Bison Good, Cattle Bad??

Among some prairie enthusiasts, there seems to be a perception that plains bison are magical creatures that live in complete harmony with the prairie.  They eat grasses but not wildflowers, they float just above the ground to avoid stepping on plants or compacting the soil, and they create tidy little wallows that fill with rainwater for tadpoles and wading birds.  Cattle, on the other hand, are evil creatures that seek and destroy wildflowers, removing them from prairies forever.  They also stomp all over prairies, trampling plants and birds to death and causing cascades of soil erosion and water pollution.

Seriously?

These particular magical animals are at The Nature Conservancy's Broken Kettle Grasslands in northwest Iowa.

These particular magical animals are at The Nature Conservancy’s Broken Kettle Grasslands in northwest Iowa.

Let me be clear: I’m a big fan of bison.  I feel very fortunate to spend time at The Nature Conservancy’s Niobrara Valley Preserve and other big prairies where I can observe and photograph bison up close.  Bison are distinctive, attractive animals that evoke a sense of history and grandeur… but they are also big stompy animals that go wherever they want, poop all over the place, rub on trees, trample plants (and animals), and can cause erosion issues.  None of that is good or bad; it just is.

I’m a fan of cattle too.  They have big beautiful eyes, individual personalities, and can be more playful than their typically stoic faces might hint at.  I enjoy spending time around cattle at our Platte River Prairies and in my own family prairie.  In both places, they are a major part of our prairie management strategy, which is aimed at creating and maintaining diverse plant communities and high quality wildlife habitat.  (And yes, cattle are also big stompy animals that go wherever they want, poop all over, rub on trees, trample plants and animals, and cause erosion issues.)

 

TREES AND PONDS

While both bison and cattle can be engaging creatures, there are a few real differences between the way bison and cattle utilize and impact prairies.  However, those differences are less stark than you might think.  Based on the best available research and expert knowledge, the biggest distinction between bison and cattle behavior in prairies essentially boils down to this: cattle hang around water and trees more than bison do.

That general pattern is reported in many studies comparing the two, but was most reliably demonstrated in a recent study at The Nature Conservancy’s Tallgrass Prairie Preserve in Oklahoma, where GPS collars tracked animal locations through time.  That study looked at bison and cattle at similar stocking rates and under the same management regime (patch-burn grazing) – though the bison were grazing year-round in a 23,000 acre pasture while cattle were only present for 7 months/year in pastures of around 1000-2000 acres.  The GPS collars showed that cattle were attracted to ponds and trees while bison tended to avoid areas near water and showed no attraction to trees.  Importantly, the same study also showed strong similarities between bison and cattle behavior, namely that both were strongly attracted to the most recently burned areas of pastures and tended to avoid steep slopes.

The conclusion that cattle are attracted to water and shade fits with one of the big objections to cattle grazing by some prairie enthusiasts – that cattle tend to “wreck” areas near ponds and tree groves by repeatedly stomping around and defecating in those places.  While that can be true, those impacts are highest under high stocking rates, and can be avoided by fencing out ponds and trees or greatly reduced by providing long rest periods between grazing bouts.  Those impacts are also less severe in larger pastures, especially when multiple water and shade options are available and cattle are encouraged (or forced) to use each area intermittently.  The attraction of cattle to wet and shaded areas can be a real challenge, but it’s not an insurmountable one.

These cattle almost look ashamed of their tendency to hang around in water.

These cattle almost look ashamed of their tendency to hang around in water.  In this case, however, we were actually encouraging it as a way to help us control invasive cattails.  We pulled the cattle out the next season and this little spot was a great shorebird area, with mud flats with scattered sedges and rushes.

DIET

The other beef prairie enthusiasts have with cattle (sorry) has to do with their diet.  The perception of many is that bison subsist solely on grass, leaving wildflowers untouched, while cattle eat a high percentage of forbs (broad-leaved plants), often leading to the decline of those species over time.  The purported result is that bison-grazed prairies maintain high plant diversity, including an abundance of rare plant species, while cattle-grazed prairies become degraded as numerous forb species are grazed out of existence.  While that’s a big overgeneralization, it’s an understandable one because a number of research projects have reached that conclusion.

Unfortunately, those research projects have largely compared bison and cattle under very different circumstances.  Diet comparisons are usually made between bison in a single huge pasture (often under patch-burn grazing management) and cattle in a rotational grazing system – often at a higher stocking rate.  As a result, it’s not clear whether observed differences between bison and cattle diets are due to biological differences or grazing systems.

Imagine if you were given 30 days’ worth of groceries at the beginning of each month. You’d likely eat many of your favorite foods first and then make do with whatever’s left toward the end of the month. Comparing your diet to that of someone who was allowed to go grocery shopping every day would be completely unfair, wouldn’t it?  Unfortunately, that’s essentially the comparison made by many research projects comparing the diets of cattle and bison.  Cattle in a rotational grazing system can only choose from the available plants in their particular paddock, and don’t get a new set of choices until they are moved into a new paddock.  In contrast, cattle or bison that spend their whole season in a large pasture, especially one in which a portion has been recently burned, can regulate their diet much more freely.  They spend most of their time eating their favorite foods (mostly grasses) in the most recently burned patch, but they can also travel elsewhere if the supply in that patch runs low.  In addition, by regrazing their favorite plants over and over, livestock can keep them in a state of high nutritional value for much of the season.

We did some research back in 2001 in which we evaluated the forage choices of cattle in a patch-burn grazing system under a moderate stocking rate (Helzer and Steuter 2005).  Our data showed that those cattle were very selective toward grasses, and ate very few forbs under those conditions.  That research, along with observations other scientists and cattle managers at patch-burn grazed sites, has led to an altered perception of the forage selection differences between cattle and bison – namely, that many of the differences are driven more by grazing system than by biology.

This photo shows the kind of selective grazing cattle can do in a patch-burn grazing system with a moderate stocking rate.  Ungrazed forbs in this photo include purple prairie clover and stiff sunflower, among many others.

This photo shows the kind of selective grazing cattle can do in a patch-burn grazing system with a moderate stocking rate. Ungrazed forbs in this photo include purple prairie clover, Illinois bundleflower and stiff sunflower – among many others.  We like the impacts of this kind of grazing on both plant diversity and insect/wildlife habitat.

CHOICES

Prairie managers have to make difficult decisions about how to create and maintain diverse plant and animal communities at their sites.  One big choice is whether to graze or not to graze a particular prairie.  Regardless of whether it is grazed by bison or cattle, a grazed prairie is going to look and act very differently than an ungrazed prairie.  Many plants will be stepped on and eaten.  Some portions of the prairie will be more heavily visited than others and will get trampled down.  Short-lived opportunistic plants will become more abundant, due to the weakening of dominant grasses through repeated grazing.  Some managers will see those effects as positive, but others will not – depending upon the management needs of a particular prairie.  Regardless, deciding whether or not to graze has far greater consequences than the subsequent decision about whether to graze with bison or cattle.

If the decision to graze has been made, it’s important to recognize the appropriate criteria for deciding between bison and cattle.  Bison do act somewhat differently than cattle, especially around water and trees.  However, those differences depend heavily on scale.  Both cattle and bison create areas of bare soil around drinking water sources, and both create trails as they move from one favorite place to another.  In small pastures, those impacts are multiplied because both bison and cattle are forced to visit the same places repeatedly, which can lead to repeated trampling of plants, soil compaction, and other issues.  The differences between a small bison-grazed pasture and a small cattle-grazed pasture are pretty minimal.

In larger pastures (thousands of acres in size), grazing animals have room to spread out.  At that scale, bison-grazed pastures tend to have fewer heavily grazed and trampled areas near trees and standing water than cattle pastures do.  While that can certainly be a perk of using bison, it’s also important to remember that even in large cattle-grazed pastures, the proportion of the overall pasture that receives that kind of heavy impact is very small.  In addition, there are management options that can be used to minimize the size and severity of those impacts by cattle.  Those include fenced exclosures around sensitive areas and tactics that shift the locations where cattle spend most of their time (such as creating new burned patches, turning on/off drinking water facilities, and moving mineral feeders around).  The upshot is that there can be some prairie conservation benefits of using bison.  However, those benefits accrue most strongly in very large pastures, and even at that scale, there are cattle management strategies that can close that gap considerably.  On the flip side, bison come with their own set of complications and costs.

These bison are grazing in a 10,000 acre pasture at The Nature Conservancy's Niobrara Valley Preserve in Nebraska.

Bison at The Nature Conservancy’s Niobrara Valley Preserve in Nebraska.  These animals are in a 10,000 acre pasture where they have plenty of room to roam.

I spend most of my time working at our Platte River Prairies, and I’m often asked why we don’t have bison at those sites.  There are several good reasons for that, starting with management flexibility.  The cattle that graze our Platte River Prairies belong to our neighbors, and our lease arrangements allow us to dictate how many, where, and for how long cattle graze each year.  Between years, or even within years, we can pretty easily change those plans if we get unexpected weather patterns or just don’t like the way things look.  That kind of adaptive management is much more difficult with bison, especially because if we had bison, we’d have to own the herd and keep them on our prairies year round.

A second reason we use cattle is financial.  It takes a much lower investment in infrastructure and personnel to lease cattle than to own bison.  We have to provide a good perimeter fence (usually a four-wire barbed wire fence) to hold cattle in our pasture, and provide water for them to drink.  Beyond that, the owner of the cattle trucks them in when we ask for them, and then gathers and trucks them away again when we’re done.  If we owned a bison herd, we would need a much stouter, and more expensive fence, and a very expensive corral system to use for an annual roundup, sorting, and inoculation process.  In addition, we would be responsible for conducting that roundup, doctoring animals when if needed, and for dealing with buying/selling animals to maintain our desired herd size.  All of that takes time and people, and that’s expensive.  At our Niobrara Valley Preserve, the 22,000 acres of bison pasture can hold enough bison that income from selling excess animals covers many of those costs. That wouldn’t pencil out in our much smaller prairies down on the Platte River.

Conservancy employee Doug Kuhre runs the hydraulic-operated gates at a bison sorting corral at the Niobrara Valley Preserve.

Conservancy employee Doug Kuhre runs the hydraulic-operated gates at a bison sorting corral during an annual roundup at the Niobrara Valley Preserve.

The last reason we run cattle instead of bison is that in our relatively small prairies (200-600 acres), the behavior of bison would not be very different than that of cattle.  We might see less stomping around in standing water and under trees, but we can already manage those impacts by controlling whether/how often cattle have access to those areas.  Most importantly, through our use of patch-burn grazing, electric fence enclosures and exclosures, and our ability to set and change grazing intensity, timing, and frequency, we are getting the prairie management impacts we want by using cattle.  We can get cattle to graze very selectively in order to suppress grasses and give wildflowers a chance to flourish, and to create the kind of patchy habitat structure many wildlife and insect species need to thrive.  In other cases, we can get them to graze much less selectively in order to create a particular habitat structure or other impact.  As a result, we are maintaining resilient and diverse prairies – and that is our ultimate goal.

Cattle aren't so bad when you get to know them...  More importantly, they can serve as very effective tools for prairie conservation... even if they don't look exactly like bison.

Cattle aren’t so bad when you get to know them… More importantly, they can serve as very effective tools for prairie conservation… even if they don’t look exactly like bison.

CONCLUSION

Plains bison nearly disappeared completely from the grasslands of North America as European settlement spread across the continent.  The ongoing recovery of bison is an important indicator of prairie conservation success, and I hope that upward trend continues.  At the same time, I worry about the tendency of some to heap accolades upon bison while dismissing cattle as inherently destructive.  The differences between them simply don’t warrant that kind of broad categorization.  If grassland conservation is our goal, we should be sure we’re open to using whatever strategies (or animals) can help achieve that.  In very large prairies, bison may be the best fit – assuming the logistics and costs of owning bison make sense.  In other situations, however, deciding whether bison or cattle are most appropriate is not a simple matter.  It’s a decision that should be based on facts and management objectives – not on aesthetics or mythology.

Embracing Unpredictability in Prairie Management

Much of what determines the outcome of prairie management treatments is out of our control.  Sure, we can decide when to burn a prairie or set the timing and stocking rate for grazing treatments, but cascades of interactions between countless factors such as weather, insect population cycles, and many others can easily overwhelm any decisions we make.  Over the holiday season, I found time to analyze some plant community data for one of our Platte River Prairies.  The results provide a thought-provoking look at the unpredictable ways prairies respond to management.

Cattle

The results of grazing treatments are always a little unpredictable because while they tend to follow certain patterns, cattle can still make their own decisions about what to graze and what not to.  However, variability in management results goes much beyond just the way cattle choose to act in a certain year.  Burning, haying, and other management treatments can also have very different results from year to year.  High-diversity restored prairie – The Nature Conservancy’s Platte River Prairies, Nebraska.

The following data are from a prairie that was managed with variant of patch-burn grazing, in which a different portion of the prairie was burned each year (in the spring) and cattle had access to both burned and unburned portions of the prairie during most of the growing season.  As typically happens, cattle grazed the most recently burned patch pretty heavily and lightly grazed the remainder of the pasture.  Details about the fire and grazing treatments can be found at the end of this post.

If you look at the two graphs below, you can see that there was a significant increase in the average number of plant species (species richness) per square meter between 2012 and 2013 in the portion of prairie that was burned in 2012.  There was no significant change in species density in the unburned areas of the prairie – which were also grazed, but much less intensively.  Data were collected during June in both years.

Two graphs

Two graphs showing the average number (Mean N) of plant species per square meter in one of our Platte River Prairies.  The left graph shows an increase from about 9 spp/m to 11 spp/m in a patch of prairie burned in 2012, and the right graph shows data from the remainder of the prairie, which was not burned in either 2012 or 2013 and had about the same species richness/meter in both years.  The entire site was grazed in both years, with the 2012 burned patch getting much more intensive grazing than the unburned areas.  The error bars show 95% confidence intervals.

We see this pattern of higher species richness after fire/grazing treatments over and over in our prairies.  My explanation of the phenomenon is two-fold, and was covered in more detail in a previous post.  First, the burn exposes soil (and seeds) to light, allowing relatively high germination rates of seeds waiting for an opportunity.  Second, the concentrated heavy grazing in those burned areas weakens the dominant grasses, prolonging the light exposure of the soil/seeds and also reducing the root masses of those grazed grasses, thereby opening up space belowground for new plants to gain a foothold.  Those new plants start both from seed germination and from the rhizomes and buds of existing perennial plants.

The color-coded table below shows some species-level data from the same site that help explain the above graphs.  The numbers indicate the frequency of occurrence (the percentage of sample plots each species was found in) each year.  Some plant species appear to have responded positively or negatively to the burn and subsequent grazing intensity, while others seem unaffected by those management treatments.

Table 1

Plant species frequency (% of occurrence within sample plots) between 2012 and 2013 in a portion of the prairie that was burned in 2012 and the remainder of the prairie that was not burned.  The entire prairie was exposed to livestock grazing in both years.  An * indicates species with particularly high abundance, for which frequency is shown at the 1/10 m scale.  The remainder of the data are from 1  m square plots.

So far, so easy.  Fire and grazing are having positive effects on the vigor and occurrence of some species, negative effects on others, and no effect on still others.  Cumulatively, the effects add up to an increase in the number of plant species per square meter in the year following the burn.  Simple and clean.  The next two graphs (below) seem to fit the same pattern, showing similar increases in small-scale species richness in burned patches back in 2007 and 2008, respectively.

Two other graphs

Two more graphs, showing results from burned patches from 2007 and 2008, respectively, and an increase in the number of plant species per square meter in the year following each burn.  Again, cattle grazing was much more intensive in these burned patches than in the unburned remainder of the prairie each year.  Error bars indicate 95% confidence intervals.

Here’s where it gets interesting…  The next table (below) shows how individual plant species responded within the three burn patches (2007, 2008, and 2012) between the year of the burn and the subsequent year.  Of the 29 most abundant species, only THREE showed the same response to fire/grazing in each of the three years, and another two were consistent in that they didn’t appear to respond at all to management in any of the three years.  The remaining 24 species were inconsistent in their responses – some wildly so.  Look, for example at indiangrass (Sorghastrum nutans), rough dropseed – aka tall dropseed – (Sporobolus compositus), and blue prairie violet (Viola pratincola, aka Viola sororia).  Each of those three species showed a strong increase in frequency of occurrence in the burn patch one year, but a strong decrease in another.

Table 2

Plant species frequency (% of occurrence within sample plots) between the year of burn and the subsequent year in prairie patches burned in 2007, 2008, and 2012.  The entire prairie was grazed in each of the years, with higher grazing intensity in the more recently burned patches.  An * indicates species for which the frequency is shown at the 1/10 m scale – the remainder of the data are from 1 m square plots.

So what are we to make of all this?  How can we manage prairies effectively if the impacts of very similar management treatments are so different from year to year?

As far as the first question, it’s clear that other variables – particularly weather – interact strongly with management treatments to influence the response of plant species.  Every species has a different optimum range of temperature and moisture conditions, so the timing and intensity of rains and warm/cool spells affects the competitive balance between species differently each season.  Many other factors and interactions are also in play.  Year-to-year changes in population size of various seed-eating species can influence the seed bank, for example. In addition, the success of a particular plant species in one year catalyzes or suppresses other species (plant, insect, mammal, etc.) in the following year.  All of those interactions are signs of healthy prairies, but make it very difficult to predict how those prairies will respond to our management.

As to the question of how we’re supposed to manage prairies in light of all this variability, there are at least two ways to respond.  The first is to throw our hands up in disgust because we can’t seem to predict results well enough to make useful decisions.  The second option is to relax, embrace the variability, and roll with it.

prairies

Healthy prairies have a great diversity of plant and animal species, but also a great diversity of responses to year-to-year stresses imposed by both managers and the environment.  Tallgrass prairie in Richardson County, Nebraska.

Our human nature makes us want (need?) control over our environment.  In agriculture, landscape architecture, engineering and many other fields, the objective is to manipulate the world to our benefit – often by reducing the variables and controlling the remaining ones.  However, when managing ecosystems in order to conserve the diversity of species and their functional roles, that approach simply doesn’t fit.  Instead,we need to think differently about both short-term objectives and long-term goals.

To help me deal with unpredictability, I tend to consider prairie management objectives in terms of ecological resilience, rather than in terms of desired responses from particular species.  (See this earlier post on ecological resilience for background.)  I think of a prairie as a ball in a bowl.  The bowl represents a range of conditions, within which the prairie (the ball) maintains its integrity as a prairie – even if it rolls around quite a bit.  Some disturbances, such as plowing or broadcast herbicide can quickly push a prairie out of its bowl and into another state, from which it is tremendously difficult to recover.  Other disturbances, such as drought, tree encroachment, or intensive grazing may push the ball toward the edge, but as long as those disturbances don’t continue for too many years in a row, the ball doesn’t leave the bowl.

My management objective is not to prevent the metaphorical ball from moving, or to push it toward some optimal part of the bowl.  Rather, I have two big objectives:

1.)   Make sure the ball can move freely around the bowl in response to disturbances, but nudge it back from the edge when necessary.  I celebrate the fact that our Platte River Prairies change in appearance from year to year.  That tells me they are rolling around that bowl as they need to do.  In order to prevent an exit from the bowl, I make sure that we’re suppressing tree encroachment before a prairie becomes a woodland, and that we’re avoiding the kind of chronic intensive grazing that can push some prairie species to local extinction.  During extended droughts, we modify our management to avoid imposing too much additional stress on prairie communities.

2.)  Keep the bowl as large as possible by maintaining a high diversity of prairie species, along with the functional roles each contributes.  That diversity of function allows the prairie to absorb stress and respond to adversity without leaving the bowl.  Maintaining that diversity means manipulating the field of competition between prairie species so that every species can win now and then (by reproducing) and maintain itself within the community.  We create an annual patchwork of various fire, grazing and rest treatments and shift the location of those patches from year to year to provide for the needs of as many plant and animal species as possible.

Prairies are dynamic, and thank goodness for that.  Their ability to flex and respond to various stresses is a key characteristic that has allowed them to survive for thousands of years.  As prairie managers, we need to facilitate that flexibility instead of becoming frustrated with our inability to predict how prairies will respond to our management.  After all, our job is to keep prairies healthy, not turn them into something they’re not just to help ourselves feel more in control.

Management Details

For those of you who might be interested, here is some additional information about the management treatments applied to the prairie in the above example.  The pasture the burns were conducted in is often grazed in conjunction with adjacent prairies, so the total grazed area varies in size from year to year.  In each year, the overall management was patch-burn grazing, in which cattle had access to the entire grazing area, but did most of their grazing in the most recently burned patch.  The stocking rate shown (AUMs/ac) is calculated for the entire pasture and entire season.

2007 Burn (North 1/2 burned on Apr 16, South 1/2 on May 2)

240 acres grazed overall in 2007.  27 pairs from 4/1 – 10/31 (Approx. 1 AUMs/ac)

 

2008 Burn  (Burned on March 18)

171 acres grazed overall in 2008.  27 pairs from 4/1-5/20, 15 pairs till 9/15 (Approx. 0.7 AUMs/ac)

 

2012 Burn (Burned on March 30)

300 acres grazed overall in 2012.  75 pairs 4/20-Jun 1, 50 pairs till 10/1  (Approx. 1.3 AUMs/ac)