Effects of the soil microbiome on the demography of two annual prairie plants

Abstract Both mutualistic and pathogenic soil microbes are known to play important roles in shaping the fitness of plants, likely affecting plants at different life cycle stages. In order to investigate the differential effects of native soil mutualists and pathogens on plant fitness, we compared survival and reproduction of two annual tallgrass prairie plant species (Chamaecrista fasciculata and Coreopsis tinctoria) in a field study using 3 soil inocula treatments containing different compositions of microbes. The soil inocula types included fresh native whole soil taken from a remnant prairie containing both native mutualists and pathogens, soil enhanced with arbuscular mycorrhizal (AM) fungi derived from remnant prairies, and uninoculated controls. For both species, plants inoculated with native prairie AM fungi performed much better than those in uninoculated soil for all parts of the life cycle. Plants in the native whole prairie soil were either generally similar to plants in the uninoculated soil or had slightly higher survival or reproduction. Overall, these results suggest that native prairie AM fungi can have important positive effects on the fitness of early successional plants. As inclusion of prairie AM fungi and pathogens decreased plant fitness relative to prairie AM fungi alone, we expect that native pathogens also can have large effects on fitness of these annuals. Our findings support the use of AM fungi to enhance plant establishment in prairie restorations.


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REYNOLDS Et aL. individual (in terms of offspring) to the next generation. Complete studies of microbial effects on fitness should integrate survival and reproduction at different stages of the host organism's life (Antonovics & Alexander, 1989;Malmstrom & Alexander, 2016).
Such studies are rare and are not trivial given that the soil microbiome includes diverse organisms and both mutualists and pathogens.
Microbes that are often mutualistic include types of nitrogen-fixing bacteria (Rhizobium, Azospirillum) and arbuscular mycorrhizal (AM) fungi. The latter group of fungi form particularly important associations with the roots of host plants, providing water and phosphorous in exchange for sugars produced by the plant and potentially providing resistance to pathogens (Smith & Read, 2008). By supplying the plant with these benefits, AM fungi can greatly increase plant growth (Hoeksema et al., 2018;. AM fungal species are, however, not always mutualists. The degree to which a particular plant-AM fungal interaction is mutualistic or pathogenic depends on the plant species, AM fungal species, and abiotic factors such as soil nutrient and water availability (Cheeke, Zheng, Koziol, Gurholt, & Bever, 2019;Hoeksema et al., 2018;Johnson, Graham, & Smith, 1997;Jones & Smith, 2004). Most work on plant-AM fungal interactions has focused on agronomic plants; there have been fewer studies of the effects of AM fungi on demography of wild plants. Notably, work by Koide and coauthors has demonstrated that the presence of AM fungi can have large positive effects on plant reproduction, seed size, and germination of Abutilon theoprasti (Koide & Dickie, 2002;Stanley, Koide, & Shumway, 1993). While the identity of AM fungal species has been shown to have large effects on plant growth (Cheeke et al., 2019;Koziol & Bever, 2016), less is known on the importance of AM fungal species composition on elements of plant demography.
Soil pathogens also have diverse effects (Ampt, van Ruijven, Raaijmakers, Termorshuizen, & Mommer, 2019;Jarosz & Davelos, 1995;Thrall et al., 1997). For example, infection by Pythium can lead to increased seed and seedling mortality and decreased seedling growth (Alexander & Mihail, 2000;Hendrix & Campbell, 1973;Mills & Bever, 1998). In India, a build-up of a soil-borne fungus, Fusarium semitectum, under an introduced weedy plant resulted in suppression of plant height in native and naturalized plants (Mangla & Callaway, 2007). Much of our inference on the importance of pathogens in plant community structure comes from plant-soil feedback experiments (Bever, Westover, & Antonovics, 1997;Crawford et al., 2019), which have emphasized short assays (e.g., microbe effects on plant growth) as proxies for fitness. Notable exceptions include work by Burns et al. (2017) and Dudenhöffer, Ebeling, Klein, and Wagg (2018), who have focused on entire plant life cycles, including effects of soil microbes on plant reproduction. Miller, Perron, and Collins (2019) have studied feedback at the seed stage.
The demographic effects of microbes on plants are relevant in the tallgrass prairie. For thousands of years, prairies covered much of central North America but this ecosystem was largely lost with EuroAmerican settlement in the mid-1800s and subsequent agricultural use (Samson & Knopf, 1994). Extensive plowing of the soil, as well as chemical treatments, led to postagricultural soils with a degraded soil biotic community (Oehl et al., 2003). Anthropogenic disturbance can favor weedy AM fungal species .
However, small never-plowed remnant prairies do occur with diverse plant and microbial species. Reintroduction of these native prairie soil microbes, through either inoculation with AM fungi or wholesoil additions, can be important in establishing prairie plants in restoration sites in degraded postagricultural soils Lubin, Schultz, Bever, & Alexander, 2019;Middleton & Bever, 2012).
Late successional native plant species have been found to be sensitive to AM fungal species composition and particularly benefit from reintroduction of native AM fungi (Cheeke et al., 2019;Koziol & Bever, 2016Middleton et al., 2015).
Most work on native prairie soil communities has focused on AM fungi. The extent to which loss of native prairie pathogens might affect the establishment of native plants following agricultural disturbance is not known. However, in studies where both early and late successional prairie plants were inoculated with whole prairie soil, there were positive effects of soil addition on plant growth for only the late successional plants (Middleton & Bever, 2012). Native soil pathogens may have disproportionally affected the performance of early successional plants. Indeed, early successional plants appear to be more susceptible to pathogen effects than are their late successional counterparts, perhaps due to the differences in their life history (Bauer, Mack, & Bever, 2015;Herms & Mattson, 1992). Early successional species, including many annuals with rapid growth, may not allocate as much energy to pathogen resistance as longlived later successional plants (that may need pathogen resistance in order to survive long enough to reproduce). Due to these differences between early and late successional plants, pathogen build-up in the soil microbiome may be a driver of ecological succession (Bauer et al., 2015;Kardol, Bezemer, & van der Putten, 2006;Van der Putten, Vandijk, & Peters, 1993). As pathogens accumulate in the soil, early successional plant populations are diminished, and midand late successional plants can begin to grow.
We examined the effects of the soil microbial community on the fitness of two species of annual tallgrass prairie plants. Specifically, we measured both plant survival and reproduction in a field study where plant soil was manipulated. We focused on three soil treatments: native whole prairie soil (never-plowed remnant prairie soil containing both mutualists and pathogens; hereafter, native whole soil), soil enhanced with only native prairie AM fungi (hereafter, native AM fungi-enhanced soil), and uninoculated postagricultural soil. A priori, we expected that plants grown with (a) native AM fungi-enhanced soil to perform better than those in postagricultural soil if AM fungi are acting as a mutualist in the former soil, (b) native AM fungi-enhanced soil to perform better than those in the native whole soil if negative effects of the pathogenic component of the native soil community are greater than positive effects of AM fungi, and (c) the native whole soil to perform better than those in postagricultural soil if the mutualistic component of the community is most prevalent (and the opposite to occur if pathogens dominate the interactions).

| Study organisms
Chamaecrista fasciculata (Fabaceae, "showy partridge pea," Figure 1a) is an annual species commonly found in central and eastern North America (Kartesz, 2015). Mature plants typically grow to heights ranging from 0.15 to 1 m and are found in prairies, old fields, and roadsides (Haddock, Freeman, & Bare, 2015). This species has been well studied from an ecological and evolutionary perspective, including geographic patterns of genetic variation (Etterson, 2004) and root interactions with nitrogen-fixing bacteria (Keller & Lau, 2018). For the latter, Chamaecrista associates with the genus Bradyrhizobium (Parker & Kennedy, 2006;Tlusty, Grossman, & Graham, 2004).
Coreopsis tinctoria (Asteraceae, "plains coreopsis," Figure 1b) is found across central North America (Kartesz, 2015). This annual species is found in prairies, floodplains, and moist disturbed sites and reaches heights of 0.6-1.2 m (Haddock et al., 2015). Inflorescences consist of capitula with many small individual flowers. For simplicity of referring to the same terms for both plant species, we refer to capitula of Coreopsis tinctoria as "flowers." From here onwards, we refer to both plant species by their generic names.
Both species have low coefficients of conservatism (Coreopsis = 1, Chamaecrista = 2) (Freeman, 2014). This scale ranges from 0 to 10; these low values are consistent with the annual plants' ability to establish themselves in recently disturbed areas; later successional perennial plants typically have higher scores (Herman et al., 1997).
Consistent with these coefficients, Coreopsis was one of the first species to colonize areas near forb-sown prairie restoration plots (Jaksetic, Foster, Bever, Schwarting, & Alexander, 2018) and it is a poor competitor with perennial grasses (Elliot & Van Auken, 2014).
Similarly, Chamaecrista is found primarily in disturbed areas, including recently burned or animal-disturbed parts of prairies and roadside habitat (Galloway & Fenster, 2000). Native AM fungi are less likely to benefit the growth of plant species with low coefficients of conservatism ; such plant species are also less sensitive to AM fungal identity (Cheeke et al., 2019;Koziol & Bever, 2016).

| Soil inocula
We had three soil inocula treatments: native whole soil, native AM fungi enhanced, and uninoculated. The prairie soil used for the native whole inoculum was taken from a portion of the Anderson County Prairie Preserve which was to be destroyed for road development in The uninoculated soil was produced by autoclaving prairie soil in a steamer cart for approximately 2.5 hr at a temperature of 76°C. The steaming process was done twice for all of the uninoculated soil in this experiment. Although the soil for this treatment was sterilized in the early stages of the study, we refer to this treatment as "uninoculated" as opposed to "sterile" due to the fact that all Chamaecrista seedlings had rhizobia additions and all seedlings were planted into a postagricultural field environment, and thus experienced a full set of microbes. For the native AM fungi-enhanced soil, AM fungi taken from prairie remnants were added to autoclaved soil. This soil was created with a 1:2 ratio of native AM fungal inocula to autoclaved prairie soil. See Koziol et al. (2018) for details of AM fungal culture methods and Appendix 1 for more details of remnant prairie soil collection and AM fungal inocula species.

| Seedling establishment
Seeds were purchased from Missouri Wildflowers (http://mowil dflow ers.net/) for Coreopsis and Hamilton Native Outpost (https:// www.hamil tonna tiveo utpost.com/) for Chamaecrista. We lack data on the genetic variability present in the seed lots, but the original source of seeds for both species was <300 km from the study site.
Specifically, the Coreopsis seeds were collected from wild plants in Newton County, MO (~275 km southeast of the study site) in 2016 or 2017. Details for Chamaecrista are less certain, but the likely original wild population was a prairie in Gentry County, MO (~150 km northeast of the study site).
Coreopsis seeds were not scarified, while Chamaecrista seeds were scarified by placing the seeds in a bag of coarse sand, followed by vigorous shaking and rubbing. Seeds of both species were then sowed into flats of autoclaved potting soil and placed into cold stratification for 4 weeks. Once the seedlings were large enough (approximately 5.0 cm tall for Chamaecrista and approximately 3.0 cm rosette diameter for Coreopsis), they were planted into groove tubes (98 ml, Stuewe and Sons GT51D) filled with their respective soil type (native whole, native AM fungi enhanced, uninoculated, see above). The Chamaecrista seedlings began to wilt and lose color, so they were treated twice with rhizobia (Bradyrhizobium frederickii and Bradyrhizobium niftali) purchased from Prairie Moon. A mixture of 1.23 ml of rhizobia with 1,000 ml of water was distributed evenly over the ~150 seedlings. After the treatments, seedlings revived and regained healthy coloration. The seedlings remained in groove tubes in the greenhouse for 9-10 weeks before they were transplanted into the field plots.
We lack data on survival from sown seeds to the seedlings that emerged in the flats. We also lack data on survival of seedlings from planting into the groove tubes until seedlings were transplanted into the field plots, although our notes suggest that survivorship was very high for these species.

| Field plots
Seedlings in the three treatments were planted into twice-tilled field plots at the University of Kansas Field Station. The experimental site was historically tallgrass prairie; Kettle, Rich, Kindscher, Pittman, and Fu (2000) examined the General Land Office survey records from 1856 to 1860 and found the site was prairie with no woody vegetation recorded. From at least 1870-1970, the land was in agricultural use with both cropland and pasture (D. Kettle, personal communications). Hence, we refer to the soil as postagricultural. Cool-season nonnative grasses have predominated for the last 50 years. Postagricultural soils such as these do have a microbial community with both mutualists and pathogens. However, AM fungal species in such degraded soils tend to be weedy and less likely to have positive effects on growth of prairie species Koziol et al., 2018). Plots were 1.5 m 2 with 0.5 m aisles between plots within a treatment, and 2 m aisles between soil treatments. The native whole-soil and uninoculated plots each received 75.71 L of soil in the center of each plot, which was then raked in and tilled one more time. The native AM fungal treatments received 3.63 L of AM fungal inoculum onto the tilled postagricultural soil (no autoclaved soil was added to plots in this treatment). Our study was part of a larger study examining the effects of soil types, plant species richness, and plant phylogenetic relationships on plant communities among 18 species across three families (396 plots). We focus here on the 136 plots that had seedlings of Chamaecrista or Coreopsis. The remaining 16 species are perennials and fitness studies thus require multiple years of data.
In each of these plots, 18 seedlings were planted per plot equidistant from each other. These plots included monocultures of Chamaecrista or Coreopsis, as well as plots where each of these species was planted in conjunction with other species. The latter included plantings of 2 species, 3 species, 6 species, and 18 species. Within the 2, 3, and 6 species plots, plots had plants of Chamaecrista or Coreopsis and also other species that were either phylogenetically similar (i.e., other species within the same family) or phylogenetically diverse (i.e., other species from different families). Phylogenetically similar species were from the Fabaceae for the plots, then raked in. No data were recorded for this study from plants germinating from added seed. We focused only on the planted seedlings, which were watered for establishment daily during the first week, every other day for the second week, and every third day for the third week. After 3 weeks, watering was discontinued. See Appendix 1 for experimental details.

| Plant survival and reproduction
We collected data on survival and reproduction of Coreopsis and Chamaecrista by sub-block, 4 weeks after seedlings were transplanted into the field plots (5-25 July 2018). We assessed if plants were present, and if they were flowering. If the plant was determined to be both present and flowering, we counted the number of flowers (defined to include flowers, buds, and seed heads/ pods).

| Seed head collection (only Coreopsis)
We used the plant richness assigned to a plot to determine the number of plants to be sampled per plot (2 plants for mono-, bi-, and tricultures, 1 plant for 6 and 18 species plots). Within a plot, we randomly chose a plant and then collected a sample of mature seed heads where seeds had not dispersed (10% of the previously recorded flower number) on 2-3 August 2018. The harvested seed heads were collected from throughout the plant and placed in a paper envelope labeled with the plant and number of seed heads collected. The envelope was then dried and weighed (to nearest 0.001 g).

| Environmental data
Given that the effects of microbes on plants are often affected by environmental conditions, we determined the centimeters of precipitation at the KU Field Station from 1 January to 31 July 2018 using the CoCoRaHS network (all our data collection was finished in early August). Pooled soil samples from each treatment within each of the six sub-blocks (18 samples total) were analyzed for soil abiotic properties and soil microbial composition. One 2 cm diameter by 20 cm deep core of soil was collected from six plots within each inocula treatment*subblock randomly chosen to represent the six different plant richness treatment (0, 1, 2, 3, 6, and 18 planted species). Soil from the plots was pooled into one sample which was partitioned into one part for analysis of abiotic properties and a second part for extraction of DNA for analysis of microbial composition. Soil texture, pH, organic matter, total C, total N, and total P were analyzed by Kansas State University Soil Testing Laboratory (Manhattan, KS).

| DNA extraction and sequencing processing
DNA was extracted from 0.25 g fresh soil following the manufac-  After sequencing, the primary analysis of raw FASTQ data was processed with the QIIME2 pipeline (Bolyen et al., 2019). Briefly, after demultiplexing and removing primers, sequences were quality filtered, trimmed, denoised, and merged using DADA2 (Callahan et al., 2016). Chimeric sequences were identified and removed via the consensus method in DADA2. The OTUs that only appeared 5 times or fewer across all samples were discarded to preclude inclusion of sequences from potential contamination or sequencing errors. Taxonomy was assigned to all ribosomal sequence variants in QIIME2 using a feature classifier trained with the SILVA 99% OTU database for bacteria (Quast et al., 2012) and the UNITE 99% database for fungi (Version 18.11.2018). Putative pathogens from the fungal community were categorized based on the FUNGuild database (Nguyen et al., 2016), and only OTUs with tropic mode as "Pathotroph" were used for the subsequent analysis. For AM fungal LSU amplicons, we excluded non-AM fungal sequences by generating a phylogenetic tree that included a curated database base of AM fungal sequences (House et al., 2016;Krüger, Krüger, Walker, Stockinger, & Schüßler, 2012) and used sequences with Mortierella elongata as an out-group . On average, 1,401 (398-2,078) quality 16S sequences, 8,490 (3,909-15,914) quality ITS sequences, and 73 (9-253) quality LSU sequences were obtained per sample, and OTU tables were rarefied to a sequencing depth of 398, 3,909 reads per sample for bacterial and fungal communities, respectively, prior to downstream analyses. For AM fungal LSU sequences, one sample was discarded when doing the analyses due to low amplifications, and we did not do the rarefication because of low reads.

| Statistical analysis
Statistical analyses were conducted on two types of plant variables.

| Coreopsis
The analyses for probability of survival were not computable due There were no significant differences among treatments in average mass per seed head ( in plants inoculated with native AM fungi-enhanced soil, approximately 10 times greater than plants in uninoculated plots, and 7 times greater than those in the native whole-soil treatment (Table 2 and Figure 3d).

| Environmental data
The 2018 value (34.87 cm) for 1 January-31 July rainfall was the lowest for the same months in the 10-year period of 2010-2019 (average 56.36 cm). There were no significant differences in soil properties among three inoculation treatments. The soil on average contains 12% sand, 58% silt, and 30% clay, with a pH of 5.90.

| Microbial communities among different soil inoculations
For soil microbial communities (bacteria, fungi, pathogenic fungi, and AM fungi), no significant differences were observed among the three soil inoculations as to Shannon diversity and OTU richness ( Figure A2). The PERMANOVA of bacterial composition did not show differences between inocula treatments ( Figure A3, p = .23); however, we did observe significant differences in composition with inoculation for fungi overall (inoculation treatment pseudo R 2 = .14, p = .011), for pathogenic fungi (inoculation treatment pseudo R 2 = .15, p = .014), and AM fungi (inoculation treatment pseudo R 2 = .14, p = .056). Differences in composition are illustrated using principle component axes that were most sensitive to the inoculation treatment (Figure 4).

F I G U R E 4
Principal component analysis (PCA) ordinations of fungal (a), fungal pathogen (b), and AM fungal (c) communities in three soil inoculations. The two most sensitive axes are shown in the plots. Each dot corresponds to an individual sample, colored by soil treatments. "AMF", "whole soil," and "uninoculated" represent native AM fungal enhanced soil, native whole soil, and uninoculated postagricultural soil, respectively

| Response to arbuscular mycorrhizal fungi
For both annual plant species, the addition of native AM fungi had major positive effects on plant survival, reproduction, and fitness relative to the uninoculated treatment. Additionally, we saw that the native whole-soil treatment had either no effect or a positive effect on plant performance, which suggests that soil mutualists were an important component of the whole prairie soil. The strong positive effects of native AM fungi on annual species in our work are in contrast to other studies that show early successional species to have relatively little response to AM fungal additions or sensitivity to AM fungal composition (Cheeke et al., 2019;. Major positive effects of native AM fungal additions (or native whole-soil additions) have been primarily found in studies of longer living perennial plants Koziol et al., 2018;Middleton & Bever, 2012;Middleton et al., 2015).
Our results are consistent, however, with a recent mesocosm study which found a native annual grass showing strong benefits of locally adapted native AM fungi (Bauer, Koziol, & Bever, 2020). A consistent aspect of our study, and the previous mesocosm study, is that they were performed in an early successional competitive context. As succession proceeds and later successional species are established, it may well be that these same annual species that once benefited from native AM fungi would then be competitively suppressed because of the differential advantage of later successional plant species to native AM fungi.
The effect of AM fungi on plant performance can also depend on the environmental context (Hoeksema et al., 2010(Hoeksema et al., , 2018. Longterm nutrient addition experiments at this site identify that the plant community can be colimited by N and P (B. Foster, personal communication). The fact that native AM fungi led to enhanced annual plant performance is consistent with the fact that the study was done in degraded soil, likely lacking in nutrients like phosphorous. Moreover, there was a severe drought for the duration of this study which may have increased the dependence of plants on AM fungi.

| Response to soil pathogens
We found that Coreopsis and Chamaecrista performed better with native AM fungi-enhanced inocula than with native whole-soil inocula. Given that the native whole-soil inocula likely include both native AM fungi and native soil pathogens, it appears that these early successional annuals were vulnerable to native pathogens. This result is consistent with previous work showing negative effects of native whole soil on early successional plant species (Middleton & Bever, 2012). Moreover, given that pathogens often have host-specific effects that can drive feedbacks (Bever, Platt, & Morton, 2012;Crawford et al., 2019), our results are consistent with evidence of strong negative plant-soil feedbacks on early successional plant species (Bauer et al., 2015). The ratio of host-specific pathogens to mutualists in the native whole-soil type likely largely depends on the presence, and abundance of plant species at the location the soil was taken from. We note that Chamaecrista was present at the source of the remnant prairie soil, but Coreopsis was not (T. Michaels, personal communications). Our use of a soil with history of occupancy with Chamaecrista could have contributed to this plant species' poorer performance in native whole soil relative to uninoculated soil for flower number. In contrast, Coreopsis performed significantly better for flower number in native whole soil than in uninoculated soil, suggesting that the benefits of native AM fungi outweighed the negative impacts of pathogens (Table 2 and Figure 3a-c). Importantly, our evidence of pathogen impacts in this study comes from a single season of growth following tillage of the field plots. It is likely that subsequent years of growth in these same plots will result in even stronger negative impacts due to accumulation of host-specific pathogens (Crawford et al., 2019).
The decreased performance in native whole soil compared to soil enhanced with native AM fungi is consistent with the effects of native pathogens. However, the AM fungal community in the native AM fungi-enhanced soil is also different from that in the native whole soil, as only a subset of the AM fungi present at the prairie from which the soil was derived were successfully cultured. Further, these AM fungal cultures were then supplemented by cultures of AM fungi derived from other prairies. This change in composition of native AM fungi is confounded with the difference in native pathogens in the two treatments and thus creates a second plausible hypothesis for the different response of the two plant species to the native whole soil compared to native AM fungi-enhanced soil.
Environmental sequencing of our experimental plots cannot differentiate the pathogen and AM fungal mechanisms, as it identifies that the inoculation treatments were successful in changing both fungal pathogen and AM fungal composition. Further, we do not know whether the densities of AM fungal spores were similar in the AM fungi-enhanced soil and in the native whole soil. While particular AM fungal species do have differential effects on plant species growth rates, early successional species tend to be less sensitive to different AM fungal species than late successional species (Cheeke et al., 2019;Koziol & Bever, 2016). We also note that late successional plant species responded similarly to the native AM fungal enhanced soil and the native whole-soil inocula (Wagner, unpublished data). This result suggests that differences in AM fungal composition are unlikely to be responsible for the differences between the native AM fungi enhanced and native whole-soil treatments.

| Plant life cycles and importance of soil inocula in prairie restorations
Associations between soil microbes and plant roots likely devel- Future studies should address other factors affecting fitness, such as possible maternal effects (Alexander et al., 2014) or treatment effects on seedlings prior to transplantation into the field site. Although we were unable to obtain seed head mass for Chamaecrista, we did have such data for Coreopsis. We found no differences across the treatments for average mass per seed head.
This could suggest that the number of seeds produced per flower and mass per seed in each soil type is the same even though the intriguing, however, that Koide and Dickie (2002) found that as plant densities increase (as is typical of annual prairie plants in early years of a restoration), the positive effects of AM fungi often decline. Further, soil pathogens that infect these annuals would be expected to accumulate. Given that inoculation of prairie restorations with native soils (with a developed microbial community) particularly benefit late successional prairie species, the overall effects of native soil microbe additions are likely an acceleration of succession in prairie restorations Lubin et al., 2019;Middleton & Bever, 2012). Adding native AM fungi and other microbes to the soil is thus a promising approach for more effective conversion of damaged landscapes into ecosystems that resemble the diverse prairies that were once so abundant in center of North America.

ACK N OWLED G M ENTS
We acknowledge support from the National Science Foundation (NSF DEB-1556664, DEB-1738041, and OIA 1656006). Kristen Mecke, Terra Lubin, Peggy Shultz, and Liz Koziol provided important assistance for this project. We appreciate the input by anonymous reviewers.

CO N FLI C T O F I NTE R E S T
None declared.   Figure A1. While 18 seedlings were planted into each plot, a given plant species would be represented in plots in which it was present as anywhere from 1 to 18 seedlings depending on the species richness treatment (1, 2, 3, 6, 18 species per plot).

Soil collection and source of inocula
Native prairie field soil was collected from a previously unplowed section of Anderson County Prairie Preserve, located approximately 97 km south of the field site. F I G U R E A 1 Experimental design. Eighteen different prairie plant species were planted into plots that included a range of plant species richness (1, 2, 3, 6, and 18) and phylogenetic dispersion levels (within family or between plant family). Each plot included eighteen individual seedlings. Plots were arranged in groupings of twenty-four plots, each of which received the same inoculation treatment. The three inoculation treatments were native prairie whole soil, native prairie AM fungi-enhanced soil, and an uninoculated control. Groupings of 24 plots of each of the treatments were arranged in spatial sub-blocks. Three sub-blocks were grouped into complete blocks, within which each plant species was represented equally within all treatment combinations