A Measure of Ecological Resilience in a Restored (Reconstructed) Prairie

Back in May of this year, I wrote about ecological resilience in prairies.  In Part 2 of that double post, I gave an example of a 1995 prairie seeding and talked about how it appears to be maintaining its plant community integrity – through wet and dry years, fire, and grazing.  Since that time, I’ve collected and analyzed more data from that same prairie seeding, and wanted to flesh out that earlier story.

With regard to prairie restoration, my objective is to use high-diversity seedings to expand and reconnect fragmented prairies and thus increase the viability of prairie species and communities.  Because of that, I don’t measure success by whether a prairie seeding looks like any particular remnant prairie.  Instead, I’m trying to establish as many native plant species as I can, let them sort themselves into communities that are adapted to today’s conditions, and use management techniques such as fire and grazing to maintain that plant diversity.  I’m assuming that by providing that plant diversity, I’m also providing the habitat needed by the animals in adjacent remnant prairies, and that those animals will move into – and through – prairie seedings, thus increasing animal population size and viability.  I’m beginning to test those assumptions, and will be ramping up that effort during the next several years.

In the meantime, I’ve been tracking the plant communities within our prairie seedings to look at how many plant species establish and maintain themselves.  More importantly, I’m tracking the long-term trajectory of those plant communities using plotwise floristic quality analysis (you can read more about that technique here).  If the prairie seedings are ecologically resilient, one measure of that resilience should be that populations of individual plant species, and overall species diversity, are stable over time – even through stress.   The 1995 seeding, for which I’m presenting data here, is located in our Platte River Prairies, south of Wood River, Nebraska, and it has certainly undergone stress.  Since it was hand-planted in 1995 by the Prairie Plains Resource Institute with approximately 120-150 plant species, it has seen both very wet years and a long severe drought (7 years), and has been managed with patch-burn grazing since 2002.  Over the years, I’ve accumulated a total plant species list of 164 species for the 45 acre seeding, which I’m very pleased with.  However, the real question is whether or not the seeding will be able to maintain its ecological integrity over time.  Below is a series of photos and graphs that tell that story – at least the story up to this point.

This is what the 1995 seeding looked like in its 5th growing season. Species such as prairie clovers, perennial sunflowers, and other "matrix prairie plants" were abundant. Management to this point in time consisted of a couple of prescribed fires.

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During the drought years between 1999 and 2006, there were times that the combination of intensive grazing and drought really stressed the plant community. This July photo shows warm-season grasses that have gone dormant, but also shows plant species such as rosinweed and prairie clover that were still green and growing - and largely ungrazed.

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Within our patch-burn grazing system, a new portion of the prairie is burned each year, and intensive grazing tracks those burned areas across the site. Once a new patch is burned, the previous burn patch begins to recover from intensive grazing. This photo shows a burned patch the year after it was burned. The combination of drought and grazing made it look like a young prairie seeding again because of the abundance of short-lived weedy plants that were able to take advantage of the weakened grasses.

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A burned patch in June, showing grazing impacts focused mainly on grasses, leaving many forbs ungrazed.

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Under a light to moderate stocking rate, cattle display their selectivity (choosing to graze grass over forbs) - resulting in a very patchy prairie with short grasses and tall wildflowers.

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In unburned patches, very little grazing occurs - providing rest for the plant community. This photo was actually taken this week, in a portion of the prairie seeding we fenced out this year to provide complete rest from grazing. We're beginning to include some periods of complete cattle exclusion into our patch-burn systems to ensure that no plant species is grazed every year. This growing season was very wet, so the rested prairie grew very tall - even though it had been grazed fairly hard in 2010.

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This graph shows the mean floristic quality of the prairie seeding between 2002 and 2011. These data are collected from approximately 100 1m plots each year. Floristic quality is calculated within each 1m plot and averaged across the site. Error bars indicate 95% confidence intervals. Mean floristic quality has remained stable during the entire sampling period.

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While the mean floristic quality of the prairie has remained stable, the frequency of some individual plant species (% of plots the species occurs in) has varied from year to year. This graph shows frequency (from top to bottom of the legend) of marestail, foxtails, annual brome, black medick, and curly dock - all opportunistic (weedy) species that would be expected to act in just this way.

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More variability in the frequency of plant species between years. This graph shows (from top to bottom) stiff goldenrod, Canada goldenrod, heath aster, western ragweed, daisy fleabane, and hoary vervain. Interestingly, the species don't seem to track with each other - indicating that each is driven by its own unique set of factors.

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In contrast to the two earlier graphs, these data show that perennial native grass species have relatively consistent frequencies between years - even though they were subjected to periodic years of severe drought/fire/grazing. From top to bottom, this graph shows data for big bluestem, Canada wildrye, indiangrass, little bluestem, prairie cordgrass, and switchgrass.

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Similar to the perennial native grasses, many long-lived prairie wildflowers are also maintaining stable frequencies between years. Species that were common in 2002 are still common now, and species that were uncommon remain the same. Though I'm only showing a subset of species in these graphs, I've not seen any plant species disappear from this prairie.

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Like others who restore prairies, I’m still experimenting with techniques for both establishing and maintaining diverse prairie plant communities.  However, data like these help me feel more comfortable that I’m being relatively successful to this point – and I see similar patterns in other seedings we’ve done.  I’m also more and more impressed with the toughness of prairies and prairie plants.  I tried to include photos that showed the kinds of variable stresses this prairie has endured during its 17 growing seasons.  Watching this and other prairies survive what they’ve survived helps keep me from worrying so much about whether the coming year will be dry or wet, or whether we’ve got the right number of cattle in the prairie each year. 

As I said earlier, there is still much to learn about how animals (vertebrates and invertebrates) are using our seedings, but that is a separate avenue of exploration.  Building resilient plant communities around and between those remnants is the first step to better prairie viability. 

So far, so good.

Innovation in the Dakotas

It’s always fun to hang out with innovative people, especially when they’re working on the same kinds of challenges I am.  I was invited to spend several days last week at a South Dakota prairie restoration (reconstruction) workshop, organized by and for staff of the U.S. Fish and Wildlife Service.  Tom Koerner, an old friend from when he worked in central Nebraska, asked me to come up and share what we’ve been doing with prairies, and I was glad for the chance to see what’s happening up north.

Tom Koerner (right) of the U.S. Fish and Wildlife Service talks with colleagues about prairie restoration near Madison, South Dakota.

The Fish and Wildlife Service refuges in the Dakotas have a long history of restoring and managing wetlands and surrounding uplands as primarily duck habitat.  Recently, a few biologists and managers have begun questioning the relatively narrow focus on ducks, in view of the much broader mission of the agency (“The U.S. Fish and Wildlife Service’s mission is, working with others, to conserve, protect and enhance fish, wildlife, and plants and their habitats for the continuing benefit of the American people.”).  Rather than planting non-native grasses and legumes as duck nesting cover, they say, the Service could be adapting high-diversity restoration techniques used in nearby states to better accomplish their broad mission.  To those of us who have been working with high-diversity prairie/wetland restoration for years, the decision seems like a no-brainer, but there are several significant obstacles standing in the way for the Fish and Wildlife Service.

The first obstacle is really inertia.  The refuge system in the Dakotas has established a strong reputation as a duck production area among the public, and refuge managers have established techniques and strategies that have been consistently used for many years.  It’s difficult to convince someone to change what they’ve been doing over their entire career, especially when you’re asking them to start using a technique they’re unfamiliar with.  To those who haven’t used it, high-diversity restoration sounds expensive and risky – and what if it isn’t good for ducks?

The second obstacle is invasive species.  In much of the Dakotas, and certainly on the sites we visited near Madison, South Dakota, Canada thistle is a pervasive and invasive threat.  Taking land out of crop production and planting perennial vegetation often produces large dense crops of Canada thistle (except when it doesn’t – but there isn’t currently a good way to predict that outcome!).  Because Canada thistle is both aggressive and a state-listed noxious weed, the Service can’t ignore large populations of the species in restored grassland areas, and has to act to control it.  Small patches can be spot-sprayed, but many areas become infested so heavily that they have to be broadcast-sprayed.  This makes planting a diversity of plant species a risky endeavor, because there’s a pretty good chance much of that diversity will have to be sacrificed during Canada thistle control efforts.

The third obstacle is the cost.  The perception is that high-diversity restoration is much more expensive than simply planting several species of exotic grasses and some alfalfa.  There is obviously some truth to that.  Particularly if you’re buying the seed you use, a diverse mixture of native prairie seed can be very expensive.  However, there are several other ways to measure and mitigate costs.  For example, if seed is harvested by agency staff and volunteers, a lot of seed can be obtained pretty cheaply.  It’s amazing how much seed a few people can harvest in just a little bit of time when they’re organized and efficient about doing it.  In addition, the alternative is Dense Nesting Cover (DNC), consisting of exotic grasses and alfalfa, which typically has to be torn up and replanted every 7 years or so when the alfalfa starts to disappear, so over the long term, the costs of that method are higher than it might seem at first.  Combining the Canada thistle threat with the perceived cost, however, makes a pretty strong counter argument to those pushing for high-diversity – and that argument was the main subject of the workshop last week.

Bryan Shultz (left) walks with others through a two-year-old seeding.

Madison, South Dakota was chosen as the location for the workshop because that Wetland Management District has been experimenting with high-diversity restoration for the last several years.  Kyle Kelsey and Bryan Schultz are leading that charge, harvesting seed and experimenting with techniques for establishing it in the face of tight budgets and Canada thistle.  Bryan, like Tom Koerner, has ties to prairie restoration work in Nebraska, having worked at the Boyer Chute National Wildlife Refuge on the Nebraska side of the Missouri River earlier in his career.  (I’m sure these Nebraska ties are just coincidence, but it IS interesting that John Leisner with the South Dakota Game, Fish & Parks, who is helping lead the way for high-diversity within that agency, also started his career in Nebraska…)

To account for Canada thistle and build diverse prairie restorations, Bryan and Kyle are trying a combination of strategies.  First, they are harvesting as much seed as they can – from local sources.  Their diversity is increasing each year, as they find more seed sources (and create their own in newly-restored prairies).  Second, they are dealing with first-year weeds by applying Plateau herbicide in the first spring.  That herbicide application helps suppress Canada thistle, along with some annual weeds such as foxtail.  They also do some mowing of annual weeds when they grow so densely that they block sunlight from hitting the ground.  Finally, if Canada thistle does appear, they control it by spot spraying, if possible, and broadcast spraying only when absolutely necessary. 

Both the Plateau herbicide in the spring and the Milestone herbicide for later thistle control are relatively selective herbicides – though grass and wildflower species that are tolerant of one are not necessarily tolerant of the other.  As we walked around the sites, it appeared to some of us that the Plateau herbicide might not be necessary, judging by some areas that were not sprayed.  The herbicide application appeared to increase the speed with which dominant warm-season grasses established, and knocked out some wildlflower species – both of which run counter to Bryan and Kyle’s objectives.  The weed control provided by the herbicide did alter the weed species composition, but it looked like the unsprayed areas were going to establish equally well (maybe better) compared to the sprayed areas – and might actually have better species diversity in the long run.  Experimentation over time will provide better answers than our brief observations last week.

The Milestone herbicide applications seem to be effective, because the chemical is certainly effective at controlling Canada thistle, and there are quite a number of wildflower species that are tolerant (recover within a year or two) to being sprayed.  Broadcast spraying definitely reduces plant diversity, but that’s only used when absolutely necessary, and spot spraying is used much more often.  That spot spraying helps maintain diversity by only applying chemical to small areas and the selectivity of the herbicide means that even sprayed areas maintain some plant diversity. 

In addition to chemical control, Service staff are working on a research project with Dr. Jack Norland of North Dakota State University to see if they can find ways to increasing seed rates of forb species that might compete strongly with Canada thistle without decreasing overall prairie diversity.  This study is intriguing because, in contrast to a couple similar projects I’m aware of, they’re targeting a single invasive species and are trying to find forb species with similar life strategies to compete with the invader.  They’re only in their second field season, so it’s difficult to say how the project will work out, but I like the way they’re thinking.

Participants of the Fish and Wildlife Service's prairie restoration conference walk through a second-year restored prairie near Madison, SD.

Bryan, Kyle, Tom, and the rest of the Fish and Wildlife Service staff in the Dakotas have a long learning curve ahead of them, but they’re doing great work.  Most importantly, they’re jumping in with both feet and building some experiment/demonstration sites that will help address the questions being asked by themselves and others about the potential for high-diversity seedings to work in the Dakotas.  Some of their young seedings are already looking great, and it’s hard to imagine standing in one of them and thinking that a seeding of exotic grasses and alfalfa would be superior.  On the other hand, success hasn’t been consistent yet (Canada thistle has come in strongly in some seedings) and it’ll be interesting to see how their plant diversity looks over time.  They’re getting tremendous growth of warm-season grasses in first and second year seedings, which is nice in some respects, but may make it difficult to obtain and maintain plant diversity in the long term.  However, as trips around the country constantly remind me, techniques and results that apply to one site often don’t apply elsewhere, so it’s good to try many different things to see what works best locally.

Lots of questions, lots of ideas, and lots of experimentation.  Sounds like prairie restoration to me!