Research Contribution 21 August 1999
SKYLINE THINNING PRODUCTION AND COSTS: EXPERIENCE FROM THE WILLAMETTE YOUNG STAND PROJECT
By
Loren D Kellogg Mark Miller, Jr Eldon D Olsen
College of Forest Research Laboratory Forestry Oregon State University The Forest Research Laboratory of Oregon State University was established by the Oregon Legislature to conduct research leading to expanded forest yields, increased use of forest products, and accelerated economic development of the State. Its scientists conduct this research in laboratories and forests administered by the University and cooperating agencies and industries throughout Oregon. Research results are made available to potential users through the University’s educational programs and through Laboratory pub- lications such as this, which are directed as appropriate to forest landowners and managers, manufacturers and users of forest products, leaders of govern- ment and industry, the scientific community, and the general public.
The Authors Loren D Kellogg is a professor, Mark Miller, Jr, was a research assistant, and Eldon D Olsen is an associate professor in the Department of Forest Engineer- ing, Oregon State University, Corvallis.
Acknowledgments The authors wish to acknowledge USDA Forest Service personnel on the Blue River, McKenzie, and Oakridge Ranger Districts of Willamette National Forest for their cooperation during the project. We also thank the following logging and felling contractors for their cooperation in the detailed and shift-level production studies: Altemus Tree Trimming (Oakridge, OR), Namitz Logging Corporation (Lebanon, OR), Regrowth Enterprises (Springfield, OR), Skyline Thinning Company (Springfield, OR), and Paul & Arnold Slaven (Oakridge, OR). The purchasers of the thinning sales, Rosboro Lumber Company and Weyerhaeuser Company, also cooperated. Data were collected with the assistance of temporary and student workers from Oregon State University. Ginger Milota, Research Assistant in the Department of Forest Engineering, Oregon State University, assisted with the preparation of this paper. This research was supported by a USDA Forest Service Willamette National Forest Research Grant, a USDA Wood Utilization Special Grant Project, and Oregon State University’s Strachan Forestry Research Fund.
Disclaimer Mention of brand names does not imply endorsement by the authors or by Oregon State University.
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SKYLINE THINNING PRODUCTION AND COSTS: EXPERIENCE FROM THE WILLAMETTE YOUNG STAND PROJECT
By
Loren D Kellogg Mark Miller, Jr Eldon D Olsen
Forest Research Laboratory Abstract
Kellogg, LD, M Miller, Jr, and ED Olsen. 1999. SKYLINE THINNING PRO- DUCTION AND COSTS: EXPERIENCE FROM THE WILLAMETTE YOUNG STAND PROJECT. Forest Research Laboratory, Oregon State University. Research Contribution 21. 33 p.
Production rates and costs for skyline harvesting were examined over a range of residual thinning intensities, operational methods, and sites. The sites included three stands of 40- to 50-yr-old Douglas-fir on the Willamette National Forest in the Cascade Mountains of Oregon. Three silvicultural treatments were studied at two sites, and one silvicultural treatment at the third site. Detailed time studies were conducted on manual felling and uphill skyline yarding with small or mid-size yarders. Separate regression equations were developed to predict delay-free fell- ing cycle time and delay-free yarding cycle time at each site. The three silvicultural treatments had no consistent influence on production rates and costs, because the initial stocking levels varied among treatments and the volume harvested did not necessarily correspond to the silvicul- tural treatment. Cost differences within sites, where operational meth- ods were uniform, were small. Cost differences among sites for each activity, such as felling or yarding, were larger because of differences in operational methods. Total harvesting costs among the three sites were similar, ranging from $58 to $64/100 ft3.
Unit Conversions 1 foot (ft) = 0.305 meter (m) 1 inch (in.) = 2.54 centimeters (cm) 1 ft2 = 0.093 m2 1 ac = 4046.86 m2 1 ft3 = 2.83 x 10-2 m3 Table of Contents
Introduction ...... 7 Project Description ...... 8 Study Sites and Treatments ...... 8 Forest Operations ...... 10 Overview...... 10 Felling ...... 10 Walk Thin and Tap Thin ...... 10 Mill Thin ...... 11 Yarding and Loading ...... 11 Walk Thin ...... 11 Tap Thin ...... 12 Mill Thin ...... 12 Study Methods ...... 13 Detailed Time Studies ...... 13 Felling ...... 13 Yarding ...... 13 Shift-Level Studies...... 14 Cost Analysis ...... 14 Results...... 15 Felling ...... 15 Walk Thin...... 16 Tap Thin ...... 18 Mill Thin ...... 19 Yarding and Loading ...... 20 Walk Thin...... 20 Tap Thin ...... 24 Mill Thin ...... 24 Yarding Sensitivity ...... 24 Harvesting Costs ...... 26 Treatment Comparisons ...... 26 Site Comparisons ...... 26 Discussion ...... 29 Conclusions ...... 30 Literature Cited ...... 31 Appendix: Hourly Owning, Operating, and Labor Costs ...... 32 List of Tables
Table 1. Physical environment and site characteristics before commercial thinning of the light thin (LT), light thin with openings (LTO) and heavy thin (HT) treatment areas at each site ...... 8 Table 2. Stand density before and after thinning and volume harvested in the light thin (LT), light thin with openings (LTO), and heavy thin (HT) treatments at each site...... 9 Table 3. Average felling cycle for each site from the detailed time study ...... 16 Table 4. Summary statistics for the independent variables significant in the felling regression equation for Walk Thin [Eq. 1] in the light thin (LT), light thin with openings (LTO), heavy thin (HT), and all treatments ...... 17 Table 5. Summary statistics for the independent variables significant in the felling regression equation for Tap Thin [Eq. 2] in the light thin (LT), light thin with openings (LTO), heavy thin (HT), and all treatments ...... 18 Table 6. Summary statistics for the independent variables significant in the felling regression equation for Mill Thin [Eq. 3] in the heavy thin (HT) treatment ...... 19 Table 7. Average yarding cycle for each site from the detailed time study; large delays were calculated from the shift-level study ...... 21 Table 8. Summary of road and landing changes and their costs ...... 21 Table 9. Summary statistics for the independent variables significant in the yarding regression equation for Walk Thin [Eq. 4] in the light thin (LT), light thin with openings (LTO), heavy thin (HT) and all treatments ...... 22 Table 10. Average number of pieces per turn, by type, and average total volume per turn for the light thin (LT), light thin between openings (LTBO), openings (Op), heavy thin (HT), and all treatment at each site ...... 23 Table 11. Summary statistics from the independent variables significant in the yarding regression equation for Tap Thin [Eq. 5] in the light thin (LT), light thin with openings 9lTO), heavy thin (HT), and all treatments ...... 25 Table 12. Summary statistics for the independent variables significant in the yarding regression equation for Mill Thin [Eq. 6] in the heavy thin (HT) treatment ...... 26 Table 13. Felling production rates and costs in the light thin (LT), light thin with openings (LTO), heavy thin (HT), and all treat- ments at each site ...... 27 Table 14. Yarding and loading production rates and costs in the light thin (LT), light thin with openings (LTO), heavy thin (HT), and all treatments at each site ...... 27 Table 15. Total harvesting costs in the light thin (LT), light thin with openings LTO), heavy thin (HT), and all treatments at each site ...... 28 Table A1. Felling costs, applicable to all sites ...... 32 Table A2. Yarding and loading costs at Walk Thin ...... 32 Table A3. Yarding and loading costs at Tap Thin ...... 33 Table A4. Yarding and loading costs at Mill Thin ...... 33 List of Figures
Figure 1. Example of a light thin with openings (LTO) treatment...... 9 Figure 2. Example of skyline corridor layout...... 10 Figure 3. Breakdown of total felling delays at each site...... 16 Figure 4. Breakdown of small yarding delays (<10 min), obtained from the detailed time study at each site...... 22 Figure 5. Yarding production rate by yarding distance for each site...... 28 Introduction
Federal forest policy and land use management objectives in the Pacific North- west have changed in emphasis from timber production to ecosystem manage- ment. Ecosystem management recognizes that natural systems must be sustained to meet the social and economic needs of future generations. A better under- standing of ecological processes has highlighted the role of biological diversity in sustaining the health and productivity of ecosystems (Kaiser 1997). Evaluation of the harvesting methods and the costs associated with alter- native silvicultural prescriptions is important to land managers needing to make sound economic and environmental decisions. In western Oregon and Wash- ington, hundreds of thousands of forested acres are in early seral stages (0–50 yr old). Management objectives for these stands vary, but, whether managers want to maximize wood fiber yield or to conserve biodiversity, commercial thinning may help them achieve their goals (Hayes et al. 1997). Further evalu- ation of existing information and large-scale trials of radical thinning regimes are needed (Curtis and Carey 1996). The Willamette Young Stand Project is a long-term, multi-disciplinary re- search effort designed to monitor the effects of managing young stands for ecosystem diversity. The primary silvicultural goals are to determine whether thinning, underplanting, and snag creation accelerate the development of late- successional habitat and increase plant and wildlife habitat diversity in 40- to 50-yr-old plantations of Douglas-fir [Pseudotsuga menziesii (Mirb.) Franco]. Major aspects of the Project include evaluating harvesting economics and resource implications, monitoring wildlife impacts and vegetation response, evaluating tree growth and yield, assessing mushroom productivity, and analyzing social perceptions of three residual thinning intensities and a control. In addition, the effects of three different logging systems used to complete the thinnings are being studied: small to mid-size skyline yarding, tractor skidding, and a cut-to-length (harvester/forwarder) system. Studies of harvesting economics and resource implications were divided into four parts: planning and layout costs, logging production and costs, soil compaction, and stand damage. This paper summarizes detailed production and cost information for the skyline logging portion of the Project. Planning and layout for the Project are described by Kellogg et al. (1998); soil compac- tion is described by Allen (1997); and stand damage, by Han (1997) and Han and Kellogg (1997). Total skyline harvesting costs for alternative silvicultural methods can range from approximately 7% to 32% more than those for conventional clearcut methods (Kellogg et al. 1996a). Previous comparisons of production rates and costs of thinning intensities found that yarding production increased and costs decreased as thinning intensity increased (Hochrein and Kellogg 1988; Kellogg et al. 1996b). This was related partly to an increase in the average number of logs per turn as thinning intensity increased. Hochrein and Kellogg (1988) also determined that yarding with a mid-size yarder (Madill 071) increased costs 11%–12%, depending on thinning intensities, over those with a small yarder (Koller K300). LeDoux and Butler (1982), however, showed that thin- ning intensity did not influence costs when harvest levels were above 80 stems/ ac and a mid-size yarder was used.
7 This report on the study of skyline logging examines production rates and costs over a range of residual thinning intensities, operational methods, and sites. Because this was an operational, rather than a strictly controlled, study, variations existed within and among sites as detailed in the Project Descrip- tion below. The objectives of the study were the following:
• to obtain information on cycle times and delays for felling and yard- ing on each site • to create regression equations that predict delay-free cycle times from significant independent variables • to determine production rates and costs for felling, yarding, and to- tal harvesting • to compare the effects of silvicultural treatments on production and costs within and among sites • to compare costs among the three sites given differences in site con- ditions, crew size, equipment, and logging methods.
Project Description
Study Sites and Treatments The study sites are located in the western Cascade Mountains of Oregon, on the Willamette National Forest. The study areas involved three timber sales, each administered by a different ranger district of the USDA Forest Service (Table 1).
Table 1. Physical environment and site characteristics before commercial thinning of the light thin (LT), light thin with openings (LTO), and heavy thin (HT) treatment areas at each site.a
Stand characteristics Site Study Tree Basal (Ranger area Slope Season Age DBH height Density area District) Treatment (acres) (%) logged (yr) (in.) (ft) (tpa) (ft2/ac)
Walk Thin All 177 0-80 45 10.1 72 205 118 (Oakridge) LT 55 5-80 Summer 45 9.8 71 233 118 LTO 75 0-80 Fall/Summer 45 10.6 73 212 126 HT 47 0-70 Winter 45 10.0 73 169 109
Tap Thin All 111 0-70 46 10.8 72 223 146 (Blue River) LT 60 5-60 Spring/Summer 46 10.7 78 260 171 LTO 32 0-40 Summer 46 10.9 68 230 149 HT 19 0-70 Summer/Fall 46 10.9 70 180 117
Mill Thin HT 69 0-50 Fall/Winter 44 11.8 75 195 149 (McKenzie) aThe stand characteristics of the study treatments were determined by cruising conifer trees >5 in. DBH.
8 All three sites were second-growth stands of Douglas-fir that had been clearcut during the mid-1940s or early 1950s. After logging, the sites had been broadcast burned and allowed to regenerate naturally for 2–4 yr before being interplanted with Douglas-fir. All stands consisted almost entirely of Douglas- fir with some scattered western hemlock [Tsuga heterophylla (Raf.) Sarg.] and western redcedar (Thuja plicata Donn ex D. Don). Elevations ranged from 2000– N 2900 ft. The silvicultural treatments at each site were designed as follows:
• Control—no thinning (This treatment was evaluated in other segments of the Willamette Young Stand Project, but is not treated in this report.) • Light thin (LT)—residual stocking 110–120 trees per acre (tpa) • Light thin with openings (LTO)—residual tpa the same as in the LT treatment, but with additional 0.5-ac openings dispersed system- atically throughout the unit to encompass 20% of the total unit 1/2 ac clearcut area (Figure 1). The average residual stocking was 92 tpa. Regular light thin (20% of unit area) (80% of unit area) • Heavy thin (HT)—residual stocking of 50–55 tpa.
The Walk Thin and the Tap Thin sites each had one replication of each of Figure 1. Example of a light thin the three silvicultural treatments. This allowed us to compare production and with openings (LTO) treatment. costs of the treatments within and between the sites. The Mill Thin site repli- cated only the HT treatment because of limitations in time and resources avail- able for the study. However, this allowed us to see the range of costs that might be expected among three sites when different, but appropriate, har- vesting systems are used. Detailed stand characteristics and the physical envi- ronment before harvest for each site and treatment are listed in Table 1. Forest Service staff planned the sales, designated the treatment bound- aries, and marked the residual leave trees. The timber sales were thinned from below, leaving the dominant and co-dominant trees after harvest. The initial stocking levels and specific treatment prescription determined the total vol- ume removed for each treatment (Table 2); thus, the silvicultural treatment
Table 2. Stand density before and after thinning and volume harvested in the light thin (LT), light thin with openings (LTO), and heavy thin (HT) treatments at each site.
Trees Stand density (tpa) thinned Volume harvested Site Treatment Preharvest Postharvest (tpa) MBF/ac CCF/aca
Walk Thin LT 233 115 118 7.16 22.49 LTO 212 92 120 8.81 27.68 HT 169 53 116 9.47 29.72 Tap Thin LT 260 115 145 9.67 30.35 LTO 230 92 138 8.44 26.50 HT 180 53 127 6.74 21.16 Mill Thin HT 195 53 142 11.19 35.13
aDerived from conversion factor of (3.14)(MBF) = CCF, obtained from scale ticket information.
9 did not necessarily correspond to the volume removed. At Tap Thin, for ex- ample, more volume was removed in the LT treatment than in the HT treat- ment. Volume removed ranged from 50% to 75% of the pre-harvest stand volume.
Forest Operations
Overview Each study site was purchased by a private timber company as a “lump sum” thinning sale (i.e., the purchaser paid for the option to remove all tim- ber not designated as a residual tree). In general, this allowed the purchaser the flexibility of either leaving the pulpwood x x x in the woods or using it, depending on the x volatile pulp market at the time of harvest. However, contractual requirements ensured utilization to at least a 4-in. top diameter. The Forest Service planned the prelimi- nary locations of the landings and spur N x roads, but allowed the contractors the flex- ibility to develop their own harvesting plans x within the scope of the study. Each timber sale had a different logging contractor. On Walk Thin and Tap Thin, the logging con-