Down A Deer Vetch Rabbit Hole

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.


About Chris Helzer

Chris Helzer is the Director of Science for The Nature Conservancy in Nebraska. His main role is to evaluate and capture lessons from the Conservancy’s land management and restoration work and then share those lessons with other landowners – both private and public. In addition, Chris works to raise awareness about the importance of prairies and their conservation through his writing, photography, and presentations to various groups. Chris is also the author of "The Ecology and Management of Prairies in the Central United States", published by the University of Iowa Press. He lives in Aurora, Nebraska with his wife Kim and their children.
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6 Responses to Down A Deer Vetch Rabbit Hole

  1. Matt BS says:

    Hi Chris,
    Have you tried any multivariate analysis on this data set? There are some powerful tools that can really help clarify those relationships.

    • Chris Helzer says:

      Hi Matt, I haven’t done too much with multivariate stats yet – the management is hard to quantify because it is different every year and often has split treatments within each site. However, one of our Hubbard Fellows is working on analysis of four of our restored sites (long-term data) and we’ll be submitting a manuscript on those data sometime this winter, I hope.

  2. James McGee says:

    I don’t think you’ve reached a saturation point yet. There are always a number of species for which such small quantities of seed are collected that they are very sparse. I expect it will be a few more decades before these species will be frequent enough to start showing up in your meter plots.

  3. Daniel Thhommpson says:

    Fascinating post, Chris. I am a biologist, legally, but I’m eager to learn and practice collecting data regarding individual plant quantity and distribution. I will keep your post for a while and examine it several times and see if and how my couple of books about statistics for biologists relate. -Daniel

  4. Gary Gerth says:

    Chris , I vote for ecological resilience. For the last 10 years I have been observing annual fluctuations on a mountain foothills site east of the continental divide in SW Montana that can be described as an ecotone between intermountain basin and short-grass prairie; i.e. Indian ricegrass, Basin wildrye, bluebunch wheat grass, western wheatgrass green-needle, needle and thread, at least 13 different grass species, and a number of forbs. There has been considerable plant fluctuation even while changes in weather conditions SEEM rather subtle. This year brought the largest expression of 6 weeks fescue and Plantago purshii I have seen, and in a drier than normal year; last fall had unusually ideal soil moisture. In only 1 year out of 10 have I seen much show on a small milkvetch. That was an unusually cool wet spring.BTW, I am happy to see the Plantago & Six Weeks Fescue since there is a lot of cheatgrass in the area.

  5. Pingback: Does Dotted Gayfeather Flower More Under Reduced Competition? | The Prairie Ecologist


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