So Similar, Yet So Different

It’s wrong to assume that successful restoration or management tactics from one prairie will work in another.  Instead, every prairie has its own “personality” and responds accordingly.  The key to success is experimentation and adaptive management.

Bill Kleiman is one of my favorite people.  We have much in common: a love of prairies and restoration, a drive to learn from our mistakes and share what we learn with others, and a strong belief in the importance of conservation.  We’ve both worked for The Nature Conservancy for a long time (he’s got a couple years on me) and have been co-leading the Grassland Restoration Network for the last several years.  He’s also a great guy and a good friend.

Bill Kleiman (white hat) leads a tour of a restored prairie at The Nature Conservancy's Nachusa Grassland.

Bill Kleiman (light-colored hat) leads a tour of a restored prairie at The Nature Conservancy’s Nachusa Grasslands.  2014 Grassland Restoration Network workshop.

However, despite the fact that Bill and I are friends and have a lot in common, there are some big differences between us as well.  Bill is much more patient than I am, and better at the social niceties needed to build close relationships with neighbors and volunteers.  I tend to say what I think – sometimes inappropriately.  Bill is not shy about expressing his opinion, but does it less frequently, and usually with kindness and self-deprecation.

Bill and I both manage grasslands for The Nature Conservancy, but just as there are differences between us as people, there are also some stark differences between our sites and the approaches we take toward prairie restoration and management.  Bill’s site, TNC’s Nachusa Grasslands, is located in rolling hills about two hours west of Chicago, Illinois.  My Platte River Prairies are on mostly flat alluvial (river-formed) soils in south-central Nebraska.  As a result, the soils, topography and climate vary greatly between the two sites.  Moreover, our sites each have unique land use histories, invasive species legacies, and social and cultural contexts.

Bill again, talking to a tour group - with the Nachusa Grasslands in the background.

Bill again, talking to the same tour group, with Nachusa Grasslands’ undulating topography in the background.

I was thinking about all of this last month as our Platte River Prairies crew traveled to Nachusa Grasslands where Bill and his team were hosting this year’s annual Grassland Restoration Network workshop.  It was fascinating to compare the land management and restoration strategies we each use, especially knowing that both of us have diligently tested and refined our methods to meet the individual challenges of our respective sites.  Below are some of the similarities and differences between our approaches.

1. Seed Mixtures and Seeding Rates

Both Nachusa Grasslands and the Platte River Prairies have been actively restoring cropland to high-diversity prairie habitats.  At both sites we broadcast our seed (as opposed to drilling it).  The seed is broadcast either by hand or with a drop spreader – a fertilizer spreader that drops seeds onto the ground.  In fact, broadcast seeding is the technique of choice for the vast majority of sites that participate in the Grassland Restoration Network.  (You can learn more about fairly universal strategies and tactics in the “Lessons from the Grassland Restoration Network” document several of us put together.)

However, while we both broadcast seeds, Bill has found that successful prairie plantings at Nachusa require much heavier seeding rates (around 50 bulk pounds of seed per acre) than we use along the Platte River (8-10 bulk pounds).  Bill’s seed mixes include lots of seed from wildflowers, sedges, and “subdominant” grasses such as little bluestem, prairie dropseed, and sideoats grama, but almost no seed from more dominant grasses such as big bluestem and indiangrass.  In our Platte River Prairies seed mixtures, dominant grasses make up about half of the weight of the mixture.

James Trager (Shaw Nature Reserve) and Nelson Winkel (TNC Platte River Prairies) look over a restored prairie at Nachusa Grasslands.  This prairie was relatively unique in that it had a fair amount of indiangrass in it.  Most of the seed mixtures have none, or very little, seed from big grasses such as indiangrass and big bluestem.

James Trager (Shaw Nature Reserve) and Nelson Winkel (TNC Platte River Prairies) look over a restored prairie at Nachusa Grasslands. This prairie was relatively unique in that it had a fair amount of indiangrass in it. Most of the seed mixtures have none, or very little, seed from big grasses such as indiangrass and big bluestem.

Both Bill and I have experimented with many variations of these seed mixtures and have settled on these broad recipes as appropriate for our respective sites.  Though we do things differently, we both end up with very diverse prairies that meet our objectives.  When Bill uses lighter seeding rates, his new prairies get swamped out by invasive species before native plants become well established.  He’s also found that adding dominant grasses to the initial seed mix leads to plant communities that become overly grassy and not very diverse.  In contrast, using lighter seeding rates on the Platte allows us to plant more acres per year with the same seed harvest effort, and while it takes longer for our plantings to establish, they still end up being very diverse.  As our plantings mature, fire and grazing management helps suppress the dominance of big bluestem and indiangrass and maintain high plant diversity.

2.  Weed Control in New Restored Prairies

Weed control strategies for new plantings also vary greatly between Nachusa Grasslands and the Platte River Prairies.  At Nachusa, Bill and his crew walk every inch of new plantings multiple times each year until the native plant community is well established.  They remove (by pulling or spraying) every invasive plant they find – focusing mostly on perennial legumes such as birds foot trefoil, crown vetch, and sweet clover.  Once the native community is established, they can relax a little, but they still watch each site very closely.  In some cases, they’ve not been able to keep up with the pressure from invasive plants and they’ve made the difficult decision to just give up and start over, rather than fighting a losing battle for years.

The soybean field on the left is a former restored prairie that just never established as Bill hoped, so he and his crew made the decision to start over.  After it is farmed for a few years, they'll try again.

The soybean field on the left is a former restored prairie at Nachusa Grasslands that never established as Bill hoped, so he and his crew made the decision to start over. After it is farmed for a few years, they’ll try again.  While it’s a lot of work to start over, it’s less work than many years of fighting weeds and never winning.

Our weed control on the Platte River Prairies looks much different.  We don’t really have problems with perennial legumes or other non-native forbs.  In fact, we pretty much ignore sweet clover, and most other “weeds” during the establishment phase of a new prairie are annuals such as foxtail, marestail, and annual sunflower that just fade away as perennial prairie plants take over.  Our major fears have to do with perennial invasive grasses, such as smooth brome and Kentucky bluegrass, and we deal with those mainly by suppressing them with fire and grazing management.  We also worry about deciduous trees, such as Siberian elms, that we have to control with herbicides because fire and grazing don’t do the job.  However, during the first few years of establishment, while Bill and his crew are painstakingly patrolling their sites, we can mostly ignore our new plantings – except for an occasional prescribed burn to limit the buildup of thatch.

3. Overseeding

A third difference between our sites has to do with overseeding.  In both remnant (never plowed) and restored prairies, we occasionally want to add missing plant species.  At Nachusa, they just burn the prairie and throw the seed out on the bare ground – and it works!  In our drier Platte River Prairies, we’ve not had very much luck with that strategy.  Using grazing to weaken the dominant grasses seems to help us get better establishment of new plants because it suppresses competition for moisture and other resources.  Bill’s crew doesn’t seem to have to worry about that – even in sites with lots of grass.

Bill (left) oversees some "data collection" during this year's Grassland Restoration Network, which was done to help tour participants evaluate an overseeding project.  Becky and Hank Hartman (volunteer stewards) have used repeated overseeding to transform an area from exclusively grasses to one with very nice wildflower diversity.

Bill (left) oversees some “data collection” during this year’s Grassland Restoration Network, which was done to help tour participants evaluate an overseeding project. Becky and Hank Hartman (volunteer stewards) have used repeated overseeding to transform an area from exclusively grasses to one with very nice wildflower diversity.

 

Mike Konen (in orange) from Northern Illinois University talks about soils during this year's workshop at Nachusa.  He is standing in prairie that is going to be grazed by the newly introduced herd of bison.  Grazing will give Bill and I one more thing to compare notes on...

Mike Konen (in orange) from Northern Illinois University talks about soils during this year’s workshop at Nachusa. He is standing in prairie that is going to be grazed by a newly-introduced herd of bison (the bison should knock the height of that indiangrass down some…) Now that Nachusa is using grazing  as a management too, Bill and I will have one more thing to compare notes on…

Bill and I have done extensive experimentation to come up with effective prairie restoration and management strategies at our respective sites, and we continue to adapt as we go along.  We can learn from each others’ experiences, but there is also much that doesn’t translate well between sites.  Some of that is due to the distance between Nachusa and the Platte, and the corresponding differences in climate and soils.  However, even prairies that are much closer together can respond very differently to management and restoration tactics.  Soil types, seed banks, topography, management history, landscape context, and many other factors combine to give every prairie it’s own “personality”.

It might seem overwhelming to learn that every prairie requires a unique set of restoration and management strategies, but it’s really not that bad.  There are a still a lot of commonalities between prairies – just like there are many similarities between Bill and me.  However, just as you would need to consider differences between Bill’s personality and mine in terms if you wanted a positive response from us, the same holds with prairies.  (If you want a favor from Bill, you might want to invite him to a little gathering and serve good beer.  On the flip side, if you want something from me, pizza would make a better bribe, and while I’m not against parties, the less small talk needed, the better…)

Above all, beware of anyone who tells you’ve they’ve figured out the magic formula for how to manage or restore prairies.  It’s just not possible.  Instead, take a look at what others do, learn from their experiences, and then experiment with a variety of techniques at your own site.  It won’t take long to figure out what moves your prairie in the direction you want.   Fortunately, unlike Bill (I’m kidding!) prairies are pretty forgiving, so if you try something and it doesn’t work, they aren’t likely to hold a grudge.

P.S. Bill will be appalled that I’m giving him so much credit for the work at Nachusa.  Clearly, both Bill and I have crews of staff and volunteers that do most of the work and much of the thinking.  For this post, however, I was trying to build an illustration of personalities in people and personalities in prairies.  It was a lot easier to do that by focusing just on Bill and me.  Please understand that the ideas and work of Nelson, Cody, Mardell, Hank, Becky, Karen, Al, Bernie, Jay, Susan, Leah, and many others are represented here as well.  (There, does that make you happier Bill?)

The Right Metaphor for Prairie Restoration

Prairie restoration can be a powerful tool for grassland conservation, but we’re not taking advantage of its full potential.  Too often, we think and talk about prairie restoration (aka prairie reconstruction) in the wrong way.  Instead of trying to restore an ecosystem, we try to reproduce history.

Nelson Winkel, land manager for The Nature Conservancy’s Platte River Prairies, harvests grass seed using a pull-behind seed stripper.

I was in Washington D.C. a couple weeks ago and visited Ford’s theater, where President Lincoln was assassinated in 1865.  After the death of the president, the building went through drastic changes, including being completely gutted after a partial collapse of the interior.  By the time the decision was made to restore the building for use as a historic site, the National Park Service basically had to start from scratch.  Regardless, through painstaking research and a lot of hard work, the theater was rebuilt to closely resemble Ford’s theater of 1865.

The rebuilding of Ford’s theater is a decent metaphor for much of the early prairie restoration (or reconstruction) work dating back to the 1930’s in North America – as well for some of the restoration work that continues today.   In the case of prairie restoration, someone identifies a tract of land that used to be prairie but has been converted into something completely different (usually cropland), and tries their best to restore what was there before it was converted.  Just as in the restoration of Ford’s theater, the prairie restoration process requires lot of research and hard work to identify, find, and reassemble what had been there before.

Unfortunately, the Ford’s theater approach has turned out to be a poor fit for prairie restoration.  Prairies aren’t buildings that have specific architectural plans and well-defined pieces that can be collected and assembled to create a pre-defined end product.  Prairies are dynamic ecosystems that are constantly changing and evolving, and their components include organisms that interact with each other in complex ways.  Trying to recreate a prairie that looks and functions just as it used to – especially on a small isolated tract of land – is nearly impossible.

Reseeded prairie at The Nature Conservancy’s Kankakee Sands Restoration Project in Indiana. If the plant community today looks different than it did before it was farmed, is that really a failure of the restoration project?

That doesn’t mean small scale prairie restoration is a bad idea.  I think reestablishing vegetation that is similar to what was at a site many years ago can have tremendous historic and educational value, and can also provide important habitat for many grassland species.  Where this kind of prairie restoration falls flat is when we expect too much from it.  It’s really easy to find glaring differences between the restored prairie and what we know or think used to be there – soil characteristics are different, insect and wildlife species are missing, plant species are too common or too rare, etc.  These “failures” have led some people in conservation and academia to become disillusioned with the whole concept of prairie restoration.

In reality, prairie restoration has proven to be very successful, and is a tremendous tool for grassland conservation.  We just need to find and apply a better metaphor.

A Better Metaphor for Ecological Restoration

Unlike efforts to restore old buildings, prairie restoration projects should not be aimed at recreating something exactly as it existed long ago.  Instead, effective prairie restoration should be like rebuilding a city after large portions of it are destroyed in a major disaster.  When reconstructing a metropolitan area, replicating individual structures is much less important than restoring the processes the inhabitants of the city rely on.  The people living and working in a city depend upon the restoration of power, transportation, communication, and other similar functions.  Those people don’t care whether roads, power lines, or communication towers are put back exactly as they were before – they just want to be able to get the supplies and information they need, and to travel around so they can to do their jobs and survive.  Restoration success is not measured by how much the rebuilt areas resemble the preexisting areas, but by whether or not the city and its citizens can survive and thrive again.

Similarly, restoration of fragmented prairie landscapes should not be an attempt to recreate history.  It should be an attempt to rebuild the viability of the species – and, more importantly, the processes – that make the prairie ecosystem function and thrive.  Success shouldn’t be measured at the scale of individual restoration projects, but at the scale of the resultant complex of remnant and restored prairies.  Are habitat patches sufficiently large that area-sensitive birds can nest successfully?  Are insects and animals able to travel through that prairie complex to forage, mate, and disperse?  Are ecological processes like seed dispersal and pollination occurring between the various patches of habitat?  When a species’ population is wiped out in one part of the prairie because of a fire, disease, or other factor, is it able to recolonize from nearby areas?

Pollination is an example of an important process that drives prairie function. Increasing the size and/or connectivity of prairies by restoring areas around and between prairie fragments can enhance the viability of pollination and other processes.

At first glance, choosing the appropriate metaphor for prairie restoration may seem insignificant compared to other challenges we face in grassland conservation.  However, if we’re going to successfully restore the viability of fragmented prairies, we can’t afford to waste time and effort worrying about whether or not we’ve matched pre-European settlement condition, or any other historical benchmark.  Instead, we need to focus on patching the essential systems back together.

After all, we’re not building for the past, we’re building for the future.

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Read more on this subject…

– An earlier blog post about using prairie restoration as a landscape scale conservation tool.

– A prairie restoration project case study, with ideas about how to measure its success.

– Some recent early attempts we’ve made to measure restoration success by looking at the responses of bees and ants.

– A post about the importance and definition of ecological resilience in prairies.