Presentation on theme: "W. Neil Gillies Frank Rodgers Cacapon Institute High View, WV A LOW COST DEER EXCLUSION APPROACH FOR FORESTED RIPARIAN BUFFER PLANTINGS."— Presentation transcript:
W. Neil Gillies Frank Rodgers Cacapon Institute High View, WV A LOW COST DEER EXCLUSION APPROACH FOR FORESTED RIPARIAN BUFFER PLANTINGS
It is not the number of trees planted but the number of trees we grow that will restore our forests and protect our waters.
The Lab and other partners on the Hampshire County Riparian Buffers Task Force developed this riparian buffer demonstration project in They did a good job with the planting, and no trees survived – despite repeated attempts.
In 2005 we helped replant the Yellow Spring site, this time using tree tubes. This was one of the first two WV Potomac Tributary Strategy Implementation Team demonstration projects, and was funded by the Chesapeake Bay Program. Trees were planted in 2 and 4 tubes by a WV CREP contractor.
Species Planted Yellow Spring White Ash15 Shagbark Hickory 15 Sugar Maple15 Northern Red Oak 15 White Oak15 Yellow Poplar20 Black Walnut15 Crabapple35 Buttonbush35 Washington Hawthorne 35 Hazelnut35 Flowering Dogwood 35 Chinese Chestnut 35 Total Count species were planted. We even put up a new sign.
Now that the trees were in tubes, how did the plantings fare?
Deer browsing was a huge problem! After two years, only a few scraggly Hawthornes and crabapples were growing much past the top of the tubes, every plant that could be browsed was, and survival was dropping fast.
How can you have successful riparian plantings in areas with abundant deer at a reasonable cost? I started a backyard experiment in 2006 testing the use of parallel electric wires run through a riparian zone in a very high deer area. Initial results were very promising. Trees planted without tubes were not browsed. Natural recruitment was observed. No unprotected trees outside the fenced area that are < 7 high survive on this 54 acre property.
Based on the early success of this backyard experiment, WVDEP provided us with a small grant to do pilot trials on two study sites. The first site was the Yellow Spring riparian site, set up in May It had two experimental blocks with three wire perimeters, two control blocks with a single electric wire running along one side, and one control block with no electric wires. All blocks were 60 x 100. Power was from a solar charger.
All of the trees at this site (that had grown to the top of their tube) had been browsed repeatedly over the previous two years. Many were quite weak.
We replaced a number of the dead trees in each study block with chestnut oak, ash, silky dogwoods and persimmons in May in 1 tubes for rodent protection.
Yellow Spring Results Browse damage in Experimental plots in August 2007 was probably due to heavy weed growth that reduced voltage on the electric fence to less than 2500V.
May 2007 June 6, 2008 May 2007 June 6, 2008 Hazelnut Silky Dogwood Experimental
Hawthorne June 6, 2008 May 2007 June 6, 2008 May 2007 Sugar Maple Experimental
June 6, 2008 May 2007 Hazelnut June 6, 2008 May 2007 Hawthorne Control
Yellow Spring Results Experimental SitesControl Sites Median height of highest intact leaf above tube.
Yellow Spring Results Experimental SitesControl Sites Sample size of plants with intact leaves above tube.
Site 2 is a USDA-CREP (Conservation Reserve and Enhancement Program) site near Baker, WV. Forest condition in the area and the landowner indicated a deer problem exists. This area was planted and a high tensile, electric cattle fence installed in the spring of 2007 under CREP. The two control and two experimental test blocks are 100 feet long and ~35 feet wide, the standard buffer width in WV. There are two perimeter wires spaced four feet apart. Fence was initially powered via a tap from the high tensile fencing.
There were problems at Site 2: Early browsing in experimental plots led to discovery that CREP fence powering the site had insufficient voltage (<2500V) Installed solar fence charger for test blocks in July 2007, but still had some browsing in early August Discovered a short in fence that reduced voltage to ~2200V. Sigh. Fixed short, voltage >5000, browsing problem eliminated in September Vegetation got ahead of us in June 2008, fence voltage down below 3000V. All of the above issues led to training to the fence inconsistency. Despite the problems, how did the plants fare?
CREP Site Results
May 2007 June 26, 2008 Inside exclosure Outside exclosure
Experimental Block East Experimental Block West Control Block East Control Block West
Bears Hell Results Median height of highest intact leaf above tube. Experimental SitesControl Sites
Bears Hell Results Sample size of plants with intact leaves above tube. Experimental SitesControl Sites
Estimated Material Costs per Acre AreaFenceTubes and stakes One acre $ 668 $ 758 Two acres $ 1,045 $ 1,516 Three acres $ 1,423 $ 2,274 Four acres $ 1,800 $ 3,032 Notes: 1. assume weed mats used for each setting 2. Retail prices for materials 3. Tree tube stakes are estimated, probably cost more. 4. Assume 2-wire perimeter fence installed with temporary fence materials.
How is my backyard experiment doing? A significant amount of natural recruitment has taken place, including: black walnut, witch hazel, hornbeam, hophornbeam, linden, red maple, oak spps, hickory, dogwood, cherry, ash, box elder, tulip poplar, locust. There have been only two plants slightly browsed in two years. Every tree outside the fence exclosures is heavily browsed. Three non-tubed plants were lost overwinter to vole damage. Lack of browse = potential for proper forest structure below 6 ft.
Here is a summary of what we observed between June 2007 and June 2008: If the fence is properly installed, energized, and clear of heavy weed growth, protection within fenced areas can be ~100%. In the first few weeks after installation, check the fence for damage as the deer get very upset when they first get in it. The inner wire is more likely to be broken than the outer wire. There does not appear to be much of an edge effect (if any) where trees near the fenced area are protected. Failure to maintain the fence reasonably clear of heavy weed growth results in lowered voltage on the fence and, over time, dramatically reduced success. Just as the literature says, voltages in the voltage range are not terribly effective against deer. The fencing sadly doesnt protect against drought, insects, or rodents.
We are going ahead with the planting this weekend and installing two fenced areas according to your specifications on "site 1" of your study for the walnut planting here at the farm. One of the plots is about 360ft x 30ft and another is about 250ft by 180ft.... The trees that will be within the perimeter of the fence are going to have to fare without tree tubes. (Fall 2007) June 2008: Our trees are... doing very well. We have two plantings. The one on a hillside has been easy to access and is mown regularly. The other planting was underwater for some time this spring and the grass got away from us while we could not get to it with the little mower. I am not sure how those trees are doing at the moment. The maintenance has been the major downside, we have had to mow with a garden mower and the tractor took out the outside strand at one point this spring. Fortunately, repair is easy. Other than maintenance, we are very pleased with the very high survival rate and healthy growth of the trees. Louise McDonald The Bower Farm A local landowner used our fence design on their planting project.
We have a National Fish and Wildlife Foundation grant to expand this project to other riparian sites, and also to upland forest settings, in the Chesapeake Bay watershed. We are looking for cooperators to help select suitable sites and participate in the project by by performing routine maintenance. Please let me know if you are interested.
When white tail deer are too abundant, both the understory and the forest floor layers become degraded, sometimes severely. The understory becomes thin, with few or no new seedlings given a chance to grow, and few leaves left below the deer browse height. The accumulation of fallen leaves that forms much of the litter layer on the forest floor can largely disappear. The role that a thick bed of decaying leaves and good forest soil structure play in slowing runoff, storing moisture, and cycling nutrients may be diminished as a result. If true, this would lead to drier hillsides, more erosive runoff, less infiltration (less groundwater recharge), and flashier streams that dry up easily. Thanks to the National Fish and Wildlife Foundation grant, CI is starting a long-term study to determine if exclusion of deer from sections of forest leads, over time, to an increase in leaf litter retention, restoration of a healthy forest soil structure, and an increase in retained moisture.
Any questions? It is not the number of trees planted but the number of trees we grow that will restore our forests and protect our waters. Cacapon Institute at