In summer 2020, Team Echinacea established two plots south of experimental plot 8 for a pilot experiment examining fire effects on Big bluestem (Andropogon gerardii) reproduction. Neither plot was burned during 2020. During spring 2021, we randomly selected the western plot to be burned. In spring 2022, we burned the eastern plot. Spoiler: there was a very distinct rectangular patch of flowering Andropogon where we burned this year. We are very curious whether pollination also improved in this dense patch!
In summer 2022, we revisited the 23 random points in both the eastern and western plots. We counted the number of flowering Andropogon culms within a circular 1m2 subplot centered on each random point (within 56.4 cm) and harvested all seed heads within the subplot. Circle 18 in the eastern plot had the highest count: 96 culms.
Elif x-rays Andropogon in the lab
In the lab, Elif has been developing a protocol for cleaning and x-raying Andropogon. She x-rayed the Andropogon that we harvested in 2020 and 2021, and she found quite a bit of variation in seed set. Stay tuned for more details!
Samples or specimens collected: Seed heads collected from 2020, 2021, and 2022 are currently stored in Jaredâs office. The 2022 heads have been dried and will be cleaned/x-rayed to quantify seed set.
Products: Stay tuned!
You can read more about the Andropogon fire and flowering in exPt08 experiment, as well as links to prior flog entries about this experiment, on the background page for this experiment.
As part of the Echinacea Project’s long-term efforts to monitor reproductive fitness in the remnant populations, we harvested 330 Echinacea seed heads from 23 remnants during summer 2022. We randomly selected 15 heads from each population where we conducted phenology. If a population had fewer than 15 flowering plants, we harvested a randomly selected head from all flowering plants. In the fragmented populations we study, flowering plants often fail to produce viable seed due to limited mating opportunities. By harvesting seed heads and quantifying seed set, we can better understand how the spatial location and flowering phenology of Echinacea contribute to reproductive fitness.
We are keenly interested in understanding how fire influences reproductive outcomes in fragmented prairies. To this end, we harvested seed heads from 7 populations experimentally burned during spring 2022. We will examine how fire influences mating opportunities and seed set across different populations ranging in size. The heads harvested in 2022 are currently in the CBG lab. Volunteers and students have cleaned, rechecked, and scanned all 330 heads, and they have randomized and x-rayed 249 of the heads so far. We are making great progress!
Priti randomizes a head from 2022Allen counts Echinacea fruits (achenes)
Start year: 1996
Location: Roadsides, railroad rights of way, and nature preserves in and around Solem Township, MN
Data collected: The master data sheet of harvested heads is located here: ~Dropbox\remData\150_clean\clean2022\rem2022MasterDatasheetWithLetNos.csv
Samples collected:Â 330 seed heads were collected and are currently at the Chicago Botanic Garden lab.
Products:Â
We will compile seed set data from 2022 into a dataset with seed set data from previous years.
Padmini, a student from Carleton College, used some of the remnant data for her externship project this winter.
You can read more about reproductive fitness in remnants, as well as links to previous flog entries mentioning the experiment, on the background page for this experiment.
In late summer 2021, we began collecting data in remnant patches of prairie to quantify fire effects on the reproduction of Big Bluestem (Andropogon gerardii). In summer 2022, we revisited the same 378 random points across 27 remnant patches and counted the number of flowering Andropogon culms rooted within 1 m of the random point. Across the 378 plots, we counted 2442 culms. The highest density we observed was 197 culms in one plot at Loeffler Corner West, which beats our record from last year, 163 culms at KJs.
We also collected seed heads from all culms within 1 m of the random points to x-ray and quantify seed set. We initially visited random points on September 8, but some of the Andropogon was not ready to harvest, so we returned a few days later. We finished harvesting on September 19. In the lab, Elif has been developing a cleaning and x-ray protocol for Andropogon. Stay tuned for more details!
Manogya harvests Andropogon at Loeffler Corner West
Start year: 2021
Location: Patches of remnant prairie in and around Solem Township, MN
Data collected: Field datasheets are located in Dropbox: ~burnRems\remAndro\fieldData2022\remAndro2022DataSheet.scanned.pdf. We still need to do data entry.
Samples or specimens collected: Seed heads collected during summer 2022 are currently in the seed dryer but will reside in Jaredâs office. These samples will be cleaned, processed, and x-rayed to quantify seed set.
Products: Stay tuned!
You can read more about the Andropogon fire and flowering in remnants experiment, as well as links to prior flog entries about this experiment, on the background page for this experiment.
In summer 2021, Team Echinacea collected data on 70 Green Milkweed (Asclepias viridiflora) plants across 8 patches of remnant prairie in our study area in western MN. During summer 2022, we revisited these same individuals and found 58 additional plants. We collected demographic data on all 128 plants and harvested 52 seed pods. We will score ovules to quantify what proportion contain embryos, grow seedlings, and sow seed in western MN to propagate this species.
In addition to our reproductive and demographic work, we began collaborating with Mary Ashley and her group at the University of Illinois at Chicago to learn more about the genetic structure and mating patterns of green milkweed in fragmented prairie remnants. We collected tissue samples from 100 plants in the field. Mary’s research group is now extracting DNA and genotyping plants.
Start year: 2021
Location: Remnant patches of prairie in and around Solem Township, MN
Overlaps with:
Data collected: Spatial, demographic, and seed data are housed in the remav Bitbucket repository
Samples or specimens collected:
Seeds: 2022 harvest has been cleaned, counted, randomized, and X-rayed but still needs to be classified.
Tissue samples: tissue samples are at UIC
Products: Stay tuned!
You can read more about the Asclepias viridiflora demography, as well as links to prior flog entries about this experiment, on the background page for this experiment.
In 2021, Team Echinacea established 76 transects (each 4 m long) across 32 patches of remnant prairie in the study area. We planted seeds in one randomly selected segment per transect in fall 2021 but germination trials in the lab and seedling searches in the remnants during summer 2022 revealed that we had used a bad batch of seed đ In fall 2022, we repeated seed addition experiment using seed harvested in summer 2022. Jared harvested Echinacea seed heads from Nice Island and Hutching’s hills. High seed predation from Hutchings left us with 155 heads from Nice Island. Stuart, Lindsey, and Alex sowed seed within randomly selected segments in November 2022. For fall 2022, we added 12 seedling transects (beng, fern, hutch, torge) and eliminated transects at two disturbed sites with the goal of maximizing variation in fire history across the study area. We sowed seed in 84 transects across 36 remnant prairie patches in 2022.
Start year: 2021
Location: 36 patches of remnant prairie in and around Solem Township, MN
You can read more about the Fire and seedling fitness in remnants experiment, as well as links to prior flog entries about this experiment, on the background page for this experiment.
Beginning in summer 2021, we have been studying fire effects on Liatris aspera across patches of remnant prairie in Solem Township, MN. Six of these remnants burned in spring of 2021, and five remnants burned in spring 2022. During 2022, we expanded our efforts and collected data at five additional (smaller sites). The (absurdly) high density of flowering Liatris during summer 2022 led us to establish 1 meter wide, randomly placed transects in many sites. Despite our efforts and stated goal of not mapping as many Liatris as we did in summer 2021 (when we mapped 2400+ flowering plants across 23 remnant patches), we managed to overshoot our 2021 counts by at least 33%. Yes, we mapped well over 3200 flowering Liatris during summer 2022 with but a single functioning GPS… We harvested seed from 291 randomly selected Liatris.
Start year: 2021
Location: 28 patches of remnant prairie in and around Solem Township, MN
Overlaps with: Foolishness and shenanigans
Data collected: Demographic and spatial data housed in the remla Bitbucket repo
Samples or specimens collected: Harvested seed heads have been dried and are located in Jared’s office. These need to be inventoried, cleaned, randomized, scored for seed predation, X-rayed, and classified.
Products: Stay tuned!
You can read more about the Liatris fire and flowering project, as well as links to prior flog entries about this experiment, on the background page for this experiment.
In 2022, we collected data on the timing of flowering for 1373 flowering plants (2291 flowering heads) in 23 remnant patches. We identify each plant with a numbered tag affixed to the base and give each head a colored twist tie, so that each head has a unique tag/twist-tie combination, or âhead IDâ, under which we store all phenology data. We monitor the flowering status of all flowering plants in the remnants, visiting at least once every three days (usually every two days) until all heads are done flowering to obtain start and end dates of flowering. In most remnants, we monitor the phenology of all flowering Echinacea. In 2022, record high flowering led us to sub-sample from select sites (namely alf, nwlf, lfe, lfw, lce, and lcw) and exclude some sites (e.g., ri, aa, and a large chunk of alf).
Linking this detailed phenology data with information about seed production will help us understand how the timing of reproduction influences pollination and reproductive fitness. Additionally, we are excited to investigate whether fire synchronizes flowering in remnant populations. Eight of the populations in which we collected phenology data were burned during spring 2022.
Start year: 1996
Location: Roadsides, railroad rights of way, and nature preserves in and around Solem Township, MN
Data collected: We managed the data in the R project âaiisummer2022Ⲡand will add the records to the database of previous yearsâ remnant phenology records. The 2022 phenology data set needs to be cleaned and prepared for integration with phenology data from previous years and is still located in the aiisummer2022 repo.
Products: Stay tuned!
You can read more about the Flowering phenology in remnants project, as well as links to prior flog entries about this experiment, on the background page for this experiment.
After a foolhardy effort to single-handedly census every flowering Lilium philadelphicum across Solem Township in 2021 and threatening the global supply of orange pin flags in the process, Jared came to his senses and focused on Echinacea in summer 2022… oh who are we kidding, Jared mapped a bunch of lilies in summer 2022. Rather than census flowering plants, Jared established seven 60 x 40 meter plots across sites with varying burn histories and mapped all flowering plants within those study plots (N = 361 flowering individuals). Pods were harvested from 23 plants.
Echinacea who?
Start year: 2021
Location: Remnant patches of prairie in and around Solem Township, MN
Overlaps with: Sleep
Data collected: Spatial and demographic data housed in the remlp Bitbucket repository
Samples or specimens collected: Pods/seed collected during summer 2022 currently reside in Jaredâs office. These seeds need to be cleaned, counted, and scored for seed set.
Products: Stay tuned!
You can read more about the Lilium fire and flowering project, as well as links to prior flog entries about this experiment, on the background page for this experiment.
During summer 2021, we began collecting data in remnant patches of prairie to quantify fire effects on the reproduction of Porcupine grass (Hesperostipa spartea). In summer 2022, we decided against collecting further data. A few very late spring burns that seemed to affect Hesperostipa, our smaller than expected summer crew, and a long list of projects led us to conclude it would be better to prioritize other projects.
Start year: 2021
Location: Remnant patches of prairie in and around Solem Township, MN
You can read more about the Fire and seedling fitness in remnants experiment, as well as links to prior flog entries about this experiment, on the background page for this experiment.
Between June 3 and June 12 (2022), members of the Echinacea Project planted 503 Green Milkweed (Asclepias viridiflora) seedlings across four sites in Solem Township. These sites included an area south of Experimental Plot 8 (149 seedlings planted June 3), a hilltop at Hegg Lake WMA (117 seedlings planted on June 9), a disturbed area at Staffanson Prairie Preserve (117 seedlings planted on June 10), and a hilltop at Eng Lake WPA (aka eth, 120 seedlings planted on June 12).
I promise this photo contains a green milkweed seedling we planted…
We hope these seedlings grown from locally-collected seed will establish new thriving populations of this declining plant species and provide a reliable seed source for future restorations. They may even provide future research opportunities to learn about the reproductive biology and demography of green milkweed! Thanks to the MN DNR, the Nature Conservancy, and USFWS for giving us permission to plant seedlings.
This lovely bee is the 610th insect that we collected this summer for the Pollinators on Roadsides project. There's only one container of bees left to pin! This project is funded by @mnenrtf. https://t.co/VgJYZGbdo8
