Numerous studies of Scots pine (Pinus sylvestris) morphological diversity
were conducted in Russia in the 20-th century (Pravdin, 1964; Schymanuk, 1970;
Ìamaev, 1973; Bobrov, 1978; Vidiakin, 2001 et al.). While these studies covered
the entire species range and developed much information on the characteristics
of the species population structure, the data collected on Scots pine
intra-population variability is insufficient for understanding the species
eco-genetic structure, which understanding is pre-requisite for effective Scots
pine genetic diversity conservation decision-making. Certain problems regarding
credibility of research results occur because most research studies of
distribution of trees within Scots pine populations are based on elementary
characteristics of diversity of individual tree forms, whereas complex phenotype
features are considered very rarely. As elementary characteristics provide no
insights into real multi-dimensional objects, the use of appropriate methods to
investigate population phenotypic diversity has become crucially important.
A number of research scientists applied multivariate statistics in taxonomy
(Ìenytzky, 1971; Schmidt, 1984; Schemberg, 1986; , Ìiliutin, Kravtzov, 1984;
Zhivotovsky, 1991) and population genetics (Taylor, Mitton, 1974; Glotov,
Semerikov, 1978; Zhivotovsky, 1994 et al.). However, taxonomists mainly use
genus- or species-level taxons, i.e. they take a species or a population as an
elementary unit. Although these efforts deserve credit, investigating
intra-population polymorphism provides much valuable information in terms of
understanding mechanisms of population adaptation and species temporal and
spatial self-maintenance.
The use of multivariate analysis in intra-population polymorphism investigations
allows to consider different aspects of Scots pine tree form diversity and
forest stand condition. Investigating environmental Scots pine tee resistance,
for example, requires to use a complex approach, since organisms exhibit
specific and nonspecific responses to the environment that determine the
occurrence of organism forms resistant to certain ecological factors or their
combinations (Òarakanov et al., 2005). Since there exists a wide variety of
these combinations, versions of intra-population tree resistance might be as
wide.
Biota is known to survive climatic and other natural cataclysms in refugiums.
Application of different research methodologies allowed to locate refugiums of a
big number of coniferous species (Gribanov, 1954; Krylov, 1961; Pravdin, 1964;
Smirnov, 1966; Semerikov et al, 2003; Semerikova, Semerikov, 2007 et al.).
Although some geneticists propose to develop unconventional genetic methods of
tree form diversity conservation and the current ecological and politic
situation is favorable for that, such efforts are evidently unnecessary, as
their goals and results are obscure and they are money-taking and
time-consuming. The measures currently taken to conserve diversity of Scots pine
tree forms found both in natural forest stands and plantations should be scaled
up by focusing on conserving big populations or groups of populations proceeding
from northwest to southeast, i.e. along the vector of changes of hydrothermal
conditions and the greatest Scots pine inter-population genetic differences,
with a special emphasis placed on particularly valuable populations
characterized by the highest diversity of ecological niches, as well as those
found in refugiums.
* This research was financially supported by the Russian Academy of Science,
Siberian Branch through Integration Project ¹ 53
Note. Abstracts are published in author's edition