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
Special publications on the nature of the most valuable
natural areas of Moldova are mainly restricted by four collections of articles (Гербовец
кий лес, 1970; Природа заповедника "Кодры", 1984; Rezervatia naturala "Codrii" -
25 ani, 1996), a section in the book Current state of environment in Moldova (Starea
actuala mediului ambiant in Moldova, 1999), as well as a small number of scarce
articles. The most diverse data are presented in the collection “Заповедники и
памятники природы Молдавии (Кравчук, Верина, Сухов; 1976), but they have the
form of scientific essays, which compromises the possibility of comparative
analysis. All these data provide sufficiently detailed presentation of only the
oldest reserve “Codru”.
Over the last three decades, the state of wildlife and
vegetation changed to a large extent, which is reflected, e.g., in the growth of
the number of threatened species, as well as pre-conditioned by widely known
economic transformations. Therefore, an undetermined part of materials of
previous years is outdated, on the background of the totality of information,
which is far away from completeness.
It should be emphasized, that faunistic and floristic studies
were outside the priorities of Moldavian Academy of Sciences over 1970-80s, were
never provided with special or target financing, and were primarily performed at
expense of scientific enthusiasm of researchers. In 1990s they were prevented by
inadequate level of science financing.
Estimate of the main potential areas of the Eco-Network
(chiefly, its core areas) was performed was mainly on the basis of the data of
experts, which were published only partially. These data cover the majority of
professional data available from research institutions.
Table 1 of below lists the most general data on estimates.
Table 1
The number of estimated areas of Moldova, which were
categorized as core areas
(Int – International level, N - national, Z - zonal, L - local) or were not
| Estimated core areas |
Total |
Int |
N |
Z |
L |
Re-estimation is required |
Others |
| Scientific reserves and the domain of the planned National park |
6 |
4 |
2 |
- |
- |
- |
- |
| Landscape reserve |
23 (+2=25)1 |
1 |
4 |
2 |
6 |
2 [7]2 |
8 |
| Nature monuments |
8 |
- |
- |
- |
- |
2 |
6 |
| Nature reserves |
15 (+2) |
- |
1 |
2 |
6 |
1 |
5 |
| Multiple-use areas |
3 (+1) |
1 |
- |
1 |
1 |
- |
1 |
| Parks |
1 |
- |
- |
- |
- |
- |
1 |
| Sites outside the Fund of protected natural areas |
12 |
1 |
1 |
- |
8 |
2 [3] |
- |
| Wetlands outside the Fund of protected natural areas |
14 |
- |
- |
- |
6 |
7[1] |
- |
| Total |
82 (+5) |
7 |
8 |
5 |
26 |
14 [11] |
21 |
1 The number of areas without merging
adjacent areas is given in round brackets;
2 The number of areas, including those categorized at higher level,
despite the scarcity of data on them, is given in square brackets.
Consequently, only 28.7% of positions were made possible to
estimate, in the majority of cases, the estimate concerning each of them being
based on the incomplete data. As a result, real significance of some areas
requires a re-estimate using new data. Such re-estimate is extremely necessary
from the standpoint of identifying the protection level.
Table 2 reflects relevant geological materials.
Table 2
Completeness of information on the most important areas of
the Eco-Network of Moldova
| Type of area |
Number of positions |
| Partly estimated |
Not estimated |
Fully estimated |
| Scientific reserves and the domain of the planned National park |
37 |
5 |
3 |
| Landscape reserve |
41 |
134 |
0 |
| Nature monuments |
9 |
47 |
0 |
| Nature reserves |
23 |
82 |
0 |
| Multiple-use areas |
4 |
17 |
0 |
| Parks |
2 |
5 |
0 |
| Sites outside the Fund of protected natural areas |
11 |
52 |
0 |
| Wetlands outside the Fund of protected natural areas |
14 |
67 |
0 |
| Total |
141 |
409 |
3 |
Even those elements of the future Eco-Network, which are
placed under state’s protection, are scarcely characterized, especially in terms
of wildlife; additionally, data on flora are outdated, at least, partially. But
the current situation is specific, because identification and biological
justification of designation of new protected areas are even more fundamental.
It should be emphasized, that placing an area under
protection or changing the status is not viewed as an obligatory withdrawing
from economic use, as well as a reason for the improvement of land-use or
prevention of degradation along with deterioration of qualities in terms of both
their value for nature protection and economic value.
Imperfection of the structure of protected areas in terms of
their management is strikingly evident. Probably, this structure reflects the
history of designating areas for protection, rather than standardised criteria.
It should be mentioned that many agricultural enterprises
listed in the table and in Law on the fund of natural areas, protected by the
state, do not exist any longer. The law stipulates the jurisdiction of local
authorities over appropriate reserves. However, they are not owners of these
areas, which belong to the state, and not to the local communes. Formal
transmission of these areas from previous state enterprises was not performed,
and in legal terms, they do not have any owner. This is confirmed by the
proposal of D. Kiseev, Prime Deputy President of Executive Committee of Gagauzia
to surrender the aforementioned areas under jurisdiction of local public
authorities (in response to the request of I. Trombitki, a Member of Parliament
of the Republic of Moldova, nr. 92 of 15.12.00.).
During the developing of the concept, possibilities of
expanding the system of protected areas were also found, as well as some options
like buffer reserves (e.g., Radoaia), however, they require a survey on a
different level.
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