The great difference in the level of chloroplast variation and its geographic structure among the three main species studied here demonstrates that forest species do not form a homogeneous group. Hazel shows a genetic structure similar to many other thermophilous species and this structure, in combination with fossil evidence, indicates that the post-glacial colonisation of most of Europe originated in a refugium in western France while the Balkan and Italy were colonised from a south-eastern refugium. In sallow and silver birch the chloroplast DNA variation and its structure does not fit with a scenario of glacial restriction to southern refugia and survival at intermediate latitudes is suggested for both species. The chloroplast DNA variation in silver birch suggests the presence of one western and one eastern European post-glacial colonisation route and limited contribution of southern populations in the colonisation of the rest of Europe. Unique haplotypes by the Ural Mountains indicates the possibility of a separate glacial origin of these populations. The study of chloroplast DNA in species closely related to sallow and silver birch indicate that extensive hybridisation and cytoplasmic gene flow occurs within both the Salix and Betula genera in Europe. The nuclear and chloroplast phylogenies of 14 Betula species were not in complete agreement with each other or with the classical division of the Betula genus into subgenera or sections. The phylogenetic structure implies that hybridisation has played a role in the evolution of the Betula genus. This thesis focuses on the chloroplast DNA variation in three forest tree genera: Corylus, Betula and Salix. Chloroplast PCR-RFLP is used to evaluate the post-glacial history of hazel, Corylus avellana, silver birch, Betula pendula and sallow, Salix caprea and to explore the possibility of introgression in the Salix and Betula genera. In addition, the chloroplast matK gene, its flanking regions and the nuclear ADH gene were used to study the phylogenetic relationships within the Betula genus.

No description available.

This thesis compare various uses of silver birch (Betula pendula Roth.) as a preparatory species during afforestation by silver fir (Abies alba Mill.). In this experiment, silver fir was planted at fall of 2015 and measurements were conducted in the vegetation season 2016. There were four variants of experiment with respect to the silver birch: clearcut, birch stand with 50 % stocking density, narrow embankment cut and birch stand with a full stocking density. Air temperature, precipitation, vapor pressure deficit, soil moisture and transmittance of photosynthetically active radiation were measured from the environmental variables. On plants, the growth increment, chlorophyll fluorescence, shoot water potential and needle mas per area were studied. Preparatory forest stand eliminated extreme temperatures, both positive and negative. Maximum temperatures were by 7 °C lower under the forest canopy than on clearcut. Spring frost was eliminated by 2.2 °C which was enough to protect fresh shoots from freezing. On the other hand soil moisture under the birch was by 23 till 47 % lower than at the clearcut. Tallest growth increment of 12 cm was at the clearcut, shortest of 7 cm under the birch without thinning. Needle mass per area corresponded to light availability and it was highest at clearcut and lowest under the birch. Chlorophyll fluorescence in dark did not suggest any differences between treatments (Fv/Fm was higher than 0.80) and therefore differences in growth can be accounted to the light availability. Data suggest that for the silver fir saplings is best to grow under severely thinned silver birch canopy with low stocking density which allows for enough light and soil moisture but still protects saplings against inclement weatherFormula clause:I declare that I am working, "Birch as a preparatory tree species in reforestation calamity clearings silver fir: the impact of environmental conditions and selected ecophysiological parameters fir" worked independently and all used sources and information mention in the list of references. I agree that my work has been published in accordance with § 47 b of the Act no. 111/1998 Coll., On universities, as amended and in accordance with directives on the publication of university theses. I am aware that my work covered by Act no. 121/2000 Coll., The Copyright Act, and the Mendel University in Brno has the right to conclude a license agreement and use this work as school work pursuant to Section 60 paragraph. 1 of the Copyright Act. I also agree that, before drawing up licensing agreements on the use of a work by another person (the subject), I request a written opinion by the university that the subject license agreement is not contrary to the legitimate interests of the university and undertake to pay any contribution to the costs associated with the creation of the work, and up to the full amount

Surface coal mining heavily disrupts vast areas of landscape. Previous studies conducted in these areas reveal that succession processes on unreclaimed sites support close to nature community. It's crucial to understand and be able to predict these processes in order to include spontaneous succession into restoration plans. The aim of my thesis is to clarify establishment and dispersion mechanisms of dominant pioneer woody species willow (Salix caprea), birch (Betula pendula) and aspen (Populus tremula). Study carried out on unreclaimed sites on a large colliery spoil heap near the town of Sokolov. I have studied establishment and growth of pioneer woody species on both graded and ungraded sites, representation of individual woody pioneer species was on sites in different distance from the edge of the spoil heap, birch's population age structure and reproduction potential of willow in accordance to age. All pioneer woody species establish and grow better on ungraded sites. The amount of willow decreases while the number of aspen individuals remains the same and the amount of birch increases with growing distance from the edge of the spoil heap. Birch's population age reveals establishment of new individuals in favourable climatic conditions. Willow is reproductively capable at the age of 10 years...

Darbo objektas – naujai sukryžminti hibridinės drebulės (Populus tremuloides x Populus tremula) ir karpotojo beržo ( Betula pendula) hibridai. Darbo tikslas – Atlikti tolimąją hibridizaciją ir išauginti augalus-regenerantus nesubrendusių gemalų kultūroje bei įvertinti genetinę įvairovę. Darbo rezultatai. Sukryžminus gauta skirtingi hibridai. Jų įvairovė įvertinta APPD metodu. Išmatavus augimo tempus nustatyta, kad hibridai 16.2 ir 16.4 auga greičiau nei hibridinės drebulės klonai. Ištyrus adaptacijos nesterilioje aplinkoje sąlygas, nustatyta šaknijimosi tempai. Tyrimo metu pastebėta, kad ūgliukų sodinimas į durpių substratą Jiffi tabletėse su šaknimis ir be jų ilgesniam nei 3 mėnesių laikotarpiui, neturi augimo skirtumų. / Aim of the work: new crossbred hybrid aspen (Populus tremuloides x Populus tremula) and birch (Betula pendula) hybrids Objekt of the work: make long hybridization and grow up new regeneration plants in unformed embrio culture and rate genetical variation Results: After crossing get new hybrids. His variation rated by RAPD metod. After measure growing speed, set that hybrids 16.2 and 16.4 growing faster than hybriding aspen clons. In adaptation study set root growing speed. In study notice that plants with root and without in Jiffi tablet peat substratum after 3 month get same height .

Ziel des Forschungsprojektes war der Gewinn umfassender verjüngungsökologischer Kenntnisse zu den Pionierbaumarten Sandbirke (Betula pendula Roth), Salweide (Salix caprea L.) und Eberesche (Sorbus aucuparia L.) im Hinblick auf eine natürliche, eingriffsfreie Wiederbewaldung von Schadflächen (z.B. nach Sturmwurf). Die Abschätzung des Besiedlungserfolges von Schadflächen durch Pionierbaumarten ist aufgrund unzureichender verjüngungsökologischer Kenntnisse gegenwärtig noch mit großen Unsicherheiten verbunden. Die Untersuchungen fanden auf fünf 4-12 ha großen Kyrill-Sturmwurfflächen in den Hoch- und Kammlagen (750-900 m ü. NN) des Thüringer Waldes statt. Alle potenziellen Samenbäume der Pionierbaumarten wurden in den angrenzenden, geschlossenen Fichtenbeständen lokalisiert. Als Versuchsdesign wurde in Abhängigkeit der vorgefundenen Samenbaumdichten und -verteilungen ein Kreuz- bzw. Sterntransekt auf den Sturmwurfflächen etabliert. Entlang der Transektlinien wurden alle 20 m Samenfallen installiert. Als Samenfallen kamen für die Sandbirke Netztrichterfallen (0,2 m²), für die Salweide Klebfallen (0,043 m²) und für die endozoochore Ausbreitung durch frugivore Vogelar-ten Kotfallen (0,25 m²) zum Einsatz. Für die Modellierung der Samenausbreitung von Sandbirke und Salweide wurden inverse Modelle bzw. geostatistische Modelle erstellt. Zudem wurden auf einer der Sturmwurfflächen genetische Nachkommenschaftsanalysen bei Sal-weide mittels Kern-DNA-Primer durchgeführt. Die Bodensamenbankuntersuchungen fanden in jeweils drei geschlossenen Birkenbeständen, Fichten-Birken-Beständen, Fichtenbeständen mit einer einzeln eingemischten Birke und reinen Fichtenbeständen im Tharandter Wald und Thüringer Wald statt. Mittels eines 10,2 cm breiten Stechzylinders wurden 10 cm tiefe Bodenproben gewonnen. Die Lagerung der Proben fand im Kaltgewächshaus statt, wo alle 14 d die gekeimten Samen erfasst wurden. Weiterhin wurde ein Eingrabungsexperiment installiert. Dafür wurden Sandbirkensamen, Ebereschensamen und Ebereschenfrüchte in 2 cm, 5 cm und 10 cm tiefen Mineralboden vergraben und in sechsmonatigen Intervallen jeweils eine Keimprobe zum Test der verbliebenen Keimfähigkeit entnommen. Die Auswertung der Bodensamenbankuntersuchungen erfolgte mittels GLM und GLMM. Während der zweijährigen Untersuchung zur zeitlichen und räumlichen Samenausbreitung von Salix caprea auf fünf Sturmwurfflächen konnten ein schwächeres und ein stärkeres Samenjahr nachgewiesen werden. Des Weiteren erstreckte sich der Samenflugzeitraum im Frühjahr in Abhängigkeit von den klimatischen Bedingungen über 12 Wochen in 2015 und 6 Wochen in 2016. Die höchsten Samenmengen von 23-156 Samen je Falle wurden jeweils unter den Kronen von Salweiden-Samenbäumen nachgewiesen. Ab einer Entfernung von 350 m zum Samenbaum bis zur untersuchten Distanz von 870 m wurden, unabhängig von der Distanz, der Hangneigung, der Anzahl der Samen-bäume und der Windrichtung (Anisotropie), im Durchschnitt 0,6-2,1 Samen je Falle er-fasst. Die genetischen Analysen zur Nachkommenschaft ergaben, dass 29 % der untersuch-ten Verjüngungspflanzen von einem der 20 lokalisierten Elternbäume in der bewaldeten, 500 m breiten Suchzone abstammten. Die Ausbreitungsdistanzen der nachweislich am erfolgreichsten verjüngten Samenbäume betrugen dabei 550-800 m. Insgesamt zeigte die Salweidenverjüngung eine höhere Allel-Variation, als die 20 Elternbäume, was auf einen externen Genfluss und lange Samen- und Pollenausbreitungsdistanzen hinweist. Im Zuge des zweijährigen Untersuchungszeitraums zur Samenausbreitung von Betula pendula auf zwei Kyrill-Sturmwurfflächen konnten ein Mastjahr und ein Zwischenjahr nachgewiesen werden. Die Ergebnisse der inversen Modellierung mittels isotroper Mo-delle ergaben dabei flächenunabhängig Produktionsmengen für einen Samenbaum von 20 cm im Bhd von 300.000-366.000 Samen je Baum im Zwi-schenjahr 2015 und 1.430.000-1.530.000 Samen je Baum im Mastjahr 2016. Mittels räumlicher Modellierung der Samenausbreitung konnte keine Anisotropie belegt werden. Unabhängig von den beprobten Flächen und Un-tersuchungsjahren, belegen die Modellschätzungen allesamt eine isotrope Ausbreitung der Samen. Die mittleren Ausbreitungsdistanzen (MDD) beliefen sich dabei hangaufwärts auf 86-97 m und hangabwärts auf 367-380 m. Maximal ab-gelagerte Samendichten von 2.015 n m-² im Zwischenjahr und 9.557 n m-² im Mastjahr fanden sich bis 40-50 m Entfernung zum Samenbaum. Die Untersuchungen der endozoochoren Samenausbreitung auf fünf Sturmwurfflächen weisen auf eine bevorzuge Nutzung der Vogelarten von Rast- und Sitzgelegenheiten (Strukturelemente) auf Freiflächen zum Absetzen von Kot hin (2,7 Kothaufen je m²). Unter Freiflächenbedingungen - ohne Strukturelemente - ergaben sich im Mittel 0,4 Kothaufen je m². Die höchsten mittleren Kotdichten wurden unter aufra-genden Totästen (20 n m-²), umgeklappten Wurzeltellern (4,6 n m-²) und Hochstubben (3,9 n m-²) nachgewiesen. Schwach dimensionierte Verjüngungspflanzen der Sandbirke, Eberesche und Fichte, und Strukturelemente unter einem Meter Höhe wurden dagegen weitgehend für das Absetzen von Kot gemieden. Das Vermögen zum Aufbau einer Bodensamenbank durch Betula pendula und Sorbus aucuparia unterschied sich deutlich. 56-100 % der eingegrabenen Sandbirkensamen wa-ren auch nach 2,5 Jahren keimfähig, wohingegen lediglich 3-16 % der eingegrabenen Ebereschensamen ohne Fruchthülle und 0-19 % der eingegrabenen Ebereschensamen mit Fruchthülle vital waren. Die Auswertung mittels GLM prognostizierte einen kom-pletten Verlust der Keimfähigkeit nach 12 Jahren, 4,5 Jahren und 3 Jahren der Sandbirkensamen, sowie der Ebereschensamen mit und ohne Fruchthülle. Ein Einfluss der Lagerungstiefe war nur für Sandbirke nachweisbar. Die Untersuchungen der Bodensamenbank von Birke in Fichtenbeständen mit unter-schiedlichen Birkensamenbaumanteilen ergab einen straffen Zusammenhang zwischen der Anzahl von Samenquellen und den nachgewiesenen Samendichten im Boden. In den Birkenbeständen fanden sich stets die höchsten Dichten von 489-1.142 Birkensamen je m². Die Analyse unterschiedlicher Bodenschichten zeigte zudem signifikant abneh-mende Birkensamendichten mit zunehmender Bodentiefe. Die Ergebnisse der Untersuchungen zeigen, dass die Fruktifikation von Betula pendula, Salix caprea und Sorbus aucuparia durch klimatische Verhältnisse beeinflusst wird, weshalb die drei Pionierbaumarten nicht alljährlich hohe Samenmengen produzieren (Mastjahre und Zwischenjahre). Zum Ausgleich von Produktionsdefiziten in den Zwischenjahren unter-scheiden sich die Pionierbaumarten in ihrer Strategie. Dies gilt es bei der Umsetzung des Konzeptes einer natürlichen, eingriffsfreien Wiederbewaldung von Schadflächen nach Sturmwurf durch die Naturverjüngung von Pionierbaumarten zu beachten. Die einzige der drei Pionierbaumarten, die dem allgemeinen Bild einer Pionierbaumart ent-spricht, ist die Salweide. Ihr Besiedlungserfolg ist allein von den aktuellen, alljährlich variierenden, aber dennoch stets hohen Samenproduktionsmengen und den enorm weiten Aus-breitungsdistanzen (>800 m) abhängig. Hinsichtlich der Samenausbreitung haben die Him-melsrichtung, die Position der Samenbäume und die Anzahl vorhandener Samenquellen ab einer Distanz von 50 m zur Schadfläche keinen bedeutenden Einfluss auf die abgelagerten Samenmengen mehr. Die auf 86-380 m limitierte Samenausbreitung von Sandbirke wurde dagegen stark vom Geländerelief (Hangneigung), der Position der Samenbäume (Tal, Kuppe, Hanglage) und der Distanz der Samenbäume zur Sturmwurffläche beeinflusst. Zum Ausgleich der limitierten Samenausbreitung und deutlich reduzierten Samenmengen im Zwischenjahr ist Sandbirke jedoch zum Aufbau einer short-term persistenten Bodensamenbank befähigt. Den gesamten Verjüngungszyklus betrachtend entspricht die Eberesche eher einer Schluss-waldbaumart. Unter ungünstigen klimatischen Bedingungen kommt es häufig zum kompletten Ausfall der Samenproduktion. Ihr enormes Wiederbewaldungspotential von Sturmwurfflächen speist sich hauptsächlich aus dem Aufbau einer Sämlingsbank und weni-ger durch den aktuellen Samenregen oder der short-term persistenten Bodensamenbank. Die limitierte Samenausbreitung von Sandbirke und Eberesche macht eine „räumliche Optimierung“ der Samenbaumpositionen durch die Forstwirtschaft erforderlich. Aufgrund der allgegenwärtigen Omnipräsenz von Weidensamen ist dies für Salweide nicht zwingend not-wendig. Das detailreiche Wissen zur Verjüngungsökologie der untersuchten Pionierbaumar-ten ermöglicht eine gezielte waldbauliche Steuerung im Sinne des Vorhalts und der Pflege von Pionierbaumarten im Wirtschaftswald. Dies ist gegenwärtig und zukünftig vor allem von besonderer Bedeutung, da aufgrund der zu erwartenden Zunahme von Schadereignissen und deren Unvorhersehbarkeit die Fähigkeit der Wälder zur natürlichen Wiederbewaldung von Schadflächen durch Pionierbaumarten zunehmend an Interesse gewinnen wird.:Table of abbreviations III Summary IV Zusammenfassung VIII Chapter 1 – General introduction 1 1.1 Introduction 2 1.1.1 Importance and relevance of the study 2 1.1.2 Research interest - regeneration ecology 5 1.3 Aims, scope and hypotheses 9 1.4 Study outline 12 1.5 References 13 Chapter 2 – Seed dispersal capacity of Salix caprea L. assessed by seed trapping and parentage analysis 25 2.1 Abstract 26 2.2 Introduction 26 2.3 Materials and methods 29 2.3.1 Study area 29 2.3.2 Experimental design 31 2.3.3 Genetic analysis 32 2.3.4 Seed trap data analysis 33 2.3.5 Geostatistical models 34 2.4 Results 36 2.4.1 Temporal patterns of seed dispersal 37 2.4.2 Dispersal distance and spatial patterns of seed dispersal 37 2.4.3 Genetic parentage analysis 40 2.5 Discussion 42 2.5.1 Seed production and temporal patterns of seed dispersal 42 2.5.2 Dispersal distance and spatial patterns of seed dispersal 43 2.5.3 Genetic parentage analysis 45 2.6 Conclusions for silvicultural practice 46 2.7 References 48 Chapter 3 – Restrictions on natural regeneration of storm-felled spruce sites by silver birch (Betula pendula Roth) through limita-tions in fructification and seed dispersal 57 3.1 Abstract 58 3.2 Introduction 58 3.3 Materials and methods 60 3.3.1 Study area 60 3.3.2 Experimental design 63 3.3.3 Data analysis 64 3.3.4 Seed dispersal model 64 3.3.5 Simulations for practical management decisions 66 3.4 Results 66 3.4.1 Seed production 66 3.4.2 Seed dispersal and spatial patterns 68 3.5 Discussion 71 3.5.1 Seed production 71 3.5.2 Directionality 72 3.5.3 Spatial patterns and seed dispersal distances 72 3.6 Seed dispersal scenarios for silvicultural management decisions 74 3.6.1 Seed dispersal scenarios 74 3.6.2 Conclusions for silvicultural management decisions 76 3.7 References 78 Chapter 4 – The impact of structural elements on storm-felled sites on endozoochorous seed dispersal by birds – a case study 85 4.1 Abstract 86 4.2 Introduction 86 4.3 Materials and methods 88 4.3.1 Study area 88 4.3.2 Experimental design 90 4.3.3 Data analysis 91 4.4 Results 92 4.5 Discussion 95 4.6 Conclusions for silvicultural practice 97 4.7 References 98 Chapter 5 – Soil seed banks of pioneer tree species in European tempe-rate forests: a review 104 5.1 Abstract 105 5.2 Introduction 105 5.3 Methods of literature search 107 5.4 Species-specific reproductive ecology determining the potential of soil seed banks 110 5.5 Characterization and classification of soil seed banks 112 5.5.1 Soil seed bank of Betula spp. 114 5.5.2 Soil seed bank of Alnus glutinosa (L.) GAERTN. 116 5.5.3 Soil seed banks of Salix spp. and Populus tremula L. 117 5.5.4 Soil seed bank of Sorbus aucuparia L. 118 5.6 Conclusions 119 5.7 References 120 Chapter 6 – Do birch and rowan establish soil seed banks sufficient to compensate for a lack of seed rain after forest disturbance? 134 6.1 Abstract 135 6.2 Introduction 135 6.3 Materials and methods 137 6.3.1 Study areas 137 6.3.2 Data collection 139 6.3.3. Statistical analysis 140 6.4 Results 141 6.4.1 Study A - Artificial seed burial experiment 141 6.4.2 Study B - Soil core sampling in the forest 145 6.5 Discussion 147 6.5.1 Study A - Artificial seed burial experiment 147 6.5.2 Study B - Soil core sampling in the forest 149 6.6 Conclusions 151 6.7 References 152 Chapter 7 – General discussion 160 7.1 Discussion of important aspects of regeneration ability 161 7.1.1 Fructification and seed production in Salix caprea, Betula pendula and Sorbus aucuparia 165 7.1.2 Ecological processes within the regeneration cycle of Salix caprea 167 7.1.3 Ecological processes within the regeneration cycle of Betula pendula 168 7.1.4 Ecological processes within the regeneration cycle of Sorbus aucuparia 169 7.2. Conclusions for silviculture and management recommendations 172 7.3 References 175 Table of appendix i / The aim of the study was to obtain comprehensive knowledge of the regeneration ecology of the pioneer tree species silver birch (Betula pendula Roth), goat willow (Salix caprea L.) and rowan (Sorbus aucuparia L.). The findings should contribute to better management of the natural regeneration of disturbed sites (e.g., windthrown sites) by pioneer tree species. Insufficient knowledge of the regeneration ecology of pioneer tree species renders forest managers’ abilities to assess the success of regeneration of windthrown sites uncertain. The study took place in the years 2015 and 2016. The study sites were located on the slopes and mountain tops (plateaus) of the Thuringian Forest (715-900 m a.s.l.), on five windthrown open areas (4-13 ha) created by the storm ‘Kyrill’ in January 2007. All seed trees of pioneer tree species were mapped within the forested search zone around each site. This zone extended 200 m for silver birch and rowan and 500 m for goat willow. Following the mapping of these seed trees and an analysis of their spatial distribution, seed traps were placed along two or four crossing line transects, with intervals of 20 m between traps. The traps were funnel shaped net seed traps for silver birch (0.2 m²), seed traps with a sticky, non-drying glue for goat willow (0.043 m²) and dropping traps for seeds dispersed endozoochorously by frugivorous birds (0.25 m²). A phenomenological model and model-based geostatistics were used to investigate silver birch and goat willow seed dispersal. For goat willow a parentage analysis was performed at one of the study sites using nuclear-DNA-primers. The soil seed bank study was carried out in three birch stands, spruce stands with admixed birch, spruce stands with one isolated birch tree and pure spruce stands in the Tharandter Forest and in the Thuringian Forest. Soil core samples with a diameter of 10.2 cm were taken from the litter layer and the mineral soil to a depth of 10 cm. The soil samples were placed in a greenhouse and seed germination was checked every 14 days. An artificial seed burial experiment was also carried out. Silver birch seeds, rowan seeds and rowan fruits were buried in mineral soil at depths of 2 cm, 5 cm and 10 cm. At intervals of 6 months sample sets were removed from the soil and the germination capacity checked. The analysis of the soil seed banks was based on generalized linear mixed models (GLMM) and generalized linear models (GLM). The 2-year study of the temporal and spatial dispersal of seeds of Salix caprea on five Kyrill-felled areas involved one year with lower seed production and one with more bountiful seed production. The duration of the spring seed rain was about 12 weeks in 2015, and only 6 weeks in 2016 because of contrasting weather conditions. The highest seed numbers of 23-156 n per trap occurred close to the base of the seed trees. Beyond 350 m from the seed trees, up to the maximum distance in the study of 870 m, the average numbers of seeds per trap (0.6-2.1 seeds) were independent of the dispersal distance, inclination, the number of seed sources and the dispersal direction (anisotropy). Parentage analyses showed that 29% of the saplings stemmed from one of the 20 parent trees within the 500 m search zone extending from the edge of the open area. The seed dispersal distances of the most successful seed parents were between 550-800 m. The saplings revealed a higher allelic variation than the 20 parent trees, indicating external gene flow and long seed and pollen dispersal distances. During the 2-year study of Betula pendula seed dispersal on two Kyrill-felled areas there was a mast year and a non-mast year. Independent of the site, the seed production rate of a silver birch seed tree with a mean diameter at breast height (dbh) of 20 cm predicted by isotropic inverse models was approximately 300,000-366,000 seeds in 2015 and 1,430,000-1,530,000 seeds per tree in the mast year 2016. Directionality (anisotropic inverse modelling) of seed dispersal around an individual seed tree could not be confirmed. The model results revealed the isotropic model (no directionality) to be an appropriate approach for all sites and years. The mean dispersal distances (MDD) were 86 m and 97 m (uphill) and 367 m and 380 m (downhill). The maximum seed numbers occurred within 40-50 m of a seed tree, amounting to 2,015 n m-² in the non-mast year and 9,557 n m-² in the mast year. The study of endozoochorous seed dispersal on the five sites felled by the storm Kyrill showed a preference of frugivorous birds for perches and resting places (structural elements) from which to defecate onto open areas (2.7 droppings per m²). On completely open areas – with no structural elements – an average of 0.4 droppings per m² was recorded. The highest mean bird dropping density was observed under towering dead branches (20 n m-²), upturned root plates (4.6 n m-²) and high stumps (3.9 n m-²). Young, small diameter silver birch, rowan and spruce trees, and structural elements less than 1 m in height generally, were avoided by frugivorous birds as a place from which to defecate. The abilities of Betula pendula and Sorbus aucuparia to form a soil seed bank differed. Between 56-100 % of the buried silver birch seeds were still viable after 2.5 years, whereas only 3-16 % of the rowan seeds buried without pulp and 0-19 % of the rowan seeds within pulp were viable. The maximum durations of storage in the soil predicted for silver birch seeds and rowan seeds with and without pulp by GLM were 12 years, 4.5 years and 3 years. An influence of the storage depth was found for silver birch seeds only. The investigation of the soil seed banks of birch in three birch stands and nine spruce forests with different numbers of admixed birch seed trees showed a strong correlation between the number of seed sources and the seed density in the soil. The birch stands contained the highest mean densities of viable birch seeds in soil, between 489-1,142 n m-². The analysis of the different soil layers showed significantly declining birch seed densities with increasing soil depth across all sites. The results of the study showed that the fructification of Betula pendula, Salix caprea and Sorbus aucuparia is influenced by weather conditions, with the three pioneer tree species failing to produce high numbers of seeds every year (mast and non-mast years). The three species differed in their strategies to compensate for low seed production in non-mast years. This must be considered when implementing a concept for the reforestation of disturbed sites based on natural regeneration by pioneer tree species. Goat willow was the only one of the three specie studied with characteristics corresponding to the general assumptions made about pioneer tree species. The regeneration success of goat willow is dependent upon the variable but generally high annual seed production and long seed dispersal distances (> 800 m). The azimuth direction, position and number of seed trees have no meaningful influence on seed numbers at a distance of more than 50 m from the seed source. The limited mean seed dispersal distances of 86-380 m determined for silver birch were influenced by site inclination, the seed tree location (valley, slope or plateau) and the distance between the seed tree and the windthrown site. Silver birch seed shadow is also influenced by the number of seed sources. To compensate for the limited dispersal distances and the significantly lower seed production in non-mast years, silver birch is able to build up a short-term persistent soil seed bank. The regeneration cycle of rowan is more reminiscent of that of a shade-tolerant tree species. Unfavorable weather conditions often result in a complete failure to produce seeds. The enormous regeneration potential of rowan on disturbed sites stems primarily from a seedling bank, which is built up over years. The seed rain in any given year and its short-term persistent soil seed bank are of secondary importance. Forest management targeting a ‘spatial optimization’ of silver birch and rowan seed trees is necessary to ensure successful natural regeneration given the limited seed dispersal. The omnipresence of goat willow seeds renders specific spatial management measures for its establishment unnecessary. Detailed knowledge of the regeneration ecology of the studied pioneer tree species makes possible an approach to silviculture that is targeted to the conservation and revitalization of pioneer tree species in managed forests. The expected increase in the frequency of disturbances, and their unpredictability, means that the ability of forests to naturally regenerate using pioneer tree species is likely to grow in importance.:Table of abbreviations III Summary IV Zusammenfassung VIII Chapter 1 – General introduction 1 1.1 Introduction 2 1.1.1 Importance and relevance of the study 2 1.1.2 Research interest - regeneration ecology 5 1.3 Aims, scope and hypotheses 9 1.4 Study outline 12 1.5 References 13 Chapter 2 – Seed dispersal capacity of Salix caprea L. assessed by seed trapping and parentage analysis 25 2.1 Abstract 26 2.2 Introduction 26 2.3 Materials and methods 29 2.3.1 Study area 29 2.3.2 Experimental design 31 2.3.3 Genetic analysis 32 2.3.4 Seed trap data analysis 33 2.3.5 Geostatistical models 34 2.4 Results 36 2.4.1 Temporal patterns of seed dispersal 37 2.4.2 Dispersal distance and spatial patterns of seed dispersal 37 2.4.3 Genetic parentage analysis 40 2.5 Discussion 42 2.5.1 Seed production and temporal patterns of seed dispersal 42 2.5.2 Dispersal distance and spatial patterns of seed dispersal 43 2.5.3 Genetic parentage analysis 45 2.6 Conclusions for silvicultural practice 46 2.7 References 48 Chapter 3 – Restrictions on natural regeneration of storm-felled spruce sites by silver birch (Betula pendula Roth) through limita-tions in fructification and seed dispersal 57 3.1 Abstract 58 3.2 Introduction 58 3.3 Materials and methods 60 3.3.1 Study area 60 3.3.2 Experimental design 63 3.3.3 Data analysis 64 3.3.4 Seed dispersal model 64 3.3.5 Simulations for practical management decisions 66 3.4 Results 66 3.4.1 Seed production 66 3.4.2 Seed dispersal and spatial patterns 68 3.5 Discussion 71 3.5.1 Seed production 71 3.5.2 Directionality 72 3.5.3 Spatial patterns and seed dispersal distances 72 3.6 Seed dispersal scenarios for silvicultural management decisions 74 3.6.1 Seed dispersal scenarios 74 3.6.2 Conclusions for silvicultural management decisions 76 3.7 References 78 Chapter 4 – The impact of structural elements on storm-felled sites on endozoochorous seed dispersal by birds – a case study 85 4.1 Abstract 86 4.2 Introduction 86 4.3 Materials and methods 88 4.3.1 Study area 88 4.3.2 Experimental design 90 4.3.3 Data analysis 91 4.4 Results 92 4.5 Discussion 95 4.6 Conclusions for silvicultural practice 97 4.7 References 98 Chapter 5 – Soil seed banks of pioneer tree species in European tempe-rate forests: a review 104 5.1 Abstract 105 5.2 Introduction 105 5.3 Methods of literature search 107 5.4 Species-specific reproductive ecology determining the potential of soil seed banks 110 5.5 Characterization and classification of soil seed banks 112 5.5.1 Soil seed bank of Betula spp. 114 5.5.2 Soil seed bank of Alnus glutinosa (L.) GAERTN. 116 5.5.3 Soil seed banks of Salix spp. and Populus tremula L. 117 5.5.4 Soil seed bank of Sorbus aucuparia L. 118 5.6 Conclusions 119 5.7 References 120 Chapter 6 – Do birch and rowan establish soil seed banks sufficient to compensate for a lack of seed rain after forest disturbance? 134 6.1 Abstract 135 6.2 Introduction 135 6.3 Materials and methods 137 6.3.1 Study areas 137 6.3.2 Data collection 139 6.3.3. Statistical analysis 140 6.4 Results 141 6.4.1 Study A - Artificial seed burial experiment 141 6.4.2 Study B - Soil core sampling in the forest 145 6.5 Discussion 147 6.5.1 Study A - Artificial seed burial experiment 147 6.5.2 Study B - Soil core sampling in the forest 149 6.6 Conclusions 151 6.7 References 152 Chapter 7 – General discussion 160 7.1 Discussion of important aspects of regeneration ability 161 7.1.1 Fructification and seed production in Salix caprea, Betula pendula and Sorbus aucuparia 165 7.1.2 Ecological processes within the regeneration cycle of Salix caprea 167 7.1.3 Ecological processes within the regeneration cycle of Betula pendula 168 7.1.4 Ecological processes within the regeneration cycle of Sorbus aucuparia 169 7.2. Conclusions for silviculture and management recommendations 172 7.3 References 175 Table of appendix i

Colour and appearance of hardwood are of great importance for the interiorand furniture industry. The widespread use of transparent surface treatmentand a fashion that prescribe light colour on many species, means that deviationfrom the ideal have considerable impact on the industrial operations. Kilndrying is generally regarded as the process that has the greatest impact on thecolour of Nordic hardwood species. The lack of satisfactory explanation modelsfor many types of discoloration, however, complicates the control of the dryingprocess.This thesis is an attempt to increase the knowledge of which factors thatcontrol the appearance of some commonly found discolorations associated withdrying of beech, birch and oak. The main focus is on convection drying but alsothe influence of timber storage, pre-steaming and press drying has beeninvestigated for individual species. The studies have been conducted ascomparative studies based on design of experiments in which the colour wasdetermined using a colorimeter.Results show that reddish and dark discoloration of beech and birch duringconvective drying is mainly dependent on the temperature and time of exposurewhen the local moisture content exceeds the fibre saturation point. Theconversion of naturally occurring substances in birch into coloured compoundsis not due to active precursors created at high moisture content levels duringthe subsequent drying at low moisture content levels. Interior grey stain inbeech is caused by slow initial drying at low temperatures. Log storage in coldwinter and spring climate does not cause discoloration in beech. Birch becomeslighter when press-dried at high temperatures, resulting in a colour comparableto that of traditionally kiln dried wood. Steaming of oak before kiln dryingreduce the presence of brown discoloration, a general darkening of the woodoccurs at temperatures above 50°C.

Diss. (sammanfattning) Alnarp : Sveriges lantbruksuniv. / Härtill 5 uppsatser.

Diss. (sammanfattning). Umeå : Sveriges lantbruksuniv., 2003. / Härtill 6 uppsatser.

Submitted by (lucia.rodrigues@ufrpe.br) on 2016-08-23T12:51:07Z No. of bitstreams: 1 Anna Goreth de Figueiredo Almeida.pdf: 423236 bytes, checksum: 1d025c565ca6aeb9c56bee365857c606 (MD5) / Made available in DSpace on 2016-08-23T12:51:08Z (GMT). No. of bitstreams: 1 Anna Goreth de Figueiredo Almeida.pdf: 423236 bytes, checksum: 1d025c565ca6aeb9c56bee365857c606 (MD5) Previous issue date: 2009-05-22 / The use of quality seeds that assure propagation, growth and establishment of vigorous seedlings is an important point in the reforestation programs and restoration of the forest ecosystem. Therefore, the objective of this work was to study the germination and initial growth of seedlings of two native forest species, Parkia pendula (Willd.) Benth. ex Walpers and Samanea tubulosa (Benth. ) Barneby & Grimes to establish methodology for germination and vigor tests to contribute for analysis and technology of native forest seeds. The obtained information are useful for researchers and technologists of forest seeds, once in the current Rules for testing of seeds the norms and patterns ideals are not prescribed for the germination of seeds of the species in study. For dormancy breaking of Parkia pendula seeds, besides the seeds without any treatment (control), were used the following pregerminative treatments: mechanical scarification in the part distal of the seed with sandpaper for mass nº80 without and with soak for 24 hours; chemical scarification with concentrated sulfuric acid (98%) for 30 seconds, 1 and 2 minutes; submission of seeds at 10ºC for 24 and 48 hours; stratification into vermiculite at 10ºC for 24 and 48 hours; immersion in water at 80º C until cooling. Already for Samanea tubulosa seeds the first three treatments above were used increased by the following treatments: soak of intact seeds for 24 hours; chemical scarification with concentrated sulfuric acid (98%) for 15, 30 and 60 seconds; stratification into vermiculite at 18ºC ± 2 for 24 hours; immersion in water at 80º C until cooling; submission of seeds in fast drying at 80ºC for 1 minute. For evaluation of the germinativeperformance seeds of both species were tested different substrates (into sand, sugarcane bagasse, coconut fiber, waste of sisal, vermiculite and paper towel) and different temperatures (25, 30, 35, 20-30, 25-35), for the two species was used continuous light. The following parameters were evaluated: germination (%), first germination count (%), germination speed index, length of the primary root and hypocotyl, dry weight matter of seedlings. Mechanical scarification with sandpaper for mass nº 80 in the part distal of Parkia pendula and Samanea tubulosa seeds, without soak, promoted the biggest and speedy germination. The constant temperature of 30ºC and the substrates into sand and paper towel favored the germination and vigor of Parkia pendula seedlings. Samanea tubulosa seeds germinated in larger percentage and speed in the temperatures alternate 20-30 and 25-35ºC and in the substrates paper towel, into vermiculite and sand; therefore, they are recommended for evaluation of the physiological quality of these seeds. In all substrates tested, the is null or drastically reduced at 35ºC. / A utilização de sementes de qualidade, que assegurem propagação, crescimento e estabelecimento de plântulas vigorosas é um ponto importante nos programas de reflorestamento e restauração do ecossistema florestal. Por isso, o objetivo deste trabalho foi estudar a germinação e crescimento inicial de plântulas de duas espécies florestais nativas, o visgueiro (Parkia pendula (Willd.) Benth. ex Walpers) e a abobreira (Samanea tubulosa (Benth.) Barneby & Grimes), para estabelecer metodologia para testes de germinação e vigor e contribuir para análise e tecnologia de sementes florestais nativas. As informações obtidas são úteis para analistas e pesquisadores de sementes florestais, uma vez que nas Regras para Análise de Sementes (RAS) atuais não estão prescritos normas e padrões ideais para a germinação de sementes das espécies em estudo. Para a superação da dormência das sementes de visgueiro, além das sementes sem qualquer tratamento (testemunha), foram utilizados os seguintes tratamentos pré-germinativos: escarificação mecânica na parte distal da semente com lixa para massa nº80 sem e com embebição por 24 horas; escarificação química com ácido sulfúrico concentrado (98%) por 30 segundos, 1 e 2 minutos; submissão das sementes a 10ºC por 24 e 48 horas; estratificação, em vermiculita, a 10ºC por 24 e 48 horas; imersão de sementes em água a 80ºC até resfriamento. Para as sementes de abobreira, além das sementes sem qualquer tratamento (testemunha), foram utilizados os seguintes tratamentos pré-germinativos: escarificação mecânica na parte distal da semente com lixa paramassa nº80, sem e com embebição, por 24 horas; embebição das sementes intactas por 24 horas; escarificação química com ácido sulfúrico concentrado (98%) por 15, 30 e 60 segundos; estratificação das sementes, em vermiculita a 18º ± 2 por 24 horas; imersão de sementes em água a 80ºC até resfriamento; submissão das sementes em estufa a 80º C por 1 minuto. Para avaliação do desempenho germinativo de sementes de visgueiro e abobreira foram testados os substratos: entre areia, bagaço de cana, pó de coco, resíduo de sisal, vermiculita e papel toalha e diferentes temperaturas: (25, 30, 35, 20-30ºC, para visgueiro e para abobreira acrescentou-se 25-35ºC), para as duas espécies foi usada luz contínua. Foram avaliados os seguintes parâmetros: germinação (%), primeira contagem da germinação (%), índice velocidade de germinação, comprimento da raiz primária e da parte aérea, massa seca de plântulas. A escarificação mecânica, com lixa para massa nº 80, na parte distal da semente de visgueiro, sem embebição e de sementes de abobreira, com embebição por 24 horas promoveu maior e mais rápida germinação. A temperatura constante de 30ºC e os substratos entre areia e papel toalha, favoreceram a germinação e vigor das plântulas de visgueiro. As sementes de abobreira germinaram em maiores porcentagem e velocidade nas temperaturasalternadas 20-30 e 25-35ºC e nos substratos papel toalha, entre vermiculita e entre areia, sendo, portanto, recomendados para avaliação da qualidade fisiológica das sementes desta espécie. Nos substratos testados, a germinação de sementes de visgueiro e abobreira é nula ou drásticamente reduzida a 35ºC.