Does Dotted Gayfeather Flower More Under Reduced Competition?

Late summer is definitely a season of yellow flowers in prairies, with goldenrods and sunflowers in the vanguard.  However, there are exceptions to the yellow rule, and one of the most prominent of those in our prairies right now is dotted gayfeather (Liatris punctata).

Dotted gayfeather punctuated an otherwise yellow-dominated plant community last week at our family prairie south of Aurora, Nebraska.

Last week, I was collecting data on the number of flowering stems within various management treatments at our Platte River Prairies, and noticed an apparent pattern with dotted gayfeather.  In particular, I thought I was seeing more flowering stems on gayfeather plants in one treatment than another right next to it.  I had a little extra time, so I tested the observation by counting the stems on a bunch of plants in each treatment, and sure enough – I was right.  Where we had burned and intensively grazed the prairie last year, there were more than twice as many flowering stems per plant (on average) as there were in the unburned, lightly grazed patch right next to it.  Both areas were in the same restored prairie (planted in 2000).  You might recall a post I wrote back in mid-August about this same site, which included photos of both the 2016 burn and unburned areas…

Error bars represent 95% confidence intervals

I collected my dotted gayfeather data pretty simply – I just walked through each part of the prairie and counted the ramets (stems) of every plant I encountered.  In total, I counted stems on 58 plants in the unburned patch and 53 plants in the 2016 burn.  The average number of stems per plant in the unburned/lightly grazed patch was 6.12, compared to 12.5 in the burned/grazed patch.  A big majority (76%) of the plants in the unburned area had 10 or fewer stems per plant, and the highest number of stems on any plant was 17.  By comparison, only 56% of the plants in the 2016 burn patch had 10 or fewer stems and eleven plants (21%) had more than 17 stems.  There were some extraordinarily large plants in the 2016 burn patch, including plants with 39, 40, 42, and even 51 stems!

One of the larger plants in the 2016 burn patch

Now, this is a single site and it’s really important not to draw too many conclusions from a one year sample.  I’ll be looking at the same site again over the next couple years to see how things change as future management is applied differently to each patch.  The unburned area is slated to be burned and grazed in 2018, for example, so it will be really interesting to see how dotted gayfeather plants look in both 2018 and 2019.  I’m not sharing my data from this year because I think there are conclusions to be drawn from it, but rather because it’s fun to speculate about what might have caused the apparent pattern.  I’m hoping some of you will enjoy speculating with me, and maybe even look around in prairies near you for similar patterns.

In that spirit, here are a few thoughts running through my head.  First of all, the 2016 burn patch in this restored prairie was grazed really intensively all of last season, which severely weakened the vigor of dominant grasses.  Coming into this season, most of those grasses were very short in stature, allowing a lot of light to hit the ground, and their root systems were greatly reduced, allowing space for a flush of opportunistic plants to flourish – including dandelions (Taraxacum officinale), yarrow (Achillea millefolium), hoary vervain (Verbena stricta), stiff goldenrod (Solidago rigida) and many others.  However, we also saw abundant seedlings of long-lived, more conservative plants as well, especially white and purple prairie clover (Dalea sp).

Many of the opportunistic plants that flourish in times of abundant light and root space do so through establishment of new plants from seeds waiting in the soil.  However, that’s not the only way plants can respond.   Most perennial plants, including dotted gayfeather, grow new stems each year from buds that are produced at the base of the plant or on rhizomes (underground stems).  Each bud represents a potential future flowering stem, and healthy plants can have quite a few of those buds and deploy them as needed.

Here is the 2016 burn patch about a year ago, after a spring burn and season-long intensive grazing. You can see ungrazed dotted gayfeather flowers blooming. but most grass leaves have been grazed short.

It makes sense to me that dotted gayfeather plants in our 2016 burn patch deployed more buds this spring than plants in the nearby unburned patch where surrounding vegetation is more dense.  Long-lived plants like dotted gayfeather should benefit from producing extra flowers/seeds in years when their competition is weakened.  Maybe abundant bud deployment happened because gayfeather plants were able to expand their root systems last year and reach new resources, or maybe the short stature of surrounding vegetation allowed more light to hit the base of the plant this spring, triggering buds to open.

Of course it’s also possible that all my speculation is complete bunk.  Maybe the plants in the 2016 burn patch are always bigger than those to the east, regardless of management, and I just hadn’t noticed before.  If so, I’ll know that after a couple more years of sampling.  Either way, it’s sure fun to wonder what might be happening and then collect data to test whether or not I’m right.  Opportunities like that are exactly why I love being a scientist.

Please share your thoughts and experiences related to this topic, and if you get a chance to go look at dotted gayfeather plants in patch-burned grazed prairie or other similar situations, let me know what you see!

Chuck Norris of the Prairie

A big topic of conversation at this year’s Grassland Restoration Network (GRN) workshop had to do with designing seed mixes to combat potential invasive plant problems.  When converting cropland to prairie vegetation, the first few years of establishment are sometimes a race for dominance between prairie plants and invasives.  Once a strong native plant community becomes established, it is more difficult (but still possible) for invasive plants to become dominant, so those first few seasons are critically important.  Over the years, a number of people have tried using extra high seeding rates of various native plants to see if those natives could help stave off invaders.  In an ideal scenario, a high abundance of some showy wildflower would outcompete invasive plants but allow other native plants to establish.  Nice, right?  Lots of pretty flowers during establishment, no invasive species to worry about, and a nice diverse prairie community in the long run.

Black-eyed susans (Rudbeckia hirta) in restored prairie - TNC Platte River Prairies, Nebraska.

Black-eyed Susan is a species that has shown some promise as a species that can compete against invasives but still allow the establishment of a diverse plant community around it.   The Nature Conservancy’s Platte River Prairies, Nebraska.

I first heard about this idea at the 2004 North American Prairie Conference.  In one of my favorite presentations of all time, Shawn Schottler of the Science Museum of Minnesota compared various plant species to celebrities.  As he described his experiments, he said he was trying to find Chuck Norris plants (tough good guys) that could fight off Mike Tysons (aggressive invasives) while still allowing Patsy Clines (less competitive natives) to establish.  As I recall, he was having some luck with Chuck Norris species such as black-eyed Susan (Rudbeckia hirta), wild bergamot (Monarda fistulosa), and others.  At this year’s GRN workshop, Jack Norland of North Dakota State University described recent results of some similar experiments on U.S. Fish and Wildlife restoration projects.  The “spike” treatments they used consisted of ultra high seeding rates of species such as plains coreopsis (Coreopsis tinctoria), purple prairie clover (Dalea purpurea), Canada wild rye (Elymus canadensis), and others.  His data showed Canada thistle to be much less abundant in spike treatments than in the controls.

Interestingly, we’ve had some accidental experience with this topic here in our Nebraska Platte River Prairies.  During the drought years of the early 2000’s, some of our prairie plantings ended up with lots and lots of Canada wild rye.  In some cases, the species was so abundant that our plantings looked like wild rye monocultures.  We weren’t the only ones.  Prairie Plains Resource Institute had plantings that looked much the same during those years.  There was some hand wringing about whether or not the plantings had failed, especially given the drought conditions at the time, but Bill Whitney of Prairie Plains assured us that it wasn’t a big deal.  He was right, as usual.  The plantings eventually emerged from their wild rye phase and turned into very nice prairies.  In fact, our site that had the “worst” wild rye infestation is now the showiest (in terms of big colorful wildflowers) prairie we have.  I’m not sure the wild rye helped suppress any invasive species, but a high density of wild rye plants didn’t seem to keep Patsy Clines from eventually thriving.

This 2004 shows one of our Platte River prairie plantings in its third year of growth.  Canada wildrye is visually dominant, but other species are present as well.

This 2004 photo shows one of our Platte River prairie plantings in its third year of growth. Canada wild rye is visually dominant, but other species are present beneath its canopy.  Many of our young plantings from about that time period looked much like this for several years in a row.

After this prairie was seeded in 2000, it was a near monoculture of Canada wild rye for several years but today is our showiest wildflower patch.

After this prairie was seeded in 2000, it was a near monoculture of Canada wild rye for several years.  Today it is among our most diverse prairies and showcases our showiest wildflower patches.  (July 2015 photo)

Spike treatments/Chuck Norris species/etc., are really just variations on the idea of using a cover crop – planting something intended to establish early and then fade away (mostly or completely) as the desired vegetation takes hold.  In some places, cover crops are very useful in agricultural systems as a way to prevent soil erosion and loss of fertility, suppress weeds, and/or preserve soil moisture.  It seems logical that they would also help with prairie restoration establishment.  In fact, I recently talked to someone with the Natural Resources Conservation Service (NRCS) in north central Nebraska who says their best successes in restoring sandhill prairie come when they use a cover crop of millet.

On the other hand, I remember a GRN workshop about five or six years ago when we had a group discussion about our experiences with various cover crops.  Participants from across the Central U.S. seemed to reach consensus that cover crops were as likely to be counterproductive as helpful to prairie restoration efforts.  This seems to conflict with the successes seen by people like Shawn Schottler, Jack Norland, and others.  Why the differences?

Part of the issue is certainly that we’re still experimenting with different species, and still have a lot to learn.  Beyond that, though, anyone who has spent many years restoring prairie knows that establishment results can be very difficult to predict, even within the same site.  Just when you think you’ve got something figured out, your next planting turns out completely unlike what you’d expected.  Those kinds of inconsistencies, combined with differences in site attributes such as soil texture and fertility, rainfall, and latitude make it almost impossible to come up with restoration recommendations that apply everywhere.  In fact, if we’ve learned anything through the Grassland Restoration Network, it’s that it’s important to start big projects by doing some small experimental plantings to see what works best in that place before investing in larger scale work.

Grassland Restoration Network Meeting.  Hosted by TNC Minnesota.

There is great value in getting a bunch of restoration practitioners together in one place.  We often bring home new ideas to try.  Sometimes they even work.  2015 Grassland Restoration Network workshop – Minnesota.

Clearly, the idea of “spike” treatments and similar strategies hold a great deal of promise if they fulfill their promise of preventing invasives while facilitating establishment of diverse plant communities.  However, since it’s also clear that successful strategies from one site don’t always translate well to others, we may each have to find our own formula for success.  Hearing about Dr. Norland’ experiments in the Dakotas has inspired us to do some more experimentation here.  Maybe we can find a few Chuck Norris species to keep the peace in our Platte River Prairies.

If you’ve had positive or negative experiences with cover crops in prairie restoration, or have found your own Chuck Norris of the prairie, please share what you’ve learned in the comments section below.  Thanks.

P.S.  You may have seen or heard some of the many Chuck Norris jokes out there that play on the idea that he is seemingly invincible.  My 14-year-old son likes to share them with me now and then.  A few of my favorites are:

Chuck Norris doesn’t wear a watch. He decides what time it is.

Chuck Norris makes onions cry.

There used to be a street named after Chuck Norris, but it was changed because no one crosses Chuck Norris.

When Chuck Norris does a push up, he isn’t lifting himself up, he’s pushing the Earth down.

A bulletproof vest wears Chuck Norris for protection.