Prairie Seed Dispersal

Plants don’t have the ability to walk or fly, but many can send their seeds far out into the world.  Some seeds have the capability to travel very long distances, giving plants the opportunity to colonize new places.

There are few seeds more familiar to prairie hikers than milkweed seeds.

In reality, most seeds don’t travel far from their parent plant.  If you’ve ever come across a milkweed plant with recently-opened pods, you’ve seen that the ground around the plant is often covered with milkweed seeds – even though milkweed seeds have the capability to ride the wind.  While it might seem like failure, dropping a high percentage of its seeds probably makes a lot of sense.  If the plant is able to grow and produce seeds, its current location must be suitable habitat.

Although most apples don’t fall far from the tree, so to speak, some percentage of a plant’s seeds often do travel to new sites – sometimes many miles from their starting place.  Once those seeds land, the challenges are just beginning.  The vast majority of seeds never germinate and become new plants because to do so it must end up somewhere that provides just the right conditions.  The odds are very high against a seed landing in a place where there is bare soil for germination, available root and light space to grow, and suitable habitat for survival.  However, having a few seeds that do manage to establish new populations is so important to the survival of the species, plants invest a lot of resources in this high risk strategy.  Read more about the ecology of seed dispersal in an detailed article by Henry Howe and Judith Smallwood.

Prairie plants have developed an incredible array of seed transport mechanisms.  Seeds can be carried by animals, wind, and water, and each has special physical characteristics that help it travel.

Prairie wild rose fruit in cross-section, showing the hard seeds inside.

Some plants wrap large hard seeds inside fruits that animals like to eat.  When the fruit is eaten, the seeds travel through the animal’s digestive system and out the back end – usually some distance from the parent plant.  Prairie wild rose hips, for example, are a food bonanza for a number of wildlife species.  Besides being tasty and rich in Vitamin C and other nutrients, they are also available during the late fall and winter when it can be difficult for animals to find other food.  Prairie grouse, turkeys, and many other species find them particularly attractive.  While the fruits are nutritious and provide value to the animal, the seeds inside the fruit are hard enough that they pass undigested through the animal and are deposited in a pile of fertilizer – giving potential new seedlings a jump start.

Violets produce seeds in pods that pop open when ripe, ejecting the seeds a short distance from the plant.  However, the seeds of violets are also attractive to ants, which transport them to their tunnels where they are often deposited in trash heaps where conditions are favorable for germination.  (For more on prairie ants, read James Trager’s excellent introduction)

Blue violet seeds.

Sandburs, and many other species, use animals to move their seeds but not because the seeds are particularly edible.  Instead, the plants use specialized spines, hooks, or other structures that get caught on animals as they pass by.  This sometimes allows the seeds to be carried many miles before they fall – or are scraped off.  Historically, bison were major carriers of seeds and often deposited them in wallows, where the bare soil may have helped provide for successful germination.

Sandburs are loaded with spines that help them hitch rides with any animal (or hiker) that happens by.

One of the most common strategies for seed dispersal by prairie plants is to employ the help of the nearly omnipresent wind.  A wide variety of species, including asters, goldenrods, milkweeds, thistles, wild lettuces, and many others, produce long feathery appendages, wings, or other structures that help catch the wind and carry seeds long distances.  Others simply produce seeds so small and light that they can easily be blown around.  While wind dispersal often carries seeds further than animals do, it is also the strategy that gives plants the least control over the final destination.  Animals are fairly likely to carry and drop seeds within the same habitat type, giving seeds at least some hope of finding good places to grow, but casting seeds to the wind is much riskier.

The last seed of a wild lettuce flower hangs on - until the next gust of wind happens by.

Seeds that grow in wetlands or wet prairies often build seeds that float and can be dispersed by moving water (or by wind blowing them across water bodies).  This seems like a logical strategy to help seeds move because it keeps them within the moist habitats they need for establishment.  Some water-dispersed seeds are simply so small that they don’t break through the surface tension of water.  Others have hairs or other structures that help them float.  Still others have hollow spaces that make them buoyant.

Wetland seeds floating on the water's surface.

Regardless of the particular strategy a plant species uses to disperse its seeds, prairie plants can benefit from the ability to transport seeds away from their parent.  Many perennial plants employ rhizomes or runners, in addition to seeds, to help start new plants short distances from the parent, and those reproductive stems help new plants establish because they have an “umbilical cord” of support from their parent.  However, that asexual reproduction doesn’t allow plants to move their progeny very far, and doesn’t involve cross-pollination that can help a species maintain high genetic vigor.

For annual plants, seed production is the only strategy for movement and survival because the parent dies after a single season.  Because annuals only get one shot at flowering, they usually do so prolifically, and spread their seeds far and wide.  This helps them be prepared for any kind of disturbance (burrowing animals, intensive grazing, etc.) that creates bare ground or suppresses surrounding vegetation – the perfect conditions for annuals to grow and flower.

Whether seeds are transported by animals, wind, or water, they are built for the task.  Seed dispersal is one of my favorite discussion topics during prairie hikes because people of all ages can appreciate the amazing strategies plants have developed to move their seeds around the landscape.  In fact, it’s such an interesting subject, it’s easy to get carried away…

Behind the photos – several of the photos in this post were taken in a simple homemade photo studio made from a cardboard box, tissue paper and a desk lamp.

A homemade photo studio – cardboard box, tissue paper, and a desk lamp.

Lessons from the Grassland Restoration Network

I’ve been involved with high-diversity prairie restoration (reconstruction) since I joined The Nature Conservancy in 1997, learning the basics from Bill Whitney at Prairie Plains Resource Institute.   We’ve now planted over 1,500 acres of Platte River cropfields to prairie vegetation, using seed mixes of between 150 and 230 species.  Those restorations are being used to enlarge and reconnect existing remnant grasslands along the Platte River.

About 10 years ago, I started reaching out to other sites doing similar work.  Gus Nyberg, then at the Kankakee Sands Restoration in Indiana, and I set up a reciprocal visit between our projects, during which I took some of my staff (and Bill Whitney) to Indiana and the Kankakee staff came to Nebraska.  That experience was really valuable for all of us, and convinced us that we needed to do it more often – and to include as many others as possible.  Thus began the Grassland Restoration Network.

The Grassland Restoration Network (GRN) is a loose affiliation of projects and project staff engaged in the restoration of diverse native grassland communities.  The Network was formed in 2003 by The Nature Conservancy and a wide variety of other conservation organizations, government agencies, and private landowners.  There are three major objectives of the GRN:

  1. Facilitate communication and cross-site learning among large-scale grassland restoration sites.
  2. Identify and close critical knowledge gaps regarding grassland restoration and measures of restoration success.
  3. Foster a “grassland restoration culture” that increases the quantity and quality of grassland restoration.

Grassland Restoration Network workshop participants discuss restoration strategy in a restored Nebraska prairie in 2009.

The Network sponsors annual workshops that are hosted by various restoration projects around the country.  In addition to tours, workshops include presentations and discussions on topics including seed harvest/planting, invasive species control, long-term management, and research and evaluation strategies.  Those workshops have been attended largely by people working in the central United States, but have also included participants from the Pacific Northwest, long-leaf pine ecosystem in the southeast, and even other countries, including Canada and The Netherlands.

GRN workshops differ from other conferences in that the Network focuses on the use of high-diversity restoration as a tool for increasing the ecological viability of prairie ecosystems.  For example, we try to enlarge or reconnect small and/or isolated prairies through the conversion of adjacent cropland to high-diversity grassland communities.  In other words, we are trying to defragment the prairie landscape to increase the effective population sizes of prairie species (plants, insects, vertebrates) and benefit the whole ecosystem.  Success in those cases is measured not only by the establishment of plant species in seedings, but also by whether or not those seedings have increased the viability (long-term sustainability of ecological function) of the remnant prairie(s).

Bringing together people working toward this particular objective has had several benefits.  It has increased communication between sites to the point that we know what each other are doing and are learning from their experiences.  We have also identified common challenges and research questions, and have started several joint research projects to try to address those.  Finally, we have been able to take advantage of the size and experience of the group by collecting a number of “lessons learned” regarding the logistics and mechanics of doing prairie restoration.

Most large-scale prairie restoration sites have found that broadcasting seed (rather than drilling) is the most efficient and effective planting technique.

Several of us who have helped facilitate the Network have summarized many of those lessons in a manuscript that will be published in the upcoming Proceedings of the 22nd North American Prairie Conference.  The organizer of that Conference, the Tallgrass Prairie Center at the University of Northern Iowa, has graciously given me permission to post a PDF of that manuscript here, even though the Proceedings have not yet been published.  (click here to download – GRNLessons2010)

The manuscript covers a wide variety of subjects, including seed harvest and cleaning, planting, invasive species control, and overall project planning.  It also includes a selection of the most pressing research questions facing prairie restoration, as identified by Network participants.  If you’re interested or involved in prairie restoration work, I hope you’ll find the manuscript helpful.

Here is a selection of some of the broader lessons learned, excerpted from our manuscript:

1. Match your methods to your objectives.  The biggest key here is to define specific objectives.  Why are you doing the restoration project?  If your primary objective is to create grassland bird habitat, plant species diversity may not be all that critical, but the particular plant species you select may be.  If, on the other hand, you’re trying to enlarge a small remnant prairie so that all of the plants, insects, and animals in that prairie can have larger population sizes, the species diversity and composition of your seed mix becomes much more important.  (It’s also important to be sure you’re evaluating your success based on those same objectives.  If you’re interested in enlarging a prairie, be sure to measure the response from insects and other organisms – not just plants.)

2. Start slow, and increase the scale of restoration over time.  Many restoration projects, especially those trying to restore hundreds or thousands of acres, feel like they need to start restoring large portions of the total right away.  In almost every case where this has been done, the project manager has regretted it later.  Because every site is different, it’s important to start by spending a few years doing small scale seedings in order to build up a database of seed harvest sites, test the effectiveness of techniques, and gauge the level of invasive species suppression that is needed.  Be sure to experiment with a variety of strategies (seeding method, seeding rates, site preparation, etc.) during those first years so that you can learn as much as possible.  Once you feel like you’ve got a handle on effective strategies, you can start ramping up the scale of the effort exponentially.  This approach helps avoid initial large seedings that fail to produce the anticipated results, and that become management headaches down the road.

3. Restore a site over multiple years, rather than all at once.  This is related to number two, but applies to any site, regardless of scale.  Anyone who has spent many years restoring prairies knows that every seeding is unique.  The relative establishment of plant species, the response of weedy species, and many other factors vary year to year – often for reasons we can’t yet define.  Make that variability a positive thing.  If you have 100 acres to plant, seeding 20 acres a year for five years can produce five unique prairie communities that complement each other and increase overall heterogeneity and diversity of habitat and species composition, rather than one large seeding that looks pretty much the same across the whole site.  Another approach is to “checkerboard” a seeding; break each year’s seeding effort into several locations, scattered across the larger site, and fill in more blanks every year.

4. If you want plant diversity, maximize that diversity in your initial seedings – don’t plant a low diversity mixture with the idea of coming back later to add diversity.  It is much more difficult to enhance the diversity of an established prairie restoration than it is to establish that diversity during the initial seeding process.  Attempts to do so tend to have inconsistent results at best.

Efficient seed harvesting is an important part of prairie restoration when trying to maximize both acres and species diversity.

5. Adapt your technique as you go.  Even if you start small and figure out some apparently effective methods before attempting larger seedings, it’s still important to continue experimenting.  Including a couple small experimental plots (1 acre or so in size) within each year’s restoration work, in which seeding rate or other treatments are varied, can provide tremendous information that can help refine your techniques over time.  Collecting data from those plots can be as simple as visual observation of differences or more intensive, but without those experiments, you’ll never know whether or not you could be doing better restoration work.

6. Develop a plan, and capacity, for dealing with invasive species before you start.  Invasive species are expensive to fight, but the success of that fight is the difference between restoration success and failure.  In fact, when a restoration effort is designed to benefit an adjacent remnant prairie, a seeding full of invasive species can actually put the remnant at greater risk than before.  There are two factors that should drive the number of acres you plant each year: the amount of seed you can harvest to obtain the desired species composition in the seedings, and the number of acres on which you can deal with invasive species.  This is one of the great advantages of starting small – you can evaluate the threat posed by invasive species on small seedings before jumping into large seedings that could overwhelm your available resources.  It’s better to do high-quality, but small, seedings than mediocre (or worse) large ones.

7. Finally, one of the most interesting facets of prairie restoration is that there are many ways to do it successfully.  It is a field full of innovation and creativity, and it’s wonderful to see varying approaches to common problems.  However, through polling participants, we’ve found that there seems to be one set of restoration techniques that is universally successful, regardless of geographic location or other factors.  Excepting extraordinary circumstances, a dormant season broadcast seeding onto Roundup Ready soybean stubble will always establish a diverse prairie plant community.  This doesn’t mean that the Network is prescribing that specific technique – in fact many of us have had great success with other techniques.  But we think it notable that we could identify at least one combination of techniques that consistently produces successful prairie establishment.

Whether you’re creating prairies for educational, historic, aesthetic, or ecological reasons, it can be a rewarding (if challenging) experience.  Because every site responds uniquely to prairie restoration, much of what works for you will likely be learned through experimentation.  However, there is also much to learn from others who have been doing similar work in other places.  I hope this partial summary of that information will help you.

The 2011 GRN workshop has not yet been planned.  Stay tuned to this blog for updates about the date and location.