Contrasting Approaches to Prairie Management: Leopold, Land Health and Cabbages.

“A Land Ethic” is the concluding essay in Aldo Leopold’s 1949 book, A Sand County Almanac, and is the most powerful and relevant piece of conservation writing I’ve ever read.   Leopold’s essay spells out the changes we need to make in the way we view our relationship with the land, and it is both impressive and frustrating that nearly everything in that essay still reads true today.  If anyone reading this blog post has never read A Sand County Almanac, please stop reading this, go pick up a copy of the book, and read it.

I’ll wait…

Instilling a land ethic in my kids is one of my highest priorities as a parent.

Instilling a land ethic in my kids is one of my highest priorities as a parent.

One of my favorite parts of “A Land Ethic” is the section titled “Land Health and the A-B Cleavage”.  I’m always blown away by how neatly Leopold synthesizes the field of conservation into the first three sentences of that section:

A land ethic, then, reflects the existence of an ecological conscience, and this in turn reflects a conviction of individual responsibility for the health of the land. Health is the capacity of the land for self-renewal. Conservation is our effort to understand and preserve this capacity.

The very next paragraph introduces an issue I’ve been wrestling with for a long time.

Conservationists are notorious for their dissensions. Superficially these seem to add up to mere confusion, but a more careful scrutiny reveals a single plane of cleavage common to many specialized fields. In each field one group (A) regards the land as soil, and its function as commodity-production; another group (B) regards the land as a biota, and its function as something broader.

Leopold goes on to describe how some in his field of forestry are “quite content to grow trees like cabbages” while others have a less agronomic and more ecological approach.  He also points out that the fields of wildlife management and agriculture each have their own parallel examples of this dichotomy.  These contrasting views of the world still exist in various forms, from the way farmers think about their fields to the way people in cities value natural resources.

I see Leopold’s A-B cleavage very clearly in prairie management.  One example can be found in the way prairies are used for livestock production.  Many livestock producers see prairies primarily as grass farms, and the worth of a plant is determined by its palatability and nutritional value to livestock.  Broadcast herbicide application is commonly used in an attempt to remove “weeds” and leave only the grasses cattle or other livestock most like to eat.  Optimization of grass production also manifests itself in grazing strategies; particularly systems that move cattle through multiple paddocks with the primary goal of increasing the production and dominance of grass.  Grass farmers are exasperated by the perennial reoccurrence of “weeds”, despite their best efforts to prevent them. They don’t see that those weeds fill ecological roles grasses can’t, including roles that improve the overall health and productivity of the land.

A grass farmer's nightmare, these ragweed plants and other "weeds" play important ecological roles and fill in open spaces created by intensive grazing or drought.

A grass farmer’s nightmare, these ragweed plants and other “weeds” play important ecological roles, including filling open spaces created by intensive grazing or drought.  Removing them with herbicide application only results in more “weeds”, which fill the same spaces again.  Perennial grasses easily outcompete these opportunistic plants under light or no grazing pressure.  In fact, a year after this photo was taken, this site was dominated by big bluestem.

Other ranchers, however, see prairies as much more than grass farms.  Instead, they recognize that their livelihood relies on an extraordinarily diverse community of organisms above and below ground.  To these ranchers, the only weeds are those that reduce the diversity of the prairie community and make the land less healthy by Leopold’s definition of health: the capacity of the land for self-renewal.  Livestock producers on this side of the cleavage understand that they and their livestock depend upon soil, plants, pollinators, predators, pathogens, and the interactions between them.  A plant’s importance is not judged only by whether or not a cow will eat it, but also by the roles it fills in the larger community.  Those contributions include the communities of microbes living in the plant’s root system, pollen and nectar for pollinators, and food for herbivores, which in turn support predators that regulate populations of their prey.  Ranchers with an ecological perspective gain as much appreciation from watching bees buzzing from plant to plant as they do from watching the weight gains of their cattle, even though the latter is what allows them to pay their taxes and keep their land.

Just as there is a broad range of perspectives among livestock producers, there are wide contrasts among those who manage prairies for recreation and conservation purposes as well.  Some prairie managers have a single species or narrow set of species as their primary management target.  Those targets are include game species such as ring-necked pheasants, white-tailed deer or ducks, but may also be butterflies or a particular class of plants or grassland birds.  Narrowly-focused managers tend to manage their prairies in much the same way each year so as to provide a consistent set of conditions that best suit their preferred species.  Over time, prairie species not favored by that kind of repetitive management regime diminish in number or disappear, decreasing the overall diversity of the prairie community.  Since ecological resilience (today’s term for Leopold’s “land health”) relies heavily on species diversity, the loss of species from the community weakens its ability to support others, including the managers’ favorites.  Ironically, as the community weakens, managers tend to become even more agronomic in their approach by adding food plots, controlling predators, or increasing herbicide use to suppress plants taking advantage of a less diverse community.

Prairie managers with a broader ecological perspective start with the premise that a diverse prairie community is of utmost importance.  They manage in ways that prevent any particular species or group from becoming too dominant at the expense of others.  These managers don’t judge success by the abundance of one species or another, they focus on processes such as pollination, predator/prey interactions, and other indicators of community diversity and ecological resilience.  Variation in the species composition of a prairie between years is a cause for celebration rather than trepidation.  Year-to-year variation means that many different species (especially insects and animals) experience success over time, rather than just the few who thrive under more stagnant conditions.  Managing for diversity is not a simple process, and requires a careful eye and flexible approach, but the result usually produces strong and stable populations of all species – including those desired by more narrowly-focused managers.

Prairies managed for overall diversity have strong ecological processes that support all species - including game animals, songbirds, insects, plants and livestock. Prairies managed for overall diversity have strong ecological processes that support all species - including game animals, songbirds, insects, plants and livestock.

Prairies managed for overall diversity have strong ecological processes that support all species – including game animals, songbirds, insects, plants and livestock.

Whether we are managing for livestock, game species, butterflies, or flowers, the approach we take is critically important.  There is a strong temptation to continually maximize what we think are the enabling conditions for the species we’re most interested in, but that approach ignores the broader complex system those species depend upon.  The grass that cattle eat relies on productive soil, and that soil’s productivity is supported by a diversity of plants, microbes, pollinators and other prairie community members.  Similarly, the fate of butterflies, pheasants, and deer all depend upon the roles played by their fellow citizens of the prairie.

Trying to deal with all of that complexity may seem daunting, but take another look at Leopold’s definition of land health and conservation: Health is the capacity of the land for self-renewal. Conservation is our effort to understand and preserve this capacity.  Note that Leopold doesn’t say conservation entails fully grasping and perfectly managing the complexities of the land.  Instead, he defines conservation as the effort to do so.   I like that.  We don’t have to know everything to be successful.  Instead, conservation is an adaptive process of learning, incorporating new knowledge into our actions, and then trying again.  That means that conservation is accessible to anyone who appreciates the broad complexity of natural systems and attempts to work within them, rather than against them.

…And isn’t that more fun than just growing cabbages?

Disclaimer:  The author of this post intends no disrespect to those who grow cabbages.  Instead he was simply referring to a quote from earlier in the post to reinforce a point and attempt to end a long and heavy essay with something a little lighter.  Cabbage growing is a perfectly legitimate and important activity, especially when done with appropriate consideration for the broader ecological context of soil and other ecosystem processes required to sustain long-term production…  …Ok, I’ll just stop now.

Previous related posts you might be interested in:

Calendar Prairies

Are Botanists Ruining Prairies?

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?)