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ASSESSMENT AND MAPPING OF FOREST
ECOSYSTEMS, THEIR CONDITION AND
PROVIDED ECOSYSTEM SERVICES OUTSIDE
NATURA 2000
elaborated under project
„Forests and woodland - ecosystem services mapping
and assessment in the Bulgarian forest territories
outside NATURA 2000 network - FOR ОUR FUTURE“
Co-financed with the financial support of the Financial Mechanism of EEA
2009–2014
International Scientific Conference
"MAPPING AND ASSESSMENT OF ECOSYSTEM SERVICES
- SCIENCE IN ACTION"
6-7 February 2017 PROGRAMME BG02 „INTEGRATED MARINE AND INLAND WATER MANAGEMENT “
PROGRAMME BG03 „BIOLOGICAL DIVERSITY AND ECOSYSTEMS”
Necessity of the study The performed study activities under the project are steps forward to the implementation of Target 2, Action 5 from the EU Biodiversity Strategy 2020, adopted by the European Commission :
•Target 2: MAINTAINING AND ENHANCING ECOSYSTEMS AND THEIR SERVICES:
By 2020, ecosystems and their services are maintained and enhanced by establishing green infrastructure and restoring at least 15 % of degraded ecosystems.
•Action 5: IMROVE KNOWLEDGE OF ECOSYSTEMS AND THEIR SERVICES IN THE EU
Member States, with the assistance of the Commission, will map and assess the state of ecosystems and their services in their national territory by 2014, assess the economic value of such services, and promote the integration of these values into accounting and reporting systems at EU and national level by 2020.
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Policies and legislation in the field of
ecosystem services
• National Strategy for the development of the forest sector in Republic of Bulgaria (2013-2020):
Goal 3: „Enhancement the input of the forest sector to the green economy”,
Priority 4 „Utilization of the potential of the forest sector for the development of the green economy“,
4.4. „Establishment of conditions for sustainable and compensatory payments for the use of ecosystem services, provided by the forest territories “.
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Policies and legislation in the field of
ecosystem services
• Strategic plan for the development of the forest sector (2014-2023):
Operational Objective 20 „Sustainable and compensatory use of ecosystem services, provided by the forest territories “:
Action 20.1: “Preparation and implementation of a methodology for the assessment of ecosystem services and their socially sustainable management “,
Action 20.2. „Preparation, adoption and implementation of a package regulations governing the activities for the evaluation of ecosystem services and schemes for compensatory use of public ecosystem services, provided by the forest territories and for compensatory payments for the forest territories incl. those in NATURA 2000”
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Policies and legislation in the field of
ecosystem services
• EU Biodiversity Strategy is reflected in the Bulgarian legislation - the acting Law on forests (2011 г.) has a Chapter 17: „Public ecosystem benefits of the forest territories”.
9 compensatory benefits of the forest territories are defined, the main directions for development of these territories in terms of ecosystem benefits are foreseen, which favor the management activities; also is foreseen the opportunity concrete forest territories with possible payments to be defined in the regional plans for development. The income will be distributed in between the forest owners with adopted forest plans and programmes – state forest and hunting enterprises, municipalities, etc.
• Under elaboration is a draft Regulation (art. 249).
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Main activities
The project activities related to the assessment and
mapping of forest ecosystems are:
– Activity 3.1: Data Verification
– Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology
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Working modalities Methodology for the assessment and mapping of the conditions of the
woodland and forest ecosystems and of the ecosystem services in Bulgaria,
B 4 – Woodland and forests
•Defining the habitats according to EUNIS (European nature
information system) based on inventory check lists and the types of
forest ecosystems according to EUNIS on a stand level for the forests
outside NATURA 2000.
The algorithm for their identification is developed on the basis of
information and parameters from the inventory check lists from the forest
data base. Tree species, number of layers, species composition, origin,
management class, forest type, type of the forest compartment, soil type,
altitude, etc. To define each type of ecosystem forming level 4, a different
combination of parameters is used. For each indicator there are unique
values pointed out in order to define the very type of ecosystem. 6-7/02/2017
Working modalities • Assessment of the ecosystems conditions
Using the Methodology of the PO - MOEW, the condition of each
stand is assessed with 5 groups of structural and functional
indicators: biotic heterogeneity, abiotic heterogeneity, energy budget,
matter budget, water budget. Together with the indicators, there are
23 indexes with the respective parameters. The total assessment of
the ecosystems condition is performed on a stand level (sub
compartment).
After the assessment with all indicators (according to Table 5 from
the Methodology), the IP-index for the forest ecosystems
performance is calculated by a formula, and in the following scale: IP
0-0,2 – very bad, 0,21-0,4 – bad, 0,41-0,6 – moderate, 0,61-0,8 – good,
0,81-1,0 – very good.
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Working modalities
• Assessment of the ecosystem services
The system of Burkhard which is a common matrix of the main
types of forest ecosystems and the provided services is the used
method of assessment of ESs.
Each EU country was able to elaborate a matrix on a national level
for the assessment of ESs according to the available for the
country indicators and possible sources of information.
The elaborated model for identification and assessment of the
types of ESs uses mainly the present information from the forest
data base and automatically calculates the results according to the
35 algorithms for each type of ESs on a 5-ranged scale.
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Main goals and tasks of the project
• Goal of the project:
Identification, reliable assessment and mapping of all types
of forest ecosystems outside NATURA 2000, as well as of the
provided ecosystem services (the working polygons are the
sub compartments, e.g. the min. forest inventory objects);
• Subject of the study:
725 000 sub compartments outside NATURA 2000 - 1 803 000
ha as a total.
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Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology - main steps
• Data base conversion from ZEM – to SHAPE and DBF – conversion of 180 digital models.
• Transformation of the initial spatial data from the forest management plans (data from forest inventory and common forest management map bases) for the forests outside NATURA 2000, from coordinate system 1970 to the World Geodetic system WGS 84 (UTM) 35 N.
• Topological processing of the forest data base outside NATURA 2000, including analyzes of the quality of the initial data, elimination of the duplication of data or of forest compartments and sub compartments.
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Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology - main steps
• Defining the types of ecosystems according to EUNIS on a stand level for the forests outside NATURA 2000: 4 main sub types of forest on a level are defined, and on next level 3 the typology consists of 4 main types of habitats according to EUNIS, and on the last level 4 after some studies, discussions and decision of the expert council, 26 sub types of ecosystems are included as a total, incl. 3 new types (mixed broadleaved forests G1.0, mixed coniferous forests G3.0 and mixed coniferous-broadleaved and broadleaved – coniferous forests G4.0). An algorithm to define the habitats according to the EUNIS is also elaborated;
• Assessment of the condition of the forest ecosystems and assessment of ESs according to Methodology by MOEW.
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Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology
Elaboration of analytical models and algorithms
• Algorithm to define the EUNIS habitats;
• System for assessment of the condition of the forest ecosystems, incl. algorithm for assessment of the biotic diversity, algorithm for abiotic diversity, methodic for assessment of the dead wood and tree cover (in percentage).
• Algorithms for assessment of the types of ESs
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Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology
Data sources
• The Forest management plans secure data for 100% of the
forest territories. The forest data base is been updated each 10 years since 1955 while preparing the forest management plans for the respective state forest and hunting enterprises.
• CORINE project, scientific publications, In situ data, statistic data from various institutions, administrations and scientific institutes in Bulgaria and EU, additional remote monitoring and field work.
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Approved Methodology and elaborated algorithms -
results from the application
1. Assessment of the condition of the forest ecosystems – common assessment of the condition of the ecosystem types - EUNIS – level
4
• The biggest group with a total area of 1 506 212 ha have IP index 0,6-0,8 (good). There are mostly forests from type G 1.7 (thermophilous coppice and high stem broadleaved forests – 536 713 ha), G 3.F (coniferous
plantations – 302 730 ha), G 1.6 (beech woodland – 177 328 ha), G 1.A
(meso- and eutrophic coppice and high stem broadleaved forests – 158 394 ha), G 1.C (planted coppice and high stem broadleaved deciduous plantations – 137 812 ha) и G 3.4 (Scots pine forests – 75 344 ha).
• In very good condition with an assessment 0,8 – 1,0 are forest ecosystems with an area of 285 811 ha, mainly type G 1.7 (thermophilous coppice and high stem broadleaved forests – 196 970 ha) and G 1.A (meso- and
eutrophic coppice and high stem broadleaved forests – 43 098 ha).
• The smallest area of 11 817 ha take the ecosystems with a moderate condition 0,4 – 0,6. Mainly G 3.F (planted coniferous – 6 063 ha) and G 1.7 (thermophilous coppice and high stem broadleaved forests – 3 213 ha).
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Approved Methodology and elaborated algorithms -
results from the application
2. Assessment of the types of ecosystem services
- provisioning, regulating, cultural
The model for identification and assessment of the types ESs uses mainly the present information from the forest data base and automatically calculates the results according to 35 algorithms for the respective type of ESs according to 5-ranged scale :
1 – low relevant capacity to provide the particular ES;
2 – relevant capacity;
3 – medium relevant capacity;
4 – high relevant capacity;
5 – very high relevant capacity.
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Example:
Assessment of the provisioning ecosystem services by sub types and definitive codes of service classes from Р 1 to Р 11
EUNIS code Р 1 Р 2 Р 3 Р 4 Р 5 Р 6 Р 7 Р 8 Р 9 Р 10 Р 11
F2.4 coniferous 0 1 2 2 3 3 0 3 3 2 0
G1.0 coppice broadleaved 1 4 1 2 3 3 2 2 3 3 3
G1.0 high stem 1 4 1 2 3 3 2 4 3 3 3
G1.1+2+3 coppice broadleaved 1 4 1 2 3 3 2 2 3 3 3
G1.1+2+3 high stem 2 4 2 2 3 3 3 4 3 3 4
G1.6 coppice broadleaved 1 3 1 3 3 3 3 2 3 2 4
G1.6 high stem 1 4 1 3 3 3 4 4 3 3 5
G1.7 coppice broadleaved 2 3 1 2 3 3 3 1 3 3 4
G1.7 high stem 1 4 1 3 3 3 3 4 3 3 4
G1.7D high stem 1 4 2 2 3 2 3 4 3 2 3
G1.Avcoppice broadleaved 2 3 1 2 3 3 3 2 3 3 4
G1.A high stem 2 4 1 3 3 3 3 4 3 3 4
G1.C coppice broadleaved 2 4 1 2 3 3 2 2 3 3 4
G1.C high stem 1 4 1 2 3 3 3 3 3 3 3
G1.D gardens 1 4 2 2 3 3 2 3 3 3 3
G3.0 mixed coniferous 1 2 2 2 3 3 4 4 3 2 3
G3.1 coniferous 1 2 2 2 3 3 4 5 3 2 4
G3.4 coniferous 1 2 3 2 3 3 4 4 3 2 3
G3.5 coniferous 1 2 3 2 3 2 4 4 3 2 3
G3.6 coniferous 0 2 1 2 3 3 4 4 3 2 3
G3.F coniferous plantations 2 2 3 2 3 3 4 4 3 2 3
G4.0 mixed conif.and broadleaved 0 2 2 2 3 3 0 3 3 2 0
G4.0 mixed broadleaved and conif. 2 3 2 2 3 2 3 4 3 2 3
G4.5 mixed scots pine - beech 1 3 2 2 3 3 4 4 3 2 4
G4.6 mixed fir - spruce - beech 0 3 2 2 3 3 4 4 3 2 4
G4.F mixed plantations 2 2 2 2 3 3 3 4 3 2 3
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Example:
Assessment of the regulating ecosystem services by sub types and definitive codes of service classes from R 1 to R 18
EUNIS code R 1 R 2 R 3 R 4 R 5 R 6 R 7 R 8 R 9
R
10
R
11
R
12
R
13
R
14
R
15
R
16
R
17
R
18
F2.4 coniferous 2 3 3 4 3 4 5 3 2 3 3 3 4 3 3 1 3 3
G1.0 coppice broadleaved 3 3 3 4 3 3 3 3 3 2 4 4 3 3 3 2 3 2
G1.0 high stem 3 3 3 4 3 3 3 4 3 2 4 4 4 3 4 3 3 2
G1.123 coppice broadleaved 3 3 3 4 3 3 4 4 3 2 3 4 4 3 3 2 3 2
G1.123 high stem 3 3 3 4 3 3 4 4 3 2 3 4 4 3 4 3 3 2
G1.6 coppice broadleaved 3 3 4 4 4 4 5 4 3 2 3 3 4 3 4 2 4 3
G1.6 high stem 3 3 3 4 4 4 5 4 3 2 3 3 4 3 4 3 3 3
G1.7 coppice broadleaved 3 3 3 4 3 3 4 4 2 2 4 4 3 3 3 1 3 2
G1.7 high stem 2 3 3 4 3 3 4 4 2 2 3 4 4 3 3 2 3 2
G1.7D high stem 3 3 3 5 4 3 4 3 3 2 4 4 3 3 3 3 3 3
G1.A coppice broadleaved 3 3 3 4 3 3 4 4 3 2 3 3 3 3 3 2 3 3
G1.A high stem 3 3 3 4 3 3 4 4 3 2 3 3 4 3 4 2 3 3
G1.C coppice broadleaved 3 4 3 4 3 3 3 4 3 2 3 3 3 3 4 2 3 2
G1.C high stem 3 3 3 4 3 3 3 4 3 2 3 3 3 3 4 3 3 3
G1.D gardens 3 3 3 4 3 3 3 3 3 2 3 3 2 3 3 2 3 2
G3.0 mixed coniferous 3 3 3 4 4 3 4 4 3 2 4 4 2 3 2 3 3 3
G3.1 coniferous 3 3 3 4 4 3 4 4 3 2 3 3 4 3 3 3 3 3
G3.4 coniferous 3 3 3 4 4 3 4 4 3 2 3 3 3 3 3 3 3 3
G3.5 coniferous 3 3 3 4 4 3 4 4 3 2 3 3 3 3 3 3 3 3
G3.6 coniferous 2 3 3 4 4 4 5 4 2 2 3 3 4 3 3 2 3 3
G3.F coniferous plantations 3 3 3 5 4 3 4 4 3 2 3 3 3 3 3 3 3 3
G4.0 mixed conif. dnd broadleaved 3 3 3 5 3 3 4 3 3 2 3 4 4 3 3 3 3 3
G4.0 mixed broadleaved and conif. 3 3 3 4 4 3 4 4 3 2 4 4 4 3 4 3 3 3
G4.5 mixed scots pine - beech 3 3 3 4 4 3 4 4 3 2 4 4 4 3 4 3 3 3
G4.6 mixed fir - spruce - beech 3 3 3 4 4 3 4 4 3 2 4 4 4 3 4 3 3 3
G4.F mixed plantations 3 3 3 5 4 3 4 4 3 2 4 4 3 3 3 3 3 3
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Example:
Assessment of the cultural ecosystem services, by sub types and definitive codes of the service classes from С 1 to С 6 EUNIS code C 1 C 2 C 3 C 4 C 5 C 6
F2.4 coniferous 1 1 0 2 1 3
G1.0 coppice broadleaved 1 2 0 2 2 2
G1.0 high stem 1 2 0 2 2 2
G1.123 coppice broadleaved 1 2 0 3 2 2
G1.123 high stem 1 2 0 3 2 3
G1.6 coppice broadleaved 1 2 0 2 1 2
G1.6 high stem 1 1 0 2 2 2
G1.7 coppice broadleaved 1 2 0 3 2 2
G1.7 high stem 1 1 0 2 2 2
G1.7D high stem 1 1 0 2 2 2
G1.A coppice broadleaved. 1 2 0 2 2 2
G1.A high stem 1 1 0 2 2 2
G1.C coppice broadleaved 1 2 0 3 2 2
G1.C high stem 1 2 0 3 2 2
G1.D gardens 1 2 0 2 2 2
G3.0 mixed coniferous 1 1 0 2 1 2
G3.1 coniferous 1 2 0 1 1 2
G3.4 coniferous 1 2 0 2 1 3
G3.5 coniferous 1 1 0 2 1 3
G3.6 coniferous 1 2 0 3 1 3
G3.F coniferous plantations 1 1 0 2 2 2
G4.0 mixed conif. and
broadleaved 1 1 0 2 2 2
G4.0 mixed broadleaved and
conif. 1 1 0 2 2 2
G4.5 mixed scots pine - beech 1 2 0 2 2 3
G4.6 mixed fir - spruce - beech 1 1 0 2 2 2
G4.F mixed plantations 1 1 0 2 2 2
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Activity 3.1. Data verification • The data verification is implemented over 10% of the total forest territory
outside NATURA 2000, incl. over 2% field work and 8% office work, resp.: 43 561,73 hа, e.g. 2,4% on the field and 149 172 ha in the office, e.g. 8,27%. Data verification was performed by experts Forest data, field experts of EFA and experts Forest protection in no evenly distributed sub compartments within the 16 Regional Forest Directorates.
• Visiting each sub compartment a check list is filled – filed check of the inventory indicators, assessment of the condition of the stands and of the provided ESs and additional data. At the same time, plots to define the quantity of dead wood and grass cover for each sub compartment were set. Additional data for invasive species, threatened species, abiotic and biotic damages, places of cultural interest and etc. was also collected.
• The NA data like grass cover, dead wood volume is assessed with empiric models. The models are prepared on the basis of field measurements in all habitats, age classes and canopy density. The total number of stands where real measurement is done is over 2 500.
Activity 3.1. Data verification
6-7/02/2017
real 2% field
verification
in forests
outside
NATURA
2000 verified 2% %
8% office
verification in
forests outside
NATURA 2000 verified 8% %
Reg. For. Directorate number of stands area, ha area, ha area, ha area, ha
Berkovitsa 44 435 87 366,00 1 747,32 1741,1 100% 6 989,30 7 009 100%
Blagoevgrad 51 029 163 261,40 3 265,23 3 300,60 101% 13 060,90 13 071,50 100%
Burgas 19 916 121 983,60 2 439,67 2 961,40 121% 9 758,70 9 778,30 100%
Varna 14 666 51 248,20 1 024,96 1 108,90 108% 4 099,90 4 520,90 110%
Veliko Tarnovo 63 582 143 977,40 2 879,55 2 905,50 101% 11 518,20 11644,8 101%
Kardzhali 32 265 131 665,70 2 633,31 2 674,90 102% 10 533,20 10553,1 100%
Kyustendil 53 167 127 458,40 2 549,17 2 652,40 104% 10 196,70 10201,6 100%
Lovetch 43 027 87 053,80 1 741,08 1 892,30 109% 6 964,30 7 234,70 104%
Pazardzhik 22 400 85 248,80 1 704,98 1 697,80 100% 6 819,90 6892,2 101%
Plovdiv 23 559 77 225,80 1 544,52 1 545,30 100% 6 178 6 183,90 100%
Ruse 17 503 64 296,90 1 285,94 1 750,20 136% 5 143,80 5 650,40 110%
Sliven 14 019 79 065,50 1 581,31 2 269,50 144% 6 325,30 6 418,60 101%
Smolyan 36 140 114 156,50 2 283,13 2 335,30 102% 9 132,52 9 229,90 101%
Sofia 78 881 226 642,40 4 533 4 591,03 101% 18 131,30 20 328 112%
Stara Zagora 29 824 123 398,10 2 467,96 2 796,20 113% 9 871,90 10 537,90 107%
Shumen 26 334 119 814,40 2 396,29 2 812,60 117% 9 585,20 9917,3 103%
570 747 1 803 862,90 36077,42 39035,03 108% 144 309.03 149 173 103%
field expert EFA 2966,0
field expert EFA 778
field expert EFA 782,7
total, field experts 4526,7
Total
Activity 3.1. Data verification Results
First results of the verification of the model of assessment of the condition of forest ecosystems:
• 55% confirmation in the field checks;
• 96% confirmation if not taking into account the assessment using the parameter “red list animal species”;
• Still awaiting results from the verification of the model for assessment of the ecosystem services.
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Activity 3.2: Mapping of the ecosystem services according
approved by MOEW Methodology • Mapping of types of ecosystems – 77 maps produced with detailed color codes
for visualization;
• Mapping of the condition of the ecosystems - 77 maps produced with the
results of the calculation of the IP index for the types of ecosystems, with
detailed color codes for visualization;
• Mapping of the ecosystem services - 77 maps produced presenting the results
of the calculated capacity of the ecosystems to provide provisioning, regulating
and cultural services, with detailed color codes for visualization.
All maps are produced оf a scale 1: 125 000, in PDF, as each data frame consists
of one plot of 50 km coordinate grid of the EEA that defined the number of
each type of maps to be 77 or altogether - 231 maps. Data mapping and their
processing is performed using ArcMap and ArcCatalog, and the data base format
is ESRI GDB.
.
.
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Activity 3.2: Mapping of the ecosystem services according
to approved by MOEW Methodology Map of the types of forest ecosystems
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Activity 3.2: Mapping of the ecosystem services
according to approved by MOEW Methodology Map of the assessment of the condition of the forest
ecosystems
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Activity 3.2: Mapping of the ecosystem services according
to approved by MOEW Methodology Map of the assessment of the ecosystem services
CONCLUSIONS
As a result of the project activities, there is a centralized data base
established, comprised of :
• National layer Forests outside NATURA 2000 with topologically
processed spatial data;
• forest ecosystems typology;
• assessment of their functional state;
• assessment of the present ecosystem services that they provide to the
society;
• maps produced according the requirements of the Methodology and
visualizing the result of the three types of study.
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CONCLUSIONS
• Though the significant scale of the studies performed, the
elaborated models and the based on them analytical algorithms do
have imperfections and gaps with insufficient information.
• The Methodology for the assessment and mapping of the
conditions of the woodland and forest ecosystems and of the
ecosystem services in Bulgaria should be refined due to some
unclear definitions of indicators and parameters or their
unavailability.
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CONCLUSIONS Further work:
• To perform and analyze the compliance and verification of the data
from the elaborated models (algorithms) for assessment of the
condition of the forest ecosystems and the provided ecosystem
services, compared to the data collected on the field. Assessment of
the two main models, resp. for defining the condition of the forest
ecosystem and of the provided ecosystem services must be done.
• In terms of data provision, a Methodology for assessment of the
grass cover and the dead wood using remote sensing methods should
be elaborated.
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6-7/02/2017
. THANK YOU FOR YOUR
ATTENTION! Krasimir Kamenov
Rosica Horozova
Lyubcho Trichkov
Georgi Tinchev
Vasko Raychinov
Georgi Gogushev
Executive Forest Agency, Sofia
Regional Forest Directorate, Kardzhali
Regional Forest Directorate, Blagoevgrad
http://fofproject.bg/