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Botanical Inventory of Prairie Ridge State Natural Area, Jasper County,
Illinois
Gordon Tucker1, Sean A. Jones1, Bob Edgin2 and
John E. Ebinger1
1Dept. of Biological Sciences, Eastern Illinois
University
2Illinois Nature Preserves Commission, 9940 E 500th Ave., Newton, IL
62448
Introduction
Although Illinois is known as the “Prairie State,”
grassland habitats come at a premium in Illinois, and so do many grassland
birds. Prairie Ridge is rated as one of the five most significant grassland
habitat complexes in Illinois and is well known for supporting the only
population of Greater Prairie Chickens in the state. Besides the Prairie
Chickens, the site also has the largest wintering and breeding populations of
Northern Harriers and Short-eared Owls in Illinois (Simpson & Esker 1997). Also
breeding on the site are King Rails, American Bitterns, Upland Sandpipers, and a
growing population of Henslow’s Sparrows, all endangered in Illinois. While the
grasslands and wetlands of Prairie Ridge are the most unique feature of this
area, a wide variety of habitats is nearby, including forested areas and Newton
Lake.
Prairie Ridge State Natural Area comprises about 1100 ha in the Southern Till
Plain Natural Division (Figure 1). The preserve, which was established in 1960,
now includes 15 separate tracts, and is located ca. 10 km S of Newton, Illinois
(Figure 2). Government Land Office Survey notes of 1820 indicate that 87% of the
site was prairie, with the balance forest. Following extensive settlement of
Jasper County, these prairie areas were converted to agriculture.
There is abundant information on the site’s fauna, especially breeding birds
(Simpson, 1998). However, only two studies have focused on the plant life. A
natural prairie restoration was studied by Edgin & Ebinger (2000), and the five
tracts of man-made prairie restorations were surveyed by Kessler, Tucker &
Ebinger (2001). In total, these two studies dealt with only about 20% of the
preserve.
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Figure 1. County Map of Illinois, showing the
location of Prairie Ridge in the southeastern part of the state. |
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Figure 2. Map of Prairie Ridge State Natural
Area, Jasper County, Illinois. |
Methods
Our study had two goals: complete inventory
of species and quantitative study of plant communities. In addition to
occasional visits by the authors since 1998, the site was visited by the
authors 25 times during the growing seasons of 2004 through 2006, to
observe and collect plant specimens. Field work covered the growing season
from April through October. Specimens were identified, labeled, and
accessioned into the Stover-Ebinger Herbarium of Eastern Illinois
University. Vegetation sampling of the community was carried out using
standard methods (Mueller-Dombois & Ellenberg 1974). Quantitative
abundance of herbaceous and woody species was determined using standard
methods (Bailey & Poulton 1968). We sampled 12 grassland areas using 50 m
transects.
Results
We found a total of 508 vascular plant species.
Of these, 411 were native. We found two new state records (Penstemon tubaeflorus,
Figure 3, and Schoenoplectus americanus; Tucker 2002). No other state listed
rare species were found. However, we did document a total of 40 new county
records for Jasper County. A number of interesting species was seen, including
two orchids, Platanthera peramoena and Liparis lilifolia. Some genera are
especially well represented. We are not aware of any other site in the state
that has so many species (8) of Asclepias (milkweed) as does Prairie Ridge
(Figure 4). The percentage of exotic species (19%) is substantially less than
that of Illinois as a whole (31%); cf. Mohlenbrock (2002). The average
coefficient of conservatism, following the method of Taft et al. (1997) for
Illinois, was 3.1 for all species and 3.75 for native species only (cf. Figure
5). The average number of species per transect was 12.75 (range: 9 to 18).
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Table 1. Floristic
integrity assessment summary data comparing various prairie tracts at
Prairie Ridge State Natural Area, Jasper County, Illinois |
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Parameter |
Galbreath
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Lew’s |
McGraw
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Frohning
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Fuson |
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Restoration Age (Years) |
7 |
30 |
9 |
1 |
25 |
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Size (Hectares) |
2.4 |
2.0 |
1.6 |
4.0 |
2.4 |
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Total Species Richness |
81 |
62 |
41 |
29 |
29 |
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Native Species Richness |
67 |
50 |
35 |
26 |
20 |
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% Adventive |
17.28 |
19.40 |
14.63 |
10.34 |
31.0 |
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Floristic Quality Index (FQI) |
25.20 |
21.57 |
18.12 |
13.57 |
9.85 |
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FQI (natives only) |
27.75 |
24.04 |
19.58 |
14.33 |
11.85 |
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Mean Conservatism (C) |
2.80 |
2.74 |
2.83 |
2.52 |
1.83 |
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Mean C (natives only) |
3.39 |
3.40 |
3.31 |
2.81 |
2.65 |
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Figure 3 Penstemon tubaeflorus
(beardtongue), a new state record discovered by Bob Edgin at Prairie
Ridge. |
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Figure 4. Asclepias tuberosa, one of
eight species of Asclepias (milkweed) at Prairie Ridge. |
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Figure 5. Comparison of Coefficient of
Conservatism vales (cf. Taft et al., 1998) for selected sites. Solid bars
indicate native species; hatched bars indicate all species. |
Discussion
Grassland communities fell into two types (Table 2): cool season grasslands,
managed by mowing and co-dominated by Festuca arundinacea and Agrostis gigantea
and warm season grasslands, managed by fire or mowing, and co-dominated by
Andropogon gerardii and Sorghastrum nutans. However, Solidago canadensis
was
typically the most abundant species in most sites. The number of exotics that
are genuinely plentiful and widespread at the preserve is small.
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Table 2. Comparison of Warm and Cool
Season Grasslands; Importance values are given for an example of
each type, with summary for all 12 tracts of grasslands at Prairie
Ridge. Exotic species are marked with an asterisk. |
There was no direct correlation between age of the restored site and quality of
the site. Many variables existed between the sites, such as seed source, number
of burns, and other maintenance practices. For example, Lew’s Prairie, the
oldest of the sites, ranked second to Galbreath Sanctuary, the third oldest of
the sites. Lew’s Prairie had a FQI of 21.57, compared to an FQI of 25.20 for
Galbreath Sanctuary. Based on the results of this study, Galbreath proved to be
the best quality of restored prairie at Prairie Ridge State Natural Area.
Techniques applied in this area should serve as a starting point for future
restoration projects.
Exotic Species are sometimes a problem in grassland, forest, and wetlands, and
in site management plans. The number of exotics that are genuinely plentiful and
widespread at the preserve is few. Phragmites australis occurs at one tract in a
localized patch that could be removed. Woody exotics are few in the grassland
areas, apparently effectively controlled by mowing and burning practices.
Future Research Plans: Because the 2005 season included several weeks of
drought, we are making regular visits to Prairie Ridge during the 2006 growing
season, to search for species that may not have been evident last year. Also, we
plan to monitor the wetlands for additional species. A series of vernal pool
wetlands was created last year for amphibian breeding habitat; these sites may
well be a source of additional species.
References
Bailey, A.W. & C.E. Poulton. 1968. Plant communities
and environmental relationships in a portion of the Tillamook Burn, northwestern
Oregon. Ecology 49: 1-13.
Edgin, B., & J.E. Ebinger. 2000. Vegetation of a successional prairie at Prairie
Ridge State Natural Area, Jasper County, Illinois. Castanea 65: 139-146.
Kessler, A., G.C. Tucker, & J.E. Ebinger. 2001. Prairie Restorations at Prairie
Ridge State Natural Area, Jasper County, Illinois. Transactions of the Illinois
State Academy of Science 94: 127-138.
Mohlenbrock, R. 2002. Vascular Flora of Illinois. SIU Press, Carbondale &
Edwardsville.
Mueller-Dombois, D., & H. Ellenberg. 1974. Aims and methods of vegetation
ecology. John Wiley and Sons, New York, New York.
Simpson, S. A. 1998. Prairie Ridge State Natural Area: a grassland bird success
story involving 40 years of cooperation among public agencies, private
conservation organizations and dedicated individuals. Illinois Audubon 266:4-9.
_____ & T.L. Esker. 1997. Prairie Ridge State Natural Area Habitat Plan.
Illinois Dept. of Natural Resources: Division of Natural Heritage. vii + 80 pp.
Taft, J.B., G.S. Wilhelm, D.M. Ladd, & L.A. Masters. 1997. Floristic quality
assessment for vegetation in Illinois, a method for assessing vegetation
integrity. Erigenia 15: 1-95.
Tucker, G.C. 2001. Scirpus sensu lato (Cyperaceae) in Illinois: an update.
Transactions of the Illinois State Academy of Science 94: 53.
Acknowledgements
IDNR site managers Scott Simpson and Terry Esker (IDNR)
Brent Wachholder, Jason Cunningham, April McDonnell, Matt Zmich, Zhi Wei Liu,
Vicky Tucker, Daniel Tucker, and Sarah Tucker for help with field work
Illinois Dept. of Natural Resources (Non-game Wildlife Fund) for major funding
Eastern Illinois Dept. of Biological Sciences for vehicle use and equipment
Illinois Audubon Society, Illinois Nature Preserves
Commission and Illinois Department of Natural Resources for allowing this study
to be conducted on properties under their care.
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