Friday, December 23, 2011

Request for Photos...

Photos from Brosnan Forest, summer 2005...

Photos from Carolina Sandhills NWR...

Photos from our Greenhouse space...

Photos from Cowpens National Battlefield...

Photos of our rare plants at the SC Botanical Garden...

Photos from Savannah River Ste...

Photos from SC Taylor Nursery...

Friday, November 4, 2011

Native Seed Collection - Regions Map

This map was created from USFS, TNC, and EPA data.  It depicts ecoregions we are collecting seed from for our common garden study.  Regions of interest include the Mid-Atlantic Coastal Plain (MAC) in blue, the South Atlantic Coastal Plain (SAC) in purple, and the sandhills (SH) in white, shaded with dots. 

The following map shows potential seed collections sites.  The northernmost property is Alligator River NWR and Osceola NF represents the southernmost extent.

Tuesday, November 1, 2011

Chesnee Weather and Hexastylis naniflora trends

Thus far, I have been able to compile means for temperature (Min/Max) and precipitation between the Fall of 2006, when our Hexastylis project was initiated, and the Fall of 2010.  We have collected data on plants and flowers from the Fall of 2006 through the Spring of 2011.  Chart 1 shows the temperature and precipitation means by month.  Maximum temps are in orange, minimum temps are in purple and precipitation is shown in blue.  Notice our highest temps were during summer 2007 (prior to Spring 2008 burns) and our lowest precipitation was in the spring of 2008 during the time-frame that our Rx burns occurred.  The lowest summer temps were during 2009 and the following fall and winter had the highest precipitation. [*Sorry about the ridiculously small text, but these charts have not been very cooperative]

Chart 1.

Chart 2 shows the number of plants per square meter during times of data collection (Fall and Spring).  Burn plots are in red and control plots are in green.  The number of plants per square meter between Burn and Control plots were similar throughout the experiment.

Chart 2.

Chart 3 shows the comparison of number of leaves per square meter (only measured during Fall) between Burn and Control plots.  These measures are similar between treatments until Fall of 2009, 18 months post-burn, when we see Burn plots with 1 and a half times as many leaves per square meter.  In Fall 2010, we again see more leaves per square meter although not as great a difference. 

Chart 3.

Chart 4 shows the comparison of flowers per square meter (only measured during Spring) between Burn and Control plots.  These measures were similar throughout the experiment until the Spring of 2010, 24 months post-burn, where Burn plots have over twice as many flowers per square meter than Control plots.  This is also true for Spring 2011 measurements not shown in this chart.

Chart 4.

Wednesday, September 21, 2011

Ft. Gordon - Erosion control test

Overcoming Erosion
Testing an erosion control blanket at Fort Gordon, GA – Mar. 2010 to Nov. 2010

The northwestern portion of TA 18 has a clay slope that may pose problems in getting native grasses established.  Several re-vegetation options were discussed and we decided that an erosion control blanket could be a viable solution.  During the first week of March 2010 Gary Pringle was able to get (at no cost) approximately 1000 square feet of erosion control blanket, which we installed on the clay-slope.  We seeded this the next day with some left-over’s from our collections and seeded the same amount over an adjacent area of similar size for future comparison.  We periodically checked in during site visits and were consistently impressed with how well the erosion control blanket seems to establish seedlings. 

Erosion control blanket - Nov 2010                                              No erosion control blanket - Nov 2010


As these photos taken in November 2010 show, this technique is worthy of further investigation.  After just 8 months there is a remarkable difference!

This is an ECSC-2 double net straw/coconut rolled erosion blanket.  The blanket is made to a standard dimension of 7.5 feet wide by 120 feet long (900 square feet) rated for erosion protection and vegetation establishment on slopes up to a 1:1 grade (45 degree angle, 100% slope) for up to 24 months.  The blanket consists of 70% straw and 30% coconut fiber and is stitched together with a degradable thread between a layer of UV-stabilized top netting and a bottom layer of polypropylene netting.  This particular blanket was old and in the process of degradation, but as we can see is still doing the job.

And here is a faux time-lapse showing establishment of vegetation on this clay slope with help from an erosion control blanket.

...and these from my latest visit...

Erosion control blanket - Sep 2011                                               No erosion control blanket - Sep 2011

Monday, September 12, 2011

Looking for Tephrosia virginiana...

We are trying to collect seed from Tephrosia virginiana, commonly known as goat's rue ... a densely hairy perennial herb growing erect, but only 1 to 2 feet tall.  Leaves are alternate and pinnately compund, flowers are pea-like with yellow, cream, and pink coloring. Flowers of T. virginiana are on shorter stalks than T. spicata.

We are interested to know if the pods (densely hairy) are still intact with seeds inside... flowers from May to June and fruits during July through October.

Tephrosia spp. should be growing in dry, open woods and the best places to collect seed would have been burned this past spring. 

Line drawing from: Britton, N.L., and A. Brown. 1913. An illustrated flora of the northern United States, Canada and the British Possessions.

Please let us know if you have a nice clump we could collect for our common garden study!

...all photos from the Southeastern Flora website:

Monday, July 25, 2011

Restoration at Fort Gordon

Local, Sustainable, and Army Green: restoring native groundcover at Fort Gordon
by Bryan Mudder

In the summer of 2008, the Fort Gordon Natural Resources Division approached Joan Walker, research plant ecologist with the Forest Service Southern Research Station, with the challenge of figuring out how to establish native grasses and herbaceous plants on a typical southern forest stand just after harvest, to improve wildlife habitat while restoring ecosystem structure and function.  As a research technician working with Walker, I soon find myself pondering a sun-scorched sand hill at the Fort Gordon United States Army Installation near Augusta, GA, envisioning its eventual conversion from barren clear cut to the browns, yellows and greens indicative of a longleaf pine-wiregrass savanna.

The Army slogan, “If you don’t conserve it, you don’t deserve it!”, conveys the intense personal commitment to national security and to environmental services expected of those serving on military bases.

Land managers at Fort Gordon, home to The Signal Corps and Signal Center, face a formidable stewardship challenge.  How do you provide training sites for soldiers, while managing all of the natural resources over approximately 56,000 acres?  This means ensuring clean air, water, and habitat for endangered species, improving soil, and providing recreation opportunities, including hunting and fishing all while ensuring an economic return from timber.  Hot, humid, and harsh describe the nutrient deficient soils of the Fort, which sits on the Fall Line, a relatively thin geological boundary that runs from Columbus to Augusta, and separates the crystalline rocks of the Piedmont from the sedimentary rocks of the Atlantic Coastal Plain.

 Bringing Back the Grasses

At the time of European settlement an estimated 90 million acres, extending from Virginia south to Florida and west into Texas, were dominated by longleaf pine forest.  Currently, only about 3 million acres of the former longleaf pine forest exists in its historic range.  Factors contributing to this decline include exploitation of longleaf pine for timber, the harvest of turpentine used for naval stores, conversion of forestland to agriculture, exclusion of fire, and the onset of urbanization.  Longleaf pine forests are among the most species rich forest types in North America, supporting one of the most diverse understory plant communities in the world.  There are approximately 122 endangered or threatened plant and animal species, including the red-cockaded woodpecker and the gopher tortoise, that call this ecosystem home.  Restoring the natural diversity is one reason ecologists, natural resource managers, and private landowners are interested in restoring the longleaf pine ecosystem.

Back at Fort Gordon we set out to start restoration on a site we affectionately call TA 18.  Training area (TA) 18 is approximately 46 acres of undulating sand hills that were clear cut between February and April of 2008.  Clear cutting is a system where all (or most) of the mature forest canopy is removed to set the stage for artificially regenerating (that is, planting) a forest stand.  In this case, Army land managers cut the loblolly pine trees that don’t belong on the sand hills to plant longleaf pine, a species better-suited to the soil and environmental conditions at TA 18.

By February 2009, our blank canvas was prepared.

The harvesters cut all the loblolly pine trees from the site, leaving only mature longleaf pine and some hardwood trees, the latter mostly oaks and cedars. The logging debris was piled for later burning, and we started with was a landscape devoid of any ground-layer vegetation or substantial forest over story. 

                We needed to answer two basic questions before we could restore grasses and other plants native to the site.  What kind of forest sites would provide a seed mix best suited for TA 18?  What site preparation did we need to get plants started from seed?  We installed a pilot study during March 2009 to test two types of locates for seed collection -- one type had mostly wiregrass and the other had wiregrass mixed with bluesgtem grasses -- combined with four site preparation methods. To prepare the site for planting we used 4  treatments ranging in intentisy from no treatment at all to raking and digging.

Control - no site preparation

Clipping - remove all above-ground vegetation by clipping at soil level

Raking - remove surface litter, scarify soil layer leaving exposed bare mineral soil

Digging - remove aboveground and belowground vegetation tilling the soil much like a garden bed

                Native seeds in general have relatively low rates of germination.  We hypothesized that digging or raking would be best for establishing seedlings and that the mixed seed location would yield more successful germination.  We installed the treatments, collected data, analyzed, and pondered.   Our results showed that raking, followed by digging established the best conditions for seedling development and that the two seed collection types yielded similar numbers of seedlings.  Initial questions answered.

                By the end of this pilot study in November 2009 managers had burned the large piles of slash and applied an herbicide to inhibit growth of hardwood sprouts, notorious for derailing restoration plantings.  The site remained mostly devoid of vegetation.  Applying what we learned from our pilot study, we mimicked the raking treatment with a drum chopper,...

... then decided to use seed from any site that had desirable native species, desirable soil types, species deemed important for our restoration goals, and few aggressive weeds.  Seed was most abundant on sites that had been burned recently...

...We collected seeds both by hand and with the aid of a seed flail-vac, best described as a giant motorized dust buster mounted to the front of a small tractor.  Though frustrated by the paucity of suitable sites, we still collected about 20 pounds of seed.

                We sowed seed on approximately 3 acres of TA 18 in January 2010, then planted  12,500 wiregrass plugs (seedlings grown in containers under ideal conditions) on an additional 4 acres by the end of March 2010...

...Longleaf pine tree seedlings were planted across the entire site in April 2010.  Though small, our initial success has already been realized with the emergence of a continuous layer wiregrass, bluestems, and various native herbs on TA 18! 

Cirsium spp.

Liatris spp.

                Slow and steady wins the race, right?  Our short-term goal is to work out the kinks of native seed collection, storage, and sowing to establish desirable vegetation on TA 18.  We hope to eventually restore our site to what forest ecologists call a “reference condition,” one that represents the species composition, structure, function and health of an ideal tree-dominated biological community – in this case longleaf pine - on that specific plot of land.  Or as measured by that old Army slogan, “We do conserve it and we do deserve it!”

Based in Clemson, SC, Bryan Mudder is a biological science technician with the SRS Longleaf Pine Ecosystems unit.