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?)

Hubbard Fellowship Post – S’Mammals with Jasmine

This is a post written by Jasmine Cutter, one of our 2014-15 Hubbard Fellows.  All photos are by Jasmine.

Howdy, Prairie Ecologist friends!
I remember how much I looked forward to the Fellows’ posts before coming to the Platte River Prairies, so I apologize for the glacial pace of my updates.  A considerable amount of my time and brainspace over the last two months has been occupied by small mammals (or s’mammals, as I prefer to call them). There are definite challenges to undertaking a project during the growing season (namely balancing project time and stewardship time), and throughout the process of the project and the summer there have been some unexpected surprises (mostly good), and a lot, a lot of learning.

Mike Schrad, Nebraska Master Naturalist and my small mammal project mentor.

Mike Schrad (left), Nebraska Master Naturalist and my small mammal project mentor.

In the briefest of terms, I’ve been tromping through our Derr sandhills (a unit which includes both restored and remnant prairie on the edge of the Platte River Valley), battling cows, thunderstorms, and a lack of sleep in the pursuit of learning more about the small mammal community in this unit. I was initially drawn to this site because the Derr sandhills contain pocket mice (Perognathus flavescens) and Northern grasshopper mice (Onychomys leucogaster). The pocket mice are minute, streamline and silky, whereas the grasshopper mice are beefy and aggressive (and probably also soft, but getting your finger near enough to find out is tricky), yet, despite their differences, they’re both endemic to sandy soils. As these critters are relatively unusual, my study will give us a chance to learn more about their habitat preferences, and hopefully enable us to manage the site in a way that ensures the continuation of healthy populations. Although these two species have remained the most endearing through out my study, my affection has also expanded to include shrews (they have venomous saliva and black-tipped teeth!), voles (ferocious teddy bears) and harvest mice (very agile and keep a neat nest). Deer mice tend to have a heavy parasite load and botfly sores (not to mention the possibility of hantavirus and carrying lyme disease), and therefore are often pretty icky. At this point, I am done with trapping for the most part. Soon, I will be collecting vegetation and site data for each trap site (that’s ~370 sampling points!), and this winter, I will be seeing if there are any relationships between the presence of certain species and site characteristics.

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Beefy lil grasshopper mouse, so-called due to their carnivorous diet. At night, they sing to defend their territories.

Pocket mouse. The clip on its tail is what is attached to the scale used to weigh them. While it is undoubtedly a little uncomfortable, there is no permanent damage. The clip is a helpful way to hold onto animals so I can take a photo. It’s essential to my study that I am able to document how the pelage (fur) color varies between individuals.

Pocket mouse. The clip on its tail is what is attached to the scale used to weigh them. While it is undoubtedly a little uncomfortable, there is no permanent damage. The clip is also a helpful way to hold onto animals so I can take a photo. It’s essential to my study that I am able to document how the pelage (fur) color varies between individuals.

Scary shrew teeth. Unlike the rest of the similarly-sized critters I caught, shrews are not rodents. They are in the order Soricomorpha. They are mostly carnivorous and have saliva that paralyzes their prey.

Scary shrew teeth. Unlike the rest of the similarly-sized critters I caught, shrews are not rodents. They are in the order Soricomorpha. They are mostly carnivorous and have saliva that paralyzes their prey.

There have been a few surprises during this project. For example, I have discovered that cows don’t like science. They have eaten my flags, licked my traps several feet off my transect, and squashed a few for good measure. If only their curiosity could be used more constructively!

One of the best surprises was opening one of my traps and finding a least weasel inside! I was waaayyy more intimidated by this critter than it was by me. Despite its ferocity, it was impressively lightweight. This littlest weasel was longer than the thirteen-lined ground squirrels that I also caught that day, but considerably lighter. The ground squirrels maxed out my 100 gram scale, whereas the weasel was only 70 grams! The weasel was also impressively smelly, living up to the family name of mustelidae.  I was a little worried that no other small mammals would go into that trap the next night because it smelled of predator, even after I sprayed it with Lysol. However, the harvest mouse I caught the next night was undeterred. No wonder s’mammals have such a short lifespan. Another surprising find on a different transect was an embarrassed-looking leopard frog. My bait seems to attract a lot of crickets, so I imagine that’s what lured the frog. And the cutest capture was these two baby voles that managed to wander into one trap.

Thirteen-lined ground squirrel (Ictidomys tridecemlineatus). When I open a trap, I gently plop the critter into a bag in order to minimize handling exposure. I can weigh, identify and sex the critter while it’s in the bag. It’s safer for me, and the animal is only in there for a few seconds to a minute.

Thirteen-lined ground squirrel (Ictidomys tridecemlineatus). When I open a trap, I gently plop the critter into a bag in order to minimize handling exposure. I can weigh, identify and sex the critter while it’s in the bag. It’s safer for me, and the animal is only in there for a few seconds to a minute.

Weasel tryptic. Although none of these manage to capture the full length of the weasel (Mustela nivalis), they do manage to capture what you’d be likely to see - a reddish blur.

Weasel tryptic. Although none of these manage to capture the full length of the weasel (Mustela nivalis), they do manage to capture what you’d be likely to see – a reddish blur.

Baby voles!

Baby voles!

In addition to the excitement of peeking into every closed trap, there have been other perks to the project. I’ve gotten to see way more sunrises and sunsets than I would have otherwise. I love the freshness of the mornings, how the grass glows orange, and the spiderwebs glisten, and how much my mood (and finger mobility) improves once the sun crests the sandhills. I’ve gotten to hear the weird robotic chirpings of the swallows at sunset. The light at these times is able to make pretty much any photo look amazing, so it’s a little less discouraging to compare some of my photos to Chris’. I have also really enjoyed the slower pace of sampling, of covering my transect by foot. I spend a lot of time in the prairies, but infrequently do I have time to slow down and appreciate how the prairie community changes meter by meter. I have gotten to know my transects well, and I look forward to seeing if/how the patterns I’ve noticed play out in the data.

I’ve taken thinking like a s’mammal maybe a little too much to heart. Whenever we visit a new prairie, I think, ‘this looks like good pocket mouse habitat, I wonder if they have any? I wish I had my traps…’. I am also really grateful that so many mammalogists have been willing to donate their time and resources. I’ve learned a lot about species identification from them, and it’s exciting to make new connections with other institutions.

Sunrise!

Sunrise!

My pile of science. Traps generously lent out by Montana State University and Kansas State.

My pile of science. Traps generously lent out by Montana State University and Kansas State.

Pocket mouse pockets. They store seeds in there to bring back to their nest cache.

Pocket mouse pockets. They use external fur-lined cheek pouches to store seeds until they can bring them back to their nest cache.

This is not to say that this project has not had its challenges. I would say the main struggles have been setting reasonable goals (never a strong suit), keeping track of all the moving pieces (Do I have all my equipment? Am I recording all the right info? When do these traps need to be mailed back to Montana?), not losing things (Luckily the two mice than ran off with my scale clips were recaptured the next day!), and figuring out how to do the majority of the sampling by myself. It has been a long, time-intensive process for just five sampling transects. And, the project has not been without its dangers. The most dangerous part of the study has definitely been cacti. You wouldn’t believe the number of cacti I’ve accidentally kneeled on, or kicked into myself! I don’t recommend it. But, when these aspects of fieldwork start to get me down, I remind myself that I caught a weasel, and that’s pretty freaking cool.