Propagation of Wood Betony (Pedicularis canadensis)

Posted on September 15, 2022 by Grassland Restoration Network blog

By Luke Dahlberg, Citizens for Conservation

I have heard from many in the restoration community over a several year period that there has been a “Pedicularis” interest in this plant, and I “wood bet’ony” that any information to continue to restore this species would be helpful (Unlike my cheap plant puns…)

In my continuing journey to understand the growth and development of our native plant species, I wanted to focus on propagating hemi-parasitic plants. This group of plants will attach to and take nutrients from neighboring plant hosts, but they can photosynthesize and take up water and nutrients on their own. I started this process last year with Swamp Betony (Pedicularis lanceolata), and had great results with that initial germination trial. This year, I wanted to step up to the next challenge to try growing from seed it’s close relative, Wood Betony (Pedicularis canadensis)

Found throughout much of the eastern United States and Canada, Wood Betony can be seen growing in prairies, savannas, and open woodlands. Much like Swamp Betony, it is a generalist when it comes to host plant preferences, but it does tend to favor aggressive warm-season grasses such as Big Bluestem (Andropogon gerardii), and Indian Grass (Sorghastrum nutans), and composites such as Goldenrods (Solidago sp.) and Sunflowers (Helianthus sp.).

At Citizens for Conservation and other Barrington Greenways Initiative preserves, Wood Betony is doing quite well in these restorations due to continuous collection and seeding of this species, and frequent burns that may be stimulating seed germination and growth. However, colonies of Wood Betony are still localized and not spreading as much as I thought it would. Their dispersal mechanism doesn’t spread them far and wide, but the plants are stoloniferous. Literature that I’ve read also tends to say that it’s “Difficult from Seed,” meaning that it’s either slow to grow from seed, or it has little to no germination. Like most early-flowering plants, Wood Betony starts going to seed early, usually around Memorial Day week in the area.

Growing research and my personal germination trials have shown that many of these species that go to seed early tend to have increased germination rates where their seed is sown from a week to a month after collecting the seed. If dried for too long, many of these species lose viability quickly or go into a prolonged dormancy where they make take at least two years to germinate. I wanted to know if Wood Betony was in this category. In general, there were several reasons why I wanted this germination trial:

  • Being partially parasitic, I wanted to know if Wood Betony needs a host plant for germination or not.
  • To see If germination increases the following spring by sowing the seed during the summer months or not.
  • If Wood Betony plugs are successfully propagated, they can be planted in dense areas of Big Bluestem (Andropogon gerardii), Indian Grass (Sorghastrum nutans), Canada Goldenrod (Solidago canadensis), Sawtooth Sunflower (Helianthus grosseserratus), Tall Goldenrod (Solidago altissima), and Woodland Sunflower (Helianthus strumosus) where seeding Wood Betony has not worked
  • To find out why it is “Difficult from Seed”

I began the process when I collected seed in June of 2021. One batch of seed went into a treatment of warm, cold, warm stratification in July, about a month after collection. Stratification is basically conditioning of the seed, and this breaks down dormancy mechanisms in the seed so the embryo knows when to germinate. The vast majority of native plants achieve this during the winter months. The second batch I kept dried out and gave them only cold stratification starting in November. For the host species, I chose two species of sedges and a grass. They were Copper-shouldered Oval Sedge (Carex bicknellii), Hairy Wood Sedge (Carex hirtifolia), and Slender Wheat Grass (Roegneria trachycaula).

Similar to how I propagate Swamp Betony from seed, I sowed the seeds of the host species about a month ahead of the betony sowing. This will give the host seedlings time to grow and develop before they have a betony seedling growing along with them. I sowed the Wood Betony in the beginning of April with the sedge and grass seedling in their individual plugs. Germination for the Wood Betony occurred in roughly two weeks from sowing the seed. The seed that was given a warm, cold, warm stratification cycle has nearly 100% germination of the seeds, while the seeds that were only given a cold period did not germinate. Even after a couple of months waiting, that second batch still did not germinate. Did they go into a longer period of dormancy, or lose viability?

I had similar results with the seedlings that did not have a host. Though I had a lot of initial germination, many of the seedlings did not make it to developing leaves. I wasn’t sure if this is normal for Wood Betony, or if it was grower error (usually, it’s the latter). As the growing season continued, the young plants continued to develop, and by the end of July were at a size to plant into the ground. Of the three hosts plants I had, the healthiest and biggest Wood Betony plants had Carex bicknellii as their host species. I plan to overwinter the plants in the plugs and plant them out in the spring either in seedbeds or into areas of dense colonies of Goldenrods and Sunflowers.

From the results I had with this experiment, the seeds of Wood Betony greatly benefit from sowing the seed about a month after collection, similar to the time frame that the plant disperses its seeds. At one of our Citizens For Conservation sites known as Flint Creek South, we sowed Wood Betony seed into a younger savanna restoration, and I’ve seen multiple Wood Betony plants the year after from this early sowing. However other factors may have been in play for good germination such as frequent burning, little competition, and soil conditions that favored the plant. For the backyard gardener, hobby grower, or experienced propagator, growing Wood Betony with the same or similar method will help this bring this important plant into our restorations.

Wood Betony (Pedicularis canadensis) seedlings with Copper-shouldered Oval Sedge (Carex bicknellii) host on 4/18/2022

Wood Betony seedlings sown in a tray without a host. This is from the warm, cold, warm stratification method. The cold stratification batch had no germination. Photo taken 5/02/2022

Wood Betony plants with sedge host on 5/09/2022, about a month after sowing the seed in the greenhouse.

Volunteers helping pot up seedlings. We cannot have the plant plugs that we have without the dedicated time and work from our great volunteers!

Wood Betony plug with sedge host on 6/08/2022

Wood Betony plug with sedge host on 7/22/2022. This plug is large enough to be planted.

Posted in Uncategorized | Tagged , , , , | 22 Comments

GRN workshop a success

Posted on September 8, 2022 by Grassland Restoration Network blog

The workshop was August 16 and 17, 2022 with the Barrington Greenways Initiative, northwest of Chicago.

Partners of the Barrington Greenways Initiative

Four sites were visited over two days, a half day for each site. There are four companion GRN blog posts that were published before the workshop.

Kevin Scheiwiller of Citizens for Conservation leads a tour for the 2022 Grassland Restoration Network workshop. Flint Creek Savanna.

Kudos to Kevin Scheiwiller who was the lead planner for the workshop. The planning team included Justin Pepper, Kristin Dapra, and Kelly Schultz. Many others helped lead tours.

The workshop highlighted a well functioning partnership between agencies, NGOs, and volunteer stewards. There is a long history in this region of people sweating the details as they restore and manage high quality natural areas.

2022 Grassland Restoration Network tour. Poplar Creek Prairie near Barrington, Illinois (Chicago suburb).

In 2023 we will have a workshop in Minnesota with our host Jeffrey Zajac.

Photos by the planning team and Chris Helzer

Posted in Uncategorized | Tagged , , , , | Leave a comment

33 years of community led grasslands restoration in NW Cook County, IL

Posted on July 28, 2022 by Grassland Restoration Network blog

By the Poplar Creek Prairie Stewards

This is the fourth of four introductions to our upcoming field trips for our GRN workshop August 16 and 17. Registration for this year’s GRN closes on 7/31, make sure to get your spot before they are all filled up. https://grasslandrestorationnetwork.org/2022/06/23/1727/

In the northwest of Cook County, the Poplar Creek Prairie Stewards (PCPS) have been working on over 225 acres of grassland restoration of a 4,430 acre protected block of natural area for the past three decades. The Forest Preserves of Cook County (FPCC) purchased a remnant gravel hill prairie and  surrounding agricultural land parcel by parcel throughout  the 1960’s. The gravel hill prairie was dedicated as a state nature preserve in 1965. In 1989, a volunteer group of stewards kicked off with support from The Nature Conservancy and FPCC. The initial goal of the project was to enhance the remnant prairie community and create a botanically rich prairie restoration surrounding the remnant. Early on, the decision was made to restore a large area of diverse, functional prairie plant communities, while balancing the needs of individual animal and plant species.

The Volunteer Stewardship Community found very early on that for a restoration to be successful, the group needed to function in many different capacities. Today, the PCPS has built a sustainable volunteer base that stewards not only the land, but also the community. At the GRN Workshop this August, tour guides will describe how two volunteer led committees oversee the vast restoration project as well as maintain a fun culture of conservation among the volunteer base. The tour will travel through decades of prairie recreation and restoration culminating in the scenic overlook of the Shoe Factory Hill Prairie Nature Preserve. The Stewards in tandem with FPCC Ecologists and Staff maintain original plantings and continue to expand the effort to restore additional swaths of grassland to this expansive corridor.

Topics to be covered during GRN Workshop:

  • Early lessons learned with grassland restoration
    • Use or misuse of tall C4 grasses
    • Strip Planting Technique in which approximately 60 acres were planted among cool season grass with the idea that plantings would eventually invade the cool season dominated areas (see Figure 2)
    • Partnership between FPCC Staff and Stewards
    • Building a community around a restoration
  • Building a Conservation Community around large restoration projects
    • Delegating responsibilities among many leaders
    • The importance of investing in volunteers

Figure 1. Tour Map including Shoe Factory Remnant and Surrounding Grassland Restoration

Figure 2. Strip Planting in Early Years

Figure 3. Poplar Creek Prairie

Figure 4. Shoe Factory Remnant Hill Prairie

Posted in Uncategorized | Tagged , , , | Leave a comment

Restoring grassland birds and healthy prairie at Galloping Hill

Posted on July 22, 2022 by Grassland Restoration Network blog

By Becky Collings, Karen Glennemeier, Justin Pepper, and Daniel Suarez

At the upcoming GRN meeting in Barrington, IL, we will visit a number of local restoration sites, including Galloping Hill in NW Cook County.The focus of this field tour will be our Qualitative Rapid Assessment, described below, but we also wanted to share an overview of the site including the restoration goals and progress and an overview of its management history.

For those that just want the high-level summary of the site, this place is special because it:

  1. Was a first, grassland bird scale, multi-partner restoration aiming for prairie birds in a rich native natural community at the 4000-acre Spring Creek Forest Preserve
  2. Had a strong early grassland bird response, largely sustained for ~17 years
  3. Is becoming a high-quality, dry-mesic prairie restoration with hand collected, local ecotype seed, largely through volunteer stewardship, now expanding from ~20 acres to 60 acres and including wetter habitats surrounding the hill itself.

Management History

In 2005, Audubon, in partnership with the landowner, the Forest Preserves of Cook County as well as Citizens for Conservation, the US Fish and Wildlife Service and the then nascent Spring Creek Stewards volunteer group, launched the restoration of Galloping Hill. The initial size of the grassland restoration project was 110 acres at the heart of the nearly 4,000-acre preserve.

Figure 1. The image above shows the extent of the fragmented 110-acre grassland prior to the project’s start. Note the brush islands in the hay meadow in the NW, the peninsula of brush to the SE of Galloping Hill and the brush on the northwest facing slope of Galloping Hill. Contrast to the following Figure 2. 

Given the scale of the area, habitat restoration at Spring Creek allowed for grassland restorations large enough to be significant for ground-nesting grassland birds. Whereas previous restoration work at Spring Creek had focused on a small remnant prairie, this project was designed specifically with the suite of grassland obligate birds in mind.

A project was designed to reduce fragmentation of the grasslands in the immediate term and to begin restoring healthy prairie habitats in the years ahead.

Initial brush mowing and the removal of trees that had fragmented the grassland occurred over the winters of 2005 and 2006. Bird results were immediate and dramatic, 950% increase of Bobolinks, 650% increase for Meadowlarks in the years immediately following the clearing work. With those encouraging early results, the Spring Creek Stewards, the site’s new volunteer stewardship group, began the decades long project of restoring a diverse prairie. We wanted grassland birds, but in a healthy, native natural community.

Figure 2. In the image above, the initial brush clearing in the haymeadow, on and adjacent to Galloping Hill has been completed. This was a good year for prairie birds at the site. The simple act of restoring grassland structure had immediate results.

Galloping Hill has remained a top priority for seeding within the Spring Creek preserves, even as the Stewards started new restorations (currently managing about 300 acres). Donated by Citizens for Conservation, seed amounts and mixes varied from year to year but were always interseeded into non-native cool season grasses at a very light seeding rate, perhaps averaging 4 lbs per acre. Seeding has been augmented by a few plug plantings through the years, primarily spring ephemerals like prairie violet, violet wood sorrel, Seneca snakeroot, prairie phlox and bastard toadflax. Native cool season grasses including porcupine grass and Lieberg’s and Scribner’s panic grass have also been reestablished.

The focus of the seeding started high and slowly worked down the hill, especially once the drain tiles at this site were mapped and valved in 2011.

Wetland/ Sedge Restoration—Following the 10 Warriors approach, wetland restoration began in earnest in 2018. Since then, more than 10,000 sedge plugs have been planted and reed canary grass has been pursued and treated with grass-specific herbicide.  

Hay Meadow Expansion—in 2020, a 20-acre expansion was initiated in a hay meadow just NW of Galloping Hill which combines with a more recent expansion to the SE to now have about 60 acres under active restoration, not just grassland management.

Figure 3. Though listed as an image from May, I believe this is later in the fall, given the color and the obvious mowed oval in the SE of the image which took place in Sept. of 2021. The extent of the warm-season grasses is evident in the image. The two pocket wetlands are identified, as is the newer planting (Expansion Area 1) volunteers have undertaken and the 20-acre haymeadow (Expansion Area 2) that contractors and volunteers are collaborating on.

Since the initial mechanical work, 90+% of the work has been done by volunteers with support from Conservation Corps, FPCC staff, and occasionally, contractors. The Forest Preserve District has prioritized burning at this site which has been critical to the progress to date. The site has been burned annually since 2005 (16 burns between 2005-2021). Most burns have occurred in the spring with the exception of fall 2009, 2020, and 2021.

How are we doing, and what do we do next?

(a.k.a. Monitoring & Adaptive Management)

Plants – Quantitative Monitoring

Vegetation transects were established early in the restoration and have shown steadily increasing floristic quality, approaching that of our region’s highest quality prairies after just fifteen years of management. 

Figure 4. Two transects have been established at Galloping Hill, Transect 1 is on the south and east facing slope, where turf grass was well established when the project started and Transect 2 is on the north and west facing slow which was much more brush dominated and had thinner turf.
 

The speed and success of the restoration are due to the steady commitment of volunteer stewards, combined with a strong partnership among volunteers, land agencies, conservation non-profits, and contractors. Galloping Hill also has benefited from the experience of earlier restorations including Somme Prairie Grove, Nachusa Grasslands, and Grigsby Prairie.

Plants and overall community – Qualitative Assessment

We have introduced a new approach to adaptive management that we call the Qualitative Rapid Assessment (QRA).  We’ll be sharing this process at our Galloping Hill tour during the conference – here’s the basic idea.  A small group visits an area and begins with 10 minutes of each person individually observing the presence of invasive, conservative and matrix species, as well as the overall diversity and the sense of subjective quality or degradation. Each person assigns a score based on a simple, defined scale.  Then the group convenes and discusses, reaching consensus on a score, but more importantly filling in the reasoning behind that score and, critically, determining what happens next. What’s missing, and how do we bring it back? How is this restoration most likely to go wrong? What’s the management history, does it explain what we’re seeing, do we think our approach needs tweaking? How, if so?

We’ve found that this method produces scores that align with quantitative floristic quality metrics. It deepens participants’ understanding of an area’s condition and management needs. It provides an actionable management to-do list.  And it’s a meaningful, enjoyable exercise for both beginners and experienced restorationists.

Birds

The initial response from the brush clearing was heartening (see Figure 5 below) and while the numbers for individual species have bounced around a bit, Galloping Hill has consistently hosted strong breeding populations of Henslow’s sparrows (14 in 2020) and Bobolinks (34 in 2020).

Monitoring has continued since the project started, but since it has occurred under different protocols, we are not presenting an unbroken sequence of results.

Figure 5. Initial grassland bird response following brush clearing in the winters of 2004/2005 and 2005/2006.

Eastern Meadowlarks, Savannah and Grasshopper Sparrows have declined from high counts in the first 5 years of the project. These three species have also shown significant population declines regionally, as recently reported by the Bird Conservation Network so it is unclear how much of this decline is a local versus regional issue.

Grasshopper Sparrows would benefit grazing or other means to return to early successional habitat, but 2022 was the year of the Grasshopper Sparrow as they were found in multiple places within Spring Creek where they had been absent for years, this includes at least 4 at Galloping Hill.

The decline of Savannah Sparrows and Meadowlarks is a bit more of a puzzle and we welcome thoughts from others on this.

Addendum: The Qualitative Rapid Assessment is available here: https://tnc.box.com/s/t1amflh005fs30yywx2ac65e6l2q9bew

Posted in Uncategorized | Tagged , , , , , , , | 7 Comments

Monitoring vegetation with GIS Field Maps

Posted on July 14, 2022 by Grassland Restoration Network blog

By Bill Kleiman

Arc GIS Field Maps, known previously as Collector, is a powerful phone app. The app is free, but you do need a GIS online program to run it, which typically means you need your employer to support you. On this image you see random round dots of a few colors, each color represents a different invasive weed. There are green diamond shapes which are native plant occurrences, which represent cool plants we want to remember to come back to, perhaps to pick seed. This morning, I noted starry campion for seed picking later.

These dots/waypoints/geo-referenced points….whatever you call them….are really handy. For instance, they help us see the pattern of infestation of weeds where sometimes a strategy can come to mind. Over time we hopefully have fewer weed dots.

Now differently, note the east west line of red dots. Each dot represents at least one birdsfoot trefoil, BFT, Lotus corniculatus. I started on the east end of this field and used my phone compass to aim west and found a district tree to aim for. I took a step, looked down for BFT. If there was a plant, flowering or not, big or small, I dotted it. There was a plant sometime every step, sometime every two steps, but rarely could I go more than 5 steps without a plant within three feet of my boots. This transect took about 45 easy minutes. I tore the plants out that I found as I did not want to carry a sprayer.

Why walk a line instead of recording all occurrences in this field? I don’t have time to record every BFT in this field. That would take a week. The point of monitoring with quadrats, whether on a transect or randomly placed, is to help us understand a field by sampling a small part of it.

I know this field rather well. In the 1980s the farmer planted birdsfoot trefoil in this pasture. The soil became full of BFT seed. Three decades ago I started to boom spray the former pasture. After this decade of boom spraying we erred in deciding to plant prairie in this field. Then we had about two decades of hard labor of back pack spraying BFT, but you can see the BFT is still there. I did this monitoring transect after we had been through the field for eight hours with seven people with packs. So these are the plants we missed. Sigh.

Lesson learned: Do not plant prairie into ground that has invasive weeds.

This method of monitoring with Field Maps is intuitive, visual, easy to understand, and stored automatically with your other data. I don’t need to write a report about these weeds. You can see the pattern as well as I can.

Here I zoom out for a more complete sense of our preserve and its weed occurrences. We spend a lot of time on these spots. How can we get to treating the weeds faster and with less time, but without doing more harm than good? No easy answers, as you know.

Posted in Uncategorized | Tagged , , , , , | 5 Comments

Grassy Lake GRN workshop field trip

Posted on July 7, 2022 by Grassland Restoration Network blog

by Kelly Schultz, Stewardship Ecologist, Lake County Forest Preserves

This post is an introduction of one of four hikes we have for our upcoming GRN workshop.

This 700-acre preserve is home to a high quality sedge meadow, prairie, and mesic woodlands, but you wouldn’t have known that 12 years ago.  Two incredibly dedicated volunteers took on this preserve and have now improved 100 acres, removing mature buckthorn thickets and the tedious small stems, managing cattails, spraying invasive plants, and adding seeds and plants to bring back the missing flora.  Staff and contractors joined the ongoing land management, providing more extensive wetland management, Rx burning, seeding, and planting.  Wildlife staff have rounded out the restoration efforts with deer management, jumping mice, and loosestrife beetles.  Birds flock to Grassy Lake; snipes and orchard orioles have come to call it home.  Tiger salamanders and frogs also live in this preserve, and are thankful for the removal of buckthorn and its emodin.

Much of the work is also thanks to the Barrington Greenways Initiative partnership!  BGI workdays are responsible for several big planting projects, not to mention sowing, collection, and buckthorn workdays.  The BGI restoration crew has been a regular asset in land management and the jointly funded Technician has been working to expand volunteer efforts at this preserve.   

Today you can find dozens of sedges – Carex stricta, pellita, lasiocarpa, interior, lupuliformis, lacustris – rushes – including the state endangered Scirpus microcarpus and more common bulrushes – alongside ferns, yellow and purple loosestrife species, gentians, pale spike lobelia, several milkweed species, and many other pollinator favorites.  The namesake lake is now visible from the trail.  The woodlands have been transformed with brush removal, seeding, planting, and deer management.  The volunteers’ dedication was the impetus for changing our brush pile burning policy across the District (formerly staff only), they have been an inspiration & beneficiary of the BGI partnership, and they were recipients of a national award for outstanding volunteers. 

Come visit this site at GRN!

Interested in registering for the workshop? There may be space. Look at this post with the details: https://grasslandrestorationnetwork.org/2022/06/23/1727/

Before stewards Carol Hogan and Wesley Wolf started work
After a decade of care by the volunteers and Forest Preserve staff
Grassy Lake

Tiger salamander

Posted in Uncategorized | Tagged , | Leave a comment

Warrior Sedge Wetland Restoration by Citizens for Conservation at Flint Creek Savanna

Posted on June 30, 2022 by Grassland Restoration Network blog

By Kevin Scheiwiller

Kevin Scheiwiller

Goals of Project:

  1. Find a technique that can be used to sustainably rebuild streamside marsh, sedge meadow, and seeps in areas formerly dominated by wetland invasives through small trial areas (<1 acre)
  2. If trial plots appear effective, then use this technique on a larger scale (≥ 3 acres) to reclaim wetlands lost to Reed Canary Grass, Cattails, and Phragmites

Measures of success:

Success is defined as the elimination or heavy reduction (>95%) of wetland invasives, with establishment of a diverse matrix of native sedge meadow species.

Technique:

Areas with heavy infestations are herbicided using a 3% glyphosate mixture in the Fall (September through November) of the year prior to planting. Project area is burned in the dormant season after initial herbicide application to remove thatch and flush seed bank. Area is then sprayed a second time with the same mixture in April.

After site prep, areas are planted during volunteer workdays using the 10 warrior sedges (List Below) based on the perceived moisture gradient of the site. Each plug is planted on 2-3 foot centers, tighter if budget allows.

In the Fall (November) areas are then seeded with custom “Sedge Meadow” and “Marsh” seed mixes. All mixes purposely keep native grass species out. This allows for the follow up of the site with a grass specific herbicide.

Two to Five years after original planting, project areas are spot treated for remerging wetland invasives. Reed Canary Grass is sprayed with a 1% Clethodim Solution during Mid-April through May. As no native grasses are present, this allows for quick application with fairly effective results (see GRN post about Clethodim vs. Glyphosate). Cattail and Phragmites are hand wicked in July and August using a 20% Glyphosate solution.

Project Area:

 Plantings over the last 5 years are found on the following map and table. 2017-2020 are considered smaller trial plots. 2021 is considered a larger planting as outline in the Goals section.

PlantingSize of Area (ac)Approx. plugs installed*Overseeded in:Approx. total amount of seed since planting (lbs)**
20170.35–2018, 2019, 202028.75
20180.182,1662018, 2019, 202028.75
20190.381,9002019, 2020, 202119.15
20200.432,1662020, 202121.41
20213.3811,096202192.78
*only includes plugs purchased, additional “rescued” sedges
 and volunteer propagated added to areas as well
**seed weights include some amount of chaff, not PLS

Topics to be covered during Grassland Restoration Network Workshop

  • Visiting each “stage” of a planting from newly planted to 5+ years establishment
  • Successes and challenges presented by each planting area
  • Evaluation of the technique and discussion on the practicality of using it on a large scale
  • Future uses, Erosion Control, and use on incised creeks  

Warrior Sedges

  • Wettest
    • Carex lacustris
    • Carex aquatilis
    • Carex utriculate
    • Carex stricta
  • Intermediate
    • Carex sartwellii
    • Carex trichocarpa
    • Carex atherodes
    • Carex emoryi
  • Driest of the wet
    • Carex buxbaumii

Carex pellita

Seed Mixes Used in 2021, most other years feature a similar mix

Sedge Meadow 

Anemone canadensis Meadow Anemone 
Angelica atropurpurea Great Angelica 
Arnoglossum plantagineum Prairie Indian Plantain 
Asclepias incarnata Swamp Milkweed 
Calamagrostis canadensis Blue Joint Grass 
Carex “Wetland” Misc. Wetland Sedges 
Carex hystericina Porcupine Sedge 
Carex vulpinoidea Brown Fox Sedge 
Chelone glabara White Turtlehead 
Eupatorium perfoliatum Common Boneset 
Euthamia graminifolia Smooth Grass-Leaved Goldenrod 
Eutrochium maculatum Spotted Joe Pye Weed 
Hasteola suaveolens Sweet Indian Plantain 
Helianthus occidentalis Western Sunflower 
Hypericum ascyron Great St. John’s Wort 
Liatris spicata Marsh Blazing Star 
Lobelia cardinalis Cardinal Flower 
Lobelia siphilitica Great Blue Lobelia 
Lycopus americanus Common Water Horehound 
Lysimachia quadriflora Narrow-Leaved Loosestrife 
Lythrum alatum Winged Loosestrife  
Oligoneuron riddellii Riddell’s Goldenrod 
Pedicularis lanceolata Fen Betony  
Pycnanthemum pilosum Hairy Mountain Mint 
Pycnanthemum virginianum Common Mountain Mint 
Rumex orbiculatus Great Water Dock 
Rumex verticillatus Riverbank Dock 
Schoenoplectus pungens Chairmakers Rush 
Schoenoplectus tabernaemontani Great Bulrush 
Scirpus atrovirens Dark Green Bulrush 
Scirpus cyperinus Wool Grass 
Scutellaria lateriflora Mad-Dog Skullcap 
Spartina pectinata Prairie Cord Grass 
Symphyotrichum puniceum Bristly Aster 
Teucrium canadense Germander 
Thalictrum dasycarpum Purple Meadow Rue 
Verbena hastata Blue Vervain 
Vernonia fasciculata Common Ironweed 

Marsh 

Acorus americanus Sweet Flag 
Alisma subcordatum Common Water Plantain 
Bidens cernua Nodding Bur Marigold 
Bidens trichosperma Tall Swamp Marigold 
Boehmeria cylindrica Swamp False Nettle 
Juncus effusus Soft Rush 
Mentha canadensis Wild Mint 
Persicaria hydropiperoides Mild Water Pepper 
Sagittaria latifolia Common Arrowhead 
Scirpus microcarpus Reddish Bulrush 
Scutellaria galericulata Marsh Skullcap 
Sium suave Water Parsnip 
Solidago patula Swamp Goldenrod 
Posted in Uncategorized | Tagged , , , | 7 Comments

2022 GRN Workshop

Posted on June 23, 2022 by Grassland Restoration Network blog

Here is the registration link: https://citizensforconservation.app.neoncrm.com/eventReg.jsp?event=102&

Agenda:

Tuesday August 16th 

8AM – 9AM: Networking and Coffee

9AM- 9:30AM: Introduction and Overview of Barrington Greenway Initiative and the GRN workshop

10AM – 12PM: First Tour Rotation: Four concurrent tours

(We will have four rotations over two days so everybody gets to do all four tours)

12PM – 1:30PM: Lunch and driving to next site

2PM – 4PM: Second Tour Rotation. The same four concurrent tours

5PM -7PM: Pizza, beer, Keynote Speaker: Philip Juras on painting the prairie. See https://www.philipjuras.com/artwork/

Wednesday August 17th

8AM – 9AM: Networking and Coffee

9:30AM – 11:30AM: Third Tour Rotation: The same four concurrent tours

12PM – 1PM: Lunch and driving to next site

1:30PM – 3:30PM: Fourth Tour Rotation: The same four concurrent tours

We have these four tours and guests will be able to participate in all tours on a rotating basis

The four tours:

  • Flint Creek Savanna – Citizens for Conservation – Restoring functioning sedge meadow using the 10 warrior sedges
  • Grassy Lake Forest Preserve – Lake County Forest Preserves – Volunteer-led effort to restore one of the largest remnant sedge meadows in Lake County
  • Spring Creek Forest Preserve – Forest Preserves of Cook County – Large-scale grassland restorations will be evaluated using the “Qualitative Rapid Assessment,” a tool designed for adaptive management and constructive feedback for stewards and land managers.
  • Poplar Creek Prairie – Forest Preserves of Cook County – a remnant gravel hill prairie surrounded by large grassland restorations accomplished over 30 years of community stewardship.
Posted in Uncategorized | Tagged , | 6 Comments

Invasive Reed canary grass control

Posted on June 2, 2022 by Grassland Restoration Network blog

By Bill Kleiman

As described in Plants of the Chicago Region, “Phalaris arundinacea, reed canary grass, is introduced from Eurasia. This grass is planted by farmers for pasture and erosion control. It is very common in marshes and other moist ground, often forming nearly pure stands…”

A past post by Bryon Walters describes how to slowly and methodically apply glyphosate mixed with imazapyr on RCG to limit off target damage. https://grasslandrestorationnetwork.org/2019/06/05/control-of-reed-canary-grass/

Below are two photo of recent treatment of RCG at Nachusa Grasslands.

A riffle with RCG treated with glyphosate and imazapyr a few weeks back. This herbicide mix is approved over water.
Glyphosate & imazpyr on RCG along Wade Creek. Sedges and forbs dominate this section of stream which also has marsh marigold, skunk cabbage, riddel’s goldenrod, and grass of parnassus.

Those who follow this blog (easy to do by clicking the “Follow the GRN” button) will remember a post by Julianne Mason comparing clethodim (a grass only herbicide) to glyphosate (all green plants controlled) on reed canary grass. https://grasslandrestorationnetwork.org/2020/04/30/herbicide-treatments-to-reed-canary-grass-clethodim-vs-glyphosate/ The following images are from recent applications of grass herbicide on RCG at Nachusa.

The bright green plant is not a grass but a sedge. The yellowing reed canary grass is hurt by the clethodim herbicide, but not sedges, rushes, forbs, shrubs, trees. But…most of us conclude some of the grass roots will still be alive and slowly emerge next year. Of late we are adding ammonium sulfate and a non ionic surfactant to the clethodim mix. If we knock back the invasive grass can the sedge meadow hold its own?
Clethodim sprayed on RCG. At first glance you see just yellowing reed canary grass, but look for the tall thin bright green sedges that are unaffected. I saw those sedges and felt confident that a quick spray of this entire RCG patch would next year show sedges and forbs starting to dominate the ground. This is the attraction of a grass herbicide.

From 2020, RCG yellowing while sedges are bright green with some sedges seeding. A missed RCG is bolting in the back ground.
We use backpacks too, but this 50 gallon sprayer on the back of the 30 hp tractor is quite nimble for getting access to modest size patches for spraying RCG. The hand nozzle on the sprayer is used much more often than the boom-less tips on the back.
A JD-9 nozzle allows spot spraying from the tractor cab or on foot with the hose on the reel.

Jim Alwill shares this image of showy goldenrod plugs in a propagation setting where clethodim suppresses the cool season grass sod.

Why we push back against invasive RCG: A 2007 image of a meadow at Nachusa dominated by plantain (Arnoglossom plantagineum) and culver’s root

A 2007 image with volunteer steward Kevin Kaltenbach in the same sedge meadow with those plantains in the distance.
Posted in Uncategorized | Tagged , , , , | 6 Comments

Can We Create a Copse of  Low Juneberry for a Remnant Restoration?

Posted on May 19, 2022 by Grassland Restoration Network blog

By Bernie Buchholz

A thriving copse of low juneberry is an attractive feature on several remnant knobs at Nachusa Grasslands. These dense clusters of identical plants offer a strong visual contrast to the lovely chaos of diverse prairie surrounding them.  

In our sandy soils Amelanchior humilis, aka low juneberry or shadblow, grows about 18 inches tall in dense copses about 30 feet across.  Prescribed fire tends to burn only part way into the cluster and fire only top-kills the perimeter plants.  

Could we create a copse on the highly degraded, but recovering, Fame Flower Knob that we’ve been restoring since 2006? We had previously planted scattered low juneberry plugs and none survived, probably due to repeated prescribed fire. 

Below photo #1: Shadblow on Doug’s Knob remnant; copyright Charles Larry. 

The Flora of the Chicago Region by Wilhelm and Rericha says the species occurs in mesic to dry-mesic woodlands and savanna. At Nachusa, copses of low juneberry  are found in upland sandy soils underlain with sandstone, arguably in both historic open prairie and historic savanna habitats.  It is promising that our remnant seed source is thriving on the same soil types as our target plantings on both remnant and adjacent planted prairie areas. 

Larry Creekmur of Creston, IL grew three trays of 38 plugs each and generously assisted with the plug planting on October 26, 2014.  We targeted one site on the remnant with the same northeast exposure as the seed source and two sites immediately adjacent to the remnant in a 2012 planting. We tried three elevation levels on the knob.  The moisture levels appear similar. 

Photo #2: Larry Creekmur with planted plugs protected with plastic cylinders. 

At each of the three planting sites we planted 38 plugs on 6-inch centers to mimic the dense growth of existing copses. To deter predation while the plants were establishing, we placed a translucent plastic tube around each plug, each supported by a metal stake. After the first winter, the survival rate was about 85%, although we did not do an actual census.   

Photo #3: Finished installation. 

Our management practice has been to burn the remnant and surrounding plantings almost annually during active restoration. We believed, however, that prescribed fire posed a considerable risk to the shrubs’ survival while the plugs were getting establish. We tried to protect the plugs from prescribed fire in different ways: by reducing adjacent plant matter within 5 feet; heavily wetting just before fire; and with fire retarding foam, also just before prescribed fire.  

We were very frustrated when fire repeatedly burned through our defensive efforts. We finally had success in fall 2020 by erecting used corrugated steel panels, but we only had the resources to protect the remnant site which was about 6’ x 5’. 

Photo #4: Corrugated protection. 

After eight years only the remnant planting site shows the making of a copse.  There are now about 150 stems of various sizes compared to the 38 stems planted. The perimeter of the cluster, however, is not noticeably larger than the original planting. 

Photo #5 Remnant location after 8 years. 

Observations about the process:

  • Planting plugs in close together seems like a sound strategy. 
  • Fire will likely penetrate, but not kill the copse for years to come.   
  • We might have planted all 114 plugs in one location creating a larger starting copse.
  • Only metal panels protected the new plugs from fire.  
  • The other two planting sites were not protected from fire and are much less vigorous and less dense. 
  • Effective protection from fire might have accelerated the plugs’ development. 
  • We might have done simple soil cores to possibly find a planting site with “depth to sandstone” like the source site. 

It looks like it will take at least another decade or two before the planted copse is wide enough and dense enough to act as a barrier to prescribed fire, thereby protecting its core. 

We think this effort will ultimately succeed. Check back in a decade, but don’t wait to try it yourself. 

Posted in Uncategorized | Tagged , , , | 5 Comments