Next Article in Journal
A Review of Research on Forest Ecosystem Quality Assessment and Prediction Methods
Next Article in Special Issue
Assessment of Forest Road Models in Concession Areas in the Brazilian Amazon
Previous Article in Journal
Breeding of Highly Virulent Beauveria bassiana Strains for Biological Control of the Leaf-Eating Pests of Dalbergia odorifera
Previous Article in Special Issue
Influence of Tree, Stand, and Site Attributes on Hardwood Product Yield: Insights into the Acadian Forests
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

The State of the Art of Forest Operations in Beech Stands of Europe and Western Asia

by
Francesco Latterini
1,*,
Andrzej M. Jagodziński
1,
Paweł Horodecki
1,
Walter Stefanoni
2,
Rachele Venanzi
2,3 and
Rodolfo Picchio
3
1
Institute of Dendrology, Polish Academy of Sciences, Parkowa 5, 62-035 Kórnik, Poland
2
Consiglio per la Ricerca in Agricoltura e l’Analisi dell’Economia Agraria (CREA), Centro di Ricerca Ingegneria e Trasformazioni Agroalimentari, Via della Pascolare 16, 00015 Monterotondo, Italy
3
Department of Agriculture, Forests, Nature and Energy, Tuscia University, Via San Camillo de Lellis, 01100 Viterbo, Italy
*
Author to whom correspondence should be addressed.
Forests 2023, 14(2), 318; https://doi.org/10.3390/f14020318
Submission received: 17 January 2023 / Revised: 1 February 2023 / Accepted: 3 February 2023 / Published: 6 February 2023

Abstract

:
Beech (Fagus spp.) is one of the most common tree species in Europe and Western Asia. The implementation of sustainable forest Operations (SFOs) in beech forests is therefore crucial in terms of sustainable forest management. This review summarises the state of the art concerning time-motion studies carried out in beech forests, defining the work productivity and the related costs of different harvesting systems applied in these stands. The main focus in recent years on felling and processing operations has been the introduction of fully mechanised systems in beech forests, obtaining satisfactory results in terms of work productivity. However, the working performance is still lower than in coniferous stands. Skidding and forwarding resulted in suitable techniques for ground-based extraction, both showing a clear inclination towards increasing working performance when applying higher levels of mechanisation. Aerial extraction by cable yarders is particularly important in beech forests, considering that these are often located in steep terrains. Further efforts should be dedicated to enhancing the training for operators to extend the application of aerial extraction systems, which ensures good levels of work productivity and limited soil disturbances. In summary, this review aimed to give a clear insight into forest operations in beech forests which could be useful for forest managers, forest engineers and researchers in the sector of sustainable forest operations.

Graphical Abstract

1. Introduction

Beech, here meant as Fagus sylvatica L. and Fagus orientalis Lipsky, is the most important and widespread broadleaf species in Europe and Western Asia [1,2]. Beech grows in a wide range of different environments. It is remarkable to observe that in Central Europe it is a component of lowland and highland [3,4] forests, while in the Mediterranean context, it often represents the timberline [5,6,7]. Beech forests play a primary role in the context of climate change mitigation [8,9,10] and biodiversity conservation [11]. They are also primary sources of timber and firewood [12,13].
The implementation of proper and sustainable management of beech forests is crucial to preserving all the ecosystem services they provide [14]. Putting into practice sustainable forest operations (SFOs) is one of the main aspects in the context of sustainable forest management (SFM) [15]. The term sustainability refers to the goal of achieving social well-being, without compromising environmental resources, through fair economic well-being [16]. It is therefore a concept based on three main aspects, the so-called pillars of sustainability—the economy, the environment and society [17]. The terms of SFOs particularly refer to the application of cost-effective logging that does not compromise environmental wellness and ensures safe and ergonomic working conditions for the operators [18]. SFOs in beech forests are of primary importance, considering some particular features of these stands. Beech forests are indeed often located in steep terrains [19]. Moreover, the architecture of beech trees still represents a challenge for fully mechanised harvesting systems [20].
In consideration of the importance of these forests, this paper aims to define the state of the art in the framework of forest operations in beech stands, summarising the results of the various time-motion studies that have been carried out in beech forests in the last 20 years (2003–2022). The purpose of the review is to give the readers a comprehensive framework of work productivity, associated costs and main issues to be solved regarding the various harvesting systems that are currently applied in beech forests, also with the aim of proposing future research directions in the topic. Following this introduction, there is a section on materials and methods that describes the literature search criteria. Then, there are two sections, one for felling—processing and one for bunching—extraction. The manuscript concludes with suggestions for future research.

2. Materials and Methods

The first step in a literature search was to consult the Web of Science and Scopus. Further documents, in particular conference proceedings and technical reports, were found through the Google Scholar database. The applied research keywords were: beech; Fagus spp.; forest operations; work productivity; time consumption; costs; logging; harvesting; skidding; forwarding and yarding. These keywords were related to the Boolean operators AND and OR. Then the snowball approach was used to find further sources of literature, starting from the reference lists of some of the most recent publications on the topic. The final selection was limited to papers in English published from 2003 to 2022.
Further selection was made after reading the titles and abstracts and finding specific criteria, which were: the paper must report the values of work productivity of a given harvesting system measured by time-motion studies; beech must be the main species of the stand with at least 50% in terms of the number of individuals, basal area, and standing volume; work productivity can be reported in PMH (productive machine hours, excluding delay time) or SMH (scheduled machine hours, including delay time), but the kind of productivity has to be clearly specified in the manuscript. As a result, there were 41 papers identified as suitable to be included in the topic of the review.
The percentage of papers dealing with the different forest operations and the geographical distribution of the various investigated studies are reported in Figure 1 and Figure 2, respectively. A consistent part of the studies dealt with bunching-extraction operations, with skidding, which was the most often applied extraction technique, followed by cable yarding, while forwarding was the least investigated. Regarding felling-processing operations, motor-manual and mechanised felling and processing at the stump were equally investigated, while less attention was given to processing operations at the landing site (Figure 1). The highest number of papers were from Italy (9), followed by Turkey and Germany (5) (Figure 2).

3. Felling and Processing Research Results

3.1. Motor-Manual Felling and Processing

Although in recent years there has been more and more interest in the application of fully mechanised harvesting methodologies in broadleaf stands [20], motor-manual felling by chainsaw is still the most important and applied methodology in beech forests [21]. Work productivity of motor-manual felling in beech stands strongly depends on the kind of intervention and on the dimension of the felled trees. As expected, thinning interventions in young stands with low-diameter trees resulted in lower productivity and higher costs per biomass unit in comparison to felling larger trees in single-selection cutting interventions.
In thinning interventions, work productivity for felling and processing by applying the cut-to-length (CTL) system was reported to be in the range of 0.40–3.50 m3 SMH−1, mostly depending on the average dimension of the felled trees [22,23]. Work productivity and related costs can be decreased by applying alternative harvesting systems, for instance the Tree Length System (TLS). This consists of just a preliminary pre-processing at the stump by removing tops and branches, while final processing is carried out at the landing site [24], where easier working conditions such as flat terrain and open space facilitate the operation. In thinning interventions in even-aged beech stands, felling and processing costs were in the range of EUR 8 m−3 applying the short wood system (SWS) with an average tree dbh (diameter at breast height) of 20 cm and EUR 1.80 m−3 applying TLS with an average tree dbh of 70 cm [24]. A similar price of EUR 8.58 m−3 was reported for felling and processing operations for beech stand thinning, with an average tree dbh of 21 cm [25].
Work productivity was much higher in selection-cutting intervention, mostly as a consequence of the bigger dimensions of the trees. In this case, working productivity can reach 20.6 m3 SMH−1 and 56.5 m3 PMH−1 by the application of the CTL system [26,27]. A recent study also investigated the use of the electric chainsaw for cutting different woody species [28]. For all the species, the level of performance of the electric chainsaw was lower than with a petrol chainsaw of similar power, but interestingly, beech was the species in which the gap was relatively large, suggesting that several technical optimisations of this kind of machine are needed to apply the electric chainsaw for cutting beech trees [28].

3.2. Mechanised Felling and Processing

Fully mechanised harvesting methodologies, for example, feller-bunchers (machines that cut and pile the trees) or harvesters (machines that are also able to perform the processing operation), were initially developed and applied in coniferous stands, but nowadays there is increasing interest in introducing them in broadleaf forests. These methodologies have shown higher work productivity and better ergonomic conditions for forest operators [29]. However, harvesting and processing timber from broadleaved species is more difficult than from coniferous tree species, as a consequence of thicker branches and higher wood density [20].
While the application of feller-bunchers is somewhat easier, not implying processing operations, there are major challenges with regard to the introduction of harvesters for broadleaf species logging. There are two possible approaches to performing this task. The first one consists of applying modified harvester heads, designed for multi-stem harvesting [30], while the second approach consists of applying conventional harvester heads but changing the way branches are separated from the main stem. Branch separation from the main stem is indeed no longer performed with the pivotable gripping arms but instead with the chainsaw used for tree felling by placing the felling head on the branch to be removed [31]. Currently, there are no initiatives to develop harvester heads that are specific for broadleaf logging [20]. Therefore, the literature on studies of the application of harvesters in beech stands all refer to the second approach described above, i.e., the application of conventional harvesters.
The values of working productivity presented in the current literature are, as also happens for motor-manual felling, largely dependent on the dimensions of the felled trees. The range is particularly high; in particular, the lowest productivity of about 3.5–6.0 m3 SMH−1 was reported in thinning interventions with trees 8–10 cm dbh and about 110 m3 ha−1 of standing volume [32], in line with the 5.35 m3 SMH−1 reported by Slugeň et al. (2014) working with bigger trees but in slope class II (about 20%) [33]. Higher values of 10.4 m3 SMH−1 were observed by Horváth et al. (2012), with an average dbh of felled trees of 27 cm [31]. The highest values of working productivity were instead given by two different studies carried out in Germany by Labelle et al. (2018; 2019), with working productivity ranging from 28 to 43 m3 PMH−1 working with trees over 35 cm dbh [34,35]. The authors reported, however, only values of net productivity and highlighted significantly lower performance (31% decrease) in comparison to the same harvester working in a spruce stand [35]. Finally, the only study found in the literature, regarding the application of feller-bunchers for whole-tree harvesting of beech trees for bioenergy purposes, revealed an impressive productivity in the range of 60–75 m3 SMH−1 [36], further highlighting how the main bottleneck for the application of fully mechanised systems in beech stands is processing rather than felling.

3.3. Processing at the Landing Site

To the best of the authors’ knowledge, there was limited data on processing operations at the landing site, with only three studies found in the reference period for the present review. All these studies focused on processing beech wood for energy purposes, specifically two for the production of firewood and one for wood chips.
Comparing the productivity of five firewood processing machines, Manzone and Spinelli (2014) reported productivity ranging from 1.1 to 2.1 tf.m. SMH−1 (tonnes of fresh material per SMH), resulting in processing costs in the range between EUR 20 and 39 tf.m.−1 [37]. Higher productivity was shown for the processing of firewood by chainsaw at the landing site and with the application of a harvester. Four chainsaw operators reached a productivity of 7.4 tf.m. SMH−1 and the harvester 14.7 tf.m. SMH−1, resulting in processing costs of EUR 19.20 and 12.00 tf.m.−1 respectively [38]. Wood chip production from beech logs by a drum chipper powered by a 95 kW farm tractor showed a higher productivity of 23.71 m3 SMH−1 [39]. It is interesting to note that processing operations, which are often not considered as much as felling and extraction by scientific time-motion studies, represent a significant cost in the overall production of beech wood, mostly when dealing with fuel wood.

3.4. Summary Table

The numerical results of the various studies dealing with felling operations are given in Table 1. Productivity using a chainsaw showed a high range of variability, ranging from about 1 m3 SMH−1 [22] to more than 20.6 m3 SMH−1 [26]. High variability was also shown by mechanised systems, with values ranging from 3.3 [32] to 75 m3 SMH−1 [36].

4. Bunching and Extraction Research Results

4.1. Skidding and Hauling

Skidding is an extraction technique that implies partially or fully dragging logs on the soil [41]. It has been the most investigated technique concerning forest operations in beech stands. In the literature database for this review, skidding was studied for different levels of mechanisation, ranging from extraction by animals to forestry-fitted farm tractors and to specific forest machineries such as cable or grapple skidders.
Extracted timber amount and extraction distance were the factors that had a major influence on work productivity.
The lowest productivity for skidding operations in beech stands was found in a salvage logging intervention in Iran after windthrow, with values of 1.54 m3 SMH−1. Such a low value is obviously related to the fact that the intervention was salvage logging, with downed trees that negatively influenced working performance [19].
In conditions of comparable extraction distance and terrain slope, there is, as expected, a growing trend of productivity moving from a low to a higher mechanisation level.
For instance, with logging interventions in slope class II (20%–40%) and a 100 m extraction distance, skidding by animals showed a productivity of 3.8 m3 SMH−1, while skidding with a forestry-fitted farm tractor equipped with a winch achieved values of 6.25 m3 SMH−1 [42]. Slightly higher values of 8.85–14.58 m3 SMH−1 were revealed by a forestry-fitted farm tractor equipped with a winch working in slope class II and with an extraction distance of 55 to 105 m, resulting in an average skidding cost of EUR 6.60 m−3 [43,44]. Similar performance and skidding costs were shown by a study carried out in the same region with similar machinery [45].
With increasing skidding distance to about 200–300 m and smaller tree dimensions skidding productivity by a forestry-fitted farm tractor decreased to about 2–4 m3 SMH−1, with related skidding costs which can reach EUR 10–15 m−3 [46,47].
Increasing the level of mechanisation further increased productivity levels. In fact, the application of cable skidders instead of forestry-fitted farm tractors allowed keeping productivity levels at about 2–9 m3 SMH−1, also at skidding distances higher than 500 m and up to 1700 m, with costs of EUR 4–7 m−3 in thinning and group selection interventions [22,48,49]. At lower skidding distances of 200–300 m and in interventions in mature stands with large-dimension trees, the productivity of cable skidders was much higher, i.e., 14.7 m3 SMH−1, but lower than for grapple skidders, which can reach up to 32.8 m3 SMH−1 working in the same conditions [50].
Some studies also reported the performance of two innovative machineries to perform merely the bunching operation by winching (hauling), that is, bringing the logs from the stand to the closest road and then transporting them by forwarding to the landing site. The first study investigated the performance of a prototype of a winch that can be installed on an excavator to winch logs in steep terrains (40% and higher), showing productivity of 7.6–8.5 m3 SMH−1 for a winching distance of 27–55 m [51]. The second study investigated instead the working performance of remote-controlled mini forestry crawlers to perform the same task described above, achieving a productivity of 6.55 m3 SMH−1 [25]. Interestingly, both solutions showed a better performance than a conventional forest winch installed on a forestry-fitted farm tractor working at a winching distance of 50 m [52].

4.2. Forwarding

The forwarding technique consists of extracting logs from a loading deck without direct contact with the ground. Only three studies dealing with forwarding were identified in the literature database of the present review; two of them investigated the performance of a proper forwarder, while another studied the productivity of the forwarding technique applied with low (animals) and medium (mini tractors) levels of mechanisation.
Forwarding logs of beech wood one meter in length by animals on terrain slope ranging from 15% to 40% and for an extraction distance of 55–950 m, resulted in an average productivity of 3.53 m3 SMH−1, while the same assortment extracted by forwarding with mini tractors on slopes of 10%–20% and extraction distances of 270–360 m resulted in gross working productivity of 2.47 m3 SMH−1 [53].
Regarding the application of a high mechanisation level, i.e., using a forest forwarder, Suadicani and Talbot (2010) reported a productivity of 9.5 m3 SMH−1 for forwarding beech sawlogs and firewood with an extraction distance of 68 m in flat terrain, corresponding to an extraction cost of EUR 9 m−3 [54]. Higher productivity, even with a much higher extraction distance of about 1 km and with a terrain slope of 25%, was reported by Zimbalatti and Proto (2010), which showed about 15 m3 SMH−1 for forwarding operations by the forwarder in shelterwood interventions in beech stands in Southern Italy [55]. This suggests the high suitability of forwarders in beech stands, also in terrains that are not flat, and their ability to achieve high work productivity in different working conditions.

4.3. Aerial Extraction Systems

Since beech forests are often located in steep terrains, aerial extraction systems were largely investigated in this kind of stand. In particular, the productivity and costs of cable yarders in logging interventions in beech forests were the focus of six papers in the reference period for this review. Also for cable yarders, yarding distance and extracted volume were the major influencing factors for work productivity. Mini cable yarders suitable for thinning interventions in the framework of small-scale forestry achieved a productivity of 1.5–2.4 m3 SMH−1, resulting in yarding costs of EUR 24–30 m−3 in thinning interventions in a beech stand located in slope class III (40%–60%) with a yarding distance of about 100 m [56]. With the same yarding distance, more powerful models are able to achieve productivity higher than 10 m3 SMH−1 [42] or have similar productivity but with yarding distances four times longer [57]. However, both for mini yarders and regular ones, downhill extraction shows lower working productivity than uphill extraction [56,57]. Working productivity in group shelterwood interventions was much higher, thanks to the higher dimensions of the trees, with 8.8 m3 SMH−1 and 8.41 m3 SMH−1 reported, respectively, by Munteanu et al. (2019) with a yarding distance of 326 m [58] and Stoilov (2021) with yarding distances of 160–250 m [59]. The same studies reported yarding costs for group shelterwood in beech forests in the range between EUR 7 m−3 and EUR 13 m−3 [58,59]. One study also analysed the working productivity of a cable car unconventionally applied for beech timber extraction in Albania. With yarding distances of 800–900 m and in a clear-cut intervention, this unconventional system reached a productivity of 4.73 m3 SMH−1 [23].

4.4. Summary Table

Data retrieved from the various studies dealing with extraction operation are given in Table 2. Both for skidding and forwarding work productivity increased moving from small-scale systems to modern forest machinery. Forwarding productivity ranged from values of about 2.5 m3 SMH−1 for small-scale systems [57] to 15 m3 SMH−1 for modern forwarders [55]. Skidding productivity ranged from about 1.5 m3 SMH−1 in salvage logging interventions [19] to more than 30 m3 SMH−1 in final shelterwood cuttings [60].

5. Conclusions

The plethora of different stand characteristics and localisations that are typical of beech forests imply great variability in harvesting productivity and related costs. Taking into account this great variability, this review aimed to summarise the findings in terms of time-motion studies conducted in beech forests in the last 20 years.
The main findings and related suggestions for future research can be summarised as follows:
  • Although motor-manual felling and processing by chainsaw are still predominant, a growing interest is expected towards the introduction of fully mechanised methodologies (fellers and harvesters) in beech forests. Research on this topic has been productive in recent years, highlighting that mechanising felling and processing operations in beech stands is possible, but that there are still different issues to be solved to achieve the productivity levels typical of these machineries in coniferous stands. The development of dedicated harvester heads specifically for broadleaf species is still far from being realised, and there are actually no research initiatives on this topic [20]. Therefore, the efforts of researchers and forest managers should be directed towards increasing the technical skills of forest operators in working with harvesters with conventional heads and applying modern technologies such as augmented reality, which can ensure effective training without compromising the safety of beginner operators [62].
  • The introduction of fully mechanised felling and processing operations in beech stands is not only limited by the intrinsic characteristics of beech trees, but also by the fact that beech stands are often located in steep mountainous terrains, mostly in the Mediterranean and Western Asia zones. In light of this, it should be interesting to implement and scientifically test the economic and environmental performance of winch-assisted harvesting in beech forests. Winch-assist systems have been proven to be suitable for introducing full mechanical harvesting in difficult terrain conditions, increasing both work productivity and ergonomics for the operators [63]. Furthermore, it is interesting to observe that these systems generally show lower soil disturbance as compared to traditional harvesting systems [64]. Therefore, their introduction in the framework of beech silviculture, after proper scientific evaluation and subsequent training of the operators, could be beneficial for the implementation of SFOs in beech forests.
  • Concerning ground-based extraction, different techniques and machineries are suitable for beech stands. Both skidding and forwarding reached comparable productivities under similar working conditions. As expected, the higher the mechanisation level, the higher the productivity. However, further time-motion studies are welcome to extend the amount of literature for comprehensive reviews and meta-analyses of the topic [65]. It is important to compare different ground-based extraction options from an environmental point of view, understanding at a deeper level the implications that a given extraction system has on various aspects of forest ecosystems, which include soil, biodiversity, natural regeneration and ecological processes [66,67,68,69].
  • Aerial extraction via cable yarders is a recommended solution in the case of harvesting in steep terrains. Besides satisfactory work productivity, these methodologies can limit soil disturbances, mostly when working with fully suspended loads [70]. It is therefore imperative to comprehend that operator training is fundamental to encouraging the use of these harvesting systems in the context of SFOs in beech forests.
In conclusion, this work has sought to define the state of the art in the framework of forest operations in beech stands. The results of 41 papers of a high scientific level were gathered. The criteria of choice included time-motion studies that have been carried out in beech forests in the last 20 years (2003–2022). It is worth highlighting that we referred to publications in the English language; it is possible that other similar works could have been published in different languages or, however, are not available from the investigated repositories; this represents the main limitation of this review.
The findings, however, provide a better understanding of harvesting systems for beech stands, namely the work productivity and associated costs, and they also highlight the main issues that still remain unsolved.

Author Contributions

Conceptualization, F.L. and R.P.; methodology, F.L.; writing—original draft preparation, F.L., A.M.J., P.H., W.S., R.V. and R.P.; writing—review and editing, F.L., A.M.J., P.H., W.S., R.V. and R.P.; supervision, A.M.J. and R.P.; funding acquisition, F.L. and A.M.J. All authors have read and agreed to the published version of the manuscript.

Funding

This study was developed in the framework of the project AIMSUSFOR “Extending assessment of the environmental impacts to the forest ecosystem due to forest management: a comprehensive approach to enhance sustainable forestry in the context of climate change”, funded under the PASIFIC Call 1 announced by the Polish Academy of Sciences. This project has received funding from the European Union’s Horizon 2020 research and innovation programme under the Marie Skłodowska-Curie grant agreement No 847639 and from the Polish Ministry of Education and Science.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are available on request from the corresponding author.

Acknowledgments

This study was carried out also within the Agritech National Research Center and received funding from the European Union Next-GenerationEU (PIANO NAZIONALE DI RIPRESA E RESILIENZA (PNRR)—MISSIONE 4 COMPONENTE 2, INVESTIMENTO 1.4—D.D. 1032 17/06/2022, CN00000022). This manuscript reflects only the authors’ views and opinions, neither the European Union nor the European Commission can be considered responsible for them.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Antonucci, S.; Santopuoli, G.; Marchetti, M.; Tognetti, R.; Chiavetta, U.; Garfì, V. What Is Known about the Management of European Beech Forests Facing Climate Change? A Review. Curr. For. Rep. 2021, 7, 321–333. [Google Scholar] [CrossRef]
  2. Tavankar, F.; Nikooy, M.; Lo Monaco, A.; Picchio, R. Long-term impact of selection cutting management on frequency of stem deformity in mixed beech forests of northern Iran. Drewno 2021, 64, 5–26. [Google Scholar]
  3. Jagodziński, A.M.; Dyderski, M.K.; Horodecki, P. Differences in biomass production and carbon sequestration between highland and lowland stands of Picea abies (L.) H. Karst. and Fagus sylvatica L. For. Ecol. Manag. 2020, 474, 118329. [Google Scholar] [CrossRef]
  4. Petritan, I.C.; Mihăilă, V.V.; Bragă, C.I.; Boura, M.; Vasile, D.; Petritan, A.M. Litterfall production and leaf area index in a virgin European beech (Fagus sylvatica L.)—Silver fir (Abies alba Mill.) forest. Dendrobiology 2020, 83, 75–84. [Google Scholar] [CrossRef]
  5. Stojanović, D.B.; Levanič, T.; Matović, B.; Stjepanović, S.; Orlović, S. Growth response of different tree species (oaks, beech and pine) from SE Europe to precipitation over time. Dendrobiology 2018, 79, 97–110. [Google Scholar] [CrossRef]
  6. Calderaro, C.; Cocozza, C.; Palombo, C.; Lasserre, B.; Marchetti, M.; Tognetti, R. Climate–growth relationships at the transition between Fagus sylvatica and Pinus mugo forest communities in a Mediterranean mountain. Ann. For. Sci. 2020, 77, 63. [Google Scholar] [CrossRef]
  7. Milios, E.; Papalexandris, C. Height growth of sprouts emerged from small stumps and seed origin saplings under shade, in low elevation Fagus sylvatica L. s.l. stands in Greece. Dendrobiology 2019, 82, 1–7. [Google Scholar] [CrossRef]
  8. Martinez del Castillo, E.; Zang, C.S.; Buras, A.; Hacket-Pain, A.; Esper, J.; Serrano-Notivoli, R.; Hartl, C.; Weigel, R.; Klesse, S.; Resco de Dios, V.; et al. Climate-change-driven growth decline of European beech forests. Commun. Biol. 2022, 5, 163. [Google Scholar] [CrossRef]
  9. Leuschner, C.; Feldmann, E.; Pichler, V.; Glatthorn, J.; Hertel, D. Forest management impact on soil organic carbon: A paired-plot study in primeval and managed European beech forests. For. Ecol. Manag. 2022, 512, 120163. [Google Scholar] [CrossRef]
  10. Vančura, K.; Šimková, M.; Vacek, Z.; Vacek, S.; Gallo, J.; Šimůnek, V.; Podrázský, V.; Štefančík, I.; Hájek, V.; Prokůpková, A.; et al. Effects of environmental factors and management on dynamics of mixed calcareous forests under climate change in Central European lowlands. Dendrobiology 2022, 87, 79–100. [Google Scholar] [CrossRef]
  11. Zumr, V.; Remeš, J.; Nakládal, O. Small-scale spontaneous dynamics in temperate beech stands as an importance driver for beetle species richness. Sci. Rep. 2022, 12, 11974. [Google Scholar] [CrossRef]
  12. Marenče, J.; Šega, B.; Gornik Bučar, D. Monitoring the Quality and Quantity of Beechwood from Tree to Sawmill Product. Croat. J. For. Eng. 2020, 41, 119–128. [Google Scholar] [CrossRef]
  13. Heshmatol Vaezin, S.M.; Moftakhar Juybari, M.; Sadeghi, S.M.M.; Banaś, J.; Marcu, M.V. The Seasonal Fluctuation of Timber Prices in Hyrcanian Temperate Forests, Northern Iran. Forests 2022, 13, 761. [Google Scholar] [CrossRef]
  14. Štefančík, I.; Vacek, Z.; Sharma, R.P.; Vacek, S.; Rösslová, M. Effect of thinning regimes on growth and development of crop trees in Fagus sylvatica stands of central Europe over fifty years. Dendrobiology 2018, 79, 141–155. [Google Scholar] [CrossRef]
  15. Marchi, E.; Chung, W.; Visser, R.; Abbas, D.; Nordfjell, T.; Mederski, P.S.; McEwan, A.; Brink, M.; Laschi, A. Sustainable Forest Operations (SFO): A new paradigm in a changing world and climate. Sci. Total Environ. 2018, 634, 1385–1397. [Google Scholar] [CrossRef]
  16. Koehler, D.A.; Hecht, A.D. Sustainability, well being, and environmental protection: Perspectives and recommendations from an Environmental Protection Agency forum. Sustain. Sci. Pract. Policy 2006, 2, 22–28. [Google Scholar] [CrossRef]
  17. Kastenhofer, K.; Rammel, C. Obstacles to and potentials of the societal implementation of sustainable development: A comparative analysis of two case studies. Sustain. Sci. Pract. Policy 2005, 1, 5–13. [Google Scholar] [CrossRef]
  18. Picchio, R.; Latterini, F.; Mederski, P.S.; Tocci, D.; Venanzi, R.; Stefanoni, W.; Pari, L. Applications of GIS-Based Software to Improve the Sustainability of a Forwarding Operation in Central Italy. Sustainability 2020, 12, 5716. [Google Scholar] [CrossRef]
  19. Iranparast Bodaghi, A.; Nikooy, M.; Naghdi, R.; Venanzi, R.; Latterini, F.; Tavankar, F.; Picchio, R. Ground-Based Extraction on Salvage Logging in Two High Forests: A Productivity and Cost Analysis. Forests 2018, 9, 729. [Google Scholar] [CrossRef]
  20. Mederski, P.S.; Schweier, J.; Đuka, A.; Tsioras, P.; Bont, L.G.; Bembenek, M. Mechanised Harvesting of Broadleaved Tree Species in Europe. Curr. For. Rep. 2022, 8, 1–19. [Google Scholar] [CrossRef]
  21. Hoffmann, S.; Jaeger, D. Insights on motor-manual tree felling in Germany, recent developments to ensure efficient operations in singletree selection harvest. Eur. J. For. Eng. 2021, 7, 39–44. [Google Scholar] [CrossRef]
  22. Sadowski, J.; Moskalik, T.; Zastocki, D. Basic parameters of timber harvesting processes in mountain beech stands in Komancza Forest Inspectorate. Acta Sci. Pol. Silvarum Colendarum Ratio Ind. Lignaria 2012, 11, 37–44. [Google Scholar]
  23. Kortoci, Y.; Kellezi, M. Comparison of time consumption and productivity during beech forest felling and processing in two different working conditions. Bilge Int. J. Sci. Technol. Res. 2020, 4, 43–47. [Google Scholar] [CrossRef]
  24. Marčeta, D.; Košir, B. Comparison of two felling & processing methods in beech forests. Croat. J. For. Eng. 2016, 37, 163–174. [Google Scholar]
  25. Berendt, F.; Fortin, M.; Suchomel, C.; Schweier, J. Productivity, Costs, and Selected Environmental Impacts of Remote-Controlled Mini Forestry Crawlers. Forests 2018, 9, 591. [Google Scholar] [CrossRef]
  26. Behjou, F.K.; Majnounian, B.; Dvořák, J.; Namiranian, M.; Saeed, A.; Feghhi, J. Productivity and cost of manual felling with a chainsaw in Caspian forests. J. For. Sci. 2009, 55, 96–100. [Google Scholar] [CrossRef]
  27. Ghaffariyan, M.R.; Naghdi, R.; Ghajar, I.; Nikooy, M. Time Prediction Models and Cost Evaluation of Cut-To-Length (CTL) Harvesting Method in a Mountainous Forest. Small-Scale For. 2013, 12, 181–192. [Google Scholar] [CrossRef]
  28. Neri, F.; Laschi, A.; Marchi, E.; Marra, E.; Fabiano, F.; Frassinelli, N.; Foderi, C. Use of Battery- vs. Petrol-Powered Chainsaws in Forestry: Comparing Performances on Cutting Time. Forests 2022, 13, 683. [Google Scholar] [CrossRef]
  29. Dembure, T.P.; McEwan, A.; Spinelli, R.; Magagnotti, N.; Ramantswana, M. A comparison between two alternative harvesting systems in the thinning of fast-growing pine plantations under the conditions of low labour cost. Eur. J. For. Res. 2019, 138, 43–52. [Google Scholar] [CrossRef]
  30. Laitila, J.; Niemistö, P.; Väätäinen, K. Productivity of multi-tree cutting in thinnings and clear cuttings of young downy birch (Betula pubescens) dominated stands in the integrated harvesting of pulpwood and energy wood. Balt. For. 2016, 22, 116–131. [Google Scholar]
  31. Horváth, A.L.; Szakálos-Mátyás, K.; Horváth, B. Investigation of the applicability of multi-operational logging machines in Hardwood stands. Acta Silv. Lignaria Hung. 2012, 8, 133–144. [Google Scholar] [CrossRef]
  32. Bergström, D.; Fernandez-Lacruz, R.; de la Fuente, T.; Höök, C.; Krajnc, N.; Malinen, J.; Nuutinen, Y.; Triplat, M.; Nordfjell, T. Effects of boom-corridor thinning on harvester productivity and residual stand structure. Int. J. For. Eng. 2022, 33, 226–242. [Google Scholar] [CrossRef]
  33. Slugeň, J.; Peniaško, P.; Messingerová, V.; Jankovský, M. Productivity of a John Deere harvester unit in deciduous stands. Acta Univ. Agric. Silvic. Mendel. Brun. 2014, 62, 231–238. [Google Scholar] [CrossRef]
  34. Labelle, E.; Breinig, L.; Sycheva, E. Exploring the Use of Harvesters in Large-Diameter Hardwood-Dominated Stands. Forests 2018, 9, 424. [Google Scholar] [CrossRef] [Green Version]
  35. Labelle, E.R.; Windisch, J.; Gloning, P. Productivity of a single-grip harvester in a beech dominated stand: A case-study under Bavarian conditions. J. For. Res. 2019, 24, 100–106. [Google Scholar] [CrossRef]
  36. Coup, C.E.; Benjamin, J.G.; Wagner, R.G. Harvesting Biomass to improve low-value beech dominated hardwood stands in Maine. In Proceedings of the 31st Annual Meeting of the Council on Forest Engineering (COFE), Charleston, SC, USA, 22–25 June 2008; pp. 1–6. [Google Scholar]
  37. Manzone, M.; Spinelli, R. Efficiency of small-scale firewood processing operations in Southern Europe. Fuel Process. Technol. 2014, 122, 58–63. [Google Scholar] [CrossRef]
  38. Spinelli, R.; Magagnotti, N.; Nati, C. Options for the Mechanized Processing of Hardwood Trees. Int. J. For. Eng. 2009, 20, 39–44. [Google Scholar]
  39. Spinelli, R.; Magagnotti, N. Performance of a small-scale chipper for professional rural contractors. For. Sci. Pract. 2013, 15, 206–213. [Google Scholar] [CrossRef]
  40. Labelle, E.R.; Windisch, J. Productivity of a single-grip TimberPro 620 harvester with a LogMax 7000 harvesting head in a beech dominated stand. In Proceedings of the 49th FORMEC Symposium, Warsaw, Poland, 4–7 September 2016; pp. 77–82. [Google Scholar]
  41. Marra, E.; Laschi, A.; Fabiano, F.; Foderi, C.; Neri, F.; Mastrolonardo, G.; Nordfjell, T.; Marchi, E. Impacts of wood extraction on soil: Assessing rutting and soil compaction caused by skidding and forwarding by means of traditional and innovative methods. Eur. J. For. Res. 2022, 141, 71–86. [Google Scholar] [CrossRef]
  42. Melemez, K.; Tunay, M.; Emir, T. A Comparison of Productivity in Five Small-Scale Harvesting Systems. Small-Scale For. 2014, 13, 35–45. [Google Scholar] [CrossRef]
  43. Ozturk, T.; Senturk, N. Productivity and time studies of MB Trac 900 tractor at beech stands on mountainous areas in Turkey. Balt. For. 2010, 16, 132–138. [Google Scholar]
  44. Ozturk, T. Productivity of MB Trac 900 tractor at beech stands on mountainous areas in Blacksea region. Afr. J. Agric. Res. 2010, 5, 28–33. [Google Scholar]
  45. Özturk, T. Productivity of New Holland farm tractor at beech stands on mountainous areas in Black Sea Region. For. Ideas 2010, 16, 39. [Google Scholar]
  46. Spinelli, R.; Magagnotti, N. Wood Extraction with Farm Tractor and Sulky: Estimating Productivity, Cost and Energy Consumption. Small-Scale For. 2012, 11, 73–85. [Google Scholar] [CrossRef]
  47. Zečić, Ž.; Krpan, A.P.B.; Vukušić, S. Productivity of C Holder 870 F tractor with double drum winch Igland 4002 in thinning beech stands. Croat. J. For. Eng. 2006, 27, 49–57. [Google Scholar]
  48. Borz, S.A.; Ignea, G.; Popa, B.; Iordache, E.; Spârchez, G. Estimating time consumption and productivity of roundwood skidding in group shelterwood system—A case study in a broadleaved mixed stand located in reduced accessibility conditions. Croat. J. For. Eng. 2015, 36, 137–146. [Google Scholar]
  49. Knežević, J.; Gurda, S.; Musić, J.; Halilović, V.; Vranović, A. Productivity of the Ecotrac 120V Skidder for Timber Skidding in the Area of Mu “Igman”. Rad. Šumarskog Fak. Univ. U Sarajev. 2018, 48, 17–32. [Google Scholar] [CrossRef]
  50. Mederski, P.; Bembenek, M.; Erler, J.; Giefing, D.F.; Karaszewski, Z. The Enhancement of Skidding Productivity Resulting From Changes in Construction: Grapple Skidder Vs Rope Skidder. In Proceedings of the FORMEC 2010 Forest Engineering: Meeting the Needs of the Society and the Environment, Padua, Italy, 11–14 July 2010; pp. 1–7. [Google Scholar]
  51. Ruch, P.; Vigneau, N.; Loye, H.; Francois, D.; Montagny, X.; Santini, O.; Vuillermoz, M. TVS20, a Multifunction Tool to Up-Grade an Excavator into a Versatile Winch-Based Haulage Equipment for Hard-to-Reach Areas: Lessons Learnt from 6 Operations with the Prototype. In Proceedings of the COFE-FORMEC 2021—Forest Engineering Family: Growing Forward Together, Corvallis, OR, USA, 27–30 September 2021; pp. 155–163. [Google Scholar]
  52. Sowa, J.M.; Szewczyk, G. Time Consumption of Skidding in Mature Stands Performed by Winches Powered by Farm Tractor. Croat. J. For. Eng. 2013, 34, 255–264. [Google Scholar]
  53. Gallis, C. Comparative cost estimation for forwarding small-sized beech wood with horses and mini-skidder in northern Greece. For. Prod. J. 2004, 54, 84–90. [Google Scholar]
  54. Suadicani, K.; Talbot, B. Extracting and chipping hardwood crowns for energy. Scand. J. For. Res. 2010, 25, 455–461. [Google Scholar] [CrossRef]
  55. Zimbalatti, G.; Proto, A.R. Productivity of forwarders in South Italy. In Proceedings of the FORMEC 2010, Forest Engineering: Meeting the Needs of the Society and the Environment, Padua, Italy, 11–14 July 2010; pp. 1–7. [Google Scholar]
  56. Spinelli, R.; Magagnotti, N.; Lombardini, C. Performance, capability and costs of small-scale cable yarding technology. Small-Scale For. 2010, 9, 123–135. [Google Scholar] [CrossRef]
  57. Eroǧlu, H.; Özkaya, M.S.; Acar, H.H.; Karaman, A.; Yolasigmaz, H.A. An investigation on roundwood extraction of Fagus orientalis lipsky, Abies nordmanniana (Stew.) Spach. and Picea orientalis (L.) Link. by Urus M III forest skyline on snow. Afr. J. Biotechnol. 2009, 8, 1082–1089. [Google Scholar]
  58. Munteanu, C.; Yoshida, M.; Iordache, E.; Borz, S.A.; Ignea, G. Performance and cost of downhill cable yarding operations in a group shelterwood system. J. For. Res. 2019, 24, 125–130. [Google Scholar] [CrossRef]
  59. Stoilov, S. Productivity and Costs of Cable Yarding in Group Shelterwood System in Deciduous Forests. For. Ideas 2021, 27, 331–342. [Google Scholar]
  60. Bembenek, M.; Mederski, P.S.; Erler, J.; Giefing, D.F. Results of large-size timber extracting with a grapple skidder. Acta Sci. Pol. 2011, 10, 5–14. [Google Scholar]
  61. Marčeta, D.; Petković, V.; Košir, B. Comparison of two skidding methods in beech forests in mountainous conditions. Nov. Meh. Sumar. 2014, 35, 51–62. [Google Scholar]
  62. Molinaro, M.; Orzes, G. From forest to finished products: The contribution of Industry 4.0 technologies to the wood sector. Comput. Ind. 2022, 138, 103637. [Google Scholar] [CrossRef]
  63. Holzfeind, T.; Visser, R.; Chung, W.; Holzleitner, F.; Erber, G. Development and Benefits of Winch-Assist Harvesting. Curr. For. Rep. 2020, 6, 201–209. [Google Scholar] [CrossRef]
  64. Visser, R.; Stampfer, K. Expanding ground-based harvesting onto steep terrain: A review. Croat. J. For. Eng. 2015, 36, 321–331. [Google Scholar]
  65. Louis, L.T.; Kizha, A.R.; Daigneault, A.; Han, H.-S.; Weiskittel, A. Factors Affecting Operational Cost and Productivity of Ground-Based Timber Harvesting Machines: A Meta-analysis. Curr. For. Rep. 2022, 8, 38–54. [Google Scholar] [CrossRef]
  66. Labelle, E.R.; Hansson, L.; Högbom, L.; Jourgholami, M.; Laschi, A. Strategies to Mitigate the Effects of Soil Physical Disturbances Caused by Forest Machinery: A Comprehensive Review. Curr. For. Rep. 2022, 8, 20–37. [Google Scholar] [CrossRef]
  67. Schweier, J.; Magagnotti, N.; Labelle, E.R.; Athanassiadis, D. Sustainability Impact Assessment of Forest Operations: A Review. Curr. For. Rep. 2019, 5, 101–113. [Google Scholar] [CrossRef]
  68. Picchio, R.; Venanzi, R.; Tavankar, F.; Luchenti, I.; Iranparast Bodaghi, A.; Latterini, F.; Nikooy, M.; Di Marzio, N.; Naghdi, R. Changes in soil parameters of forests after windstorms and timber extraction. Eur. J. For. Res. 2019, 138, 875–888. [Google Scholar] [CrossRef]
  69. Lo Monaco, A.; Luziatelli, G.; Latterini, F.; Tavankar, F.; Picchio, R. Structure and Dynamics of Deadwood in Pine and Oak Stands and their Role in CO2 Sequestration in Lowland Forests of Central Italy. Forests 2020, 11, 253. [Google Scholar] [CrossRef]
  70. Varch, T.; Erber, G.; Visser, R.; Spinelli, R.; Harrill, H.; Stampfer, K. Advances in Cable Yarding: A Review of Recent Developments in Skyline Carriage Technology. Curr. For. Rep. 2021, 7, 181–194. [Google Scholar] [CrossRef]
Figure 1. Summary of forest operations in beech forests from the investigated literature. (a) Percentage share of the investigated studies between studies dealing with felling-processing and bunching-extraction. (b) Percentage share of studies dealing with bunching-extraction, i.e., studies dealing with skidding, forwarding and cable yarding operation. (c) Percentage share of studies dealing with felling-processing, i.e., studies dealing with motor-manual felling-processing operations, mechanised felling-processing operations and processing operations at the landing site.
Figure 1. Summary of forest operations in beech forests from the investigated literature. (a) Percentage share of the investigated studies between studies dealing with felling-processing and bunching-extraction. (b) Percentage share of studies dealing with bunching-extraction, i.e., studies dealing with skidding, forwarding and cable yarding operation. (c) Percentage share of studies dealing with felling-processing, i.e., studies dealing with motor-manual felling-processing operations, mechanised felling-processing operations and processing operations at the landing site.
Forests 14 00318 g001
Figure 2. Distribution of the investigated studies among countries.
Figure 2. Distribution of the investigated studies among countries.
Forests 14 00318 g002
Table 1. Summary of data from the reviewed studies dealing with felling operations. Empty cells indicate that that parameter was not immediately retrievable from the given study.
Table 1. Summary of data from the reviewed studies dealing with felling operations. Empty cells indicate that that parameter was not immediately retrievable from the given study.
InterventionMachineryWood SystemAverage dbh (cm)Slope Class *Productivity (m3 SMH−1)Cost
(EUR m−3)
NotesReference
Group selectionChainsawSWS–TLS21–35II–III 1.80–8.00Lower productivity for SWS method[24]
Single selectionChainsawCTL88I–III20.61.05 [26]
ThinningChainsawCTL20–50II0.40–1.75 [22]
ThinningChainsawCTL50–60III3.50 [23]
ThinningFeller-buncherWTH 60–75 [36]
Selective regeneration cuttingHarvesterCTL27 10.4 [31]
ThinningHarvesterCTL8–10I3.3–5.6 [32]
ThinningHarvesterCTL35–50I29–43 Data refer to net productivity[34]
ThinningHarvesterCTL30–39I28–29 Data refer to net productivity[40]
ThinningHarvesterCTL22–27I5.35 [33]
* Slope classes: I class—0%–20%; II class—20%–40%; III class—40%–60%.
Table 2. Summary of data from the reviewed studies dealing with extraction operation. Empty cells indicate that that parameter was not immediately retrievable from the given study.
Table 2. Summary of data from the reviewed studies dealing with extraction operation. Empty cells indicate that that parameter was not immediately retrievable from the given study.
InterventionExtraction TechniqueExtraction SystemWood SystemAverage dbh (cm)Slope Class *Extraction Distance (m)Productivity
(m3 SMH−1)
Cost (EUR m−3)NotesReference
Selection cuttingForwardingAnimalsCTL15–20II55–9503.53 [42]
ThinningForwardingForwarderCTL36I689.59 [54]
ShelterwoodForwardingForwarderCTL II1000–110014–15 [55]
Selection cuttingForwardingMini tractorsCTL15–20I270–3602.47 [53]
ThinningHaulingForestry-fitted farm tractor with winchTLS15–30 501.92–4.54 [42]
ThinningHaulingPrototype for winching logsCTL III27–557.6–8.514.1–15.7Values refer only to winching operation[51]
ThinningHaulingRemote-controlled mini forest crawlerWTH21I–III17.56.5513.93 [25]
Selection cuttingSkiddingAnimalsCTL20–50II1003.80 [42]
Group selectionSkiddingCable skidderSWS–CTL21–35II–III5002.68–3.124.50–7.03Lower productivity values and higher cost for SWS wood system[61]
Group shelterwoodSkiddingCable skidderTLS I17003.12 [48]
Salvage loggingSkiddingCable skidderCTL58II3081.54 [19]
SkiddingCable skidderCTL I4903.41–9.13 [49]
Final shelterwood fellingSkiddingCable skidderTLS42–48I200–30014.70 [50]
ThinningSkiddingForestry-fitted farm tractor with winchCTL20–50II1006.25 [42]
ThinningSkiddingForestry-fitted farm tractor with winchCTL II55–1058.85–14.853.50–9.60 [43]
ThinningSkiddingForestry-fitted farm tractor with winchCTL22 25–2501.75–2.709.18–14.19 [47]
ThinningSkiddingForestry-fitted farm tractor with winchCTL II–III140–3207.70–11.354.50–8.60 [45]
Selection cuttingSkiddingForestry-fitted farm tractor with winchCTL30II2163.709.90 [46]
ThinningSkiddingGrapple skidderCTL20–50II12001.80–2.15 [22]
Final shelterwood fellingSkiddingGrapple skidderTLS42–47I200–30021.00 [60]
Final shelterwood fellingSkiddingGrapple skidderTLS42–48I200–30032.80 [50]
Clear cutYardingCable car 40II–III800–9004.73 [23]
Selection cuttingYardingCable yarderCTL20–50II10010.09 [42]
ThinningYardingCable yarderCTL40II4001.69–4.08 lower productivity values for downhill yarding[57]
Group shelterwoodYardingCable yarderCTL60II3268.807.40 [58]
Group shelterwoodYardingCable yarderCTL34III160–2508.4113.00 [59]
ThinningYardingMini cable yardersWTH17–19III67–1181.50–2.4024–30 [56]
* Slope classes: I class—0%–20%; II class—20%–40%; III class—40%–60%.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Latterini, F.; Jagodziński, A.M.; Horodecki, P.; Stefanoni, W.; Venanzi, R.; Picchio, R. The State of the Art of Forest Operations in Beech Stands of Europe and Western Asia. Forests 2023, 14, 318. https://doi.org/10.3390/f14020318

AMA Style

Latterini F, Jagodziński AM, Horodecki P, Stefanoni W, Venanzi R, Picchio R. The State of the Art of Forest Operations in Beech Stands of Europe and Western Asia. Forests. 2023; 14(2):318. https://doi.org/10.3390/f14020318

Chicago/Turabian Style

Latterini, Francesco, Andrzej M. Jagodziński, Paweł Horodecki, Walter Stefanoni, Rachele Venanzi, and Rodolfo Picchio. 2023. "The State of the Art of Forest Operations in Beech Stands of Europe and Western Asia" Forests 14, no. 2: 318. https://doi.org/10.3390/f14020318

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop