Category Archives: Prairie Management

Trying to Create Something Different in the Nebraska Sandhills

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At our Niobrara Valley Preserve (NVP), we’re experimenting with prairie management techniques to see if we can create a wider range of habitat conditions than is found throughout much of the Nebraska Sandhills.  On many Sandhills ranches, pastures look fairly similar to each other in terms of vegetation structure.  That’s because Sandhills ranchers tend to be careful in their grazing management to avoid wind erosion that can cause “blowouts” of bare sand.  As a result, pastures are rarely grazed intensively enough to create wide expanses of bare ground.  If intensive grazing does happen, it’s usually on a small scale and/or for short periods of time, which allows for quick recovery of grasses.

The Nebraska Sandhills have tremendous innate heterogeneity.  Just in this photo, you can see areas of bare sand created by pocket gophers and/or other animals, habitat structure created by various kinds of plants, including grasses, wildflowers, yucca, and shrubs.  Vegetation height varies greatly across small areas.

Overall, the ecology of the Nebraska Sandhills seems very healthy.  It’s a huge and mostly intact grassland landscape, and because of the dry sandy soils, topography and diversity of vegetation, there is quite a bit of habitat heterogeneity that is independent of management.  As you walk across most Sandhills pastures, you will move through both short/sparse vegetation and taller/dense vegetation, and occasionally come across other structural components like yucca plants or plum thickets.  Wildlife and insect species can often find the habitat structure they need somewhere in that pasture, though it might be in a small patch surrounded by other habitat types.  That seems to be true even for many bird species, which have relatively large breeding territories.  As an example, in pastures with fairly tall vegetation, we often see and hear horned larks that are (apparently) nesting in a few small and scattered patches of the short vegetation structure they prefer.  Those patches of short habitat often occur in gravelly flat areas or in favorite feeding areas for cattle, where grass growth is weak because of frequent grazing.

This late July photo shows a portion of our west bison pasture that was burned this spring and has been grazed intensively by bison all year. Because bison are in the pasture year round, they had immediate access to the burned area and started grazing regrowth as soon as it was available.

We’re trying to figure out more about how management with patch-burn grazing or other similar grazing systems affects Sandhills ecology.  Patch-burn grazing has part of the management of our bison pastures at NVP since the early 1990’s.  Because of that, we know Sandhills vegetation can recover from fires that are followed immediately by season-long intensive grazing.  However, we still don’t know much about how many animal species might respond – positively or negatively – to the kind of large patch heterogeneity created by this kind of management.  Instead of pastures with interspersed small areas of tall and short vegetation, we’re trying to create large patches (500-1000 acre patches within 10,000-12,000 acre pastures) of each habitat type and then shift the location of those patches between years.

Plains sunflower (an annual) often becomes very abundant after fires because it germinates well in exposed soil and then thrives in the absence of strong competition from perennial grasses.  This is the current year’s burn patch in our east bison pasture, where plains sunflower tall and blooming, surrounded by short-cropped grasses.

Creating large patches of various habitat types could bring both advantages and disadvantages to different species.  As an example, large patches could create an abundance of resources that support larger and more viable populations of some animal species. On the other hand, a vole who likes thatchy habitat could wake up in the middle of a 1000 acre burn, and it would have to make a long dangerous trip to find a more suitable place to live.  Trying to evaluate those potential costs and benefits is a big challenge for us.

This landscape shot shows the abundance of plains sunflower across the entire burned patch.

One possible advantage of the kind of shifting mosaic of habitat approach we’re trying is that it helps avoid risks that come from having the same habitat conditions in the same place year after year.  Just as crop rotation can help avoid buildups of pests and pathogens, shifting habitat types from place to place could have important benefits.  For example varying the location of habitat types from year to year could limit disease outbreaks and help prevent predators or herbivores from building up large and potentially destabilizing populations.

Showy evening primrose, aka fourpoint evening primrose (Oenothera rhombipetala) where the prairie was burned in 2015 and grazed intensively in both 2015 and 2016.  This opportunistic biennial is taking advantage of a long period where grasses are weakened by prior intensive grazing and haven’t yet recovered.

The most intriguing part of our experimentation for me, though, is the idea that we could create large ‘recovery patches’ where grasses have been weakened by a full season of intensive grazing and the plant community is temporarily dominated by opportunistic, mostly short-lived plant species.  That combination of short grasses and tall ‘weedy’ wildflowers can provide excellent brood-rearing habitat for some birds and important structure for reptiles and invertebrates that need to regulate their body temperature by moving quickly from sun to shade as needed.  Studies in other landscapes have shown that this kind of recovery patch habitat creates pulses of high insect biomass, which could have numerous impacts – including the provision of an awful lot of food for wildlife.  In addition, if an abundance of opportunistic plants include species beneficial to pollinators, that could provide quite a bonanza of resources for bees, butterflies, and other insects.

Zoomed out

In most of the Sandhills, patches of  ‘weedy’ habitat tend to be in small, static and widely scattered locations such as around windmills or other places where cattle or bison frequently congregate.  We’re wondering what might happen if we created big patches of the same habitat type and shifted their location from year to year.  In our Platte River Prairies, patch-burn grazing (and similar strategies) has sustained prairie plant diversity over many years, but we haven’t looked closely for similar responses in the Sandhills.  In addition, we know a little about how birds respond to patch-burn grazing in the Sandhills, but not much about impacts on other species like lizards, pollinators, small mammals, or invertebrates.  Now we’re trying to collect data on the responses from all those different organisms.

The lesser earless lizard is often found in and around sand blowouts or other habitat patches with abundant bare sand.  Will they respond positively to much larger patches of sparse vegetation?  Can they successfully shift their population locations as we burn/graze new sites?

Will pollinators such as this plasterer bee (Colletes sp) benefit from higher abundances of flowering plants in big patches of Sandhills prairie that are recovering from season-long intensive grazing?

This is part of our east bison pasture that hasn’t burned since 2012, and has been only lightly grazed during that time period.  It should support a different array of wildlife and allow different plant species to thrive than more recently-grazed areas.  Providing a wide range of habitat types across the prairie seems beneficial for biological diversity, but we still need to test that idea in the Sandhills.

I’ve really enjoyed digging into all the questions we have about our attempts to create more habitat heterogeneity in the Sandhills.  We haven’t had time to answer many questions yet, but we feel like we’re at least creating something different than what exists throughout most of the Sandhills landscape.  A few years from now, we might conclude that the heterogeneity we created didn’t really result in any significant positive or negative impacts compared to what exists elsewhere.  If that’s the conclusion, we’ll move forward with that in mind.  On the other hand, we might find that there are some important positive (and/or negative) impacts of the shifting mosaic approach we’re testing.  In the meantime, it’s exciting to have the opportunity to try something different and watch what happens.  Stay tuned…

If nothing else, huge populations of Plains sunflower like this one in our west bison pasture provide a different (and I think beautiful) look to parts of the Sandhills landscape at the Niobrara Valley Preserve.

Down A Deer Vetch Rabbit Hole

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A single observation recently led me down a pleasant rabbit hole of data, plant species trends, and unanswered questions about interactions between climate, grazing, fire, soils, and other factors.  Read on if you want to follow me down that hole…

The journey started because I noticed an abundance of deer vetch (Lotus unifoliolatus) in one of our restored prairies this year.  Deer vetch (also known as American bird’s-foot trefoil, though not the bird’s-foot trefoil you’ve probably heard of) is a native annual legume that likes sandy soils.  It’s a neat little plant and we target it during seed harvesting efforts to ensure that it shows up well in our restored prairies.  I first noticed a lot of deer vetch in the portion of prairie that was burned and intensively grazed all of last year, so I figured it was responding to that grazing.  But then I found even bigger patches of it in the other half of the same prairie where there had been no fire and only very light grazing.  Interesting…

Deer vetch, aka American bird’s-foot trefoil (Lotus unifoliolatus – formerly Lotus purshianus)

This prairie was established on former cropland in 2000, using a seed mix of about 180 different prairie and wetland species.  It is one of our showiest sites, in terms of flower abundance and color.  Below are a couple photos of from the portion of the prairie that was burned in the spring and intensively grazed all summer (as part of a patch-burn grazing system).  You can see from the images that most of the grass was grazed pretty short all season.  Many of the wildflowers in the burned patch were also grazed, but some still managed to bloom and set seed.  I apparently didn’t get any photos from the unburned/ungrazed side of the prairie last year, so you’ll just have to squint at these and imagine them with taller grass and more blooming flowers…

In 2016, the west half of this restored prairie was burned and then grazed intensively all season. This August 2016 photo shows that most of the grass was very short, though at least some wildflowers were ungrazed.

Here’s another August 2016 photo of the intensively grazed portion of the prairie. Note the grazed Canada milkvetch (Astragalus canadensis) plant near the lower left corner of the image. That species and rosinweed (Silphium integrifolium) are two of the favorites of cattle at our sites.

As it happens, I collect data from this particular site every other year as part of a project looking at how plant communities respond to management within our prairies.  To collect the data, I walk back and forth across the prairie and lay down a plot frame at regular intervals.  I list all the plant species that occur within that one square meter plot frame each time I set it down.  The data allow me to look at trends in individual species populations and at how species diversity/richness changes over time.  Here is the data for deer vetch, which confirms my observation that it is having a particularly good year.  In 2017, it showed up in about 35% of my sampling plots.

The relatively steady increase of deer vetch over time made me wonder if other short-lived plants were acting the same way.  I pulled out some of the more common annual and biennial species at that prairie and graphed them out.

In order, the species on this graph are: small peppergrass, six-weeks fescue, annual sunflower, yellow woodsorrel, black medic, and deer vetch.

Clearly, not all the short-lived plants were following the same trend as deer vetch, but it was striking to see how many had a peak in abundance in 2013, the year after our severe 2012 drought.  That makes sense since the drought was pretty hard on perennial grasses and other strong competitors in the prairie.  It created space for opportunistic plants to exploit.  However, not all of the short-lived plants followed the same pattern of response to the 2013 drought.

The plants listed on this graph are marestail, downy brome, and white sweet clover, though I lump downy/Japanese brome and white/yellow sweet clover together in my data.

None of the three species in the above graph show any noticeable response to the drought.  Instead, they each seem to be on their own path.  Marestail has declined significantly since the early days of the prairie’s existence, but had a resurgence (for some reason?) in 2015.  Sweet clover has been persisting at relatively low levels during the entire life of the restoration, and annual brome has been on a steady increase, much like deer vetch.  We’re far enough east that our average annual rainfall (25 inches/year) keeps annual brome from being problematic, so I’m not concerned about that increase, but I was curious whether or not deer vetch and annual brome were filling a gap left by the decline of other species.

Next stop on the rabbit hole journey coming up…

The species in this graph’s legend are Canada wildrye, big bluestem, Indiangrass, short-beaked sedge, and Kentucky bluegrass.

Thinking maybe declining grass dominance might explain the rise of deer vetch and annual brome, I looked at how the populations of perennial grasses are doing at the site.  In most cases, they are on an upward trend.  The above graph shows some of the more abundant perennial grasses and sedges in the prairie and the graph below shows some of the less abundant species.  (There are many more grass species not shown because they don’t appear often enough in my sampling plots to see patterns.)  A glaring exception to the overall pattern is Canada wildrye (Elymus canadensis) which seems to be following the same pattern as it does in most of our restored prairies – it is very abundant when the prairie is young and then gradually declines to about 30% occurrence after 10-15 years.

These less abundant (but still common) grasses are: Scribner’s panicum, switchgrass, little bluestem, tall dropseed, and smooth brome.

By this point, I’d kind of forgotten why I’d started my journey, but after looking at annual plants and perennial grasses, it seemed logical to look next at perennial wildflowers.  Some of those species have also been pretty steadily increasing over time, and may or may not be leveling off in recent years.

Plants listed in the legend are western ragweed, wild bergamot, woolly yarrow, and stiff sunflower.

Other perennial wildflowers have had much less predictable paths, with big jumps between sampling periods, during which they (at least) doubled their level of occurrence in my sampling plots.  Interestingly, those jumps happened in different years for each species.  Having data only from every other year makes it tricky to interpret these patterns, but it seems clear that each of these species is responding a little differently to factors such as climate, fire, grazing, and/or competition from other plants.

These species are Illinois bundleflower, hoary vervain, stiff goldenrod, and heath aster.

Many of the wildflowers shown in the above two graphs are species that I’d expect to thrive under patch-burn grazing.  With the exception of stiff sunflower (Helianthus pauciflorus), Illinois bundleflower (Desmanthus illinoensis) and heath aster (Aster ericoides), they are plants that cattle don’t particularly care to eat.  The plant species I watch most carefully under this kind of management are those that are favorites of cattle.  The graph below shows those species maintaining very steady population numbers.  None of them are super abundant, but they’re holding their places very well.

Species here are white prairie clover (purple prairie clover shows a similar pattern but is slightly less abundant), Canada milkvetch, and rosinweed.

Prairie clovers (Dalea sp) are certainly enjoyed by cattle, but rosinweed (Silphium integrifolium) and Canada milkvetch (Astragalus canadensis) must taste like brownies to our cattle – they are grazed down to the ground wherever they grow, regardless of whether they’re in the burned or unburned portion of the prairie.  Because of the affinity cattle have for species like this, we periodically exclude cattle from our prairies for an entire growing season, giving those plants a chance to bloom and produce seeds, buds, and rhizomes.  This is actually one of those years in which we’ve excluded cattle, and it’s nice to see abundant flowers from both the rosinweed and milkvetch.

Canada milkvetch is blooming prolifically this year in the absence of cattle – it is shown here in the same area that was grazed intensively all last year and grass vigor is still suppressed.

Here’s Canada milkvetch in the area not grazed hard last year – the grasses are much taller here…

Of course, looking at how individual species are doing made me wonder how all those trends add up at the community level.  Here is a graph showing how the average species richness (number of species) at the square meter level has changed over time.

This graph shows the average number of plant species found in square meter plots each year. In our part of Nebraska, 10-12 plant species per meter is a very respectable number.  It appears we may have reached a saturation point for species density in this site, though there is still variation from year to year.

Looking through all of these data, I see two main themes.  First, I see a restored prairie that is still finding its identity, even after 17 years.  Some plant species are still increasing in their abundance (including many not shown here). I expect many of those trends to level off within the next several years as those species find and colonize all the little patches of prairie where they are well adapted to growing.  That would fit with what seems to be a plateau in terms of species richness per square meter.  I don’t see any plant species (including those not shown here) that have disappeared from the site, and only a few short-lived species that have declined precipitously over time – and even those still appear to remain embedded within the community, able to proliferate whenever the right conditions appear.

Second, I see positive signs of ecological resilience in the way many of these plant species have quickly increased and decreased their population sizes over time.  Sometimes I can tell what conditions (fire, grazing, drought) might have led to those population changes, but other times I can’t.  Regardless, the ability of a community to flex and adapt as conditions change is a key component of ecological resilience, and it’s really great to see that within a restored prairie.

 

……..What was I talking about again?

Oh yeah, deer vetch.  Yep, deer vetch is doing really well this year.  Thanks for asking.

One last photo of the area burned and intensively grazed in 2016. Rosinweed (yellow flower in the foreground) can be seen blooming throughout the site, along with many more opportunistic plants such as the pink-flowered wild bergamot.