Научный журнал

European Journal of Natural History

ISSN 2073-4972

ИФ РИНЦ = 0,301

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Runova Ye.M., Savchenkova V.A.

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The problems of environmentally safe forest use, forest reproduction, maintaining at the desired level or preservation of ecological functions of the forest deserve special attention and detailed study.

A burning problem is the reduction of terms for growing forest resources, the improvement of quality state of forest restoring measures. For its solution a detailed study of the most common types of cut-over lands of the Middle Angara Area, the dynamics of their structural changes, and also initial phases of forest formation.

Changes of environmental conditions, differences in the flora, and its change reflect on the duration of the forest restoration period, at the contraction of which the forest productivity increases.

For the Middle Angara Area, after felling the plantations with pine and larch prevalence, the following types of cut-over lands are indicative: fireweed, small reed, herb, gross grass, clusterberry-small reed with green mosses presence.

Considering that the field layer defines the environs for the regeneration and initial phases of forest formation, the research on permanent and temporary sample plots for the purpose of its change dynamics study has been carried out. Annual observations allow finding out the dynamics of ground covering with some or another species of plant, stating the regeneration principles connected with the dominant kinds of grassland vegetation.

The investigations are carried out by defining the occurrence of various kinds of suffruiticous-grassland and mossy-lichenous plants, their projective cover, abundance, vital power, distributional pattern by area. A comparative analysis was carried out on the estimate results. Annual observations allowed detecting some or other plant species coverage area dynamics, establishing regeneration regularities connected with the dominant kinds of grassland vegetation.

On fresh cut-over lands the forest herbs prevail, changes begin with the cut-over age increase. The change of mossy and herb stratum in cut-over lands has a significant effect on the forest-regeneration processes. So, for example, the natural seeding of pine and fir trees occurs in the areas occupied with fireweed more often than in the areas covered with grass plants.

In table 1 the influence of grass cover representatives on the emergence of pine seedlings is shown.

Table 1. Influence of grass cover representatives on the emergence of pine seedlings

Thereat the fireweed coverage keeps the young pine and fir tree seedlings from dying off because of high and low temperatures.

In table 2 the average results of temperature and luminance measurements of the soil level during the vegetative season (the measurements were carried out from 12⁰⁰ to 13⁰⁰ on fair weather) are presented.

Table 2. Average results of temperature and luminance measurements of the soil level during the vegetative season

But the fireweed thick cover influences negatively on growth. The grass plant cover influences especially negatively on the conifer young growth. It quickly affords a sod preventing the seeds from germination and seedlings from growth. Water soluble materials, which decrease the pine and fir tree seed vigor, growth and survival ability of the young plants, come into the soil and soil level together with precipitation from herb debris.

With the field layer thickness increase of the conditions for timber species emerging and growth get deteriorated. Thus, for example, the pine natural seeding increment made 5,6-6,6 cm per annum in the piny wood in the segments with herb stratum, and without the last - 7,3-9,9 cm per annum. Especially vividly this difference is manifested in the staddle growing near grass plant blocks. The clean felling in the areas, where relatively rich sabulous and loam soils, which are disorderly covered with herbaceous vegetation rendering not only coniferous, but also hardwood species regeneration difficult after growing stock felling, prevail are repopulated least successfully. In various kinds of grass plants the sod is formed differently. So, in grassy small reed a heavy sod is formed on the soil level, and wood small reed interweaves and thickens the ground litter and mineral horizons´ top with its rhizomes. That is why the influence of these species on forest regeneration will be different.

In the felling year the conditions for timber species seed germination are favourable due to the field layer, good warming, soil ventilation and enough dampness competitive influence weakening. In the triennial and older cut-over lands the small reed thick sod hinders the emergence of seedlings.

In the first year after summer harvesting of wood the ground vegetation of the cut-over land differs little from that of under the cover. From the second year the pratal weed-grown herbaceous plants dominance (see Fig. 1) begins. After winter harvesting of wood the field layer change is observed in the first year after the felling already.

The regularity in the direction of mosses´ dying off and herbaceous vegetation abundant development manifests itself in the cover change.

Changes take place in the ground vegetation and forest litter with the felling age increase.

For clusterberry-small reed, clusterberry-green moss and gross grass cut-over types a good natural regeneration (more than 6 ths./ha) of commercially valuable species is indicative. The restoration of the vegetation cover typical of the forest community occurs 6-10 years earlier than in small reed, grassland and fireweed types of cutovers.

Fig. 1. Field layer time history after clear forest felling

Hardwood species defy competition with herbaceous plants forming no thick sods and prefer more humid soils.

On the research results one can come to a range of conclusions concerning the interrelation of forest associations, plant community structure and commercially valuable species regeneration:

• it is possible to judge on habitat conditions by herbaceous vegetation kinds;
• cut-over lands are subjected to heavy turf formation in places of relatively rich sabulous and loam soils (especially the places subjected to harvesting techniques), that hinders the development of natural regeneration;
• in some cases in apiarian runways a more successful regeneration than in the areas not subjected to skidding occurs;
• the most successful natural regeneration takes place in green-moss-grassland cutover types;
• the ground vegetation of derivative young growths is characterized by a greater, compared to the original forest type flora diversity due to the enrichment of the floristic composition with light-loving and meadow plants, retaining the species set peculiar to the original forest type.

The work is submitted to the Scientific International Conference "Scientific Research of Higher School on Priority Orientations of Science and Technology", June, 22-29, 2008, came to the editorial office on 22.05.2008.

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