Ice Jam Flooding

As I mentioned last week, recent ice jams on the Platte River caused some flooding in some of our prairies.  I was able to photograph the flooding from a couple perspectives.  On February 5, we got some aerial footage with our drone, and then late last week, I walked through some of the flooded area after most of the water had receded.

This road was closed due to flooding.  Everything to the right (north) of the road is prairie.

This road was closed due to flooding. Everything to the right (north) of the road is prairie.

windmill

Another shot of the same area from higher up.  The river can be seen at the very left edge of the photo.  A windmill can be seen in the prairie near the right edge.

This was and will be an ecologically-interesting event from several standpoints.  Floating ice and ice jams have been an important component of the Platte River ecosystem for a very long time.  Ice likely played a critical historic role by helping to scour vegetation from sandbars, allowing that sediment to be carried off and deposited elsewhere, and creating valuable habitat for many species – including the ducks, geese, cranes, and other water birds that pass through during migration.  Today, we see much less of that scouring and many sandbar islands and banks have become relatively permanent and covered by trees and other perennial vegetation.

river channels

River water flowing through prairie.  Most Platte River floodplain prairies still have their river-formed topography of sloughs (old river channels) and ridges (old sandbars).  During the flood, many of those sloughs became active (albeit temporary) river channels again.

Before the Platte River’s channels were stabilized and restricted to their current locations by human activity, ice jam flooding might have been an important driver of the shifting of channel locations over time as well.  This year’s flood created new river channels through floodplain prairies and woodland, but as the water receded, it returned to its stabilized channels.  Historically, the river was a broad series of braided channels, and flood events would have changed the shape and location of those channels frequently – though I don’t know how important ice jams were relative to annual high flows from Rocky Mountain meltwater.

I have a few predictions about how this year’s flood will impact prairies, but they are just educated guesses….

The grasslands that were covered by water for a few weeks will get a boost in their soil moisture for this upcoming season.  We’ve had a relatively dry winter, so that soil moisture should create some very different growing conditions for plants in flooded versus non-flooded prairies.  Depending upon a number of variables, flooded areas might also retain more standing water in sloughs, creating valuable habitat for many wildlife species.

fences

Floodwaters carried grass and other debris into fences and pushed them right over.

The flooding carried more than just large chunks of ice out of the river and through the prairies.  It also picked up and carried downed trees and branches, along with other assorted buoyant objects, natural and man-made.  In addition, the ice and water scraped vegetation from some places and deposited it elsewhere.  We burned a portion of prairie last year and left it ungrazed as a seed harvest site, so it was covered in tall big bluestem and other grasses.  The ice essentially shaved some of that area as it came through, scraping away most of the standing vegetation and leaving behind a site that now looks as if it had been intensively grazed.  That shaved off grass was deposited further downstream along obstacles (such as fences) and in high spots as the water levels dropped.  As a result, some areas of prairie are now covered by a foot or so of fairly dense thatch.  It will be fun to watch how that thatch affects vegetative growth and wildlife use.

shaved

This area was burned last spring and ungrazed.  Before the flood, it was a stand of tall dense big bluestem and other tall grasses.  The ice and water essentially shaved the tall stems and leaves off and carried them away.

This Canada goose appeared to view the

This Canada goose decoy appeared to view its new surroundings with equanimity (look it up, Dillon) after being deposited by receding flood waters.

this

A second decoy looked a little less at ease.

thattch

This layer of flood-deposited thatch is about a foot thick.  It will be interesting to see what impact it has on vegetation beneath it.

I’m guessing most of the impacts of this flood will be positive, or at least interesting, from a land management standpoint.  One exception is that we’ll have some fairly major fence repair to do this spring.  A bigger concern is a potential influx of invasive plants carried in to our prairies as seed or vegetative material from the river.  Phragmites, reed canarygrass, and purple loosestrife are probably the most likely and potentially serious invaders, but others such as Canada thistle, salt cedar, and Russian olive are also possible.  We’ll need to be vigilant over the next few seasons to make sure we catch new populations of those invaders before they can become well-established.

This ice

Ice fields like this make it difficult to travel across the prairie and get a full picture of what was flooded and what wasn’t.

Once the remaining ice melts away,  we’ll get out and explore more of our flooded areas.  After we have mapped out (at least generally) the boundaries of the flooded areas, we’ll watch and evaluate what impacts the ice and water actually have on the prairie this season and beyond.

And then we’ll  see how good my predictions are…

Why Does Plant Diversity Matter? Help Us Figure It Out!

How important is plant diversity in restored prairies?

Are diverse prairies more resistant to drought and invasive species than less diverse prairies?

How does plant diversity influence invertebrate communities and their ecological functions?

These kinds of questions have been the focus of multiple research projects in our Platte River Prairies over the last decade or so.  We have numerous restored (reseeded) and remnant (unplowed) prairies that provide excellent field sites, and have also established two sets of experimental research plots to help focus specifically on questions related to plant diversity.  Those plots are 3/4 acre (1/3 ha) in size and represent varying levels of plant diversity, allowing us to investigate the functional differences between them.  Researchers from the University of Nebraska, Kansas State University, the University of Illinois, and Simpson College have been involved in data collection efforts so far.

2013 photos from

2013 photos from our experimental research plots.  The plots from left to right were planted to a monoculture (big bluestem), a low diversity mixture (mostly grasses and a few late season wildflowers) and a high diversity mixture (100 plant species).  We are investigating functional differences between these kinds of plant communities.

Craig Allen, Leader of the Nebraska Cooperative Fish & Wildlife Research Unit, and I are hoping to take the next step in these efforts by bringing on either a PhD or Post-Doctoral Research Associate.  We have data to build upon, including some intriguing results regarding invasive species and insect herbivory rates at varying levels of plant diversity, but want to greatly expand upon those data.  If you or someone you know is interested in these kinds of questions, please read below and contact Craig or me with questions.

Here is the official description of the position:

Ph.D. or Post-Doctoral Research Opportunity:  Grassland diversity, restoration and resilience

Ph.D. graduate research assistantship or Post-Doctoral Research Associate.  Available starting in May 2015, to investigate the relationship between grassland restorations and ecosystem services and resilience.  The assistantship (or Post-Doc) is with the Nebraska Cooperative Fish and Wildlife Research Unit, in the School of Natural Resources at the University of Nebraska, working closely with the Nature Conservancy scientists and resource managers.   The research project will include a synthesis of literature to identify prominent knowledge gaps related to the restoration of grasslands and resilience.  In addition to synthesis, field work will occur on a suite of restorations in central Nebraska.  Some questions of interest are listed below, but ultimately, successful candidates will be expected to develop a specific research project(s).  The candidate could approach this project from a broadly ecological, or botanical, or entomological frame.

The successful applicants will be highly motivated, with a strong work ethic, strong and demonstrated writing skills, a passion for field work, and the ability to work in collaboration.  Experience in restoration ecology is helpful, but not required.  Ph.D. applicants should possess a M.S. in Wildlife, Biology, Zoology, Botany, or Entomology, or a related field and have a valid driver’s license.  Post-doctoral applicants should possess a Ph.D.

Interested applicants should send a cover letter, names and emails of 3 references, GPA and GRE scores, and an updated CV as an electronic PDF or Word document to Craig Allen, allencr@unl.edu

Review of applications will begin March 15 and continue until a qualified candidate is identified.  For more information on the Nebraska Coop. Unit and the University of Nebraska-Lincoln please visit us at:

http://snr.unl.edu/necoopunit/default.asp

Applicants should also review:

https://prairieecologist.com/

Specific projects could include all or part of the following:

Relationship between restoration diversity and ecosystem services, such as invasion resistance and herbivory; interactive effects that might mediate some resilience properties; responses to multiple disturbances; how invasions might weaken the ability to cope with disturbance; microbial diversity and ecosystem function and services; response to pulse and press disturbances and mechanisms driving responses; functional trait diversity and redundancy and resilience.