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9 For. Snow Landsc. Res. 77, 1/2: 9–16 (2002) Windthrow research after the 1990 storm Vivian in Switzerland: objectives, study sites, and projects Walter Schönenberger WSL Swiss Federal Research Institute, Zürcherstrasse 111, CH-8903 Birmensdorf, Switzerland. [email protected] Abstract In this special issue we publish a series of articles which summarise the results of ten years research on four study sites in mountain forests in the Swiss Alps.The study sites were set up after the 1990 blow-down caused by the storm Vivian. Each site was divided into the following three treatments: (1) uncleared with natural regeneration, (2) cleared with natural regeneration, and (3) planted (cleared with natural and planted regeneration). Special projects studied and compared the soils, the dynamics of the ground vegetation, the natural and artificial forest regeneration, the mycorrhiza, the impact of ungulates, the diversity of insects, the spread of bark beetles, the formation of avalanches, the surface erosion, and the timber decay in the different treatments. This paper summarises the common objectives of the projects and the characteristics of the four study sites. Keywords: disturbance, blow-down, vegetation succession, forest regeneration, natural hazards, insects, mountain forest, Switzerland 1 Introduction The majority of the contributions to this special issue on windthrow research summarise the results of ten years research on four windthrow areas carried out by the Swiss Federal Institute for Forest Snow and Landscape Research. This interdisciplinary research project was set up after the storm Vivian on February 26 to 28, 1990 to find answers to some of the questions raised in the editorial, and to support future decision-making after storms. The objectives of the research project were: (1) to document and compare the initial situations and to monitor the changes in flora, vegetation, soil and natural hazards in cleared and uncleared treatments, (2) to compare the reforestation processes in two regeneration treat- ments (natural regeneration and planting), (3) to compile a comprehensive decision-support tool for future management of windthrow areas after blowdown, and finally (4) to set up the study sites as exemplary teaching and demonstration sites. Twelve of the Swiss research projects on windthrow after Vivian used four main study sites.These sites are characterised in detail in this introductory paper. 2 Study sites and experimental treatments Four windthrow study sites (Disentis, Pfäfers, Schwanden, and Zweisimmen) in different parts of the Swiss Alps were preserved, via contract, for research. All sites were located in the oceanic northern Prealps (Fig. 1), an area that receives high precipitation. Each study site (except Zweisimmen) was divided into three experimental units which received one of three treatments: (1) uncleared: site untouched, only natural regeneration, (2) cleared: timber harvested using a cable crane, coarse woody debris removed, only natural regeneration, and
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Page 1: Windthrow research after the 1990 storm Vivian in ... · This interdisciplinary research project was set up after the storm Vivian on February 26 to 28, 1990 to find answers to some

9For. Snow Landsc. Res. 77, 1/2: 9–16 (2002)

Windthrow research after the 1990 storm Vivian in Switzerland: objectives, study sites, and projects

Walter Schönenberger

WSL Swiss Federal Research Institute, Zürcherstrasse 111, CH-8903 Birmensdorf, [email protected]

AbstractIn this special issue we publish a series of articles which summarise the results of ten yearsresearch on four study sites in mountain forests in the Swiss Alps. The study sites were set up afterthe 1990 blow-down caused by the storm Vivian. Each site was divided into the following threetreatments: (1) uncleared with natural regeneration, (2) cleared with natural regeneration, and (3)planted (cleared with natural and planted regeneration). Special projects studied and comparedthe soils, the dynamics of the ground vegetation, the natural and artificial forest regeneration,the mycorrhiza, the impact of ungulates, the diversity of insects, the spread of bark beetles, the formation of avalanches, the surface erosion, and the timber decay in the different treatments.This paper summarises the common objectives of the projects and the characteristics of the fourstudy sites.

Keywords: disturbance, blow-down, vegetation succession, forest regeneration, natural hazards,insects, mountain forest, Switzerland

1 Introduction

The majority of the contributions to this special issue on windthrow research summarise theresults of ten years research on four windthrow areas carried out by the Swiss FederalInstitute for Forest Snow and Landscape Research. This interdisciplinary research projectwas set up after the storm Vivian on February 26 to 28, 1990 to find answers to some of thequestions raised in the editorial, and to support future decision-making after storms. Theobjectives of the research project were: (1) to document and compare the initial situationsand to monitor the changes in flora, vegetation, soil and natural hazards in cleared anduncleared treatments, (2) to compare the reforestation processes in two regeneration treat-ments (natural regeneration and planting), (3) to compile a comprehensive decision-supporttool for future management of windthrow areas after blowdown, and finally (4) to set up thestudy sites as exemplary teaching and demonstration sites.

Twelve of the Swiss research projects on windthrow after Vivian used four main studysites. These sites are characterised in detail in this introductory paper.

2 Study sites and experimental treatments

Four windthrow study sites (Disentis, Pfäfers, Schwanden, and Zweisimmen) in differentparts of the Swiss Alps were preserved, via contract, for research. All sites were located inthe oceanic northern Prealps (Fig. 1), an area that receives high precipitation. Each studysite (except Zweisimmen) was divided into three experimental units which received one ofthree treatments: (1) uncleared: site untouched, only natural regeneration, (2) cleared: timberharvested using a cable crane, coarse woody debris removed, only natural regeneration, and

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10 Walter Schönenberger

(3) planted: timber harvested, site cleared (like 2) and replanted with a variety ofbroadleaved and conifer species (details in SCHÖNENBERGER this issue, Table 1). In Zwei-simmen the area was left uncleared, i.e. uncleared treatment only. The main characteristicsof the study sites are as follows:

Disentis (Fig. 2): 1400–1550 m above sea level; NW-aspect; total area including all treatmentsabout 6 ha; all treatments adjacent; pre-storm stand of pure 110- to 150-year-old Norwayspruce (Picea abies) on a low subalpine spruce-fir (Abies alba) site; dystric cambisols andpodsols on gneiss and granite; very steep slope of 30–45°; zone of potential release or transitof snow avalanches, sliding rocks, logs or trunks; study site in the middle of a windthrow ofabout 100 ha; no seed trees available, next seed trees 250–500 m distant.

cleared

uncleared

plantedcleared

uncleared

planted

Fig. 1. Location of the four windthrow research areas in the Swiss Alps established after Vivian 1990.

Fig. 2. Study site Disentis June 30, 1992. The uncleared treatment is located in the middle, the clearedadjacent on the left and the planted on the right. Photo Documenta Natura.

Schwanden

Zweisimmen Pfäfers

Disentis

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11For. Snow Landsc. Res. 77, 1/2 (2002)

Fig. 3. Study site Pfäfers June 30, 1993. The photo shows the planted treatment with completed ava-lanche barriers. Photo Documenta Natura.

Pfäfers (Fig. 3 and 4): 1430–1500 m a.s.l.; WNW-aspect; treatments separated by intact forest;total area 3 ha; pre-storm stand of 70- to 120-year-old spruce-larch (Larix decidua)-fir on ahigh montane spruce-fir-beech (Fagus sylvatica) site; highly erodible eutric cambisols onlimestone schists; very steep slope of 30–45°; landslides, avalanches and log- or trunk-sliding possible; some maple (Acer pseudoplatanus) in the cleared treatment, and seed treesof other species closer than 50 m; the planted treatment fenced against ungulate browsing,and furnished with temporary timber barriers to prevent the release of avalanches.

Fig. 4. Study site Pfäfers June 30, 1993. The uncleared treatment 1993. Photo Documenta Natura.

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12 Walter Schönenberger

Fig. 6. Study site Schwanden June 27, 2000. Photo Documenta Natura.

Fig. 5. Study site Schwanden May 20, 1992.The uncleared treatment is located at the top; below adjacentare the cleared and the planted treatments. Photo Documenta Natura.

uncleared

cleared

planted

Schwanden (Fig. 5 and 6): 900–1100 m a.s.l.; W-aspect; total area 7 ha; treatments located inan altitudinal gradient; pre-storm stand of spruce with some beech and maple on a montanefir-beech-ash (Fraxinus excelsior) site; cambisols and regosols on verrucano; slope of 20–35°;few natural hazards expected except some surface erosion; forest edge at medium distance0–150 m, some broadleaved seed trees survived on the site.

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13For. Snow Landsc. Res. 77, 1/2 (2002)

Fig. 7. Study site Zweisimmen June 22, 1992. Photo Documenta Natura.

Zweisimmen (Fig. 7): 1440–1560 m a.s.l.; NW-aspect; total area 4 ha; only the uncleared treat-ment realised; pre-storm stand of 120- to 130-year-old spruce on high montane spruce-firsite; rendzic leptosols on limestone-breccia; gentle slope of 15–30°; no natural hazards; noseed trees on the site, but surrounded by spruce stands at a distance of 0–70 m.

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3 Research projects

A linking project provided the basic information for a number of specific projects dealingwith fauna, ground-vegetation, reforestation, and natural hazards. This information wasextracted from historical records, sporadic aerial photographs, from yearly terrestrial photo-graphs (Fig. 8–9), and from image analysis with GIS. The project provided an extensive sitedescription, maps (Fig. 10), and the maintenance of the infrastructure for the benefit of allresearchers.

Fig. 8–9. Vegetation dynamics documented in photographs annually repeated in the uncleared treat-ment Schwanden, May 26, 1992 and June 27, 2000. Photo Documenta Natura.

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15For. Snow Landsc. Res. 77, 1/2 (2002)

Fig. 10. Map of treatments and installations for the different research projects, example of the study siteDisentis.

0 50 100 150 200 250 300 meters

insect trapsregeneration plotsindicator fencesoil profilesvegetation plotssnow pegsseed trapstreatment boundarieslogs25 m isolines

The projects on fauna dealt with the abundance and diversity of insects and small mammals (DUELLI et al. this issue) and the spread of bark beetles (WERMELINGER et al. thisissue). The project on ground-vegetation studied the succession of plant communities(WOHLGEMUTH et al. this issue). With regard to reforestation the natural establishment ofseedlings (WOHLGEMUTH et al. this issue) and the performance of planted and naturalsaplings (SCHÖNENBERGER this issue), the impact of browsing ungulates on the forestregeneration (SENN et al. this issue), and the role of mycorrhiza for the establishment andperformance of seedlings (EGLI et al. this issue) were investigated. Natural hazards werelooked at in projects on changes in soil properties (LÜSCHER this issue), on snow avalanches(FREY and THEE this issue), on rockfall, landslides, and surface erosion (GERBER et al. thisissue), on the preventive effects of downed logs against natural hazards, and on the de-composition process of timber (FREY and THEE this issue).These contributions are all basedon data obtained in the four study sites.

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16 Walter Schönenberger

AcknowledgementOur research was funded by the Swiss Agency for the Environment, Forests and Landscape, theCantons, the municipalities, the forest services and the forest owners of the study sites.

4 References

DUELLI, P.; OBRIST, M.K.; WERMELINGER, B., 2002: Windthrow-induced changes in faunistic bio-diversity in alpine spruce forests. For. Snow Landsc. Res. 77, 1/2: 117–131.

EGLI, S.; PETER, M.; FALCATO, S., 2002: Dynamics of ectomycorrhizal fungi after windthrow. For.Snow Landsc. Res. 77, 1/2: 81–88.

FREY, W.; THEE, P., 2002: Avalanche protection of windthrow areas: A ten year comparison ofcleared and uncleared starting zones. For. Snow Landsc. Res. 77, 1/2: 89–107.

GERBER, W.; RICKLI, C.; GRAF, F., 2002: Surface erosion in cleared and uncleared mountain wind-throw sites. For. Snow Landsc. Res. 77, 1/2: 109–116.

LÜSCHER, P., 2002: Humus dynamics and changes in rooting patterns in windthrow areas. For.Snow Landsc. Res. 77, 1/2: 49–59.

SCHÖNENBERGER, W., 2002: Post windthrow stand regeneration in Swiss mountain forests: thefirst ten years after the 1990 storm Vivian. For. Snow Landsc. Res. 77, 1/2: 61–80.

SENN, J.; WASEM, U.; ODERMATT, O., 2002: Impact of browsing ungulates on plant cover and treeregeneration in windthrow areas. For. Snow Landsc. Res. 77, 1/2: 161–170.

WERMELINGER, B.; DUELLI, P.; OBRIST, M.K., 2002: Dynamics of saproxylic beetles (Coleoptera)in windthrow areas in alpine spruce forests. For. Snow Landsc. Res. 77, 1/2: 133–148.

WOHLGEMUTH, T.; KULL, P.; WÜTHRICH, H., 2002: Disturbance of microsites and early treeregeneration after windthrow in Swiss mountain forests due to the winter storm Vivian 1990.For. Snow Landsc. Res. 77, 1/2: 17–47.

Accepted 29.10. 02


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