Table of content:
Acknowledgements & Authors
Summary
List of abbreviations
Introduction
1. Ecological Network of Moldova
1.1. Components of Eco-Network
1.2. Geographical Aspects of NENM
1.3. Levels of Components of the Eco-Network
1.4. Eco-Network as Informational System
2. System of Criteria for Estimate of Value of Components of Ecological Network
2.1. Criteria for Attribution of Particular Status to Core Areas with Natural and Semi-Natural Ecosystem Cover
2.2.
Criteria for Ranking Areas of the Eco-Network which are Not Core
Areas
2.3.
Principles for Designating Areas Intended for Ecological Restoration
and for Establishing Biological Corridors in Conditions of Excessive
Economic Land Use
2.4.
Use of Lands for Establishing Biological Corridors and Restoration,
which Not Meet Criteria of Areas Intended for Ecological Restoration
3. Operational Checklists
3.1. Operational Checklist of Vascular Plants
3.2. Operational Checklist List of Endemic Vegetation Associations
3.3. Operational List of Insects
3.4. Operational List of Terrestrial Vertebrates
4. Objects of Eco-Network
5. Main Actions Concerning National Eco-Network of Moldova
6. Estimation of Potential and Some Recommendations for Establishing National Ecological Network
of Moldova
6.1. Main Conditions for Establishing NENM
6.1.1. Elaborating the Concept of
Eco-Network in Moldova
6.1.2. Ecological and Socio-Economical
Conditions of Forming Eco-Network
6.1.3.
Analysis of Legal Framework for
Establishing National Eco-Network
6.2. Comment on Results of Area
Estimations, Based on Main Components of Ecological Network of Moldova (by
Biological Indicators)
6.2.1. Estimation of Core Areas
6.2.2. Designated
Components of Eco-Network in the Structure of the Country’s Area
6.3. Recommendations
6.3.1. Concerning the
Development of a System of Management for Natural Protected Areas
6.3.2. Priorities of
scientific estimation of core areas
6.3.3. Law on Modification and Completion of some
Legislative Acts (Draft)
Conclusion
References
Map of the Ecological Network
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6.2.2. Designated Components of Eco-Network in The Structure of the Country's Area
In the current state of natural ecosystems in Moldova, two
types of biocoenosa can be clearly distinguished – forests and pastures.
- Forest areas, irrespective of their quality,
mainly have stabilizing geo-systemic effects.
Under established structure of land-use, the areas of forest
fund (irrespective of their ownership) comprise ca 12,5 % of the surface area of
the country. They are distributed very unevenly (Table 4), comprising 27,5 % of
the surface area of Codrii Forest district and 2,7 % of Balti Steppe district.
- Commonly, pastures are covered with degraded
herbaceous communities, where as a rule, species composition is extremely
impoverished, soils are exhausted or washed away.
Table 3.
Distribution of forest area over natural districts
| N |
Name of district |
Surface area, thousand ha |
Proportion of forests, % |
| District |
Forest |
| 1 |
Northern-Moldavian forest-steppe |
463 |
47,58 |
10,3 |
| 2 |
Middle-Prut forest-steppe |
293 |
31,17 |
10,6 |
| 3 |
Belti steppe |
192 |
5,11 |
2,7 |
| 4 |
Ciuluc-Olonet steppe |
169 |
16,85 |
10,0 |
| 5 |
Dniester-Raut forest-steppe |
248 |
36,33 |
14,6 |
| 6 |
Middle Dniester forest-steppe |
192 |
17,45 |
9,1 |
| 7 |
Codru forest |
474 |
130,02 |
27,5 |
| 8 |
Lower Prut forest-steppe |
181 |
14,36 |
8,0 |
| 9 |
South-Moldavian forest-steppe |
355 |
53,30 |
15,0 |
| 10 |
Bugeac steppe |
321 |
19,54 |
6,1 |
| 11 |
Lower Dniester forest-steppe |
304 |
37,06 |
12,2 |
| 12 |
Lower Dniester steppe |
192 |
14,02 |
7,3 |
| Total over the
country |
3384 |
422,79 |
12,5 |
Table 4.
Saturation of biological corridors with core and buffer
areas
(Int – International level, N - national, Z - zonal, L - local)
| Number and name of corridor |
Core area surface, ha |
Geo-systemic buffer, ha |
Total, ha |
| Int |
N |
Z |
L |
N |
Z |
L |
| International biological corridors |
| 1. Prut |
7723 |
|
|
7002 |
|
373 |
1285 |
16383 |
| 2. Dniester |
585 |
1774 |
50 |
11650 |
|
2368 |
2595 |
19022 |
| 3. North Moldovan |
|
|
|
517 |
|
|
155 |
672 |
| 4. South Moldovan |
|
540 |
|
|
|
|
10 |
550 |
| National biological corridors |
| 5. Ialpug |
5177 |
1762 |
56 |
6936 |
4712 |
2321 |
729 |
21693 |
| 6.Cahul-Sarata |
|
|
2519 |
|
|
343 |
504 |
3366 |
| 7. Reut-Cubolta |
|
|
73 |
200 |
|
337 |
846 |
1456 |
| 8. Camanca-Ciugur |
|
|
|
17 |
|
|
168 |
185 |
| 9. Larga |
|
|
|
|
|
|
|
|
| 10. Dniester-Prut |
|
6142 |
|
680 |
|
|
791 |
7613 |
| 11. Dniester-Ialpug |
1100 |
|
|
1387 |
|
|
519 |
3005 |
| 12. Reut |
|
|
|
|
|
|
127 |
127 |
| Local biological corridors |
| 13. Racovat |
|
|
|
48 |
1353 |
4325 |
238 |
5964 |
| 14. Nistru-Raut |
|
|
|
|
2634 |
|
|
2634 |
| 15. Ciuluc |
|
|
149 |
|
|
|
|
149 |
| 16. Iagorlic |
|
836 |
|
|
|
|
|
836 |
| 17. Nirnova |
|
|
|
|
|
|
|
0 |
| 18. Grigoriopol |
|
|
|
|
|
|
|
0 |
| 19. Salcea |
|
|
|
307 |
|
|
64 |
371 |
| 20. Ustia |
|
|
|
|
1162 |
|
|
1162 |
These areas present the centres of desertification. All
should be restored under one or another procedure, and this is the only
alternative to complete degradation. Potentially, the productivity of such areas
(ca 11 % of the area of the country) can be significantly raised, but depends on
the level of soil degradation. The main prerequisite is full change of grazing
system. In the context of the issue under discussion, these are restoration
areas, for which the need of designation for restoring should be preconditioned
by the issue of ensuring unity of the Eco-Network. From this standpoint,
especially eroded areas present another reserve.
At present, the surface areas of main biological corridors,
covered with geo-systemic buffers and core areas, were identified (Table 5).
Surface areas of corridors, covered with the lands of
restoration areas and water-protection bank strips, can be identified only in
case of survey at a different scale.
Saturation of the country’s natural districts with main
non-linear components of Eco-Network is very uneven (Table 5).
Table 5.
Distribution of core and buffer areas over natural
districts
(Int – International level, N - national, Z - zonal, L - local)
| N |
Name of district |
Surface area, thousand ha |
Core areas (CA), ha |
Geo-systemic buffer areas (GB), ha |
Share of CA and GB in the structure of district |
| Int |
N |
Z |
L |
N |
Z |
L |
thousand ha |
% |
| 1 |
Northern-Moldavian forest-steppe |
463 |
585 |
1100 |
|
3091 |
1353 |
6330 |
2421 |
14.9 |
3.2 |
| 2 |
Middle-Prut forest-steppe |
293 |
6032 |
|
|
8061 |
1162 |
|
383 |
15.6 |
5.3 |
| 3 |
Belti steppe |
192 |
|
|
149 |
200 |
|
|
128 |
0.5 |
0.3 |
| 4 |
Ciuluc-Olonet steppe |
169 |
|
|
73 |
|
|
|
827 |
0.9 |
0.5 |
| 5 |
Dniester-Raut forest-steppe |
248 |
|
1174 |
|
250 |
3683 |
306 |
|
5.4 |
2.2 |
| 6 |
Middle Dniester forest-steppe |
192 |
|
836 |
|
8700 |
|
394 |
216 |
10.2 |
5.3 |
| 7 |
Codrii forest |
474 |
5177 |
7404 |
|
8532 |
4712 |
2694 |
2011 |
30.5 |
6.4 |
| 8 |
Lower Prut forest-steppe |
181 |
1691 |
|
|
30 |
|
343 |
1319 |
3.4 |
1.9 |
| 9 |
South-Moldavian forest-steppe |
355 |
|
|
2575 |
1647 |
|
|
842 |
5.1 |
1.4 |
| 10 |
Bugeac steppe |
321 |
50 |
540 |
|
884 |
|
|
90 |
1.6 |
0.5 |
| 11 |
Lower Dniester forest-steppe |
304 |
|
|
2218 |
|
|
|
133 |
2.4 |
0.8 |
| 12 |
Lower Dniester steppe |
192 |
7300 |
|
50 |
970 |
|
|
770 |
9.1 |
4.7 |
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