conservation management actions in oak forests in natura 2000
TRANSCRIPT
Conservation management actions in oak forests in Natura 2000 SAC sites of Bükk National Park Directorate,
Hungary
FRANK, Tamás – BÖLÖNI, János – ÁDÁM, Réka – CSIKOS, Valéria -HARMOS, Krisztián – VERÉB, Krisztina – JÓZSEF, Júlia – ASZALÓS, Réka
Pannonian-Balcanic Quercus cerris-Quercus petraea woodlands2,7% the proportion in the forestsof Hungary
Sessile oak-hornbeam woodlands3,9% the proportion in the forestsof Hungary
Bölöni, J. (2011): Á-NÉR 2011 habitats, maps and descriptions, …
Bölöni, J. (2011): Á-NÉR 2011 habitats, maps and descriptions, …
The area of Sessile oak-hornbeamwoodlands has decreased by 53% to 230 years. (Biró M., Bölöni J., Molnár Zs. (2016): Long-term area
changes of 20 habitat types in Hungary (1783-2013).
Submitted paper.)
The area of Pannonian-Balcanic Quercuscerris-Quercus petraea woodlands hasdecreased by 66% to 230 years. (Biró M., Bölöni J., Molnár Zs. (2016): Long-term area
changes of 20 habitat types in Hungary (1783-2013).
Submitted paper.)
The distribution area in Hungary of …
The homogenising effect of the clearcut forest management system
Homogeneous forest structureImpoverished stand compositionOnly a few habitats
Diverse stand structure and compositionVariety of habitats
2. 1.
The conservation management actions were initiatedin two oak forest stands in the operational area of the Bükk National Park Directorate (BNPD)
SK
A
HR
SLO
SRB
RO
UA
yellow line: operational area of the BNPD
1st site, core area of Bükk National Park, treatment started in 2009
2nd site, Kelet-Cserhát Landscape Protection Area, treatment started in 2014
1st site, Bükk National Park Pannonian-Balcanic Quercus cerris-Quercus petraea woodlands and Sessile oak-hornbeam woodlands 113.7 ha; 87-110 year-old stands; treatment started in 2009
Gaps created in 2009 in the 1st site
The goals of the treatments:- Enhancement of the structural stand diversity- Reduction of the area of Robinia pseudoacatia groups- Fostering the development of the few Q. petrea trees against the numerous
Q.cerris
1st site treatments in 2011:- Extension of the existing gaps - Creation of new gaps
…in 2014 and 2015:-Marking the locations of new nature conservation management actions (see details in the case of the 2nd site)
…and organisation of trainings.
2nd site, Kelet-Cserhát Landscape Protection Area Pannonian-Balcanic Quercus cerris-Quercus petraea woodlands and Sessile oak-hornbeam woodlands, 34.3 ha; 70-80 year-old stands; treatment started in 2014
2nd site, Kelet-Cserhát Landscape Protected Area
In 2014, complex and detailed set of goals were defined at the stand and the tree-individual level.
I. Maintenance of tree and shrub individuals:
1. Support of the oversized, old tree individuals in the canopy layer
2. Maintenance of the individuals of admixing species in the canopy layer
3. Maintenance of the individuals of admixing species in the understorey
4. Support of shrub species or group of shrub individuals
II. Creation of gaps
5. Creation of gaps
6. Extension of existing spontaneous gaps
The I. and II. set of goalswere implementedby the creation of deadwoodand felled timber.
III. Creation of deadwood:
7. Creation of standing deadwood with stem ringing
8. Creation of lying deadwood with the felling of tree individuals
9. Creation of high (1 m – 1.6m) stumps
10. Making barkless patches on the stem with bark-peeling
Standing deadwood
Lying deadwood
High stump and felled timber
High stump and lying deadwood(with the felling direction)
Making barkless patcheson the stem
Map of treatments in 2015/2016 winter and 2016 spring
In 2015/2016 winter and 2016 spring - pictures of management actions
Examples of the treatments and habitat creation
Felling of oak trees – creation of felled timber and high stumps
Lying deadwood with a snag and a normal stump
Examples of the treatments and habitat creation
Maintenance of two Cerasus avium individuals in the understorey with creating a stump
Maintenance a Sorbus torminalis in the understorey with making lying deadwood and felled timber
Maintenance of a group of shrubs and young trees in the shrub layer with generating lying deadwood.
Examples of the treatments and habitat creation
Creation of standing deadwood
Wounded tree trunkwith bark microhabitats
Creation of standing deadwood withbark microhabitats
Making a woundedtree trunk withbark microhabitats
Proportion of artificially created deadwood and timber
2015/2016
Felled timber49%
Standing deadwood25%
Lying deadwood24%
Stump2%
All artificially created deadwood
51%
(13,7 m3/ha)
Monitoring scheme:
• A systematic monitoring survey was elaborated to monitor the effect of the conservation management actions
• The network survey is accomplished in a 40 x 40 m net
• At all net points the survey of forest stand, shrub layer and dead wood arecarried out in a defined-sized circular plot
• Baseline monitoring (before the treatments) was carried out in 2015
• Control monitoring (after the treatments) is currently taking place
Monitoring plots (218)
Monitoring scheme:
Counting the larger individuals of saplings and shrubs
Counting the smaller individuals of saplings and shrubs
Measurement of the DBH, social position, and health status of trees (DBH ≥ 5 cm) in a circle of 8.91 m radius (250 m2). Measurement of the height of 1-2 typical tree individuals with Vertex
Living trees Dead trees Shrub layerCanopy
density
stem/ha m2/ha m3/hastanding stem/ha
standing m2/ha
standing m3/ha
lying m3/ha
total, m3/ha
largestem/
ha
smallstem/ha
%
705 27.80 324 31.6 0.52 4.3 6.0 10.3 2040 3242 88,2
Data on living trees, deadwood, the shrub layer and canopy density according to 104 monitoring points of the baseline survey (before the treatments)
Future plans
1st site:-Marking the locations of nature conservation management actions in a similar manner to the 2nd site
-Building new wild forest fences around the gaps as well as around smaller parts (1-3 ha) of forest stands
- Creating new gaps; extension of already existing gaps
- Continuous control monitoring of the treated forest area
2nd site:- The treatments will be countinued - Baseline survey will be continued on those
sampling sites which have not been treated and assessed so far
- Building wild forest fences around the gaps as well as around smaller parts (1-3 ha) of forest stands
- Planning to design a multiple-species (birds, bats, saproxylic beetles, reptiles and polypores) monitoring programme
Thank you for your attention!