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Soil Characteristics and Microbes Influencing
Establishment of Prairie Species
M. Jernegan, V. Hustad, M. Tonsor, R. Jadhav, G. Ahrens and J. Coons
Eastern Illinois University, Department of
Biological Sciences
Abstract
Illinois is known as the Prairie State, however
prairie that once covered 22 million acres of the state now occupies a mere
0.01% of the original. Restoration of tallgrass prairies often is impeded by
failure to establish diverse native prairie species because of soil
characteristics including both physical and microbial factors. In Coles County
(IL) attempts to establish prairie species in one area between a bike trail and
a road have failed, yet prairie remnants and restored prairie exists at other
nearby sites. Hence the objective of this study was to determine if soil
characteristics or microbes affect emergence of prairie species from soils
collected at these three sites (remnant prairie, restored prairie, and attempted
restoration site). Soil was collected from each site, and analyzed to determine
texture, pH, moisture, organic matter and nutrients. Half of the soil was
autoclaved and the other half was not. Three common prairie species (Chamaechrista
fasciculata, Dalea purpurea, and Monarda fistulosa) were
planted in each type of soil in trays. Weekly observations were made for
emergence, leaf number and height of planted species. Plants from seed bank also
were counted weekly. After four weeks, mass and leaf area were measured. Soil
had more clay, lower organic matter and higher pH at the restoration site than
at remnant or restored prairies. The remnant prairie had higher moisture,
phosphates and sulfates than the other sites. Plants in autoclaved soil tended
to have greater emergence and faster plant development than those in
non-autoclaved soil. Grass and forb emergence in autoclaved soil was reduced
relative to not autoclaved soil. Plants grown in soil from the remnant prairie
developed more rapidly than those in soil from the other two sites. Hence,
problems with establishment at the restoration site may relate to soil
characteristics.
Introduction
The original tallgrass prairie remaining in Illinois
is scattered in small remnants along railroad tracks, in cemeteries and in
restored areas. Prairies began to diminish when European settlers started to
build railroads and houses, stopped using fire, and began to farm the fertile
soil (Miller, 1997; Sampson and Knopf, 1996). In the 20th century, ecologists
realized that tallgrass prairies in the Midwest were diminishing, and
restoration of these historic grasslands began (Allison, 2002; Curtis and
Greene, 1949). Soil conditions are essential to prairie vigor. Microorganisms
including both beneficial ones (mycorrhizal fungi and nitrogen fixing bacteria)
and harmful plant pathogens (fungi and bacteria) are found in soil (McClain,
1997). In Coles County (IL), attempts to establish prairie species in one area
between a bike trail and a road have failed, yet prairie remnants and restored
prairies exist at other nearby sites. The purpose of this study was to determine
if soil characteristics or microbes affect emergence of prairie species from
soils collected at these three sites. Information gained will aid with prairie
restoration efforts.
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Figure 1. Remnant prairie |
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Figure 2. Restored prairie |
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Figure 3. Attempted restored prairie |
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Figure 4. Soil samples from remnant
prairie, restored prairie and attempted restoration site. |
Methods
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The remnant prairie is along an old railroad that is
now a bike trial, the restored prairie was an agricultural field restored to a
prairie, and the attempted restoration site is near a bike path & highway.
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Fifteen soil cores (15-35 cm deep and 2 cm wide)
plus 3 shovelfuls of soil were collected from each site.
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Percent soil moisture, soil nutrients, and organic
matter were determined using protocol from “The Science Source”, Waldoboro,
Maine, Chemical Composition of Soil #2000.
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Soil texture was determined by shaking 5 ml soil, 30
ml distilled water, and 3 drops dispersing solution (Lamotte Chetertown,
Maryland). After 1 week, heights of sand, silt and clay were measured to
calculate percentages of each. Then a soil triangle was used to determine
texture.
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pH was measured with a soil water-slurry mixture
using a Corning pH meter Model 7.
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For plant development studies, half of the soil was
autoclaved for 3 hours and half was not.
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For each site and autoclave treatment, three trays
(10 X 20 X 6 cm) were planted with 20 seeds each of Chamaechrista fasciculata,
Dalea purpurea, and Monarda fistulosa.
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Trays were placed in growth room with light
intensity of 78.3 ± 9 µmol/m2/sec at 25.0 ± 2.1şC.
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Plant species emerging from the seed bank were
recorded as either grasses or forbs.
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After 4 weeks, emergence, height, leaf number, leaf
area, and fresh and dry masses were measured.
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Data were analyzed using two-way analysis of
variance followed by mean separations using Duncan’s multiple range test at 5%
level where appropriate.
Results
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Table 1. Soil traits for different
sites. |
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Table 2. Plant Growth: Soils from
Different Sites
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Table 3. Plant Growth: Soils with Different
Autoclave Treatments
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Table 4. Emergence of Grasses, Forbs and
Planted Species
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Soils of remnant & restored prairies were lower in
clay & higher in organic matter than soil of the attempted restoration site.
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Moisture was highest in the remnant prairie.
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pH was highest at the attempted restoration site.
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Soil nutrients at these sites exhibit no consistent
patterns.
Significance
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Overall growth for Dalea purpurea and
Monarda fistulosa was greater when planted in soil from the remnant prairie
than other sites.
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Growth for Chamaechrista fasciculata was not
affected by site.
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Plants in autoclaved soil grew significantly better
or similar to those in not autoclaved soil.
References
1. Allison, S.K. 2002. When is a restoration
successful? Results from a 45-year-old tallgrass prairie restoration. Ecological
Restoration 20 :10-17.
2. Curtis, J.T. and H.C. Greene. 1949. A study of relic Wisconsin prairies by
the species-presence method. Ecology 30:80-92.
3. McClain, W.E. 1997. Prairie Establishment and Landscaping. Technical
Publication #2. Division of Natural Heritage. Illinois Department of Natural
Resources. Springfield, IL.
4. Miller. R.M. 1997. Prairie underground: The Tallgrass Restoration Handbook
for Prairies, Savannas, and Woodlands. Packard, S. and C.E. Mutel (eds.), Island
Press, Washington D.C. p.23-27.
5. Sampson, F.B. and F.L. Knopf. 1996. Prairie Conservation: Preserving North
America’s Most Endangered Ecosystems. Island Press. Washington D.C. p. 41.
Acknowledgements
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