| | Biomass Removal for Red-Cockaded Woodpecker Habitat Round Oak, GA Piedmont National Wildlife Refuge Submitted by Carl Schmidt, Supervisory Forester, Fish and Wildlife Service | | | Project ID: 1022 1. Name - Biomass Removal for Red-Cockaded Woodpecker Habitat
Context | Objectives | Treatment Specifics | Utilization | Targets | Pre Treatment data | Post Treatment data | Links | | | | Managing the red-cockaded woodpecker (RCW) is the first priority for the Piedmont National Wildlife Refuge (PNWR), and biomass removal has been crucial to improving woodpecker habitat. The refuge has 50 managed RCW cluster sites, of which 38 were active in 2005, and the long-term goal is 96 active cluster sites. The RCW requires mature pine trees in stands of 40 to 80 square feet per acre basal area with little to no midstory. Silviculture is an important tool for the management of RCWs since appropriate practices can restore and maintain the required habitat. PNWR pine stands are managed using the two-aged system with a 100-year rotation. Two-aged stands are created by modified seed tree and irregular shelterwood methods. This style of forestry is compatible with RCW management. Timber thinning is important in reducing stand density to the desired basal area range, thereby creating the desired habitat. Prescribed fire is necessary in controlling the midstory in a two-aged stand.
 Hydro-Ax feller buncher
In the 393 acres of the treated area (Compartment 22), three RCW cluster sites were present. In addition to habitat benefits, 70 acres of Compartment 22 had WUI benefits, and most of the rest of the treatment had hazardous fuel benefits. Many of treated stands were loblolly pine or pine-hardwood uplands. The prescription was generally to remove half of the trees and one-third of the volume. This promoted a thinning from below, concentrating on the trees greater than 10 inch DBH. This provided enough larger trees to make the sale marketable while creating or maintaining the openness desired by the RCW. For the harvest, pine stands were combined with upland hardwood and bottomland hardwood stands. In the upland hardwood stands, a crop tree release was designed to increase acorn production of good quality oaks. Similarly, in the bottomland sites, scattered low quality hardwoods (mostly sweetgum) and pines that overtopped oak trees were removed to release mast-producing trees, increasing acorn production.

Harvesting within cluster sites was carefully controlled, with no activities occurring within a cluster site during the RCW breeding season (April to July). Harvesting in cluster sites was also avoided within at least one or two hours of dawn or dusk. Heavy equipment use was restricted within 50 feet of cavity trees. The plan called for a prescribed burn within two to three years of the harvest. Waiting at least one growing season after harvest before burning would give the logging slash time to cure, allowing better fuel consumption. It would also let leaf litter and needle cast cover skid trails, permitting the fire to better carry across the unit. Burning before three or more growing seasons had passed would take advantage of the open nature caused by the logging and would better achieve the objectives.
The total value to the government of this project was over $69,000, while costs to the government to implement the sale were about $14,000, for a net gain of $55,029. The material removed was as follows:
- Pine pulpwood: 2,382.13 tons. Value: $10,124
- Pine sawtimber: 1,412.84 tons. Value: $45,243
- Hardwood pulpwood: 983.95 tons. Value: $10,823
Links | | | | 2 | Land Ownership Fish and Wildlife Service
| | | | 3 | Location Round Oak, Georgia | | | 4 | Forest Type Loblolly pine
| | | | Context |  | | | 5 | Is this project a part of a landscape plan? Yes
| | | | 6 | In a Wildland Urban Interface (WUI)? Yes
| | | | 7 | Acreage treated 393 ac
| | | | 8 | Type of contract Timber sale
| | | | 9 | Funding source
| | | | 10 | Collaborators and partners
| | | | 11 | Project start date 2006
| | | 12 | Project completion date 2007
| | | | Treatment Goals |  | | | 13 | Restoration, watershed, or habitat improvement
| | | | 14 | Reduce fuel load
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| | | | Treatment Specifics |  | | | 18 | Primary treatment objective Red-Cockaded Woodpecker Habitat | | | | 19 | How does biomass removal fit with other objectives? Well
| | | | 20 | Treatment description Thinning from below
| | | | 21 | Description of contractors
| | | | 22 | Travel distance for contractors
| | | | 23 | Type of equipment used Hydro Ax feller buncher; grapple skidder | | | | 24 | Treatment of residual slash if any Prescribed fire
| | | | 25 | Treatment cost per acre Revenue $177 - cost $37 = profit $140/ac
| | | 26 | Trucking costs
| | | | Utilization |  | | | 27 | Products from project Pulpwood, sawtimber | | | | 28 | Price for products Pine pulp: $4.25/ton; Pine Saw: $32/ton; HW pulp: $11/ton; | | | | 29 | Date of Sale 2007
| | | | 30 | Did biomass markets exist previous to project? Yes
| | | | 31 | Type of utilization
| | | | 32 | How well did the woody biomass match the utilization options?
| | | 33 | Distance to utilization
| | | | Treatment guidelines, targets, limitations |  | | | 34 | Diameter limit
| | | | 35 | Basal area reduction
| | | | 36 | Crown coverage
| | | | 37 | Fuel loading Reduce
| | | | 38 | Retention guidelines
| | | | 39 | Treatment of snags and downed logs
| | | | 40 | Soil impacts
| | | 41 | Other ecological impacts monitored
| | | | Pre Treatment |  | | | 42 | Fuel load
| | | | 43 | Stem density (stems/ac)
| | | | 44 | Basal area (ft2/ac)
| | | | 45 | Canopy closure (%)
| | | | 46 | Height to live crown base
| | | | 47 | Snags and downed woody material
| | | | 48 | Size class distribution Skewed to small trees
| | | | 49 | Tree species composition
| | | | 50 | Presence/absence of invasive species
| | | 51 | Soil and other ecological data
| | | | Post Treatment |  | | | 52 | Fuel load
| | | | 53 | Stem density (stems/ac)
| | | | 54 | Basal area (ft2/ac)
| | | | 55 | Canopy closure (%)
| | | | 56 | Height to live crown base
| | | | 57 | Snags and downed woody material
| | | | 58 | Size class distribution
| | | | 59 | Tree species composition
| | | | 60 | Presence/absence of invasive species
| | | | 61 | Soil and other ecological data
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