Prairie Word of the Day – Disturbance

It’s been too long since the initial installment of what was intended to be a regular feature of this blog – the Prairie Word of the Day.  Since one blog post does not make a series, I figured I’d better at least write one more.  I will try to add more to the series relatively soon. 

If you read this blog or any other source of information about prairie ecology or management, you’re likely to have seen the term “disturbance” used in some context (e.g., “ecological disturbance,” “disturbance regime,” “disturbance in the force”).  Ok, that last one is from a different context, but nevertheless.

Outside of prairie ecology or other ecological conversations, a disturbance is often something that requires contacting the police.  However, in almost every case, prairie managers would appreciate you not calling the police in response to disturbances in a prairie.  So what does the word “disturbance” mean in an ecological context?

Fire is one of the big three historical disturbances to which prairies are adapted to and rely on.

Fire is one of the big three historical disturbances to which prairies are adapted to and rely on.

It’s probably easiest to think about a disturbance in a prairie as something that disrupts the lives and processes of prairie organisms and creates a shift in the competitive balance among those species.  Historically, the big three disturbances in grasslands were fire, grazing, and drought.  Fire and grazing are still used as management strategies today, along with mowing/haying and, sometimes, herbicide treatments.  Drought (and other significant weather events such as a flood) is not something managers prescribe or apply to a prairie, but it certainly has significant impacts.

Both “natural” disturbances and those prescribed by prairie managers are critically important to the health of prairies, despite the fact that they have significant impacts on species.  In fact, many animals, plants, and other organisms often die as a result of disturbances.  Prairies, however, more than most other ecosystems, are not only well suited to survive disturbances, they are defined by and rely on those disturbances.  Without fire and drought, for example, prairies wouldn’t even exist – they would be woodlands instead (and who wants that??).

Every time a fire burns through a prairie, grazers chomp off much of the vegetation, or an extended drought turns a prairie brown in mid-summer, the competitive balance in a prairie is altered.  Depending upon the timing and intensity of a fire, for example, it’s likely to kill some trees and “top-kill” others, forcing them to restart from buds at or below the surface of the ground.  Fires can also kill or suppress the growth of other plant species, especially those most actively growing at the time of the fire.  At the same time, fires create opportunities for other plants – especially those in direct competition with the ones suppressed or killed.  Plants that thrive best in full sunlight and don’t do well under layers of thatch or beneath tall plants also respond very favorably after a fire.

These cedar trees died in a recent fire, but the vegetation around them is regrowing strongly. In fact, the cattle (in the distance to the top right) in this prairie will be attracted to that growth and graze this part of the prairie much harder than unburned parts.

These cedar trees died in a recent fire, but the vegetation around them is regrowing strongly. In fact, the cattle (in the distance to the top right) in this prairie will be attracted to that growth and graze this part of the prairie much harder than unburned parts – adding a second disturbance to the first.

Of course, fires can also kill or injure wildlife or insect species (not to mention microorganisms and other life forms) that are aboveground at the time of the fire and can’t evade the heat and/or smoke.  The season in which a fire burns plays a big role in which organisms are affected.  Dormant season fires can kill insects and other species that overwinter in vegetation or along the surface of the ground, but growing season fires cause even more fatalities because so many more species are active during that time of year.  Even animals that survive the fire itself may have to travel to unburned areas in order to find suitable habitat, and those trips can be hazardous as well.

Despite the immediate negative impacts of fire on individual insects, wildlife, and other species, however, periodic fire usually has longer-term benefits – even for those species that suffer fatalities.  Without fire – or some other disturbance that removes vegetation – prairies can become so overgrown that most species can’t survive there.  Suffocating layers of thatch, encroachment by trees and shrubs, and the potential for diseases and predator populations to build up over time are all conditions that can be found in prairies that go undisturbed for long periods of time.  In addition, if the same habitat and growing conditions prevail year after year in a particular patch of prairie, some species will thrive but others will not – leading to a loss of species diversity and overall prairie health.

Without going into details here, the impacts of drought and grazing on prairie species are similar to those of fire – each event will favor some species over others.  Prairie plants are well adapted to periodic burning, grazing, or drought.  Perennial plants have numerous buds at their base, from which they can grow new shoots after they’ve been burned or cropped off, and most can enter dormancy during a severe drought in order to conserve resources for better days.  Shorter-lived plants often rely on disturbances to create opportunities for them to grow with less competition from nearby perennials.  Those annual and biennial plants produce copious amounts of seed that fall to the ground and wait until the next time conditions favor their germination and growth.

Every vertebrate and invertebrate animal species relies on a particular set of habitat conditions.  Some thrive when vegetation is short and sparse, and others prefer tall dense vegetation.  The highest diversity of animals and insects is usually found where perennial plants have been recently weakened by fire, grazing, and/or drought, and short-lived plants are thriving while those perennials recover.  In any case, habitat conditions are tied to disturbances – some conditions are created during or in response to a disturbance, and others (tall dense vegetation) are created when a disturbance hasn’t occurred for a while.

Prescribed fire, along the grazing and mowing, are important ways for prairie managers to introduce disturbances into grasslands in order to maintain prairie health and biological diversity.

Prescribed fire, along the grazing and mowing, are important ways for prairie managers to introduce disturbances into grasslands in order to maintain prairie health and biological diversity.

As prairie managers, our job is to provide habitat and growing conditions for as many prairie species as possible.  We burn, graze, and mow prairies at prescribed intervals (and usually in patches, rather than across an entire prairie) in order to maintain a competitive environment in which all those prairie species can survive.  Whenever we burn a prairie or introduce large grazers to it, we know that some species will be harmed by that action, but that others will flourish because of it.  As long as we allow a patch of prairie to recover between disturbances and create a patchwork of habitats (some recently disturbed and others not), the prairie community will remain diverse and resilient.

Prairie management is complicated, and it can be difficult to make decisions and take actions that you know are going to negatively impact some species.  On the other hand, the other choice is to do nothing.

And that would be disturbing.

Photo of the Week – November 5, 2015

As I was looking at some of my recent photos from our Niobrara Valley Preserve, I realized that I have a series of photos from approximately the same vantage point that illustrates the site’s recovery from the major wildfire back in 2012.  If you’ve followed this blog for several years, you’re probably aware that we have a significant timelapse project going on at the Niobrara Valley Preserve that is documenting that recovery as well.  Those images will provide a very comprehensive look at change over time, but those cameras weren’t installed until after the fire.  The three photos below are interesting because they represent shots taken before, immediately after the fire, and a few years later.

October 1, 2011

October 1, 2011

The above photo was taken in the fall before the big 2012 wildfire.  The big pine tree on the right is a good landmark to watch as you compare this photo to the next two.  The following photo was taken just a few days after the wildfire.

July 25, 2012

July 25, 2012

The last photo (below) was taken just a few weeks ago.  The grass and other vegetation has clearly recovered nicely from the fire.  That’s not really a surprise to any of us who are familiar with grassland fires.  Even a very hot summer fire in the midst of severe drought is not typically fatal to most prairie plants.  In fact, the drought was harder on prairie plants than the fire was, but even so, those plant species are well adapted to both.

TNC Niobrara Valley Preserve, Nebraska.

October 23, 2015

More interesting than the recovery of grasses and wildflowers is the recovery of woody plants.  The two small pine trees on the left side of the image look happy and healthy, despite the fact that young ponderosa pines tend to be vulnerable to fire.  If you look closely at the image taken immediately after the fire, you can see both of those trees.  The one on the right, especially, had the majority of its needles burned by the fire, but both appear to have come out of that stressful period just fine.  Why were those two trees able to survive (along with the big tree) here when just across the river, almost every single pine on the south-facing slope died?  Most likely, there are multiple reasons, including slope, fire intensity, and the fact that these trees were surrounded mostly by grasses instead of lots of other pine trees (and eastern red cedars).  The point of showing these photos isn’t to answer these kinds of questions as much as it is to stimulate them.

It’s also interesting to note that most of the oaks and other big deciduous trees seem to have survived.  That is the case across most of the Preserve, although many of the bur oak trees that were growing close to pine and eastern red cedar trees were top-killed by the fire and are now regrowing from the base.  A few oaks and other deciduous trees (especially cottonwoods) did die from the fire, but most didn’t.

I’m hoping to put together some timelapse sequences this winter that will help tell the story of recovery from multiple locations across the Preserve.  For the most part, those stories will show that the natural communities along the Niobrara River are well-adapted to major disturbances such as the drought and fire that occurred in 2012.  The big exception is the pine woodland that was nearly completely wiped out across big swaths of the landscape. The density of pine and cedar trees led to fire intensity that caused 100% mortality in many stands, and while those areas will recover, they will be grassland and/or shrubland for a very long time, and their long-range future as pine woodlands is far from assured.

Aside from those pine woodlands, however, the natural communities across the Preserve did what natural communities usually do in response to fire, drought, and other major events – they continued to thrive.