The Prescribed Fire Training Center is holding a Workshop for Resource Specialists – Dec 2 – 7, 2012

The Prescribed Fire Training Center is holding a Workshop for Resource Specialists – Dec 2 – 7, 2012

Who?

Prescribed Fire Training Center logo

Resource Specialists, which may include but are not limited to: Wildlife Biologists, Hydrologists, Range Managers, Forestry and Silviculture Specialists and Techs, Land Managers, Botanists, Archeologists, and any discipline that may benefit or be affected by the presence/absence of fire.

Course Objectives

This workshop’s flexible curriculum is based on the participant’s expectations. The schedule is a combination of classroom presentations, discussions, projects and field trips to various managed areas with active fire programs. The overarching goals are to pro-mote the attendee’s knowledge of fire as a management tool and to engage the resource specialist’s active participation in a prescribed fire program by:

  • Facilitating the exchange of experience and knowledge among and between cadre and participants

  • Identifying the differences in fire effects between prescribed fire and wildfire

  • Exposing participants to resource management programs that are successfully con-ducting a burn program through an interdisciplinary approach

  • Addressing fire utilization for resource benefit. Discussing concerns and mitigation steps necessary to incorporate resource needs with fire program needs.

Location

The Workshop will be held in Florida, the location to be determined by weather and field activity opportunities. However, field trips will be taken in a variety of sites and management agencies.

Application Deadline is October 25, 2012.For Additional Information and Application Form Visit the PFTC Website http://www.fws.gov/fire/pftc/

Contact

Greg Seamon, Fire Training Specialist, 850.523.8631 (office); 850.556.8613 (cell); gseamon@tnc.org

Fire frequency and hardwood re-sprouting

Fire frequency and hardwood re-sprouting

Fire frequency and hardwood re-sprouting

By Kevin Robertson, Fire Ecology Research Scientist

One of the primary goals of prescribed burning in southern pine forests is killing the above-ground portion of hardwoods such as oaks and hickories ("top killing") to promote the growth and survival of pine and herb species. These hardwood species typically re-sprout after being top-killed, which requires them to be burned again soon after. 

We conducted research to look at the response of hardwood resprouting to burning at one versus two-year fire return intervals, in the late winter (February-March) versus the early growing season (April-June), and in old-field pine versus native longleaf pine communities. We followed individual resprouting hardwood plants of multiple species for five years, comparing their above-ground biomass at the end of one fire-free interval with their above-ground biomass at the end of a second fire free interval, to see if there was a net growth or decrease in biomass over time under the different fire regimes and community types.

Burning to control hardwood re-sprouts

Results showed that hardwood re-sprouts generally grow back to about the same size as they were before being top killed from one fire-free interval to the next at a given fire return interval (one or two years). However, smaller re-sprouts do tend to get a little larger from one fire-free interval to the next, whereas larger re-sprouts appear to have reached an equilibrium where they do not get larger from one fire-free interval to the next (See figure below). This may be because of increasing competition for resources as the re-sprouts, and presumably their root systems, get larger over time. It may also be due to changes in above-ground versus below-ground allocation of resources within the plant, where smaller re-sprouts save more energy in their roots and thus can re-sprout to larger sizes after being top killed.

Timing of fire had an effect on resprouting, where burns conducted in the early growing season caused re-sprouts to come back at smaller sizes than when they were burned in the late dormant season, although a net decrease in total above-ground biomass was found only in native pine communities burned annually in the growing season.  Less vigorous resprouting in the growing season has been shown in other studies of the southeastern pine forests, attributable to greater above-ground allocation of resources within the plant during the growing season and therefore greater losses to fire. Changes in total above-ground biomass from one fire-free interval to the next were about the same under the one versus two-year fire return intervals, but mortality rates of genetic individuals were highest with annual burning.   

Management implications are that, in the short-term (a few fire-free intervals), hardwood re-sprouts will come back to about the same size as they were before burning, without some other treatment such as herbicide. However, over longer periods of time, growing season burns appear to resist growth hardwood re-sprouts more than dormant season burns, and annual burning permanently kills more of the hardwood re-sprouts than burning every other year, assuming the area was completely burned. Except for burning annually in the growing season in native longleaf pine communities, total above-ground biomass of hardwood re-sprouts is expected to reach an equilibrium under a given fire regime and community type.

Graph

Change in above-ground biomass (log transformed) of hardwood re-sprouts (circles) from the end of one 1-year fire free interval (t1) to the end the next 1-year fire-free interval (t2), showing the line for the best fit equation (solid bold) and 95% confidence intervals (solid light). Smaller re-sprouts return as larger re-sprouts, but larger re-sprouts return to about the same size.

Late Summer Land Management Recommendations


August Management Recommendations

 

Fire Ecology

  • Prescribe burn logging slash or build brush piles.
  • Finish growing season burns in native ground cover before arrival of fall.

Forestry

  • Plan for regeneration by conducting a visual survey of mature longleaf pine trees for cone production
  • Order seedlings early if regeneration is planned and cone crop is poor. Planting containerized seedlings in the fall can achieve better survival than waiting until later in the year.
  • If adequate cone crop, plan for site preparation burn to capture regeneration.
  • Mow between alternate rows within pine plantations to eliminate competition and create different heights of vegetation.

Game Bird

  • Supplemental feed at 1-2 bu/ac/yr.
  • Manage for nest predators if needed.

Land Management

  • Good month to spray herbicides, girdle or fell hardwoods.
  • Plant second round of millet in dove fields, for those who want grain available for the second phase of dove season.
  • Wetter dove fields should be planted with Japanese millet during this wetter month.
  • Plan deer survey route for spotlight counts (Florida only).
  • Mow roads and repair woods roads.

Vertebrate Ecology

  • Good time to replace worn-out artificial cavities for Red-cockaded Woodpeckers. Juveniles start roosting in cavities this time of year and will adopt clean cavities quickly.
  • Lake and pond draw-downs at this time of year can provide benefits for migrating shorebirds and wading birds.
  • Chimney Swifts begin to stage for migration and may use novel roosting sites, including the chimneys of abandoned tenant homes.
  • Swallow-tailed and Mississippi Kites gather in large migratory flocks and may forage over open fields.
  • Early songbird migrants appear; look for Yellow Warblers & Louisiana Water Thrushes along brushy wetland edges.
  • Hummingbirds that venture from breeding habitats may show up at feeders almost anywhere; maintain feeding stations.
  • Gopher Tortoise nests start hatching; keep heavy equipment away from tortoise burrows.
  • Allow some lightning-struck trees to die and decay naturally for the benefit of snag-nesting wildlife.

September Management Recommendations

 

Fire Ecology

  • Execute late growing season prescribed burns for native ground cover.

Forestry

  • Apply fall herbicides for control of hardwoods.
  • Conduct site-preparation burns to capture longleaf regeneration.

Game Bird

  • Begin to mow or chop hunting lanes in late September.
  • Mow thickets, and areas that were too wet to mow in the spring
  • Begin dog training.
  • Begin conditioning of horses and mules.
  • Continue supplemental Feeding at 1-2 bu/ac/yr.
  • Discontinue Predation Management.

Land Management

  • Plant fall food plots, if rainfall is sufficient.
  • Begin mowing or harvesting dove fields.
  • For those who want grain available for the third phase of dove season, plant second round of millet in dove fields.
  • Implement deer surveys to determine harvest strategy.
  • Apply herbicide for exotic grasses.
  • Apply herbicide for hardwood control.

Vertebrate Ecology

  • Fall songbird migration begins in earnest; watch for colorful birds along streamside zones and in hardwood forests.
  • Early Bald Eagles start to return to stake out territories and begin courtships.
  • Red-cockaded Woodpecker translocations begin; trucks in the woods at night may be helping this endangered species.

Economic Impact of the Red Hills Hunting Plantations

What is the Economic Impact of the Red Hills Hunting Plantations?

Quail hunt

Hunting plantations are a major economic driver in the Red Hills.

An important part of protecting the rural character of the Red Hills region has been Tall Timbers’ ability to demonstrate that these rural lands pay more than their fair share to support local services and infrastructure while also providing vital ecosystem services such as clean abundant water, fresh air, and wildlife habitat. 

Increasingly however, the message that truly resonates with elected officials and others who make decisions affecting the Red Hills can be summed up in one word: “Jobs.” While clean water and air is indispensable to everyday life, demonstrating the region’s economic and job-related impacts on local communities is crucial during this difficult economic time. 

Planning Coordinator Neil Fleckenstein is working on a project that will shed light on these important issues. This project will allow us to estimate the direct and indirect economic impact and job creation provided by Red Hills quail hunting properties. We believe this study will demonstrate what we have long known – that the Red Hills is a major driver of local economies and a significant contributor to the overall regional economy. 

One of the first steps in the process is developing and distributing a survey that will be sent to landowners and land managers throughout the Red Hills. This survey is a critical part of this project and the primary means of gathering the information necessary to allow us to estimate the overall economic impact and job creation associated with the Red Hills hunting community. Red Hills landowner participation is crucial as we must obtain a high response rate to accurately estimate the overall economic impact of the region. 

This project will play an important role in our continuing efforts to conserve the Red Hills and we would greatly appreciate your support of this effort. You will be hearing much more about this project in the coming weeks and months. Questions about this project can be directed to TTLC Planning Coordinator Neil Fleckenstein at 850-893-4153, ext. 335.

Midsummer Update on Quail Hatch

Midsummer Update on Quail Hatch

Midsummer update on quail hatch

By Bill Palmer, Director of Research

We compare midsummer (July 15) demographics among years to provide our first dependable indication of where quail populations are headed for the fall. Bumper hatches of quail occur when we have a very strong early hatch, often followed by a moderate late hatch. This year, with mild winter weather and an early spring, nesting began weeks earlier than normal and have continued relatively strong through July. Here are the results for our study areas in Florida and Georgia.

Albany Hatch Improved over Past Years

Below is a graph (Figure 1) showing the average for the last 10 years for 48% of nests and 27% broods produced per 100 radio-tagged hens as well as 53% summer survival of these birds. Quail demographics on the Albany Quail Project study area are above the 10-year average in all categories and are well above figures from this time last year. Indications are that chick survival is very good as brood sizes have remained large. Improvements are due to improved weather conditions combined with some management modifications on our study areas. 

July 15, 2012 Albany Quail Hatch graph

Figure 1. Mid-summer hatch statistics on the Albany Quail Project study site relative to the last five years.

Mild winter weather across the country resulted in fewer than normal migratory hawks and improved overwinter survival of quail. Nesting began early and weather was ideal during much of the early nesting season. Conservative burning and mowing, fertilization of weed fields, and adequate spring rains provided good cover conditions during covey break up and the onset of nesting season. Care was taken to keep supplemental feed in the best cover possible, even if this meant moving the feed trail. All these efforts combined helped improve the summer survival of adult nesters, which is what drives the reproductive output. Yet to be seen is what role cotton rat numbers may be playing in this increase, as we will not do our surveys until late August.

Hopefully, the weather will continue to cooperate for the remaining summer months and populations will be able to recover from last year's drought impacted numbers. We have seen a recent increase in nesting during late July. The first half of the nesting season was excellent but we need a strong late hatch to go with it to see the kind of recovery we are hoping for.

Tall Timbers Hatch Improves over 2010 and 2011

The first half of the nesting season has been a good one. Nesting and adult survival continue to be strong as they have been over the past several years. The main difference in productivity is an increase in nesting success from last year (27%) to this year (68%) and much improved survival of chicks through the first two weeks post-hatch.

Tall Timbers July 15 Hatch graph

Figure 2. Mid-summer hatch statistics on Tall Timbers Research Station relative to the last five years.

Nesting success has increased over last year likely due to increased alternative prey and food items (Figure 2).Rodent numbers were very low last year during the drought, as were blackberries, another staple for omnivorous predators, providing fewer food items for the predator population.Cotton rats have made a surprising rebound this year likely offsetting some predation on adult quail and their nests. Our long-term study shows a direct correlation between cotton rat numbers and nesting success.

The Game Bird Lab, led by biologist Bud Bostick, has captured and banded 188, 8-day old chicks thus far. Nesting seasons, in which we have captured over 200 chicks, based on about the same number of radio-tagged hens, have been years in which our quail population on Tall Timbers increased, and the Red Hills observed above average hunting success. Other positive signs include steady nesting, large number of male incubated nests, and good adult survival. Nearly a quarter of male bobwhites have hatched a nest this year! Of the 188 chicks banded, 52 came from male incubated nests! Collectively, the wild quail demographic machine is on full steam ahead. Hopefully, August through September will bring fair weather as a late hatch on top of our base would make for a significant increase this year. 

Male bobwhite on nest

Male bobwhite incubates a nest. Photo by Bud Bostick

We are in our last year of feeding at 3 treatment levels (0.5, 1 and 2 bushels per acre per year) on Tall Timbers. The differences this year indicate the highest productivity at the 1 and 2 bushels per acre per year level, with 0.49 and 0.78 nests produced per hen, respectively, versus 0.44 nests produced per hen, for the 0.5 bushel per acre per year treatment. So, even in a fantastic weather year, the direct relationship among level of spreading supplemental feed and quail productivity continues to hold. Careful use and management of a supplemental feeding program appears to improve quail production in areas of good habitat.

South Carolina Report

Monitoring radio-tagged hens in South Carolina indicates reproductive output has been similar to the past two years. Managers report seeing good numbers of broods; and we saw good nest production in early May, but nesting success was relatively low, resulting in somewhat lower broods per hen this year compared to past years (see graph). We suspect greater depredation of nests was a result of lower cover in nesting areas due to last summer’s drought. However, since about mid-May, nest success has increased and brood production is increasing.    

Comparing the reproductive output of radio-tagged hens to last summer, we are slightly behind in the number of broods produced per 100 hens, but better than 2009 and 2010 (Figure 3). With most of the low county seeing plenty of rainfall in June and July, the cover has responded well in both the brood fields and burned woods. This should help with increased brood survival, which in turn should mean very good fall bobwhite populations. We have had good adult survival this summer, which puts us in a great position for a good late hatch, as long as the weather stays favorable through September. It’s too early to say whether we will have more birds this season than last, but with a little luck we should have just as many.  

SC Quail Hatch Graph

Figure 3. Mid-summer hatch statistics on South Carolina Quail Project study site relative to the last five years.