What Is High-Quality Prairie Anyway?

Does this look like a high-quality prairie?

What about this one?

What if I told you the first one was 2 acres in size and the second was part of a 20,000 acre grassland block? 

Would it affect your opinion if you knew the first site was isolated from any other prairie habitat by miles of cropland and was directly adjacent to a busy highway?  What if I told you the second prairie hosts three different prairie dog towns and a herd of bison?

(None of this is true, by the way.  These are just hypothetical statements meant to be thought-provoking.)

The term “high-quality prairie” is often used in conservation circles, but people have very different definitions for it.  That’s not necessarily a bad thing.  In fact, it’s fascinating to see how the quality of a prairie is defined by people in different parts of North America, let alone in other parts of the world.  The cultural context is incredibly important to the way prairies are assessed and appreciated.

Here’s another example.

Does this look like a high-quality prairie?  Would it change your opinion if you knew it was planted on former row crop land?

Taking that further, does it matter if that restored prairie is about 10 acres in size and not connected to any other natural areas?  In contrast, what if it was 50 acres in size and connected two formerly-isolated remnant (unplowed) prairie parcels together?  Does that affect its quality or value?  Does it affect the quality or value of those remnant prairie parcels?

What are the criteria we should use for evaluating prairies?

A very common way to assess prairies is by looking at their plant species.  That makes good sense.  Prairie plants are beautiful.  In addition, of course, the plant community has a huge influence on the other components of the larger prairie community, including animals, fungi, and other soil microbes.  Maybe more importantly, you can always find plants.  They are literally rooted in place. 

When you visit a prairie, you might not see a pocket mouse, a katydid, or a badger, but if there’s a population of stiff sunflower, you can go to a particular spot and see it – it might even be in flower if you time it right.  Over time, it’s easy to see how that population is doing because you can check on it whenever you want.

There are multiple ways to evaluate a plant community.  The diversity of species is usually considered to be one important factor.  The presence of rare plant species, or species that have very specific habitat or management requirements, can be another.  The second can be particularly significant in landscapes where very little prairie is left.  Finding a prairie that still hosts rare plants is a big deal.

Prairie turnip (Pediomelum esculentum) is hard to find across much of its historic range. This one is part of a large population at the Niobrara Valley Preserve.

Looking at the diversity of plants and the presence and abundance of rare species is a very sensible way to begin evaluating a prairie.  I often do it myself.  You can visit a prairie at any time of year and make at least some assessment of the plant community – though it’s much easier during the growing season. 

In contrast, you have to time your visit carefully if you want to see what the bird community looks like (many species are only present for a few months each year).  Small mammals are tricky because they’re hard to see and you probably need some kind of trap system to even find any.  You can see a lot of invertebrates if you look closely, and of course you can pick up a sweep net and very quickly gather a bunch of them to inspect.  But invertebrates are notorious for having massive swings in population size from year to year, and many are only aboveground for short periods of time each season.  That means it can take a lot of time and a lot of effort to get any picture of what’s happening with invertebrate communities.

Insects like these bush cicadas can experience huge population booms and busts between years, making it hard to evaluate invertebrate communities.

However, notwithstanding the challenges of evaluating their populations, birds, small mammals, and invertebrates are all important components of prairies, right?  Any assessment of prairie quality should probably include them – not to mention reptiles, amphibians, large mammals, fungi and other soil microbes, and lots more. 

Looking at the plant community can provide hints about some of those other organisms.  Plant diversity is strongly correlated with invertebrate diversity, for example.  However, not all prairie animals have such strong ties to the diversity of a plant community, or to the presence or absence of particular plants.

Most grassland birds, for example, are really dependent upon the size of a grassland area and the habitat structure present. Some species nest in short grass, others in tall.  Still others need a variety of habitat patch types because they use different vegetation structure for nesting, brood rearing, wintering, and/or courtship displays.  In addition, a lot of grassland nesting birds are sensitive to the size of a prairie and/or won’t nest near wooded edges, roads, etc. (or suffer poor nest success when they do).

Upland sandpipers nest on the ground in large prairie patches with short, open habitat. They then take their young chicks into cover where the habitat is open enough the chicks can feed and move around easily, but there is overhead cover (especially broad-leaved plants) they can use to hide from predators and find shade.

Small mammals, reptiles, and invertebrates also respond strongly to the kind of habitat structure in a prairie.  Just as with birds, each species has its own preferences or requirements – some looking for short/sparse habitat, others for tall/dense cover, and some need something in the middle or a mix of all of those options.  Also, like birds, many of those animals and their populations will thrive best in larger prairies than in smaller ones. 

So, in addition to a “good” plant community, you could argue that a high-quality prairie should also be one that is large and managed in a way that provides a mixture of habitat structure.  Maybe, but this is where things get really interesting. 

In many places, large prairies just don’t exist anymore.  We’re left with small remnants of grassland, surrounded by row crops, urban areas, woodlands, or other land cover types.  Does that mean none of those prairies are high-quality?  Of course not.  But the context matters.  The quality of a site is measured against objectives (what do we want a prairie to be or to provide?) and objectives are informed by local culture. 

Small prairies can still provide excellent habitat for many species, including plants, invertebrates, and many small vertebrates, though stewardship gets really tricky.  It can be really challenging to manage those sites in a way that doesn’t eliminate any animal populations (by repeatedly burning the whole site, for example) while still staving off woody plants and invasive species.  However, when comparing a bunch of small prairies to each other, we can come up with criteria for determining which are higher or lower-quality.

On the flip side, there are parts of the world where we still have huge, unplowed grassland landscapes.  These prairies have the scale to support a lot of animals that can’t survive in isolated small prairies, and – if managed appropriately – the habitat structure those species need as well.  That might even include many large animals like bison and pronghorn, or other charismatic species like prairie dogs or prairie grouse. 

The Nebraska Sandhills is 12 million acres of contiguous native prairie.
Pronghorn – one of many large prairie animals supported by the Nebraska Sandhills.

However, in some of those landscapes, much of the prairie has lost plant diversity and/or populations of plant species that used to be there, and that has big implications.  Not only is the plant community an important component of “quality”, it also supports many of the other organisms that make up a strong, resilience grassland community.  Scale and habitat heterogeneity can make up for some of that, but species diversity is also a huge component of resilience.

Looking across a landscape like this, with lots of grassland but varying degrees of plant diversity and other components, we can pick out places that we think are of higher quality than others.  The criteria we use to make those decisions, though, will surely be different than the ones we use in a landscape where only small prairie patches remain.

Here’s why all this matters:

All of us who live around and work with prairies evaluate them through our own lenses.  Some of the criteria we use are shared, but others are heavily influenced by local conditions.  That’s ok, but we should recognize the biases we each have.  More importantly, we should make sure we’re talking to and learning from each other. 

About 15 years ago, I wrote a post about these different views on prairie quality.  In that post, I talked about how some of us focus a lot on the species composition (mainly plant composition) of prairies, while others look more at habitat structure and processes.  Those tendencies tend to be correlated with geography (east/west) and with the amount of grassland remaining in landscapes. 

In that post, I was hoping to stir people to expand their definition of prairie quality and to borrow perspectives from others.  There’s been some movement in that direction, but there are still some big differences in the way people assess prairie quality, and that strongly influences the way those prairies are managed.

As examples, I would love to see people working in fragmented prairie landscapes think more about how to vary habitat structure across even relatively small prairie parcels to benefit invertebrates and larger wildlife species.  At the same time, I wish people in landscapes with much larger prairies would pay more attention to plant composition.  While we have extensive prairies where the plant communities are in terrific shape, there are also lots of places where plant diversity is relatively low and many plant species are hard to find. 

My family prairie is is surrounded by cropland. I work really hard to provide a variety of habitat structure types each year to support wildlife, while constantly striving to improve the plant community. I’ve learned a lot about how to do this (and measure success) from colleagues and friends across the country.

There are lots of ways to create more heterogeneous habitat structure in prairies – even small ones.  We also have ways of managing for, and even rebuilding, plant diversity in places where it has diminished.  Good, creative land stewards working in today’s grasslands should be able to do all of that.  However, we aim our stewardship at the goals we set for ourselves, and those goals are tied to the way we evaluate prairie quality.

It doesn’t make a lot of sense to compare a 10-acre prairie fragment in northern Illinois to a 5,000-acre prairie pasture in central Kansas and argue about which is better.  It’s ok to say both are high-quality prairies (or not), based on local criteria.  What’s crucial is that we continue trying to learn from the way we each see and value our prairies.  All of us can benefit from expanding our perspectives, right?

Lessons From a Project to Improve Prairie Quality – Part 1: Patch-Burn Grazing, Plant Diversity, and Butterflies

We recently completed a large multi-year restoration and management project at our Platte River Prairies.  Our specific objectives were to improve habitat quality for various at-risk prairie species and evaluate the impacts of our management on at-risk butterflies – particularly regal fritillaries.  The project was supported by the Nebraska Game and Parks Commission, who funded our work with two State Wildlife Grants (U.S. Fish and Wildlife Service money).  Over five years, we conducted fire/grazing management in our prairies and enhanced plant diversity through overseeding and seedling plugs.  We measured the results of that work by measuring changes in prairie plant communities and by looking at the use of our prairies by regal fritillaries and other butterflies.

Plant diversity and buttterfly habitat were the objectives of our 5-year project.

We’ve worked hard to get plant diversity in our restored prairies, including this one.  We wanted to know whether or not our management was maintaining that diversity, and also how it was affecting butterflies.  The prairie shown here was being grazed at the time of the photo – July 2009.  The Nature Conservancy’s Platte River Prairies, Nebraska.

The following is a brief summary of the major lessons we’ve gleaned from the fire/grazing component of the project, including implications for future management and restoration work.  I will summarize the overseeding/seedling work in a separate upcoming post.  If you want more details, you can see our entire final report to the funding agencies here.  As a warning, the report is 14 pages long, with an additional 21 pages of Appendices, full of tables and graphs.

What We Did
Between 2008 and 2012, we treated over 1,500 acres of prairie with varying applications of patch-burn grazing management.  During that time, we altered the timing of burning and the intensity of grazing from year to year, and included years of complete rest from grazing in some prairies.  For the purposes of this project, we evaluated the results of our work in two main ways:

–          We measured changes in plant diversity and mean floristic quality.

–          We conducted three years of butterfly surveys to evaluate how regal fritillaries and other butterfly species responded to our restoration and management work.

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