A Trip to Konza Prairie Biological Station, Part 1

Last week, several of us from the Platte River Prairies traveled south to visit the Konza Prairie Biological Station near Manhattan Kansas.  Konza Prairie includes about 8,600 acres of prairie, jointly owned by Kansas State University and The Nature Conservancy.  The prairie is managed and used as a biological station by Kansas State University’s Division of Biology, but hosts research projects from scientists around the world.  The biological station has a three-fold mission: long-term ecological research, education, and prairie conservation.

Research results from Konza Prairie have been very influential for grassland managers across the world, but particularly in western tallgrass and mixed grass prairies of North America.  Over the next couple of weeks, I’m going to report on several topics we discussed with researchers at Konza during our trip.  Today, I’ll just give you an overview of the site and our visit.

Annually-burned prairie near the headquarters of Konza Prairie near Manhattan, Kansas.  It has been very dry there since early summer, so much of the vegetation - including compass plant - is shorter than usual.

Annually-burned prairie near the headquarters of Konza Prairie near Manhattan, Kansas. It has been very dry there since early summer, so much of the vegetation – including compass plant – is shorter than usual.

We had two main reasons for our trip to Konza.  First, our two Hubbard Fellows, Jasmine and Dillon, are designing research projects on small mammals and grasshoppers, respectively, and wanted to learn from Kansas State researchers on those topics.  Second, researchers from Konza Prairie have produced some of the most important grassland science there is, and we wanted to learn as much as we could by touring the site with some of those researchers.

Our Nebraska crew in Kansas.  From left: Jasmine Cutter, Chris Helzer, Dillon Blankenship, and Nelson Winkel.

Our Nebraska crew in Kansas. From left: Jasmine Cutter, Chris Helzer, Dillon Blankenship, and Nelson Winkel.

Thursday evening, we arrived just in time to take a short hike near the headquarters as the sun was going down.  Then we went to bed early so we could get up before the sun Friday morning and accompany researcher Drew Ricketts as he checked his small mammal trap line.  Drew is comparing the small mammal communities between patch-burn grazed prairie (with cattle), annually burned/grazed prairie, and ungrazed prairie burned every four years.  Jasmine wanted to see his trapping and handling techniques and get some tips on identifying some of the species.

Checking small mammal traps at sunrise.

Checking small mammal traps at sunrise.

Jasmine (left) watches as Drew Ricketts explains how to identify a white-footed mouse.

Jasmine (left) watches as Drew Ricketts explains how to identify a white-footed mouse.

Sherman live traps laid out in a grazed portion of the prairie.

Sherman live traps laid out in a grazed portion of the prairie.

The crew watches Drew and his assistant, Kyle (right) examine and record data from captured small mammals.

The crew watches Drew and his assistant, Kyle (right) examine and record data from captured small mammals.

After we spent a couple hours with Drew, we met up with Kansas State professors Tony Joern, John Blair, and Jesse Nippert and started a four hour tour of the site that was so full of information and ideas my head is still spinning.  We looked at the portion of the site grazed by a herd of 400 bison and talked about the impacts of bison vs. cattle grazing, the role of bison in keeping cedar trees out of prairie (they’re good at it), and several other related topics.  Next, we drove through the ungrazed watersheds of Konza that have been burned on frequencies of 1, 2, 4, 10, and 20 years since as far back as 1978.  The plant composition and habitat qualities of those areas have diverged in very interesting ways through time.  We finished by looking at a (fairly) new restoration project and some small plots treated with various fire regimes and fertilizer treatments.  Along the way, we talked about myriad other topics as well…

Patch-burn grazing was being used in a portion of Konza prairie.  These cattle were grazing in the most recently burned patch, creating habitat of short grass and tall forbs (wildflowers).  Ungrazed forbs in this photo includes leadplant and purple prairie clover.

Patch-burn grazing was being used in a portion of Konza prairie. These cattle were grazing in the most recently burned patch, creating habitat of short grass and tall forbs (wildflowers). Ungrazed forbs in this photo includes leadplant and purple prairie clover.  Research has shown higher diversity of many invertebrate and other animal groups in this kind of habitat than in more uniformly short or tall grassland habitat.

The Flint Hills prairie in Kansas is named for the shallow layers of bedrock beneath the surface.  There are also many scattered rocks in the prairie that are easier to find after a fire or grazing event opens up the vegetation.

The Flint Hills prairie in Kansas is named for the shallow layers of bedrock beneath the surface. There are also many scattered rocks in the prairie that are easy to see after a fire or grazing event opens up the vegetation.

The tour group included (from left)

The tour group included (from left) Dillon Blankenship, Jesse Nippert (KSU), John Blair (KSU), Jasmine Cutter, Nelson Winkel, and Tony Joern (KSU).

By the time Tony, John, and Jesse headed back to campus, we were ready to head home – not because it was hot (it was) or because we were hungry (we were), but because we didn’t feel like we could cram any more new information into our heads.  As I said at the beginning of this post, I’ll try to synthesize some of that information for you over the next couple of weeks, but I’ll also try to put it into small manageable doses.

Stay tuned!

Nelson and the Hubbard Fellows enjoy a rainbow over the prairie.

Nelson and the Hubbard Fellows enjoy a rainbow over the prairie.

 

Earth, sky, and grass at Konza Prairie.

Earth, sky, plants, and grazers at Konza Prairie.

New Information on Tree Invasion in Prairies

One of the biggest challenges of prairie management today is the suppression of woody invaders.  Both native and non-native woody species can spread rapidly in prairie, making it difficult to maintain the open grassy habitat that most prairie species depend upon.

There has been extensive speculation about why shrubs and trees appear to be more aggressive and successful now than in the past.  Fire suppression has been a factor identified by many as a likely cause, but it’s clearly not the only factor because there are examples such as Konza Prairie in Kansas where shrubs have spread strongly under more than 20 years of regular fire application.

Fire can help suppress shrubs, but there are plenty of examples where frequent fire is not sufficient to stop their expansion.

Now, a new study from Konza Prairie may shed some light on at least some of the reasons behind the agressive expansion of shrubs in the Kansas Flint Hills and other mesic tallgrass prairies.  The research paper, written by Zak Ratajczak, Jesse Nippert and others, addresses both the initial survival of new woody plants and the subsequent spread by clonal species (such as dogwood and sumac, which spread by underground rhizomes).  It’s worth reading, and you can find a PDF here.

The question of why woody plants are able to establish more successfully in prairies now than they could several decades or more ago is still largely speculative.  Jesse Nippert explains his reasoning in an interview here.  Changing atmospheric conditions – especially higher nitrogen and carbon levels – are altering the competitive balance in grasslands to favor C3 plants over C4 plants.  Because shrubs like dogwoods (Cornus sp.) are C3 plants, higher levels of nitrogen and carbon in the atmosphere are likely giving them an advantage over C4 plants such as big bluestem and other warm-season native grasses that have historically had a competitive edge in tallgrass prairie.  This could explain why woody plants are surviving their seedling stage more now than they did in the past – but the idea still needs to be tested further.

However, while initial survival of shrub and tree seedlings is one important component of the issue, the research paper by Ratajczak et al. also addresses the subsequent spread of those shrubs – and they do so through field data collection.  They focused their work on the primary shrub species spreading at Konza Prairie – rough-leaved dogwood (Cornus drummundii).  What they found was that while most prairie plant species get the vast majority of their resources from the top foot or so of the soil profile, dogwood plants get almost half of their resources from below that level.  In other words, dogwoods are using resources – especially moisture – that most prairie plants aren’t taking advantage of.  (Yes, most prairie plants do have deep roots, but they typically reserve the use of those deeper roots for periods of drought and rely on their much more abundant shallow roots most of the time.)  Importantly, not only do “parent” stems of dogwood use deep soil water, new stems that are initiated by rhizomes (below-ground stems) do too – probably because they can pull water from their parents until they get their own deep roots established.

Taken together, the two ideas proposed by Ratzjcak, Nippert, and others provide an interesting hypothesis about how today’s shrub invasion may be taking place.  Higher levels of carbon and nitrogen in the atmosphere and/or soil provide a new competitive edge to colonizing woody plants.  That “fertilized” environment overrides the traditional advantage that warm-season grasses have over shrubs, which is that grasses are very good at monopolizing soil resources within the top foot or so of the soil profile.  Today, young woody plants are surviving long enough in that dry upper soil layer to extend their roots into deep moist soil – below where most other prairie plants mine resources.   Once those woody plants tap into that deep soil moisture, their survival is much more assured.  Woody plants that are clonal – such as rough-leaved dogwood and smooth sumac (Rhus glabra) – can then spread by rhizomes, continuing to take advantage of their ability to utilize the deep soil moisture their neighbors aren’t using.

Smooth sumac and flint hills prairie - Kansas. Konza prairie researchers have found that shrub invasion in upland prairies has much less aggressive than in lowlands. Is this because deep soil moisture is less abundant in uplands, reducing the competitive edge to those shrubs?

In addition to the carbon/nitrogen levels and deep soil moisture that both favor shrubs, anyone who has conducted prescribed fires in prairies containing large clones of dogwood or sumac knows that those shrub patches can inhibit the growth of grasses around their edges, reducing the amount of fuel for fires.  In other words, shrub patches can reduce nearby fire intensity – thus greatly reducing the effectiveness of one of the most important threats to their survival.  You really do have to admire their strategies, don’t you?

I think the hypotheses proposed by Ratajczak, Nippert, and their colleagues could explain a good portion of the puzzle.  Atmospheric conditions have certainly changed over recent decades, and that could explain why trees and shrubs have an easier time getting started in grasslands now.  However, the competition for deep soil moisture shouldn’t be much different now than it was historically.  We know there were at least some shrubs in historic prairies – why didn’t they grow into gigantic unstoppable clones?  What controlled their spread that isn’t doing so now?  Was the historic abundance of browsing animals high enough to control those clones?  Are the fewer browsers today simply overwhelmed by the increased number of new clones that are successfully establishing?  Are there other factors we’re not even considering yet?

There are plenty of questions left to answer, but it’s great that we’re moving in the right direction.  Besides the work of Ratazcjak, Nippert, and their colleagues, there are several other projects I’m aware of that are working to investigate the issue of woody invasion of prairies.  There are certainly plenty of us interested in their results!