.
According to Cochrane/Iltis, it is an active invader of roadsides, railroads,
old field, and shores. It is easy to grow, is considered a bird attractant, and
is often used in prairie seed mixes. Why isn’t it at Rettenmund? It has
certainly become dispersed all over southern Wisconsin.
Although two other species of Liatris are common at Rettenmund, Liatris pycnostachya is not present. This species is somewhat more
mesic than the other two, and may require deeper soil for establishment.
According to Cochrane and Iltis (2000), Parthenium integrifolium was once common in Wisconsin, primarily at
mesic sites. Because most mesic sites have been converted to agriculture, this
species is now found only on prairie remnants or on planted prairies. Since it
thrives on planted prairies (including those at Pleasant Valley Conservancy) why
hasn’t it become established at Rettenmund?
Oxalis violacea is
widespread in the Midwest and although primarily a mesic species, it is found
frequently in southern Wisconsin and is especially present on prairies,
including goat prairies, prairie glades, and other open habitats. It flowers
early so that it is unlikely to be missed in any floristic study.
Zizia aureus is
another widespread prairie/savanna species, which although most frequently
found in mesic habitats is also present in dry-mesic prairies. A single small
patch of Zizia aureus was actually found
at Rettenmund a few years ago, but did not return the following year. There are
large amounts of Z. aureus along
County F three miles from Rettenmund.
The related species Z.
aptera is also primarily a mesic species but does occur in dry-mesic sites.
Although not now present at Rettenmund, it was reported by Read in 1972 and by
Henderson in 1988.
It should be emphasized that, based on the presence of
existing species, suitable habitats exist at Rettenmund for all these missing
species. Extensive mesic habitat is present on the north-facing hill of the
north unit, where Phlox, Anemone canadense,
Helianthus grosseserratus, and Heuchera
richardsonii are currently thriving. Also, extensive areas of another mesic
species, Thalictrum dasycarpum are
present in the south unit.
Why are these species missing? There have certainly been
enough years for them to become dispersed. All of them flourish at nearby sites,
even in many cases spreading “on their own”. Were they once here in the large
presettlement prairie and when this prairie was fragmented, they were cut off
and disappeared?
Is the Rettenmund habitat unfavorable despite its
suitability for other species, including many typical prairie species.
Is the site too small?
Are these species now dispersing to Rettenmund but are
unable to compete with the already established flora?
Complete species list for Black Earth Rettenmund Prairie
Complete species list for Black Earth Rettenmund Prairie
Common name
|
Prairie type
|
|
Agalinis aspera
|
Rough false
foxglove
|
D-DM-M
|
Agalinis gattingeri
|
Round-stemmed false
foxglove
|
WM
|
Amorpha canescens****
|
Lead-plant
|
D-DM-M-WM
|
Andropogon gerardii****
|
Big bluestem
|
D-DM-M-WM
|
Anemone canadensis
|
Canada anemone
|
WM
|
Anemone cylindrica
|
Thimbleweed
|
D-DM-M
|
Anemone patens
|
Pasque flower
|
D-DM
|
Antennaria neglecta
|
Field pussytoes
|
D-DM-M
|
Antennaria plantaginifolia
|
Plantain pusstoes
|
D-DM-M
|
Apocynum androsaemifolium
|
Spreading dogbane
|
M
|
Apocynum cannabinum
|
Indian hemp
|
M
|
Arabis lyrata
|
Lyrate rock cress
|
D
|
Arenaria stricta
|
Sandwort
|
D
|
Asclepias syriaca
|
Common milkweed
|
DM-M-WM
|
Asclepias tuberosa
|
Butterfly milkweed
|
DM
|
Asclepias verticillata
|
Whorled milkweed
|
D-DM
|
Asclepias viridiflora
|
Short green
milkweed
|
D
|
Aster ericoides
|
Heath aster
|
D-DM-M-WM
|
Aster laevis
|
Smooth blue aster
|
D-DM-M-WM
|
Aster oolentangiensis
|
Sky-blue aster
|
D
|
Aster pilosus
|
Frost aster
|
DM
|
Aster sericeus****
|
Silky aster
|
D-DM
|
Bouteloua curtipendula****
|
Side oats grama
|
D-DM
|
Bromus kalmii
|
Kalm's brome
|
D-DM-M-WM
|
Cirsium discolor
|
Pasture thistle
|
D-DM-M-WM
|
Cirsium hillii
|
Hill's thistle
|
DM-M
|
Comandra umbellata
|
False toadflax
|
D-DM-M
|
Coreopsis palmata
|
Prairie tickseed
|
D-DM-M
|
Dalea candida
|
White prairie
clover
|
DM
|
Dalea purpurea****
|
Purple prairie
clover
|
D-DM-M
|
Dodecatheon meadia
|
Shooting star
|
D-DM-M-WM
|
Erigeron strigosus
|
Daisy fleabane
|
D-DM-M-WM
|
Eryngium yuccifolium
|
Rattlesnake master
|
DM-M
|
Euphorbia corollata****
|
Flowering spurge
|
D-DM-M-WM
|
Euthamia graminifolia
|
Grass-leaved
goldenrod
|
M
|
Fragaria virginiana
|
Wild strawberry
|
DM-M
|
Galium boreale
|
Northern bedstraw
|
DM-M
|
Gentiana puberulenta
|
Prairie gentian
|
D-DM-M
|
Gentianella quinquefolia
|
Stiff gentian
|
DM-M
|
Geum triflorum
|
Prairie smoke
|
D-DM-M
|
Helianthus grosseseratus
|
Saw-tooth sunflower
|
DM-M
|
Helianthus occidentalis
|
Western sunflower
|
D-DM-M-WM
|
Helianthus pauciflorus
|
Showy sunflower
|
D-DM-M
|
Heuchera richardsonii
|
Prairie alum-root
|
D-DM-M
|
Hypoxis hirsuta
|
Yellow star-grass
|
DM-M
|
Koeleria macrantha
|
June grass
|
D-DM-M
|
Kuhnia eupatorioides
|
False boneset
|
D-DM
|
Lactuca canadensis
|
Wild lettuce
|
D-DM-M
|
Lechea stricta
|
Prairie pinweed
|
D-DM
|
Liatris aspera
|
Rough blazing star
|
D-DM-M-WM
|
Liatris cylindracea
|
Dwarf blazing star
|
D-DM
|
Lilium philadelphicum
|
Wood lily
|
D-DM-M
|
Linum sulcatum
|
Yellow flax
|
D-DM
|
Lithospermum canescens
|
Hoary puccoon
|
D-DM
|
Lobelia spicata
|
Pale spiked lobelia
|
D-DM-M
|
Lythrum alatum
|
Winged loosestrife
|
M-WM
|
Maianthemum racemosum
|
False Solomon's
seal
|
DM-M
|
Monarda fistulosa
|
Wild bergamot
|
D-DM-M-WM
|
Oenothera biennis
|
Evening-primrose
|
D-DM-M-WM
|
Panicum leibergii
|
Prairie panic grass
|
D-DM-M-WM
|
Panicum oligosanthes
|
Few flowered panic
grass
|
D-DM-M-WM
|
Panicum perlongum
|
Long-leaved panic
grass
|
D-DM-M-WM
|
Pedicularis canadensis
|
Wood betony
|
D-DM-M
|
Pediomelum esculentum
|
Prairie turnip
|
D-DM
|
Phlox pilosa
|
Prairie phlox
|
DM-M-WM
|
Physalis heterophylla
|
Clammy ground
cherry
|
D-DM
|
Physalis virginiana
|
Virginia ground
cherry
|
D-DM-M
|
Polygala sanguinea
|
Field milkwort
|
DM-M-WM
|
Polygala senega
|
Seneca snakeroot
|
DM-M-WM
|
Polygonatum biflorum
|
Solomon's seal
|
D-DM-M-WM
|
Potentilla argute
|
Prairie cinquefoil
|
D-DM-M-WM
|
Prenanthes racemosa
|
White lettuce
|
DM-M
|
Pycnanthemum virginianum
|
Common mountain
mint
|
DM-M-WM
|
Ratibida pinnata
|
Yellow coneflower
|
D-DM-M-WM
|
Rosa spp.****
|
Rose
|
D-DM-M-WM
|
Rudbeckia hirta
|
Black-eyed Susan
|
D-DM-M-WM
|
Schizacharium scoparium****
|
Little bluestem
|
D-DM-M-WM
|
Silphium integrifolium
|
Rosinweed
|
D-DM-M-WM
|
Silphium laciniatum
|
Compass plant
|
D-DM-M-WM
|
Sisyrinchium campestre
|
Blue-eyed grass
|
D-DM-M-WM
|
Solidago canadensis
|
Canada goldenrod
|
DM-M
|
Solidago gigantea
|
Late goldenrod
|
DM-M
|
Solidago juncea
|
Early goldenrod
|
D-DM-M
|
Solidago missouriensis
|
Missouri goldenrod
|
D-DM-M-WM
|
Solidago nemoralis
|
Old-field goldenrod
|
D-DM-M-WM
|
Solidago ptarmicoides
|
White goldenrod
|
D-DM-M
|
Solidago rigida****
|
Stiff goldenrod
|
D-DM-M-WM
|
Solidago speciosa
|
Showy goldenrod
|
D-DM-M-WM
|
Sorghastrum nutans
|
Indian grass
|
D-DM-M-WM
|
Spiraea alba
|
Meadowsweet
|
M
|
Spiranthes cernua
|
Nodding lady's
tresses
|
M-WM
|
Sporobolus heterolepis****
|
Prairie dropseed
|
D-DM-M-WM
|
Stipa spartea
|
Needle grass
|
D-DM-M-WM
|
Thalictrum dasycarpum
|
Purple meadow-rue
|
M-WM
|
Tradescantia ohiensis
|
Common spiderwort
|
D-DM-M-WM
|
Verbena stricta
|
Hoary vervain
|
D-DM
|
Veronicastrum virginianum
|
Culver's root
|
D-DM-M-WM
|
Viola pedata
|
Bird's foot violet
|
D-DM-M-WM
|
Viola pedatifida
|
Prairie violet
|
D-DM-M-WM
|
Zigadenus elegans
|
White camas
|
D-DM-M-WM
|
The marked species
are the 10 most widespread species for dry lime prairies (Curtis and Greene,
1949)
D: dry; DM:
dry-mesic; M: mesic; WM: wet mesic
|
Brock, Thomas D. 2014. Legacy effects in prairie
restoration: a 73-year spatial history. Proceedings of the North American
Prairie Conference 23: 15-20.
Umbanhowar, C.E. Jr. (1992). Reanalysis of the Wisconsin
prairie continuum. American Midland Naturalist 127: 268-275.
Curtis, J.T. and Greene, H.C. 1949. A study of relic
Wisconsin prairies by the species-presence method. Ecology 30: 83-92.
Curtis, J.T. 1959. The Vegetation of Wisconsin.
University of Wisconsin Press, Madison, Wisconsin.
Henderson, Richard. A. `998. Plant species composition of
Wisconsin prairies. Technical Bulletin No. 188, Wisconsin Department of
Natural Resources, Madiosn, Wisconsin.
Cochrane, T.S. and Iltis, H.H. 2000. Atlas of Wisconsin
Prairie and Savanna Flora Technical Bulletin No. 191, Wisconsin Department
of Natural Resources, Madison.
Though I have no proof to back-up this claim, I have little doubt that a remnant prairie flora also harbors remnant prairie soil biota which strongly influences the above-ground plant species composition. To me, it stands to reason the interrelationship of countless species of bacteria, fungi, nematodes, etc etc, that influence the rhizosphere is just as old and highly developed as the plant species themselves that grow in the soil.
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