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  <title>T-Stor Collection:</title>
  <link rel="alternate" href="http://hdl.handle.net/11019/18" />
  <subtitle />
  <id>http://hdl.handle.net/11019/18</id>
  <updated>2017-11-06T07:37:45Z</updated>
  <dc:date>2017-11-06T07:37:45Z</dc:date>
  <entry>
    <title>Vegetative propagation of dieback-tolerant Fraxinus excelsior on</title>
    <link rel="alternate" href="http://hdl.handle.net/11019/1225" />
    <author>
      <name>Douglas, Gerry C.</name>
    </author>
    <author>
      <name>Namara, J.M.</name>
    </author>
    <author>
      <name>O'Connell, K.</name>
    </author>
    <author>
      <name>Dunne, L.</name>
    </author>
    <author>
      <name>Grant, Jim</name>
    </author>
    <id>http://hdl.handle.net/11019/1225</id>
    <updated>2017-07-27T01:01:31Z</updated>
    <published>2017-01-01T00:00:00Z</published>
    <summary type="text">Title: Vegetative propagation of dieback-tolerant Fraxinus excelsior on
Authors: Douglas, Gerry C.; Namara, J.M.; O'Connell, K.; Dunne, L.; Grant, Jim
Abstract: Ash trees which are tolerant to Hymenoscyphus fraxineus may be selected in all age classes among heavily&#xD;
infected populations. They may be produced also by controlled crossings of disease tolerant trees, because the&#xD;
genetic component of inheritance for disease tolerance is high. For mature and juvenile plant material, the&#xD;
deployment of disease tolerant genotypes could be potentially achieved by vegetatively propagating selected&#xD;
genotypes. We describe a system to vegetatively propagate selected ash genotypes and we discuss the prospects&#xD;
and options for using vegetative propagation on all age classes of trees. Mature trees were rejuvenated through&#xD;
the process of micropropagation to establish mother plants in large trays which were cut back repeatedly&#xD;
(hedged) to produce at least two crops of cuttings per year.&#xD;
The rooting capacity of ten genotypes was tested by a commercial nursery over a period of three years, to assess&#xD;
the feasibility of using hedged mother plants for efficient propagation. Commercial practise was to treat cuttings&#xD;
with 0.25% IBA, insert them in plug pots and maintain them covered with fine plastic within low plastic tunnels&#xD;
in a non heated greenhouse and without supplementary heating at the cutting base. In the first year, the mean&#xD;
rooting rate was 53 % for the first crop of cuttings and 35 % for the second. In the second and third years the&#xD;
rooting rates improved to over 80% for each crop of cuttings as experience was gained in handling the material.&#xD;
Rooting rate varied among the genotypes.&#xD;
We assessed the growth and development of micropropagated ash trees in the field from an observation clonal&#xD;
trial, consisting of four mature genotypes which had been established in 2002 in five replicate plots. The&#xD;
micropropagated trees were generally similar in height and dbh to seed derived control trees and developed&#xD;
normally. These observations are discussed in the context of using vegetative propagation as a tool in breeding&#xD;
and for the large scale deployment of ash with tolerance to H. fraxineus.
Description: book chapter; This publication is based on the work of Action FP1103 FRAXBACK,&#xD;
supported by COST (European Cooperation in Science and Technology)</summary>
    <dc:date>2017-01-01T00:00:00Z</dc:date>
  </entry>
  <entry>
    <title>Ash dieback on the island of Ireland</title>
    <link rel="alternate" href="http://hdl.handle.net/11019/1224" />
    <author>
      <name>McCracken, A.R.</name>
    </author>
    <author>
      <name>Douglas, Gerry C.</name>
    </author>
    <author>
      <name>Ryan, C.</name>
    </author>
    <author>
      <name>Destefanis, M.</name>
    </author>
    <author>
      <name>Cooke, L.R.</name>
    </author>
    <id>http://hdl.handle.net/11019/1224</id>
    <updated>2017-07-27T01:01:30Z</updated>
    <published>2017-01-01T00:00:00Z</published>
    <summary type="text">Title: Ash dieback on the island of Ireland
Authors: McCracken, A.R.; Douglas, Gerry C.; Ryan, C.; Destefanis, M.; Cooke, L.R.
Abstract: On the island of Ireland it is estimated that there are over half a million kilometres of hedgerows (400,000+ km&#xD;
in the Republic of Ireland (Rep. Ireland) and 113,000+ in Northern Ireland (Northern Ireland). Ash (Fraxinus&#xD;
excelsior) is the second most important component, after hawthorn (Crataegus monogyna), in large proportions&#xD;
of this hedgerow network. In the Rep. Ireland over 20,000 ha of ash have been planted since 1990, primarily for&#xD;
sawlogs and to provide material for the manufacture of hurleys, which are used in an important national sport&#xD;
called hurling, and for camogie sticks used to play camogie. Ash dieback, caused by Hymenoscyphus fraxineus,&#xD;
was first identified on the island in October 2012 and since then has been detected at 306 sites (195 in Rep.&#xD;
Ireland and 111 in Northern Ireland). In the vast majority of cases the outbreaks have been on young, imported&#xD;
trees planted within the previous 5 – 6 years and it was evident that the pathogen had been introduced on trees&#xD;
for planting. On a small number of occasions there was evidence of the pathogen cycling within a plantation or&#xD;
moving from the plantation to infect neighbouring hedgerow trees. One possible mechanism by which the&#xD;
pathogen can build up sufficient inoculum is by the formation of apothecia on infected woody tissue high up on&#xD;
the plants. Rep. Ireland and Northern Ireland have strict policies of eradication and containment, as set out in the&#xD;
All-Ireland Chalara Control Strategy. To date over 2.1 million trees have been destroyed as part of an&#xD;
eradication strategy. It is considered that this prompt and far-reaching action has had a significant impact,&#xD;
significantly mitigating and preventing the rapid establishment of the pathogen and limiting its spread. The&#xD;
interventions since the disease was first confirmed have helped to protect the considerable investment in ash&#xD;
plantations of the last 20 years. The pathogen has not, however, been eradicated from the island of Ireland and it&#xD;
remains to be seen how widespread, and how quickly ash dieback will become established on the island of&#xD;
Ireland. The latest figures from the Republic of Ireland are that 733 hectares of ash plantation has been&#xD;
reconstituted with another species as a result of Chalara and this has cost our state €2.6 million so far; in&#xD;
addition, Chalara has been found and confirmed in all 26 counties of the Republic of Ireland to a greater or lesser&#xD;
extent. As a result the current policies and procedures regarding Chalara are under review.
Description: Book section; This publication is based on the work of Action FP1103 FRAXBACK,&#xD;
supported by COST (European Cooperation in Science and Technology)</summary>
    <dc:date>2017-01-01T00:00:00Z</dc:date>
  </entry>
  <entry>
    <title>Morphological and physiological responses of Fagus sylvatica and Quercus robur seedlings to light availability</title>
    <link rel="alternate" href="http://hdl.handle.net/11019/1098" />
    <author>
      <name>Sevillano, Ignacio</name>
    </author>
    <id>http://hdl.handle.net/11019/1098</id>
    <updated>2017-01-10T02:01:34Z</updated>
    <published>2016-06-01T00:00:00Z</published>
    <summary type="text">Title: Morphological and physiological responses of Fagus sylvatica and Quercus robur seedlings to light availability
Authors: Sevillano, Ignacio
Abstract: The need to develop forest management systems other than clearfelling has resulted in a requirement for improved understanding of the potential of continuous cover forestry (CCF). One suggested method for the conversion of forest stands into CCF systems and for bringing under-performing forests into productivity is thinning in conjunction with underplanting. This study was an attempt to provide information on species suitability for underplanting of two important trees in European forestry: pedunculate oak (Quercus robur L.) and European beech (Fagus sylvatica L.). To determine the morphological, physiological and growth responses of these two species to different light conditions, beech and oak seedlings previously grown at full light for two years were covered by shading nets that provide different shade levels (62%, 51% or 28% of full light) or continued to be exposed to full light. The different shade levels were intended to mimic a range of underplanted conditions and the process of acclimation to shade was studied to provide information on the ecology and adaptation of underplanted seedlings. In addition to the controlled-shade experiment another study to determine the physiological responses of beech natural regeneration to shade was conducted under natural light conditions (from open gaps to closed canopy).&#xD;
Both oak and beech displayed similar acclimation in response to shade for most of the traits investigated. At the plant level, seedling acclimation to shade included higher biomass allocation to above than below-ground parts and greater energy investment on height than diameter growth. At the leaf level, seedlings grown under shade reduced their leaf thickness and photosynthetic rates per unit area and increased their specific leaf area. This increase in specific leaf area seems to be one mechanism that allows seedlings to perform well under shade conditions. Another acclimation to low light conditions was to increase the efficiency of the photosystem II under shade. Photosynthetic rates were higher and leaves were retained for longer in seedlings grown at full light than under shade. Hence, this probably led to a greater growth in the full light than under shade. Despite this greater growth at full light, the results of this study suggest that beech and oak seedlings would be able to acclimate and perform well if underplanted below overstories that reduce the available light to as low as 28% of full light without having any significant adverse effect on the quality of the final crop.
Description: Doctoral thesis</summary>
    <dc:date>2016-06-01T00:00:00Z</dc:date>
  </entry>
  <entry>
    <title>Broadleaf thinning in Ireland - a review of European silvicultural best practice</title>
    <link rel="alternate" href="http://hdl.handle.net/11019/1096" />
    <author>
      <name>Hawe, Jerry</name>
    </author>
    <author>
      <name>Short, Ian</name>
    </author>
    <id>http://hdl.handle.net/11019/1096</id>
    <updated>2017-02-02T02:01:17Z</updated>
    <published>2016-01-01T00:00:00Z</published>
    <summary type="text">Title: Broadleaf thinning in Ireland - a review of European silvicultural best practice
Authors: Hawe, Jerry; Short, Ian
Abstract: A substantial first-rotation broadleaf plantation resource in Ireland is progressively entering a thinning phase. Silvicultural best practice in support of such a management intervention needs to be developed for this new woodland resource to achieve its maximum commercial potential. National research trials are key to the provision of information for the development of best practice. Determining the current state-of-the-art is a prerequisite to the design and implementation of appropriate research trials. This study reviews the literature concerning the fundamental principles of broadleaf thinning with particular regard to timing, intensity and impacts on crop tree growth response, focussing on a range of commonly planted broadleaf species in Ireland. The overall aim of this review is to gain a fuller understanding of the most effective thinning methodology to be employed to maximise the production of high quality hardwood timber. In doing so it is intended that the information presented may support ongoing and future research trials with regard to potential silvicultural treatments to apply, data types and analysis and the likely results of practical application to commercial forestry.
Description: peer-reviewed; This work was carried out as part of the Broadleaf Silviculture Research and Development (B-SilvRD) project, a 5-year project funded by CoFoRD, Department of Agriculture, Food and the Marine.</summary>
    <dc:date>2016-01-01T00:00:00Z</dc:date>
  </entry>
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