Sylwester Grajewski

 

Forest regionalization for seeds and seedlings in Poland

 

Abstract

The paper presents the principles of seeds and seedlings regionalization introduced in Polish forest farms in 1994. Moreover, the hazards have been discussed resulting from absence of such legal regulations corresponding to seed and seedling material management utilized in both urban and rural horticultural plantings, afforestations, in parks and others. Temporal possibility of utilization of the Forest Regionalization of Seeds and Seedlings in Poland outside forest farms has been indicated. It corresponds to the period till the moment proper legal regulations are introduced. The regulations in focus should comprise all the enterprises or firms trading seed and seedling, as well as tree and shrub materials in Poland.

 

Key words

seed regionalization, afforestations, State Forests National Forest Holding

 

Introduction

The capability of forests and afforestations to perform various functions depends among other elements on adaptation of species, or their varieties, to the physico-geographical factors characteristic of the surface they occur on. The full adaptation is observed in the case of tree native populations which have been assimilated to both the climatic and habitat conditions for a few generations (Fonder 1992). Importing species foreign to a given tree population area, either as seeds or seedlings, will always be connected with a certain risk of lack of adaptation. The risk will be observed either as a decrease in susceptibility to unfavorable environmental conditions, worsening of the quality or diminishing in the increase of circumference and height. Wide scale introduction of trees foreign to a given region should always be preceded by a long-period research.

Some tree and shrub populations including the introduced ones are sometimes well adapted to their new conditions. They may then supplant native species from their habitats (Grajewski and Jankowski 2006). But more frequently they are first of all weaker than native species as far as their health and susceptibility to stress factors are concerned.

 


Standardization of seed and seedling material trade in Poland

Regionalization of distribution of seeds and seedlings (Załęski et al. 1994, 1996) was introduced in Poland in 1994. The aim of the process was to limit negative effects of uncontrolled distribution of various trees and shrubs populations in forest management. The regulations defining utilization of seeds and seedlings in precisely described ecological conditions have been in force for several dozen of years in majority of European countries. The current regionalization clarifies the principles of seeds and seedlings mobility basing on the so-far applied principles and regulations utilizing the natural-sylvan division of Poland prepared for the regulations to be submitted to Organization for Economic Cooperation and Development – OECD.

 

Goals of forest regionalization

The regionalization for seeds and seedlings on the area of Poland was introduced to (Matras 1992):

  1. Characterize and keep the unique features of prevailing number of natural, native or     supposedly native populations of the most important forest-creating species,
  2. Increase the seed base of the most precious trees populations in the regions of their occurrence,
  3. Popularization of the populations in the areas where the local tree-stand seed base is insufficient,
  4. Limit an uncontrolled spread of propagation material and strictly define the principles and directions of its distribution,
  5. Create a stable system of inventorying, as well as monitoring the propagation origin material.

According to the OECD regulations, a region of provenance of a given species, or subspecies or variety is an area or a complex of areas with sufficiently homogenous ecological conditions, where forest-stands have similar phenotype and genotype features. The regulations impose that the marked borders of the regions respect the existing administrative and geographical division of the country. The borders of the regions should be clearly marked on maps, and the regions should be designated either with numbers or letters.

The Polish seed regionalization accepts ecological and genetic forest-creating species, as well as climatic, geo-morphological and natural diversification of Poland as criteria of sectioning of homogenous areas. The following elements of the existing elaborations have been taken into consideration:

-        distribution of the most precious native provenances seed base of Pinus ssp., Alnus ssp.; Picea ssp., Abies ssp., Larix ssp., Quercus ssp., Fagus ssp.;

-        international micro-division  of Europe into physico-geographical provinces and sub-provinces;

-        division of Poland into regions and natural-forest districts (Trampler et al. 1990);

-        administrative division of State Forests.

26 seed macro-regions–vast areas with appropriately homogenous climatic and geo-morphological conditions- were distinguished on the basis of the borders of the physico-geographical sub-provinces and natural-forest regions. Macro-regions were denoted with two-element digital symbols e.g. 314/3. The first element 314 is an international designation of a sub-province, accepted in the physico-geographical regionalization. The other element used in Poland is the number of a natural-forest region found in a given sub-province.

106 seed micro-regions have been grouped in macro-regions. They have been selected on the basis of their seed base distribution, as well as on the base of the position of the natural-forest districts or physico-geographical regions. Thus, two types of micro-regions have been sectioned: mother/native macro-regions (for provenances) and common micro-regions (for the environment).

Mother/native micro-regions have been sectioned to preserve their natural identity, native or supposedly native trees populations, occurring in the areas with fairly balanced natural-forest conditions. The most precious provenances of Polish basic tree forest-creating species characteristic of their quality and tree increment are found on their area. The seed base is composed of large selected areas and commercial seed stands of similar genotype and phenotype features.

Common micro-regions are the areas smaller than macro-regions with fairly homogenous ecological-physiographic features, sectioned on the basis of natural-forest district borders course. Their area is characterized by a very poor seed base, without participation or with minute share of seed stands, which are not related by genotype or phenotype complex features. Micro-regions differ from each other only in respect of their natural tree growth conditions.

The most crucial difference between the mentioned types of micro-regions consists in the fact that foreign provenance tree species are not permitted for introduction into the region. Whereas in common micro-regions, if their own seed base is insufficient, both seeds and seedlings bred from seeds collected from different macro-regions or in other selected seed micro-regions, are permitted.

54 mother/ native micro-regions have been sectioned (for provenances) and 52 common ones (for the environment) have been sectioned. Micro-regions have been designated with 3-digit figure symbols. The first digit stands for the natural-forest region, and the following two are the ordinal of the micro-region in a given region. Mother/native micro-regions are denoted by ordinals from 1-50, and common ones 51-99. For instance: symbol 205 designates mother/ native region 5 in natural-forest region II, while 152-common region 2, natural-forest region I. Distinguishing the mother/native micro-regions, in which especially precious species populations can be found, aimed at creating optimum conditions for utilizing the precious seed base, as well as preventing the flow of seeds from the outside bases of lower quality.

The regional borders shown on maps are adjusted to the administrative division of the State Forests and their course can be observed along the borders of forest inspectorates and precincts owing to the fact that the seed regionalization is supposed to serve first of all trading purposes (Fig.1).

The current regionalization is not a stiff frame, which does not allow for certain modifications. The more information is obtained concerning various species the more corrections or modifications can be expected. Provenance research carried out in certain natural conditions serves the purpose of recognition and confirmation of usefulness of a given species for cultivation. This type of research has had a long-going tradition and is carried out also in Poland for many tree species (among others Pinus sylwestris L., Picea abies (L.) Karst., Larix decidua subsp. decidua Mill., Larix decidua ssp. polonica (Raciborski&Wóycicki) Domin., Fagus sylvatica L.). It would be advisable to widely utilize the results of the current research publicized so far. As utilization of best seeds, even if the purchase price is high, guarantees the financial outlays reimbursement with a high compensatory damages, the purchase price, even if it is very high, constitutes only a small section of the value of a mature tree-stand.

 

Municipal greenery

Health and high susceptibility to stress are the features which are particularly significant for the plant species constituting park and interior city greenery. Conditions present in city centers are usually unfavorable for the plant cover existing there since there are various stress-promoting factors such as: air pollution with gases, and dusts (of industrial and traffic origin), soil salinity, mechanical damages etc.

 

 

 


Fig. 1. Division into seed regions of the Regional Directorate of the State Forests in Poznań according to the Forest regionalization of seeds and seedlings in Poland

The progressing increase of the ecological and social significance of the city greeneries observed in the form of new afforestations, development of commercial greenery, plantings of both municipal and human settlements greeneries, as well as building new private gardens, brings about a high demand for planting stock indispensable for their construction and care. Increasing demand for seedlings stimulates new nurseries establishment which produce higher and higher quantities of the material. Increasing the production, as well as enlarging the profits worked out by seedlings producing nurseries, may in some cases, result in utilizing some amount of seeds of unknown origin.

Seedlings or seeds coming from areas of significantly different climatic and soil conditions or position a.s.l. are very frequently the reason of poor growth, susceptibility to various pests, diseases or frosts, which results in death of the planted trees and shrubs. The phenomenon corresponds both to native origin species and species introduced in this way (Sabor 1998). The investigation carried out among municipal greenery keepers proves that the people often pay too little attention to the discussed problems. Keeping in mind the fact that there are no legal regulations concerning the discussed problem it is suggested that the principles defined in the „Forest regionalization of seeds and seedlings” should be currently applied. It will be supportive to exclude any influence of seeds origin on possible weak growth, decreasing the level of health, or even death of both trees and shrubs in established afforestations.

 

Summary

Introduction in 1994 of legal regulations concerning counteracting of uncontrolled distribution of various tree and shrub populations in forest management has brought about a certain order to the matter of seed and seedling supplies disposal in Poland. The present regionalization in force defines the principles of seed and seedling material management. It adapts the so-far operating natural-forest division of Poland regulations to the regulations of Organization for Economic Cooperation and Development – OECD. Lack of similar regulations for the other areas of the country’s economy utilizing seed and seedling material is alarming. As long as this problem is not solved it is recommended to widely use the solutions indicated in the document called Forest regionalization of seeds and seedlings in Poland.

 

References

Fonder W. 1992: Program selekcji drzew i jego realizacja w Lasach Państwowych. Post. Tech. Leśn., 51, 28-36.

Grajewski S., Jankowski K. 2006: Wykorzystanie GIS do prognozowania zmian w ekosystemach leśnych. Zesz. Naukowe AR w Krakowie, ser. Inż. Środ. nr 28: 26-34.

Matras J. (1992): Podstawy selekcji drzew leśnych i zachowania zasobów genetycznych. Post. Tech. Leśn., 51, 9-15.

Sabor J. 1998: Nasiennictwo, szkółkarstwo i selekcja drzew leśnych. AR w Krakowie, Kraków.

Trampler T., Kliczkowska A., Dmyterko E., Sierpińska A. 1990: Regionalizacja przyrodniczo-leśna na podstawach ekologiczno-fizjograficznych. PWRiL, Warszawa.

Załęski A. 1994: Leśna regionalizacja dla nasion i sadzonek w Polsce. Fundacja „Rozwój SGGW”, Warszawa.

Załęski A. 1996: Leśna regionalizacja dla nasion i sadzonek w Polsce. Zał. nr 2 do Programu zachowania leśnych zasobów genowych i hodowli selekcyjnej drzew leśnych na lata 1991-2010. Wydaw. Fund. „Rozwój SGGW”, Warszawa.

 

Author: Sylwester Grajewski PhD, The August Cieszkowski Agricultural University of Poznań, Faculty of Forestry, Department of Forest Engineering, Mazowiecka 41, 60-623 Poznań, Poland, tel./fax: +4861 8487366, e-mail: sylgraj@au.poznan.pl , http://www.au.poznan.pl/kil .