Submitted Successfully!
Thank you for your contribution! You can also upload a video entry related to this topic through the link below:
https://encyclopedia.pub/user/video_add?id=15227
Check Note
2000/2000
Ver. Summary Created by Modification Content Size Created at Operation
1 + 1858 word(s) 1858 2021-10-21 11:01:40 |
2 update layout and reference Meta information modification 1858 2021-10-22 04:46:23 | |
3 change the definition -61 word(s) 1797 2021-10-22 04:47:04 |
Stand-Level Optimization
Edit
Upload a video

There is a vast backlog of conducted first commercial thinnings (FCTs) in Finland. The reasons are many, but probably the most crucial would be the lack of simultaneous economic incentives for participating agents, i.e., private forest owners and forest machine contractors. In this study an FCT was executed accruing to five predetermined management options: (1) Industrial wood thinning with only two timber assortments, pulpwood and saw logs, (2) Integrated procurement of industrial and energy wood, (3) Energy wood thinning solely consisting of delimbed stems, (4) Whole-tree energy wood thinning with an energy price of 3 € m−3 and (5) Whole-tree energy wood thinning with energy price of 8 € m−3. Then, a two-phase financial analysis consisting of stand-level optimization (private forest owners) and profitability assessment (contractor) was conducted in order to find out whether there would be simultaneous economic incentives for both participants of FCT. The stand-level optimization revealed the financially best management options for a private forest owner, and then, for a contractor, the profitability assessment exposed the profit (or loss) associated with the particular management option.

  • stand-level optimization
  • first thinning
  • pine
Information
Contributor :
View Times: 48
Entry Collection: Environmental Sciences
Revisions: 3 times (View History)
Update Time: 22 Oct 2021

1. Introduction

The growing stock volume of the Finnish forest resources has been accumulating steadily during the last decades, reaching a value of almost 2500 million cubic meters [1], and so too has the roundwood trade increased during recent years, ranging between ca. 60 and 71 million cubic meters per annum [1]. Despite these positive signals, first commercial thinnings (FCTs) tend to be a bottleneck of the Finnish silviculture—the area of managed/conducted FCTs falls distinctively short of the planned/scheduled area which is based on the silvicultural status and urgency [2]. For instance, in Lapland (the northernmost province of Finland), the need for FCTs within the next five years corresponds to a total of app. 470,000 hectares, while during the last five years there have been carried out app. 190,000 hectares of FCTs [3]. Such a gap between the need for FCTs and actually managed hectares of FCTs—the backlog of FCTs—would in time create problems at aggregate levels in the form of, e.g., a reduction in mean annual increment and decreased timber supply (“passive management”, see [4]). In order to avoid the problems stemming from the backlog of FCTs, potential financial incentives need to be discovered and further revealed for various stakeholders involved in FCT operations. In addition, managing young forests could generate positive socio-economic impacts both at the regional as well as on the national level [5].
In general, stand density is controlled through thinnings to increase growth and to improve stem quality by removing low-quality stems (e.g., [6]). More precisely, FCT in conifer stands affects the diameter growth of dominant trees and, in general, the vigorousness of trees—so that neglecting FCT would delay the diameter growth and, in some cases, would increase the mortality at stand level [7][8]. On the other hand, one of the main reasons for the neglected FCTs is the generally low profitability due to the small stem size and high harvesting costs [9][10]. During the years, there have been several attempts to improve the profitability of FCT, for instance, by applying delimbed-tree [11][12][13][14], or whole-tree harvesting [14][15][16][17][18], integrated harvesting of energy wood and pulpwood [14][19][20][21] or rationalizing integrated harvesting of small-diameter wood by introducing a new technical prototype [22][23]. Regardless of various attempts and existing subsidies (for subsidies, see [24][25]) to improve the profitability of FCT, there still exists a challenge to carry out a financially viable FCT, at least so that each actor (forest owner, forest machine contractor and forest industry company) involved would have a solid financial incentive to venture into business. Further, we consider that the scope of this study (to discover financial incentives related to participating actors of FCT) is eminently country-specific due to, e.g., different legal and operational practices between countries (see [18][24]) facing seemingly similar FCT problems. Thus, the primary goal is to discover the financial incentives associated with FCT country-wise, and only after comparing the results between countries.
In order to assess the financial viability of forest management in a theoretically sound way, one needs to apply stand-level optimization [26], through which the bare land value is maximized (e.g., [27]). In brief, maximizing the bare land value (BLV) yields the discounted economic surplus over an infinite time horizon [28]. In the case of rotation forestry, RF (for terminology, see, e.g., [29]) stand-level optimization reveals the timing and intensity of thinnings as well as the length of the rotation. In this study, the RF approach was adopted, and five options to conduct a FCT were simulated and further optimized (to maximize the BLV) for discovering their financial performance from the viewpoint of a private forest owner. The five options present commonly-used practices applied for FCT, ranging from pure industrial roundwood procurement to a ‘whole trees for energy wood’ alternative. The real-life data for the analyses were derived from a silvicultural database consisting of non-industrial private forest owners’ and NIPFs’ forests in Finland [30]. When stand-level optimization is executed by applying stumpage prices (here), the results, i.e., optimal solutions, refer to the profitability from the private forest owner’s point of view (e.g., [31]).
Conducting a FCT requires that all agents involved find financial incentives to participate. Thus, a financially viable result for a private forest owner does not necessary guarantee that a FCT actually takes place—for example, if there is no economic incentive for a forest machine contractor to employ a thinning, i.e., cut the trees (cf. [32]).

2. Forest Data

The simulations and, further, the financial analyses were based on stand characteristics of six individual stands located in northern Finland (Figure 1). The six stands were derived from a database consisting of NIPF (non-industrial private forests) stands with an urgent need for the first commercial thinning, FCT [30]. The chosen stands belong to specific clusters of postponed FCTs. The clusters (consisting of individual stands) were derived from the project “Timber from postponed first thinnings in Northern Finland”, implemented by the Natural Resources Institute Finland (Luke) and Finnish Forest Centre (Metsäkeskus), and funded by the Centre for Economic Development, Transport and the Environment (ELY) of Northern Ostrobothnia. The stands were selected according to: (i) the stand has passed the juvenile development phase but is not yet a mature stand (technically representing category 2 or 3 in the Finnish system) and (ii) a FCT had been suggested to be conducted in the stand within the past five years. The six chosen stands were quite similar with respect to stem number (trees per hectare) and soil type, but there was a distinctive difference in basal area and mean diameter (DBH) among the stands (Table 1).
Figure 1. A map presenting the locations of Stands 1–6 under study.
Table 1. Stand characteristics of stands 1–6.
Stand Number Main Tree Species Site Type * Stem Number/ha Basal Area, m2/ha Mean Height, m Mean DBH **, cm
1 Scots pine MT 2044 24.63 9.58 15.13
2 Norway spruce MT 1434 33.28 14.05 19.70
3 Scots pine MT 1664 25.98 10.57 15.58
4 Norway spruce MT 1689 35.68 13.67 18.33
5 Norway spruce Mtkg 1320 32.95 14.29 20.21
6 Norway spruce Mtkg 1481 26.72 12.47 17.71

* Myrtillus type (MT) on mineral soils and the corresponding site type on peatlands Myrtillus type (Mtkg) both indicate a fertile site type. For the Finnish forest site type classification, see [33]. ** Mean diameter at breast height.

3. Growth and Yield

As expected, the timing of the final cutting of the ongoing rotation fluctuated considerably, depending on the option (1–5) used to conduct the first commercial thinning (Figure 2, Table 2). For simplicity, optimal management associated with options 1–5 is presented only for stand 1 (Figure 2). In the integrated option (option number 2) the optimal rotation was 94 years, while in option 5 (energy wood, whole II) the corresponding rotation was as high as 107 years (Figure 2). Options 1 (traditional) and 3 (energy wood, stems) resulted in almost identical rotation periods of 101 and 102 years, respectively (Figure 2).
Figure 2. Volume of a growing stock associated with option 1 (traditional), 2 (integrated), 3 (energy wood, stems), 4 (energy wood, whole I) and 5 (energy wood, whole II) according to stand-level optimization in stand 1, m3 ha−1.FCT conducted at the stand age between 54 and 59 years, depending on the option.
Table 2. Thinning removal of the first thinning. Total cutting removal and rotation period associated with optimal solutions according to management options. Total cutting removal and rotation period associated with future generations also shown. Stand-level optimizations simulated with 3% interest rate.
Stand Management option Cutting Removal of the 1st Thinning, m3 ha−1 Total Cutting Removal
m3 ha−1
Ongoing b Future c
Rotation Period,
yrs
Ongoing Future
Stand 1 Traditional 45.0 (0.0) 279.1 324.0 101 98
Integrated 54.0 (10.7) a 266.2 356.3 94 104
Energywood stems 46.0 (46.0) 275.2 304.7 102 95
Energywood whole I 52.0 (52.0) 268.9 346.3 101 102
Energywood whole II 52.0 (52.0) 299.2 314.4 107 96
Stand 2 Traditional 76.0 (0.0) 303.7 404.3 110 78
Integrated 88.0 (12.5) 312.8 381.0 110 78
Energywood stems 52.0 (52.0) 311.9 426.0 111 81
Energywood whole I 59.0 (59.0) 319.2 442.6 111 83
Energywood whole II 60.0 (60.0) 315.8 420.3 110 80
Stand 3 Traditional 58.0 (0.0) 352.0 355.9 91 87
Integrated 69.0 (11.6) 361.6 369.9 91 89
Energywood stems 47.0 (46.6) 352.3 363.0 91 87
Energywood whole I 57.0 (56.8) 362.8 388.1 91 91
Energywood whole II 68.0 (67.9) 364.0 391.6 91 92
Stand 4 Traditional 82.0 (0.0) 325.3 390.8 112 79
Integrated 95.0 (13.5) 330.3 414.6 111 82
Energywood stems 64.5 (64.5) 320.9 413.1 110 82
Energywood whole I 76.0 (75.7) 335.9 437.8 112 85
Energywood whole II 75.5 (75.5) 332.4 423.3 111 83
Stand 5 Traditional 79.0 (0.0) 304.7 402.6 110 78
Integrated 91.0 (13.3) 317.0 413.8 111 79
Energywood Stems 51.0 (50.9) 317.6 425.7 112 81
Energywood whole I 63.0 (62.5) 323.3 442.8 112 83
Energywood whole II 75.0 (74.5) 332.4 423.3 111 83
Stand 6 Traditional 48.0 (0.0) 295.7 381.2 111 77
Integrated 58.0 (9.5) 325.5 428.7 111 81
Energywood Stems 45.2 (45.0) 298.2 372.4 111 76
Energywood whole I 53.3 (53.0) 303.8 385.8 111 78
Energywood whole II 54.0 (53.6) 312.6 399.2 114 80
  Traditional 64.4 (0.0) d 310.1 376.5 105.8 82.8
  Integrated 75.8 (11.8) 318.9 395.4 104.7 85.5
Average Energywood stems 50.8 (50.8) 312.7 384.2 106.3 83.7
  Energywood whole I 59.9 (59.9) 319.0 407.2 106.3 87.0
  Energywood whole II 64.9 (64.9) 326.1 395.3 107.3 85.7
a (of which energy wood). b ongoing rotation. c future rotations. d arithmetic average of stands 1–6.
On average, the integrated option (2) resulted in the highest cutting removal at the first thinning: 75.8 m3 ha−1 (Table 2). The lowest cutting removal at the first thinning was associated with option 3 (energy wood, stems), 50.8 m3 ha−1 (Table 2). However, with respect to total cutting removal of the ongoing rotation, the options 1–5 were quite close to each other, the range being from app. 310 to 326 m3 ha−1 (Table 2). For the future generations, the rotation period varied only mildly: from app. 83 to 87 years depending on the option (Table 2). The cutting removals of future generations, however, fluctuated a bit more, relatively: from ca. 376 to 407 m3 ha−1 (Table 2).

4. Financial Performance

From the private forest owner’s point of view, the best performer (expressed as MaxNPV, Equation (2)) was option 1, traditional, where only saw logs and pulpwood are procured (Figure 3a). For instance, the highest MaxNPV was reached with option 1, the value of 6999 € ha−1, while the lowest MaxNPV value was associated with option 4 (Energy wood, whole I), 2665 € ha−1 (Figure 3a). For pure energy wood alternatives (option 3, 4 and 5), the best performer was option 5 (energy wood, whole II) with a median of 4879 € ha−1 (Figure 3a). Two options (traditional and integrated, options 1 and 2, respectively) distinctively outperformed the other three options (3, 4 and 5) from the contractor’s point of view (Figure 3b). The highest profit among the six stands for a contractor at the first thinning was as much as ca. 2000 € ha−1 in option 1 (traditional), while in option 3 (energy wood, stems) a contractor might even operate at a loss (Figure 3b). Further, in option 4 (energy wood, whole I) and 5 (energy wood, II) the contractor barely makes a profit at the first commercial thinning (Figure 3b).
Figure 3. (a) Boxplots presenting the maximum NPV of options 1–5, € ha−1 (private forest owner’s viewpoint), and (b) profit associated with options 1–5 at the first commercial thinning (contractor’s point of view). (Note that bottom edge of each box illustrates the 25th percentile, upper edge the 75th percentile, a line within a box marks the median and whiskers of the boxplots indicate 5th and 95th percentiles.)

References

  1. Ihalainen, A.; Mäki-Simola, E.; Sauvula-Seppälä, T.; Torvelainen, J.; Uotila, E.; Vaahtera, E.; Ylitalo, E. (Eds.) Finnish Forest Resources; Natural Resources Institute Finland (Luke): Helsinki, Finland, 2019; p. 198.
  2. Korhonen, K.T.; Ihalainen, A.; Ahola, A.; Heikkinen, J.; Henttonen, H.M.; Hotanen, J.-P.; Nevalainen, S.; Pitkänen, J.; Strandström, M.; Viiri, H. (Eds.) Suomen Metsät 2009–2013 ja Niiden Kehitys 1921–2013; Natural Research Institute Finland: Helsinki, Finland, 2017; p. 86.
  3. Korhonen, K.T.; Ihalainen, A.; Strandström, M.; Salminen, O.; Hirvelä, H.; Härkönen, K. Riittääkö puu—VMI-tulokset. In 61. Lapin Metsätalouspäivät, Rovaniemi; METO—Metsäalan Asiantuntijat ry: Helsinki, Finland, February 2019.
  4. Ahtikoski, A.; Hökkä, H. Intensive forest management—Does it financially pay off on drained peatlands? Can. J. For. Res. 2019, 49, 1101–1113.
  5. Karttunen, K.; Ahtikoski, A.; Kujala, S.; Törmä, H.; Kinnunen, J.; Salminen, H.; Huuskonen, S.; Kojola, S.; Lehtonen, M.; Hynynen, J.; et al. Regional socio-economic impacts of intensive forest management, a CGE approach. Biomass Bionerg. 2018, 118, 8–15.
  6. Assman, E. The Principles of Forest Yield Study—Studies in the Organic Production, Structure, Increment and Yield of Forest Stands; Pergamon Press: Oxford, UK, 1970; pp. 1–506.
  7. Hakkila, P. Ensiharvennuspuun hyödyntäminen (Utilization of roundwood from first thinnings). Folia Forestalia 1996, 428–433.
  8. Stöd, R.; Siren, M.; Tanttu, V.; Verkasalo, E. Jäävän puuston ja poistuman tekninen laatu ensiharvennusmänniköissä (Technical quality of remaining trees after first thinning). Metsätieteen Aikakauskirja 2003, 2003, 6110.
  9. Nuutinen, Y.; Kärhä, K.; Laitila, J.; Jylhä, P.; Keskinen, S. Productivity of whole-tree bundler in energy wood and pulpwood harvesting from early thinnings. Scand. J. For. Res. 2011, 26, 329–338.
  10. Mäkinen, H.; Hynynen, J. Wood density and tracheid properties of Scots pine: Responses to repeated fertilization and timing of the first commercial thinning. Forestry 2014, 87, 437–447.
  11. Laitila, J.; Heikkilä, J.; Anttila, P. Harvesting alternatives, accumulation and procurement cost of small-diameter thinning wood for fuel in Central-Finland. Silva Fenn. 2010, 44, 465–480.
  12. Laitila, J.; Väätäinen, K. Truck transportation and chipping productivity of whole trees and delimbed energy wood in Finland. Croat. J. For. Eng. 2012, 33, 199–210.
  13. Petty, A. Opportunities for Cost Mitigation and Efficiency Improvements through Ration Alization of Small-Diameter Energy Wood Supply Chains. Ph.D. Thesis, University of Eastern Finland, Joensuu, Finland, 2014.
  14. Karttunen, K.; Laitila, J.; Ranta, T. First-thinning harvesting alternatives for industrial or energy purposes based on regional Scots pine stand simulations in Finland. Silva Fenn. 2016, 50, 16.
  15. Kärhä, K.; Jouhiaho, A.; Mutikainen, A.; Mattila, M. Mechanized energy wood harvesting from early thinnings. Int. J. For. Eng. 2005, 16, 15–26.
  16. Heikkilä, J.; Siren, M.; Äijälä, O. Management alternatives of energy wood thinning stands. Biomass Bioenerg. 2007, 31, 255–266.
  17. Ahtikoski, A.; Heikkilä, J.; Alenius, V.; Siren, M. Economic viability of utilizing biomass energy from young stands—The case of Finland. Biomass Bioenerg. 2008, 32, 988–996.
  18. Laitila, J.; Väätäinen, K. Productivity and cost of harvesting overgrowth brushwood from roadsides and field edges. Int. J. For. Eng. 2021, 32, 140–154.
  19. Heikkilä, J.; Sirén, M.; Ahtikoski, A.; Hynynen, J.; Sauvula, T.; Lehtonen, M. Energy wood thinning as a part of the stand management of Scots pine and Norway spruce. Silva Fenn. 2009, 43, 129–146.
  20. Kärhä, K. Integrated harvesting of energy wood and pulpwood in first thinnings using the two-pile cutting method. Biomass Bioenerg. 2011, 35, 3397–3403.
  21. Laitila, J.; Väätäinen, K. Hakkuutyön tuottavuus metsävarustellulla turvetuotantotraktorilla karsitun aines- ja energiapuun korjuussa (The cutting productivity in integrated harvesting of pulpwood and delimbed energy wood with a forestry-equipped peat harvesting tractor). Suo Mires Peat 2013, 64, 97–112.
  22. Kärhä, K.; Jylhä, P.; Laitila, J. Integrated procurement of pulpwood and energy wood from early wood from early thinnings using whole-tree bundling. Biomass Bioenerg. 2011, 35, 3389–3396.
  23. Nuutinen, Y.; Björheden, R. Productivity and work processes of small-tree bundler Fixteri FX15a in energy wood harvesting from early pine dominated thinnings. Int. J. For. Eng. 2016, 27, 29–42.
  24. Petty, A.; Kärhä, K. Effect of subsidies on the profitability of energy wood production of wood chips from early thinnings in Finland. For. Policy Econ. 2011, 12, 575–581.
  25. Ministry of Agriculture and Forestry of Finland. Available online: https://mmm.fi/en/forests (accessed on 19 May 2021).
  26. Amacher, G.S.; Ollikainen, M.; Koskela, E. Economics of Forest Resources; The MIT Press: Cambridge, MA, USA, 2009; pp. 1–448.
  27. Niinimäki, S.; Tahvonen, O.; Mäkelä, A. Applying a process-based model in Norway spruce management. For. Ecol. Manag. 2012, 265, 102–115.
  28. Faustmann, M. Berechnung des Werthes, welchen Waldboden, sowie noch nicht haubare Holzbestände für die Waldwirthschaft besitzen. (Calculation of the value which forest land and immature stands possess for forestry). Allgemeine For. Jagd Zeitung 1849, 25, 441–455.
  29. Parkatti, V.-P.; Assmuth, A.; Rämö, J.; Tahvonen, O. Economics of boreal conifer species in continuous cover and rotation forestry. For. Policy Econ. 2019, 100, 55–67.
  30. Finnish Forest Centre. Open Database on NIPFs’ Forests Including Silvicultural Status Associated with Each Stand. 2019. Available online: https://www.metsakeskus.fi/en/open-forest-and-nature-information/information-about-finnish-forests (accessed on 17 October 2019).
  31. Ahtikoski, A.; Karhu, J.; Ahtikoski, R.; Haapanen, M.; Hynynen, J.; Kärkkäinen, K. Financial assessment of alternative breeding goals using stand-level optimization and data envelopment analysis. Scand. J. For. Res. 2020, 35, 262–273.
  32. Tharakan, P.J.; Volk, T.A.; Lindsey, C.A.; Abrahamson, L.P.; White, E.H. Evaluating the impact of three incentive program on the economics of cofiring willow biomass with coal in New York State. Energ. Policy 2005, 33, 337–347.
  33. Tonteri, T.; Hotanen, J.P.; Kuusipalo, J. The Finnish forest site type approach: Ordination and classification studies of mesic forest sites in southern Finland. Vegetatio 1990, 87, 85–98.
More
Information
Contributor :
View Times: 48
Entry Collection: Environmental Sciences
Revisions: 3 times (View History)
Update Time: 22 Oct 2021
Table of Contents

    Confirm

    Are you sure to Delete?

    Video Upload Options

    Do you have a full video?
    Cite
    If you have any further questions, please contact Encyclopedia Editorial Office.
    Ahtikoski, A. Stand-Level Optimization. Encyclopedia. Available online: https://encyclopedia.pub/entry/15227 (accessed on 01 July 2022).
    Ahtikoski A. Stand-Level Optimization. Encyclopedia. Available at: https://encyclopedia.pub/entry/15227. Accessed July 01, 2022.
    Ahtikoski, Anssi. "Stand-Level Optimization," Encyclopedia, https://encyclopedia.pub/entry/15227 (accessed July 01, 2022).
    Ahtikoski, A. (2021, October 21). Stand-Level Optimization. In Encyclopedia. https://encyclopedia.pub/entry/15227
    Ahtikoski, Anssi. ''Stand-Level Optimization.'' Encyclopedia. Web. 21 October, 2021.
    Share
    Download
    Cite
    Top