Prospect 2.1 for Windows - User's Guide
Prospect 2.1 for Windows - User's Guide
Prospect 2.1 for Windows - User's Guide
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Developed to encourage the sustainable use<br />
of the world’s timber species, <strong>Prospect</strong> is<br />
the definitive database <strong>for</strong> all who research<br />
and use wood.
<strong>Prospect</strong>: the Wood Database<br />
(Version <strong>2.1</strong> <strong>for</strong> <strong>Windows</strong>)<br />
The following guide comprises of two parts: the first, describes <strong>Prospect</strong>’s background, the<br />
reasoning behind its development and details links to WCMC (World Conservation<br />
Monitoring Centre); the second part, provides a User’s <strong>Guide</strong> to the system, describing the<br />
installation procedure and system requirements, the contents and operation of the database,<br />
how data recorded can be presented to the user and how the relationship between a timber’s<br />
properties and its possible uses can be used to survey that in<strong>for</strong>mation.<br />
Acknowledgments<br />
The development of the <strong>Prospect</strong> database has been financed since its inception by the<br />
Overseas Development Administration of the British Government whose support is<br />
gratefully acknowledged. Special thanks also to Prof. Burley, Bob Plumptre, Julie Smith,<br />
Cath Dorey, Victor Burclaff, John Brazier, Simon Forrester, Sequel Design, xylarium and<br />
library support staff at the Ox<strong>for</strong>d Forestry Institute and all those who have contributed<br />
towards the development of the <strong>Prospect</strong> database.<br />
Copyright Notice<br />
Copyright of <strong>Prospect</strong>: the Wood Database, and documentation belongs to the Ox<strong>for</strong>d<br />
Forestry Institute (OFI). This product may not be used, sold, transferred, copied or<br />
reproduced, in any manner or <strong>for</strong>m, or in any medium, to any person other than with the<br />
prior consent of the OFI.<br />
All possible care has been taken in the preparation of this product, but the Ox<strong>for</strong>d Forestry<br />
Institute accepts no liability <strong>for</strong> any inaccuracies that may be found. The OFI will not be<br />
held liable <strong>for</strong> any damages, however caused, arising out of the use or inability to use this<br />
product or documentation.<br />
The Ox<strong>for</strong>d Forestry Institute reserves the right to revise all software and documentation<br />
relating to <strong>Prospect</strong> and to make changes to the database content without obligation to<br />
notify any person or organisation of this revision or change.<br />
© 1997-2004 Ox<strong>for</strong>d Forestry Institute. All Rights Reserved.
Contents<br />
Part 1 - Background<br />
1. Introduction i<br />
2. The need <strong>for</strong> <strong>Prospect</strong> i<br />
<strong>2.1</strong> Forest Degradation and Destruction i<br />
2.2 Management and Species Use ii<br />
2.3 Effects of Creaming ii<br />
2.4 Methods of Avoiding Creaming iii<br />
2.5 Disadvantages of Mixed Tropical Forest as a Resource Base iii<br />
2.6 Implications of Removing More Species iii<br />
2.7 Advantages to Management of Being Able to Utilise More Species iv<br />
References<br />
v<br />
3. Additional Data Sources vi<br />
3.1 World Conservation Monitoring Centre vi<br />
Part 2 - User’s <strong>Guide</strong><br />
1. Introduction 1<br />
2. Database Contents 1<br />
<strong>2.1</strong> Species Taxonomy 1<br />
2.2 Species Distribution 1<br />
2.3 Timber Properties 2<br />
2.4 End-Uses 2<br />
2.5 Wood Surface Images 2<br />
2.6 References 2<br />
3. Installation 3<br />
3.1 System Requirements 3<br />
3.2 Installation Instructions 3<br />
3.3 <strong>Prospect</strong> Setup 3<br />
3.4 Text Files 3<br />
3.5 Running <strong>Prospect</strong> 4<br />
3.6 Troubleshooting 4<br />
3.7 Removing <strong>Prospect</strong> 4<br />
3.8 Problems 4<br />
4. Basic Operating Hints 5<br />
5. A <strong>Prospect</strong> Session 6<br />
5.1 Search by species name 10<br />
5.2 Search by data content 19<br />
5.3 Search by multiple properties 25<br />
5.4 Potential end-uses <strong>for</strong> a species 38<br />
5.5 Summaries of database contents 44<br />
5.6 References 51<br />
5.7 Exit 53<br />
6. Appendices 54<br />
Appendix 1. Technical Aspects of <strong>Prospect</strong> 54<br />
Appendix 2. List of Timber Properties 56<br />
Appendix 3. List of End-Uses 62<br />
Appendix 4. List of Countries/Geographical Regions 63<br />
Appendix 5. List of Species 64
<strong>Prospect</strong>: The Wood Database - Background<br />
Contents<br />
1. Introduction i<br />
2. The Need <strong>for</strong> <strong>Prospect</strong> i<br />
<strong>2.1</strong> Forest Degradation and Destruction i<br />
2.2 Management and Species Use ii<br />
2.3 Effects of Creaming ii<br />
2.4 Methods of Avoiding Creaming iii<br />
2.5 Disadvantages of Mixed Tropical Forest as a Resource Base iii<br />
2.6 Implications of Removing More Species iii<br />
2.7 Advantages to Management of Being Able to Utilise More Species iv<br />
References<br />
v<br />
3. Additional Data Sources vi<br />
3.1 World Conservation Monitoring Centre vi
1. Introduction<br />
Since its inception in 1981, (as a result of a recommendation made at the 11th Commonwealth<br />
Conference in 1980), <strong>Prospect</strong>: The Wood Database has been revised and expanded to<br />
accommodate the needs of a wide range of people involved with <strong>for</strong>est management, timber<br />
conversion, and utilisation. This introduction attempts to explain the increasing importance and<br />
general usefulness of the database, whilst also considering the contribution that it can make<br />
towards aiding decision making processes with respect to such matters as timber sourcing,<br />
certification, and the various objectives and targets set by governments, industry and NGO's<br />
aimed at securing supplies of timber from 'sustainable' or 'well managed' <strong>for</strong>ests. It would seem<br />
that much debate continues to centre around defining these terms, not only between interested<br />
parties at national and international level but also between producers and consumers whose voice<br />
is increasingly being heard with persuasive effect. Whatever the outcome of this altercation, the<br />
definition of such terms will probably be subject to constant evaluation and revision, not only<br />
because of the need to consider such a broad range of social and <strong>for</strong>est management objectives,<br />
but also as a result of the need to assess how harvesting, availability, and quality of a broad range<br />
of over/well used species effects <strong>for</strong>est composition, biodiversity, and the local economy. To<br />
facilitate, not only the promotion of these lesser known species where it is considered to be of<br />
benefit, but also to ensure that processing secures maximum end product value and consumer<br />
satisfaction, access to the wide range of data on timber properties is considered essential.<br />
<strong>Prospect</strong>: The Wood Database, has been designed to enable the user, either to undertake a broad<br />
based search so that a general assessment can be made of a species characteristics, or specific<br />
data can be accessed with respect to a particular property or reference. The real benefit of the<br />
<strong>Prospect</strong> database however, lies in its ability, in an authoritative and transparent manner, to<br />
assess a particular species <strong>for</strong> an end-use or, given an end use, rank species roughly in order of<br />
suitability.<br />
2. The Need <strong>for</strong> <strong>Prospect</strong><br />
The assertion that the <strong>Prospect</strong> database is designed to encourage the use of more timbers<br />
(particularly those of tropical origin), is often met with disbelieve and seen as contrary to the<br />
general desire to conserve and protect the diminishing tropical <strong>for</strong>est resource. However, apart<br />
from the maxim 'use it or loose it', there are a number of very good reasons why the prudent<br />
utilisation of more timber species helps to conserve, and indeed stimulate, the structure of the<br />
<strong>for</strong>est. The following account looks at some of the causes of <strong>for</strong>est destruction, and why<br />
increasing the range of species harvested can significantly improve the effectiveness of <strong>for</strong>est<br />
management.<br />
<strong>2.1</strong> Forest Degradation and Destruction<br />
It is important that these two terms are clearly defined and distinguished, they are frequently<br />
misunderstood and incorrectly considered synonymous. Degradation is the impoverishment of<br />
the <strong>for</strong>est in terms of numbers of species or their relative quantities per unit area; it also indicates<br />
a reduction in the capacity of the <strong>for</strong>est to provide the goods and services that it was <strong>for</strong>merly<br />
capable of providing. Destruction is a much stronger term; it involves complete removal of tree<br />
cover and the elimination of most or all of the associated flora and fauna in that location.<br />
Recovery from this state may take several hundred years, assuming no human interference,<br />
(Keenan & Kimmins 1993), whereas recovery from degradation may be relatively rapid if<br />
adequate safeguards are implemented to limit the negative effects of timber extraction such as<br />
soil compaction.<br />
Tropical <strong>for</strong>est degradation and destruction and possible methods of combating them have been<br />
well documented (Lanly 1982, Brundtland et al. 1987, Poore et al. 1989, Repetto and Gillis 1988,<br />
World Resources Institute 1992). Total destruction almost always results from clearance of <strong>for</strong>est<br />
<strong>for</strong> agriculture, sometimes accelerated by access provided by logging roads, while degradation<br />
can result from overlogging or a variety of other factors such as fuel cutting, charcoal burning, or<br />
grazing. Ultimately, the prevention of these processes can only be achieved by determined and<br />
effective management. This requires a decision not only from governments but also from wood<br />
users and the population as a whole, that these destructive processes must be controlled. It is<br />
essential that these <strong>for</strong>est management practices provide <strong>for</strong> the needs of the people by securing<br />
i
oth <strong>for</strong>est and agricultural products. Depletion of timber supplies robs developing countries of a<br />
crucial source of <strong>for</strong>eign exchange (WRI 1992). Failure to realize the full implications of not<br />
adopting integrated land use policies nearly always results, not only in <strong>for</strong>est loss, but also in<br />
agricultural and social degradation.<br />
2.2 Management and Species Use<br />
Forest Destruction<br />
The attempts that have been made to devise methods of reducing or halting these destructive<br />
processes are equally well documented, both in texts so far cited, and in numerous International<br />
Tropical Timber Organization (ITTO) reports, (ITTO 1990, Plumptre et al. 1991). All 53 ITTO<br />
member countries have now pledged themselves to manage their <strong>for</strong>ests sustainably by the year<br />
2000 under the 'Sustainability 2000' agreement (ITTO 1996).<br />
Destruction results from people cutting down the <strong>for</strong>est and turning the land over to some other<br />
<strong>for</strong>m of use. This can be the result of a planned process where there may be good reasons <strong>for</strong><br />
removing the <strong>for</strong>est. It is, <strong>for</strong> instance, unrealistic to expect a country with 80% <strong>for</strong>est cover, not<br />
to clear some of it to make way <strong>for</strong> agriculture to cater <strong>for</strong> a growing population. Frequently,<br />
however, destruction results from inadequate planning, or sometimes an inability or a lack of<br />
determination to implement plans. Once destruction of natural <strong>for</strong>est occurs, only plantations will<br />
re-instate <strong>for</strong>est in a reasonable length of time and invariably the full biological diversity of the<br />
<strong>for</strong>est is lost. Shifting cultivation may not completely remove this diversity but it severely<br />
reduces it.<br />
Forest Degradation : ‘Creaming’<br />
Forest degradation usually results from poor management. It frequently starts with 'creaming' of<br />
the <strong>for</strong>est <strong>for</strong> the best species: the mahoganies, afrormosia and iroko in Africa; mahoganies,<br />
rosewoods and cedar in South and Central America; rosewood, sandalwood and teak in India and<br />
Burma and the blackwoods throughout the tropics. Creaming usually occurs because net revenue<br />
per cubic metre utilised of a valuable species is greater, often very much greater, than <strong>for</strong> the less<br />
valuable trees; the market is assured, methods of handling the timber are known, export markets<br />
<strong>for</strong> the wood (and there<strong>for</strong>e access to <strong>for</strong>eign exchange) may be available; the timber is usually<br />
durable, frequently stable, and consequently tolerant of misuse such as inadequate seasoning.<br />
When the best species have been depleted the next best come into use and, in the absence of<br />
alternative supplies, the worst will eventually be used. There are very few woods that will not<br />
find a use if there is an acute shortage of timber. The final product may not be as good but<br />
'beggars cannot be choosers'; throughout most of the world there are few economically feasible<br />
alternatives to timber <strong>for</strong> most of its uses. The rule of the marketplace, there<strong>for</strong>e, is: 'take the best<br />
and the most profitable first and the less good only when you are <strong>for</strong>ced to do so'.<br />
2.3 Effects of Creaming<br />
The creaming of <strong>for</strong>est is an insidious, wasteful and destructive process. It removes the best<br />
species, usually reducing their capability to regenerate and compete with other species; it may also<br />
reduce the genetic quality of these species because there is often selection against the best<br />
individuals in the population. Many high value tropical species are of medium density and<br />
strength; they are neither the very fast growing, low density light demanders, nor the very high<br />
density, slow growing shade tolerant 'ironwoods'. They are, there<strong>for</strong>e, often moderately light<br />
demanding and regenerate best under some, but not too much shade. In Africa and South America,<br />
where the number of species marketed is relatively small in comparison with the total number<br />
available, creaming does not usually open the canopy sufficiently to favour regeneration of these<br />
species, whether naturally or artificially. In South East Asia however, the large proportion of<br />
medium density species with similar properties tends to lead to more intensive use of the <strong>for</strong>est<br />
which may be too intensive in some places. Here creaming is often less of a danger than the failure<br />
to control the size of trees taken and the total volume of timber removed per hectare at any given<br />
felling. Whitmore (1991) describes in detail the results of recent research into the ecological<br />
requirements of different species and types of <strong>for</strong>est.<br />
ii
2.4 Methods of Avoiding Creaming<br />
There are three main methods which can be used to reduce the incentive to cream <strong>for</strong>ests. One is to<br />
set ‘royalties’ or <strong>for</strong>est fees <strong>for</strong> standing timber at such a rate that it is equally profitable to cut,<br />
process and market valuable as well as non-valuable species. In many tropical countries this would<br />
be a difficult to establish, mainly because a detailed knowledge of production costs <strong>for</strong> different<br />
species, as well as the likely revenue obtainable from the different end products, would be very<br />
hard to quantify. There is also likely to be strong resistance from the local timber trade to such an<br />
idea, which relies on the valuable species to produce the major part of its revenue; high fees on<br />
valuable species may have to be balanced by very low fees on the low value trees. A second way is<br />
to improve the technology used to process the wood so as to add value to low value timbers.<br />
Finally, the third way, is to improve the marketing of the products and identify 'niche' uses <strong>for</strong><br />
previously low value timbers in order to obtain a higher value <strong>for</strong> them.<br />
2.5 Disadvantages of Mixed Tropical Forest as a Resource Base<br />
The large number of intimately mixed species in this <strong>for</strong>est result in low quantities of any one in a<br />
given area. If markets are demanding in their requirements, particularly in terms of appearance of<br />
the wood, which is common <strong>for</strong> many export markets, then it is difficult to market timbers except<br />
as individual species; this in turn makes it difficult to supply enough of any one species to supply a<br />
large market demand.<br />
The result over most of the tropics, except in parts of South and South East Asia, has been low<br />
percentage utilisation of the resource both in terms of available species and of yield per hectare<br />
which, historically, has varied between 0.3 and 2.0 m 3 ha -1 yr -1 . More recently this has increased, in<br />
Africa, with Benin logging 4 m 3 ha -1 yr -1 and Nigeria 35 m 3 ha -1 yr -1 . In South America, Brazil<br />
logging 6 m 3 ha -1 yr -1 and Costa Rica 22 m 3 ha -1 yr -1 . In Asia, Laos logging 12 m 3 ha -1 yr -1 and the<br />
Philippines 83 m 3 ha -1 yr -1 . (FAO 1990). In addition, the percentage utilisation of the individual<br />
tree has been low with only prime logs from the bole being used and branchwood discarded<br />
(Berger 1990).<br />
2.6 Implications of Removing More Species<br />
If the commercially profitable use of a larger number of species is achieved there will be less<br />
incentive to cream the <strong>for</strong>est and trees will tend to be removed in proportion to their natural<br />
occurrence in the <strong>for</strong>est. Even without any management this might merely result in the removal of<br />
all trees in the <strong>for</strong>est over the diameter which can economically be processed; the result would be a<br />
very open and immature canopy but it would probably still leave small trees on the ground roughly<br />
in the proportions in which they originally occurred. Subsequent regeneration, because of the<br />
openness of the canopy, would favour light demanders over shade tolerant trees but the <strong>for</strong>est<br />
would only be set back a few stages in its natural succession and most of the natural diversity<br />
would probably be retained. Very heavy fellings, however, cause a large amount of damage to the<br />
saplings and regeneration on the <strong>for</strong>est floor even though the destruction is often less than might be<br />
expected (Whitmore 1991). This type of situation, is by no means desirable but probably better<br />
than uncontrolled creaming. Lack of effective tropical <strong>for</strong>est harvesting and silvicultural<br />
management is, there<strong>for</strong>e, bad <strong>for</strong> the <strong>for</strong>est if many species are taken, but not necessarily any<br />
worse, than if the <strong>for</strong>est is creamed <strong>for</strong> just a few. From the short term point of view of utilising the<br />
existing resource, it is far better to remove and make useful products from a large volume per<br />
hectare of many species, than a small volume per hectare of a few. In this way, a smaller area of<br />
<strong>for</strong>est is degraded to supply a given demand <strong>for</strong> timber. The case <strong>for</strong> using more species is,<br />
there<strong>for</strong>e, good even if management is poor.<br />
In the worst case scenario it is possible that the indiscriminate removal of a large number of<br />
species is worse than creaming <strong>for</strong> a few. However, it should be noted that in the latter case the<br />
iii
temptation to re-enter the <strong>for</strong>est is often too great and further removals usually result.<br />
Consequently, regardless of the number of species initially harvested, there is no real alternative to<br />
some <strong>for</strong>m of management, <strong>for</strong> without it, the <strong>for</strong>est will eventually be destroyed.<br />
2.7 Advantages to Management of Being Able to Utilise More Species<br />
The exact silvicultural requirements <strong>for</strong> species and volume removal by harvesting will vary<br />
according to the type of <strong>for</strong>est and the objectives of management. These objectives can vary from<br />
retaining <strong>for</strong>est composition as close as possible to the natural state of the <strong>for</strong>est at one extreme,<br />
to optimising the growth of the valuable species without unduly affecting the diversity of the<br />
<strong>for</strong>est. It is assumed that the conversion of the <strong>for</strong>est to a monoculture or semi-monoculture is not<br />
desired.<br />
Mahogany (Swietenia macrophylla) in Central America is a good example; the species<br />
regenerates naturally after hurricanes and fires but does not do so easily under a closed canopy.<br />
In order to ensure that there is mahogany in the future, fairly drastic opening of the canopy will<br />
be required. The same is true of the African mahoganies, iroko and some of the South East Asian<br />
dipterocarps but the actual conditions required will vary from one ecological community to<br />
another. There is a danger of removing too much, but there is also a danger of removing too little<br />
once management is in place and providing some protection from the natural hazards to which<br />
the <strong>for</strong>est has been exposed in the past. Complete protection would eventually result in <strong>for</strong>est<br />
composed of mainly shade tolerant climax species, almost certainly less biodiversity and a set of<br />
hard heavy timbers which are difficult to utilise. Conversely, overcutting can result in almost<br />
pure crops of extreme light demanders, climber tangles and a reduction of the populations of the<br />
shade tolerant species; this again may result in lower biodiversity. Good inventories of <strong>for</strong>est<br />
composition provide essential in<strong>for</strong>mation which is required be<strong>for</strong>e sizable management<br />
decisions can be taken.<br />
When effective management of production <strong>for</strong>est is established, the great advantages of being<br />
able to harvest and use profitably a large number of species become fully apparent. If all species<br />
can be used, management merely consists of specifying which trees should not be felled because<br />
they must be kept <strong>for</strong> silvicultural or environmental reasons. Minimum diameter limits can be set<br />
below which trees of any given species must not be felled and these will not be the same <strong>for</strong> all<br />
species. Trees with sapwood that is different from the (valuable) heartwood will often be grown<br />
to a larger size than trees whose sapwood and heartwood can both be used <strong>for</strong> the same purpose.<br />
Trees which only grow to a small size (<strong>for</strong> instance some of the understorey trees) often inhibit<br />
the growth of regeneration of the valuable species, these can be felled at lower diameters than the<br />
larger trees. Many of the smaller trees grow to sizes that are quite large enough to be used in<br />
sawmills equipped to cut logs down to 20-30cm in diameter. Equipping a sawmill to cut this size<br />
of log is not usually costly if it is already capable of cutting larger logs. Trees that need to be kept<br />
to provide seed, or to give shade, can be left to grow larger than others. Trees that provide food<br />
<strong>for</strong> wildlife or non-timber products, valuable to man, can be grown to large sizes. The facility to<br />
use all or most species provides silviculturalists with the options they need, so that a more<br />
flexible approach to <strong>for</strong>est management can be adopted, while allowing <strong>for</strong>est managers to<br />
supply the <strong>for</strong>est industry with sufficiently large volumes of timber per hectare to make it<br />
profitable to operate.<br />
Access to a thorough knowledge of the properties and potential uses of as many species as<br />
possible is, there<strong>for</strong>e, extremely valuable to any <strong>for</strong>est manager, <strong>for</strong> without this knowledge,<br />
effective management is very difficult.<br />
iv
References<br />
Berger, R. (1990) Malaysia's Forests: A Resource Without a Future? Packard Chichester. 216p.<br />
Brundtland, G.H. et. al. (1987) Our common future: The World Commission on Environment and<br />
Development. Ox<strong>for</strong>d University Press. 383p.<br />
Food and Agriculture Organisation of the United Nations (FAO). Forest Resources Assessment<br />
1990. (1990) FAO Forestry Paper 112. 59p.<br />
ITTO, (1990) Selection and introduction of lesser known and lesser used species <strong>for</strong> specific enduses.<br />
Final report of ITTO project PD 18/87 Rev 1(1). 15p.<br />
ITTO, (1996) Ten years of progress ITTO 35p.<br />
Keenan. R.J. and Kimmins. J.P. (1993). The ecological effects of clearcutting. Environ. Rev. Vol.1.<br />
121-138<br />
Lanly, J.P., (1982) Tropical <strong>for</strong>est resources. Tropical Forestry Papers No. 30., Ox<strong>for</strong>d Forestry<br />
Institute, U.K. 106p.<br />
Plumptre, R.A., Jayanetti, L., Fraser, A.I., Fawcett, T., Elliott, G.K. and Gane M., (1991) Incentives<br />
in producer and consumer countries to promote sustainable development of tropical <strong>for</strong>ests. OFI &<br />
TRADA report to ITTO. 71p.<br />
Poore, D., Burgess, P., Palmer, J., Rietbergen, S. and Synnott, T. (1989) No timber without trees.<br />
Earthscan Publications, London. 252p.<br />
Repetto, R. and Gillis, M., Eds. (1998) Public policies and the misuse of <strong>for</strong>est resources.<br />
Cambridge University Press. 432p<br />
World Resources Institute, (1992) World Resources. A report by WRI, UNEP and UNDP, Ox<strong>for</strong>d<br />
University Press. 385p.<br />
Whitmore, T.C. (1991) An introduction to tropical rain<strong>for</strong>ests. Ox<strong>for</strong>d University Press. 226p.<br />
v
3. Additional Data Sources<br />
3.1 The World Conservation Monitoring Centre (WCMC)<br />
WCMC is internationally recognised as a centre of excellence in the location and management<br />
of in<strong>for</strong>mation on the conservation and sustainable use of the world’s living resources.<br />
Since <strong>Prospect</strong>’s inception in 1981, the Ox<strong>for</strong>d Forestry Institute has worked closely with<br />
WCMC to investigate and establish improved methods of data dissemination. As a result of<br />
these ef<strong>for</strong>ts we have managed to indicate which species recorded on <strong>Prospect</strong> have further<br />
conservation status data available from WCMC (see Appendix 5). Many species are unevenly<br />
distributed over large geographical areas with the result that variation in threat category (where<br />
ascertained), exist from region to region, furthermore, these data on which threat categories are<br />
based are subject to constant revision and reassessment.<br />
The Government of the Netherlands is funding a three-year collaborative project in support of<br />
the worldwide conservation of trees. WCMC and SSC (Species Survival Commission) are the<br />
major partners and are working closely with a wide range of other national and international<br />
organisations to develop a Tree Conservation In<strong>for</strong>mation Service. The goal of this project is to<br />
provide a reliable and up-to-date in<strong>for</strong>mation service on the distribution, conservation status,<br />
local uses and economic values of tree species worldwide, in order to assist countries in the<br />
planning of sustainable <strong>for</strong>est management and biodiversity conservation, through appropriate<br />
international or intergovernmental processes. Particular outputs of this project have been<br />
identified as follows:<br />
· World List of Threatened Trees using the new IUCN (World Conservation Union) threat<br />
categories<br />
· Report on sustainability of tree utilisation<br />
· World Tree Database, made available to users in electronic <strong>for</strong>mat<br />
· On-line access to tree conservation in<strong>for</strong>mation<br />
· The development of an SSC Trees Network<br />
For further in<strong>for</strong>mation on The Conservation and Sustainable Management of Trees project,<br />
please contact:<br />
In<strong>for</strong>mation Officer,<br />
World Conservation Monitoring Centre,<br />
219 Huntingdon Road,<br />
Cambridge,<br />
CB3 0DL,<br />
U.K.<br />
E-mail:<br />
WCMC URL:<br />
info@wcmc.org.uk<br />
http://www.wcmc.org.uk<br />
Tel: +44 1223 277314<br />
Fax: +44 1223 277136<br />
vi
<strong>Prospect</strong>: The Wood Database - User’s <strong>Guide</strong><br />
Contents<br />
1. Introduction 1<br />
2. Database Contents 1<br />
<strong>2.1</strong> Species Taxonomy 1<br />
2.2 Species Distribution 1<br />
2.3 Timber Properties 2<br />
2.4 End-Uses 2<br />
2.5 Wood Surface Images 2<br />
2.6 References 2<br />
3. Installation 3<br />
3.1 System Requirements 3<br />
3.2 Installation Instructions 3<br />
3.3 <strong>Prospect</strong> Setup 3<br />
3.4 Text Files 3<br />
3.5 Running <strong>Prospect</strong> 4<br />
3.6 Troubleshooting 4<br />
3.7 Removing <strong>Prospect</strong> 4<br />
3.8 Problems 4<br />
4. Basic Operating Hints 5<br />
5. A <strong>Prospect</strong> Session 6<br />
5.1 Search by species name 10<br />
5.2 Search by data content 19<br />
5.3 Search by multiple properties 25<br />
5.4 Potential end-uses <strong>for</strong> a species 38<br />
5.5 Summaries of database contents 44<br />
5.6 References 51<br />
5.7 Exit 53<br />
6. Appendices 54<br />
Appendix 1. Technical Aspects of <strong>Prospect</strong> 54<br />
Appendix 2. List of Timber Properties 56<br />
Appendix 3. List of End-Uses 62<br />
Appendix 4. List of Countries/Geographical Regions 63<br />
Appendix 5. List of Species 64
1. Introduction<br />
This guide is designed to show how to install ‘<strong>Prospect</strong> the Wood Database’, how the system<br />
operates, how the data it records can be presented to the user, and how the relationship between a<br />
timber's properties and its possible uses can be used to survey that in<strong>for</strong>mation.<br />
An outline of the structure and content of the database is given and general guide-lines are<br />
provided on operating the program, understanding selection procedures and accessing the<br />
context-sensitive help. The main part of this guide takes the <strong>for</strong>m of a <strong>Prospect</strong> session,<br />
examining the functions of each section of the program.<br />
The <strong>Prospect</strong> database currently contains in<strong>for</strong>mation <strong>for</strong> 1552 species. Of these, there are<br />
approximately 64 softwoods, and 45 species (coded by a ~) are listed as plantations species,<br />
where the data has come from plantation grown timber, some species appearing twice - one<br />
with data from plantation grown timber and one with data from natural <strong>for</strong>est grown timber. In<br />
terms of distribution the majority of species included are tropical, approximately, 40% Asian,<br />
30% African and 30% Central and South American species, with a small number of temperate<br />
species.<br />
2. Database Contents<br />
<strong>Prospect</strong> records a wide range of in<strong>for</strong>mation <strong>for</strong> each species, covering the following areas:-<br />
General in<strong>for</strong>mation<br />
Taxonomy: botanical names and synonyms/misapplied names<br />
Vernacular names: trade/commercial and common/local names<br />
Distribution: occurrence by country or geographical regions<br />
Timber in<strong>for</strong>mation<br />
Timber properties<br />
Known end-uses<br />
Wood surface images<br />
References<br />
Publications used in the data extraction<br />
<strong>2.1</strong> Species Taxonomy<br />
Species names are recorded in terms of family, genus, specific name and authority. A list of the<br />
species currently included in <strong>Prospect</strong> is shown in Appendix 5, ~ indicating that the data <strong>for</strong> a<br />
particular species refers to plantation grown trees. Vernacular names are registered as either a<br />
trade/commercial name, or a common/local name. Each common name is recorded with a link<br />
to its associated literature source. The general content in the <strong>for</strong>m of static lists relating to<br />
properties, distribution and taxonomy can be accessed through the Summaries of database<br />
contents section of the Program (see later section).<br />
2.2 Species Distribution<br />
The distribution of each species is described in terms of its known occurrence in a country or<br />
general geographical region selected from predefined lists of countries and regions (see<br />
Appendix 4 and the Summaries of database contents section).<br />
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2.3 Timber Properties<br />
The features of the timber are based on a predefined list of 92 properties, and are grouped into<br />
12 sections (property groups). Each property is defined by a possible list of descriptors. Data of<br />
a numerical nature are entered into predefined size classes. The system has the capability to<br />
record up to 20 different data sources <strong>for</strong> each timber property and any relevant conditions<br />
under which they were evaluated. These multiple data entries can be displayed to illustrate any<br />
variation of opinion in the published literature and allows the user to make their own<br />
interpretation of the data. Each data item is coupled with the reference source from which it was<br />
extracted. General comments or observations relating to any property of a given species and<br />
also the technical definition and related in<strong>for</strong>mation can be displayed. Detailed descriptions of<br />
the recorded properties are shown in Appendix 2.<br />
2.4 End-Uses<br />
Recognised end-uses are based on a predefined list, of 175, and are recorded within the same<br />
data structure as the timber properties, but with three fixed categories denoting the known<br />
degree of use. Details of the end-uses and descriptors are shown in Appendix 3.<br />
2.5 Wood Surface Images<br />
Wood surface images are provided <strong>for</strong> the majority of species, and can be displayed throughout<br />
the database, wherever there is access to a Species Home Page and in the Summaries of<br />
database contents section comparisons between images can be carried out (see relevant section<br />
<strong>for</strong> full description).<br />
It is strongly recommended that SVGA monitors be used when viewing images, VGA monitors<br />
will give a poor representation of each image, both in terms of the colour and scale. Images are<br />
shown at approximately actual size - however, as different monitors will result in some<br />
variation in the size of the displayed image, the images are displayed closest to actual size when<br />
a 800 x 600 display option is used in the <strong>Windows</strong> Setup.<br />
Wood samples were provided by the Forest Herbarium Wood Collection, Ox<strong>for</strong>d, all samples<br />
were well seasoned and freshly sanded, with no further treatment of the surface other than the<br />
removal of dust. The selection of samples aimed to produce images of a certain size, along the<br />
longitudinal grain but this was not always possible. Radial or tangentially cut surfaces were<br />
chosen in preference to a cross (or transverse) section; as if, <strong>for</strong> example, a sample is not cut on<br />
a true radius (quarter cut) it may well fail to show an otherwise attractive figure. Similarly<br />
samples from young stems were not considered initially as they would not reveal any possible<br />
contrast between heartwood and sapwood colour. It should be taken into account when viewing<br />
images, that selection due to defects such as stains, age, inadequate dimensions or damage, may<br />
result in an impression of that genus or species that is not typical of that obtained commercially<br />
in a larger quantity or dimension.<br />
2.6 References<br />
References are recorded by author(s), date of publication, title and journal or publisher. Each<br />
publication is given a unique code number by which it is referred to in the database. To view<br />
references independently of the data see References section.<br />
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3. Installation<br />
3.1 System Requirements<br />
To run the <strong>Prospect</strong> program an IBM-compatible microcomputer running <strong>Windows</strong> is required<br />
with:<br />
· 486 processor or better (Pentium recommended)<br />
· 4Mb RAM (8Mb or more recommended)<br />
· 24Mb free hard disk space<br />
· CD-ROM drive<br />
· colour VGA monitor (SVGA 256 colours recommended)<br />
· mouse or other pointing device<br />
3.2 Installation Instructions<br />
The supplied file PROSPECT.EXE will self-extract to your <strong>Windows</strong> temporary folder, then<br />
will run the install program. By default, the files will be installed to directory C:\PROSPECT,<br />
but you may install to any named directory (it is advisable to use folder names with maximum 8<br />
characters). Note that the installation will overwrite files in that directory should they already<br />
exist.<br />
Empty sub-folders PW21USER (to contain the user’s default settings and saved searches) and<br />
IMAGES (<strong>for</strong> wood surface image files) will be created. These names must not be changed. If<br />
images are required they should be downloaded from the <strong>Prospect</strong> website and extracted into<br />
this IMAGES folder.<br />
By default, a <strong>Windows</strong> Program group called “<strong>Prospect</strong> – The Wood Database” is created with<br />
icons <strong>for</strong> the <strong>Prospect</strong> program, three textual in<strong>for</strong>mation files and the Uninstall program.<br />
3.3 <strong>Prospect</strong> Setup<br />
Should you need to move the <strong>Prospect</strong> files to a new folder, you will need to run the program<br />
file SETUPLOC.EXE in the installation folder which will reset the location of <strong>Prospect</strong>.<br />
3.4 Text Files<br />
Lists of the following in<strong>for</strong>mation are provide in Microsoft Write files. Their contents can be<br />
viewed by double clicking on the relevant icons in the <strong>Prospect</strong> <strong>Windows</strong> group:<br />
· Species - lists the current names of the 1552 species recorded in <strong>Prospect</strong> Version <strong>2.1</strong><br />
· Properties - lists the 92 recorded tree characteristics and timber properties<br />
· End-uses - lists the 175 recorded end-uses<br />
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·<br />
3.5 Running <strong>Prospect</strong><br />
<strong>Prospect</strong> is started by double clicking on the “<strong>Prospect</strong> <strong>2.1</strong> <strong>for</strong> <strong>Windows</strong>” icon. The first time<br />
<strong>Prospect</strong> is run it will make copies of some system default files into the user’s working<br />
directory (PW21USER). This directory is also used to store the user’s working files, preferred<br />
system settings and program output.<br />
3.6 Troubleshooting (<strong>for</strong> <strong>Windows</strong> 3.1)<br />
The user may need to modify their system’s CONFIG.SYS file to specify the number of files<br />
which can be opened. For <strong>Prospect</strong> the value should be a minimum of FILES=70.<br />
If SHARE is in use and while running <strong>Prospect</strong> the user gets the message ‘File accessed<br />
denied’, it may be necessary to increase the parameter values <strong>for</strong> SHARE in the system’s<br />
AUTOEXEC.BAT file. This should be set to SHARE /F:4096 /L:500.<br />
The “MEMLIMIT” line in the CONFIG.FPW file in the <strong>Prospect</strong> directory controls how much<br />
memory the program can access. The user can allocate memory by specifying the percentage of<br />
available memory that the user would like <strong>Prospect</strong> to use. For example, specifying<br />
MEMLIMIT = 90, 2048, 4096 allocates 90 percent of the system’s available memory to<br />
<strong>Prospect</strong> with a minimum allocation of 2048 K and a maximum of 4096 K. For systems with<br />
exactly 4Mb, removing the MEMLIMIT statement may improve per<strong>for</strong>mance.<br />
Any modifications to the above files should be made with a text editor such as <strong>Windows</strong><br />
Notepad. If system files CONFIG.SYS or AUTOEXEC.BAT are modified the computer will<br />
need to be rebooted.<br />
3.7 Removing <strong>Prospect</strong><br />
<strong>Prospect</strong> does not install any files into <strong>Windows</strong> system folders or registry. To automatically<br />
remove the <strong>Prospect</strong> database from your computer, click on the Uninstaller icon, or use the<br />
standard <strong>Windows</strong> procedure to uninstall via the Add/Remove Programs facility in Control<br />
Panel. You will then need to delete the <strong>Prospect</strong> installation directory and all sub-directories.<br />
3.8 Problems<br />
We regret that this software is no longer supported, but we will do our best to help with any<br />
problems.<br />
Although the program has been thoroughly tested, it is possible that a ‘Program Error’ message<br />
might occur, in this event the user should choose to ‘Cancel’ rather than ‘Ignore’<br />
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4. Basic Operating Hints<br />
<strong>Prospect</strong> has a simple interface providing extensive facilities to customise searches and<br />
evaluations by way of picture button toolbars, check boxes and pull down menus.<br />
A number of basic buttons appear throughout the program, which are used <strong>for</strong> the same<br />
common operations:-<br />
- access the context-sensitive help<br />
- proceed to the next stage of the operation, having specified any<br />
required options and being ready to proceed<br />
- move back to the previous screen<br />
- move <strong>for</strong>ward to the next screen<br />
- move up to the previous line<br />
- move down to the next line<br />
- view detail of selected item<br />
- delete all displayed in<strong>for</strong>mation<br />
- print the displayed data to file, having specified print options<br />
- finish the current operation and return to the previous display<br />
Scrollable lists are used throughout the system; to choose items from these lists the normal<br />
<strong>Windows</strong>-style procedures should be used. If a one-line popup is active (highlighted), the user<br />
should simply click on it to open the full list. Then either use the scroll bar on the right of the list<br />
to find the required item; or use the keyboard by typing in quick succession the first letters of a<br />
required name. Double-clicking on an item will select it or highlight and use the tick button.<br />
Where check boxes are used to make selections, simply clicking on the relevant box will either<br />
select, the box will then appear crossed () or deselect the check box will appear blank().<br />
When printing, output is always directed to a file, RESULTS.TXT, in the User directory. Output<br />
during a <strong>Prospect</strong> session is always appended to this file and at the start of a new session the file is<br />
cleared. To view the file the user will first need to finish the current <strong>Prospect</strong> session. The file is in<br />
ASCII text <strong>for</strong>mat and can be easily imported into any word processing package; to provide the<br />
clearest output the file contents should be converted to a non-proportional font, such as courier,<br />
and via the page setup the margins be set to a minimum value. The file should be renamed or<br />
closed be<strong>for</strong>e re-entering <strong>Prospect</strong>.<br />
Throughout the program, species names are displayed such that: the family name is displayed in<br />
upper case after the species name, a species name ending with "[=...]" is a synonym or alternative<br />
<strong>for</strong> the currently accepted species name, which is shown in the brackets. If you select a synonym,<br />
the program will automatically use the current species name. Data from species with the symbol ~<br />
after their name are from plantation-grown timber.<br />
5
5. A <strong>Prospect</strong> Session<br />
The Program begins with a ‘Main Menu’ which gives access to the main sections of the program:-<br />
· Search by species name<br />
· Search by data content<br />
· Search by multiple properties<br />
· Potential end-uses <strong>for</strong> a species<br />
· Summaries of database contents<br />
· References<br />
The first two sections provide access to the in<strong>for</strong>mation recorded in the database. In the first<br />
section ‘Search by species name’, the user restricts the data they wish to view by selecting one or<br />
more species by taxonomic details or distribution; in the second section ‘Search by data content’,<br />
data viewed is related to particular properties and/or end-uses.<br />
The next two sections provide two systems of evaluating species. The ‘Search by multiple properties’<br />
section allows the user to build up a set of property requirements against which species are evaluated<br />
and enables direct comparisons between species. The ‘Potential end-uses <strong>for</strong> a species’ section uses<br />
predetermined sets of property requirements relating to specific end-uses to evaluate a species in<br />
terms of the products it might be considered suitable to produce.<br />
‘Summaries of database contents’ provides details on the general structure and content of the<br />
database, by way of lists of properties and end-uses, distribution details lists by countries and by<br />
regions and taxonomic details including lists of the families, genera, scientific names, synonyms<br />
and vernacular names found in the database. Additionally, the user may browse through all the<br />
wood surface images and make comparisons between them.<br />
The ‘References’ section allows the user to display and search <strong>for</strong> publications used <strong>for</strong> data<br />
collation, either independently of the data using free text searches or by searching <strong>for</strong> references<br />
relating to specific species and sections of the data.<br />
6
Menu Bar<br />
The ‘Menu Bar’ appears at the top of the Main Menu screen is accessible throughout the program.<br />
The menu bar ‘items’ are as follows:-<br />
· ‘Setup’ - allows the user to set a number of default options in the database<br />
·<br />
· ‘Help’ - allows the user to access the comprehensive help system and view in<strong>for</strong>mation<br />
about this version of <strong>Prospect</strong><br />
·<br />
· ‘Exit’ - allows the user to exit the program directly from anywhere within a session<br />
Setup - Prime Properties<br />
From the setup submenu the user may select a default list of ‘Prime properties’, where prime<br />
properties are a list of properties which can be pre-selected by the user to aid property data<br />
selection throughout the system and may be of special interest to the user. Selecting the prime<br />
properties option will produce the following window:-<br />
From here the user may append and insert properties, by choosing the relevant buttons and then<br />
selecting a property from a scrollable list, to delete a property, highlight it and then use the<br />
‘Delete’ button. A default list is provided with the system, which can be reinstated by pressing the<br />
‘Default’ button. Up to 17 properties may be included in the ‘prime properties’ list.<br />
7
Setup - Benchmark Species<br />
In a similar manner, the user may change the ‘Benchmark species’, where benchmark species are a<br />
list of species, which can be pre-selected by the user to aid species selection, these may be wellknown<br />
timbers <strong>for</strong> which alternatives are being sort or species of special interest to the user.<br />
Selecting Benchmark species from the setup submenu will produce a selection window similar to<br />
the prime properties selection window and is illustrated below, the ‘Add’ button at the bottom of<br />
the window will access a scrollable list of all species, from which the user may select one species<br />
at a time, to add to the benchmark list. To delete a species in the benchmark list simply highlight it<br />
and use the ‘Delete’ button. Species are displayed alphabetically, the list may not be saved with no<br />
species included but no maximum number is set. A default list is provided and can be reinstated<br />
via the ‘Default’ button.<br />
Setup - Printing Defaults<br />
The third option in the setup submenu enables the user to set printing option defaults:-<br />
It may be useful to set default print options to restrict the data printed to file. If, <strong>for</strong> example, the<br />
user has selected to print from a selection of species there may be a very large amount of data, in<br />
the <strong>for</strong>m of properties, end-uses, taxonomic details, distribution, source publications and any<br />
observations, but the user say, may not be interested in either the distribution or the vernacular<br />
names and so the output could be restricted so as not to include this particular portion of the<br />
data.The illustration above shows the various options, including printing a summarised <strong>for</strong>m of the<br />
output; to select or deselect simply check the appropriate boxes.<br />
8
Setup - Colours/images<br />
Under Colours, the user may set a default set of ‘property match indicators’, used in displaying<br />
evaluation results (in the Search by multiple properties and Potential end-uses <strong>for</strong> a species<br />
sections) and may adjust the image display (modify screen controls <strong>for</strong> the best representation).<br />
Selecting ‘property match indicators’ will produce the<br />
window illustrated here. To change any of the colours<br />
click on the appropriate box under ‘Edit?’, which will<br />
produce a selection of colours to choose from. A<br />
default selection is provided.<br />
Selecting ‘Wood Surface Image Display’ will display<br />
on screen four images of wood surfaces, this is<br />
provided to aid the adjustment of screen colour<br />
settings to display as accurately as possible the onscreen<br />
representation of the wood surface images<br />
provided in the system. The image display should be<br />
compared to the ‘Wood Image Colour Standards’ and<br />
appropriate adjustments made to the user’s monitor,<br />
e.g. to the contrast and brightness. If the user’s<br />
computer has any graphics packages loaded it is<br />
recommended that the user undertakes any screen<br />
calibrations provided with that package. Please note<br />
that the “Standards” are a page of images which have<br />
been professionally printed to represent the exact colour of the original wood sample. These<br />
images can there<strong>for</strong>e not be included in the downloadable User’s <strong>Guide</strong>.<br />
Help<br />
The help submenu enables access to the extensive help system and provides details of this version<br />
of <strong>Prospect</strong>. Context-sensitive help is provided throughout the system.<br />
Exit<br />
Exit enables the user to exit the program directly from anywhere within a <strong>Prospect</strong> session.<br />
9
5.1 Search by Species Name<br />
This section enables the user to select one or more species by name or distribution, and to then<br />
view all the in<strong>for</strong>mation about the selected species.<br />
Selecting species<br />
The initial screen allows the user to select the species or group of species that are to be examined,<br />
the scrollable list at the top of the screen shows which species are currently selected. A single<br />
species can be chosen from this list either by double clicking on the species name or highlighting<br />
and pressing the tick button, to view a selection of species choose the ‘ALL SELECTED<br />
SPECIES’ entry at the top of the list.<br />
The user may restrict the species selection appearing in the scrollable list by name or by<br />
distribution. Under the Search Range heading, the user may select (by clicking on the relevant<br />
options):-<br />
· all species<br />
· benchmark species - species of special interest to the user which may be set through the<br />
setup option from the menu bar<br />
· single genus - the user will be prompted to select a genus from a scrollable list<br />
· single species by botanical name - the user will be prompted to select a single species from a<br />
scrollable list<br />
· single species by vernacular name - the user will be prompted to enter a vernacular name (or<br />
any part of it)<br />
Similarly, the user may restrict the list by distribution, the user may select:-<br />
· all areas - selects species from all geographical regions<br />
· single country - selects species from a specific country, the user will be prompted to select<br />
the country of interest from a scrollable list<br />
· single region - selects species from a specific region, the user will be prompted to select a<br />
region of interest from a scrollable list<br />
10
If, <strong>for</strong> example, the user wished to study the in<strong>for</strong>mation available on the Hymenaea genus,<br />
selecting to restrict by single genus using the check box, will produce a scrollable list - the user can<br />
either scroll through the list until finding the required genus or type the first letters of the genus,<br />
typing ‘h’ will take the list onto the first genus beginning with an ‘h’, typing ‘h’ and then ‘y’ in<br />
quick succession will take the list onto the first genus with ‘hy’ at the beginning; having found the<br />
required genus double clicking will select it.<br />
This restriction will then be reflected in the scrollable list, selecting Hymenaea will produce the<br />
following list to select from:<br />
Species Home Page<br />
Having selected a species or range of species the appropriate ‘Species Home Page’ will then be<br />
accessed, as illustrated here <strong>for</strong> the chosen species - Hymenaea courbaril.<br />
11
The Species Home Page provides access to all the in<strong>for</strong>mation relating to each particular species.<br />
In<strong>for</strong>mation displayed on the home page includes lists of the species’ synonyms, vernacular names<br />
(common names linked to their reference source, double click on name of interest to display the<br />
reference), lists the species distribution by country and region, and displays a scanned image of the<br />
wood surface, shown at approximately actual size.<br />
From a Species Home Page all the in<strong>for</strong>mation contained in the database on one particular species<br />
can be accessed, via the picture button toolbar at the bottom of the screen:-<br />
· property data - any subset of the timber property data in detailed data <strong>for</strong>mat<br />
· end-use data - either a single end-use or all end-uses<br />
· species observations - any general observations relating to the species<br />
· user notebook - any comments entered by the user relating to the species<br />
and the user may:<br />
· move between species, using the arrow buttons to move to the next or previous Species Home<br />
Page, if a range of species had been specified at the initial screen<br />
· print - selected data related to the species to file (RESULTS.TXT)<br />
· access the context-sensitive help<br />
· exit to the initial Search by species name screen<br />
Timber properties<br />
To view any subset of the timber property data select the ‘timber properties’ button from the<br />
toolbar at the bottom of the home page screen, a property requirements box will then be accessed<br />
as illustrated here:-<br />
The following options are then available: -<br />
· to view all the properties<br />
· to view a single property chosen from a scrollable list<br />
· to select the prime properties, properties of special interest to the user, which may be<br />
defined through the setup option from the menu bar<br />
· to select any number of property groups<br />
To select simply click on the relevant choice; <strong>for</strong> property group(s) first click on property group<br />
and then the relevant check boxes. Once the selection has been made the tick button will access the<br />
required data.<br />
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Property data display<br />
Once a property selection has been made properties will be displayed in sequence, the user can<br />
page through a selection of properties using the arrow buttons in the toolbar. Properties in this<br />
section are displayed in detailed <strong>for</strong>mat (in the Search by data content section a summarised<br />
display is available). The example above shows the property data contained in the system <strong>for</strong> the<br />
‘maximum crushing strength (par to grain)’ <strong>for</strong> Hymenaea courbaril.<br />
Data are presented in tabular <strong>for</strong>m, with the descriptors listed down the side and the reference<br />
source, denoted by its code number, arranged in a vertical manner above the entries (x’s) which<br />
stemmed from it. There may be more than one ‘x’ entered <strong>for</strong> any one reference source. For<br />
example in the screen shot above, reference number 970 stated that the maximum crushing<br />
strength <strong>for</strong> Hymenaea courbaril is high to very high when the moisture content is 12 - 15% .<br />
Where properties have the provision to record the conditions or qualifiers relating to the data<br />
values (as <strong>for</strong> maximum crushing strength) the entries are displayed in colour-coded groups so that<br />
data recorded under the same conditions can be compared.<br />
From the property data display screen a number of further options are available, through the<br />
picture buttons in the toolbar:<br />
· Reference sources<br />
· Property observations<br />
· Property definition<br />
· Printing to file<br />
Reference sources<br />
Clicking on the ‘reference source’ button enables the user to link each item of data directly to the<br />
reference from which it came, as shown in the example below. The data item and related reference<br />
number appear highlighted with a grey vertical bar in the data matrix and with the corresponding<br />
reference displayed in a box at the bottom of the screen. To move the grey bar and highlight<br />
different data items and reference codes, use the directional arrow buttons in the reference box.<br />
The arrow button furthest right highlights the last data item shown, the furthest left the first, and<br />
the central arrow buttons move back or <strong>for</strong>ward one.<br />
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Clicking on the ‘exit’ button will remove the reference display and reveal the original data display<br />
screen.<br />
Property observations<br />
For a specific species, in<strong>for</strong>mation may have been researched that was considered important, relating<br />
to a particular property and that could not be displayed in the tabular <strong>for</strong>m; <strong>for</strong> example, often <strong>for</strong><br />
heartwood colour a short piece of text may convey a much clearer impression of the appearance of the<br />
timber, or an author may have made a comparison with another species, <strong>for</strong> example, stated that a<br />
lesser known species has strength properties similar to a well known timber. When a property has a<br />
related observation, the ‘property observations’ button will appear bright but when no such<br />
observation has been recorded the button appears dimmed. Selecting this button when it appears<br />
bright will produce a simple text box which can be scrolled through. Pressing the ‘exit’ button that<br />
appears at the bottom of this box will return the user to the screen underneath.<br />
Property definition<br />
Selecting the ‘property definition’ button will display the property’s technical definition and any<br />
related in<strong>for</strong>mation; where the property is quantitative, the exact values are given <strong>for</strong> the<br />
descriptive classes.<br />
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The definition shown here is <strong>for</strong> maximum crushing strength, detailing the technical definition, the<br />
values <strong>for</strong> the descriptors and the possible conditions under which the data could have been<br />
recorded. Pressing the ‘exit’ button will return the user to the screen underneath.<br />
Printing<br />
To print any of the property data to file select the ‘print’ button, this will access a print options<br />
window as shown below:<br />
This options box allows the user to restrict the amount of additional in<strong>for</strong>mation that is printed to file,<br />
by checking the required boxes, this may be useful when printing many properties. Default print<br />
options can be set through the setup option from the menu bar. Having selected press the ‘print’<br />
button to print the selection.<br />
Moving between properties<br />
To page through the properties use the left and right arrow buttons in the toolbar.<br />
Help<br />
The context-sensitive help may be accessed from this screen also.<br />
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Known uses<br />
From the Species Home Page the user can also choose to view any end-uses that have been<br />
recorded in the literature to have been made from the particular species. Pressing the ‘known uses’<br />
button produces the following ‘Use Requirements’ box:-<br />
Using the check boxes, the user can either select one single end-use, a scrollable list will appear from<br />
which to make a choice, or to view all end-uses. Once a selection has been made, pressing the tick<br />
button will access the required end-use data in detailed <strong>for</strong>mat.<br />
The end-use data is displayed in the same tabular <strong>for</strong>mat as the property data, except that an<br />
identical list of three descriptors (levels) applies to all of the recorded end-uses. The descriptors<br />
relate to the level at which the species has been used <strong>for</strong> the relevant purpose; species are either<br />
recorded as having been exported as suitable <strong>for</strong> this purpose (‘used commercially/exported’), or<br />
having been sold and used locally (‘used locally’), or recorded as used, but where the extent of use<br />
is unknown or not specified (‘used, but extent unknown’).<br />
In a similar manner, to accessing additional in<strong>for</strong>mation from the property data screen, the<br />
following options are available from the end-use data display using the picture button toolbar -<br />
viewing the reference sources, used to abstract the data displayed; viewing any end-use<br />
observations, the button appearing dimmed when no observation has been recorded; printing to<br />
file, with the same options to restrict the data output as <strong>for</strong> properties; accessing the contextsensitive<br />
help and moving between end-uses using the arrow buttons.<br />
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Species Observations<br />
During the research <strong>for</strong> a particular species in<strong>for</strong>mation may have been noted of a general descriptive<br />
nature, which was considered to be of interest, but which could not be recorded under any specific<br />
category. Where such in<strong>for</strong>mation has been recorded it can be found via the ‘species observation’<br />
button, shown bright where there is data and dimmed where no such data has been recorded. A simple<br />
text box will appear which can be scrolled through, as shown here, selecting the ‘exit’ button will<br />
return the user to the Species Home Page.<br />
User notebook<br />
From the Species Home Page, the ‘user notebook’ is provided <strong>for</strong> the user to record notes on any<br />
aspect of the current species. For example, these may include observations of facts gained from<br />
experience with the species or comments on any aspects of the recorded data. Selecting the ‘user<br />
notebook’ button will access a simple text box similar to the species observations box shown above;<br />
the notebook may be used to enter, edit or delete text, changes in content are saved on exiting the box.<br />
An additional ‘trash’ button is provided to erase all notes <strong>for</strong> the current species in one hit.<br />
Print<br />
Selecting the ‘print’ button from the Species Home Page will access the Species Print Options. In<br />
order to restrict, if required, the quantities of data that may be output, the print options overlay<br />
allows the user to select any combination of the options by checking the appropriate boxes. The<br />
user may select from the following:- synonyms, vernacular names, distribution, references, species<br />
observations, property observations, end-use observations, the user notebook, property data and<br />
end-use data. The property and end-use data may be further selected. Checking the property data<br />
box and pressing the ‘select’ button will access the property requirements window, as illustrated<br />
earlier in the properties section, from here the user may choose to select all properties, one single<br />
property, from a scrollable list, the prime properties list or any number of property groups;<br />
similarly the user may select all end-uses or one single end-use, via the end-use requirements<br />
window. If the properties check box has not been selected property observations will not be<br />
available, similarly with the end-use options.<br />
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Additionally, the user may also select the <strong>for</strong>mat, in which the data is output: either detailed, as the<br />
data is displayed on screen in this section, or in a summarised <strong>for</strong>mat, which precludes selecting to<br />
print references, this <strong>for</strong>mat will be described in the next section, Search by data content. From the<br />
species print options box, pressing the ‘print’ button will send the selected in<strong>for</strong>mation to file<br />
(RESULTS.TXT), pressing ‘exit’ will cancel the print and return the user to the Species Home<br />
Page.<br />
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5.2 Search by Data Content<br />
The second data search section, Search by Data Content, allows the user to search <strong>for</strong> in<strong>for</strong>mation<br />
by specifying the range of interest, in terms of properties and end-uses; to restrict the search range<br />
by species and distribution; to specify display options - detailed <strong>for</strong>mat, the default as in the<br />
previous section, or summarised, giving a condensed view of the data; and to highlight data from a<br />
single reference source (which precludes the summarised display).<br />
Data requirements then, may be restricted by selecting from the following property options:-<br />
· none - select to view no property data<br />
· all - select to view all property data<br />
· single property - select from a scrollable list to view data on one single property<br />
· prime properties - properties of special interest to the user, defined through the setup option<br />
from the menu bar<br />
· property group(s) - select any number of property groups<br />
and from the following end-use options:-<br />
· none - select to view no end-use data<br />
· all - select to view all end-use data<br />
· single end-use - select from a scrollable list to view data on one single end-use<br />
The Search range may be restricted by selecting from the following species name options:-<br />
· all species - select to view relevant data from all species<br />
· benchmark species - select to view data only from species of special interest, which may be<br />
set through the setup option from the menu bar<br />
· single genus - select, from a scrollable list, to view data from a single genus,<br />
· single species by botanical name - select a single species from a scrollable list<br />
· single species by vernacular name - the user will be prompted to enter a vernacular name (or<br />
any part of it)<br />
and from the following species distribution options:-<br />
· all areas - select to view data on species from all geographical regions<br />
· single country - select, from a scrollable list, to view data on species from a specific country<br />
· single region - select, from a scrollable list, to view data on species from a specific region<br />
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·<br />
Once a selection has been made, through clicking on check boxes and highlighting items from<br />
scrollable lists, pressing the tick button will produce a list of species meeting the requirements, the<br />
user can then choose to view ‘all selected species’ or highlight one particular species. The<br />
requested properties or end-uses are then displayed in sequence, if the display option is detailed, in<br />
the same tabular <strong>for</strong>m as in the previous section, with the descriptors down the left hand side and<br />
the reference codes arranged vertically above the relevant data item (x). The above illustration <strong>for</strong><br />
Chlorocardium rodiaei displays the property data <strong>for</strong> tree height in detailed <strong>for</strong>mat.<br />
In the same way, as in the previous section (Search by species name), via the picture button toolbar<br />
the user can view the reference sources, view any property observations, the property definition, move<br />
between properties, can print a selection to file, having specified the print options, and access the<br />
context-sensitive help. In addition, the user may move to the next, or back to the previous, species, via<br />
arrow buttons, and may access the Species Home Page (described in more detail later).<br />
Single Property<br />
Returning to consider the initial screen in more detail, and to specifying data requirements, if a<br />
user chooses to restrict the search to one single property, further restrictions can be applied by<br />
selecting particular descriptors or levels <strong>for</strong> the property of interest. In the following example, the<br />
user selects to restrict to a single property, clicking on ‘single property’ producing a scrollable list<br />
from which a property is then chosen.<br />
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Selecting, <strong>for</strong> example, trunk diameter, produces the following overlay box, displaying the relevant<br />
descriptors <strong>for</strong> the property, with check boxes along side each one, which can be selected as<br />
required. The user may choose to ‘Select all’, or to ‘Clear all’, the check boxes in one hit using the<br />
relevant buttons. In the illustration, the user has selected to search <strong>for</strong> species with trunk diameters<br />
of a maximum of at least 250 cm. Once a selection has been made the user should click on the<br />
‘OK’ button in the overlay box.<br />
Choosing to restrict to a single end-use will produce a similar overlay box, within which the user<br />
can specify the level of use of interest, either used commercially, used locally or used but extent<br />
unknown, where the reference has not specified the level of use. As with the property descriptors<br />
select levels via the check boxes.<br />
Where a single property, or end-use, with specified descriptors, is included in the requirements the<br />
data display will reflect this, by flagging the relevant descriptors. For the example considered<br />
previously, in relation to trunk diameter, the display would appear as illustrated below, with the<br />
relevant descriptors, ‘250 -
Data from a single reference<br />
From the display options box, on the initial screen, the user can choose to look at the data from one<br />
single reference, clicking on the ‘data from single reference’ check box, will produce the following<br />
overlay:<br />
All references are initially displayed in a scrollable list; to select from the list either double click<br />
on the reference or highlight and press the ‘select’ button (), alternatively either enter the<br />
reference code directly in the ‘Reference code’ box and press enter, limiting the list to the relevant<br />
reference, or enter some text in the ‘Text search string’, <strong>for</strong> example typing ‘timbers’ and then<br />
pressing enter will restrict the list to all those references that contain the text ‘timbers’ within<br />
either the author(s) name or title of the publication.<br />
The ‘reset’ button will restore the scrollable list to the full list of references.<br />
When a single reference has been selected this will be shown in the Display Options box on the initial<br />
Search by data content screen, having restricted the data by this means the summarised output option<br />
is not available and will be shown ‘dimmed’ in the box.<br />
Having initiated the search, the list of species meeting requirements will be displayed, from which<br />
the user may choose to view ‘all selected species’ or one specific species; the data display, with the<br />
relevant reference code and data entries highlighted, will then be shown. For example, where<br />
reference 63 has been chosen the data display, <strong>for</strong> a particular property, would appear as follows:-<br />
22
The illustration shows the density data <strong>for</strong> Pinus radiata ~ (the ‘~’ signifying data from plantation<br />
grown timber), with the data entry and its related reference code, 63, highlighted by a blue vertical<br />
bar. The display and the additional in<strong>for</strong>mation available via the picture button toolbar are otherwise<br />
the same.<br />
Summarised data display<br />
Selecting the summarised property data level display option from the initial Search by data content<br />
screen, will result in the data being displayed in a condensed <strong>for</strong>m.<br />
The display above is an example of a typical screen of output in summarised <strong>for</strong>mat, in this case<br />
some of the timber properties <strong>for</strong> Tectona grandis.<br />
The summarised <strong>for</strong>m of the data gives an overall summary of in<strong>for</strong>mation stored <strong>for</strong> each property<br />
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or end-use. For each property <strong>for</strong> which data has been entered, the number of data items recorded<br />
<strong>for</strong> each descriptor under any conditions are shown in relation to the total number of data items<br />
recorded <strong>for</strong> that property, i.e. in summarised <strong>for</strong>mat data entries are shown <strong>for</strong> each property and<br />
condition, as the ratio of the number of data items, <strong>for</strong> that particular descriptor, to the total<br />
number of data items recorded <strong>for</strong> that property/condition.<br />
In the above display, <strong>for</strong> example, 20/26 means that 20 out of the 26 data entries recorded that<br />
Tectona grandis has a density of between ‘600 - 719 air-dry’; <strong>for</strong> ‘movement in service’ 6 out of 8<br />
entries although not specifying the conditions said that teak was stable and 3 out of 4 recorded that<br />
teak had a reputation <strong>for</strong> being stable.<br />
From the summarised data display screen the user may, via the toolbar, view the Species Home<br />
Page; move between species and page through the display using the appropriate arrow buttons;<br />
print, having specified print options, selecting to print in summarised <strong>for</strong>mat from any point within<br />
the system will produce an output in the same <strong>for</strong>m as appears on screen; access the contextsensitive<br />
help and exit back to the original Search by data content screen.<br />
Choosing to view the Species Home Page from the data display (detailed or summarised <strong>for</strong>mat) in<br />
this section will display the Home Page <strong>for</strong> the species, whose data is currently being viewed.<br />
Illustrated here is the Species Home Page <strong>for</strong> Chlorocardium rodiaei, as it would appear if<br />
accessed from the Search by data content section. As in the previous section the species’<br />
synonyms; vernacular names, with associated references; distribution and wood surface image are<br />
displayed on screen and access is provided to species observations, not available when the button<br />
is shown ‘dimmed’; the user notebook and context sensitive help. To return to view the property or<br />
end-use data display, the user should select the ‘exit’ button.<br />
Comparing this version of the Species Home Page to the Home Page displayed in the Search by<br />
species name section the user will notice that the options to view any subset of the timber property<br />
data and any subset of the known end-uses are not available when in the Search by data content<br />
section. These options are removed as the user has already selected the data requirements of interest<br />
from the initial Search by data content screen.<br />
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5.3 Search by Multiple Properties<br />
This section of the program allows the user to evaluate and compare species by searching <strong>for</strong><br />
multiple property requirements. The user is first provided with a blank screen, with an extensive<br />
picture button toolbar at the bottom of the screen.<br />
Criteria Definition<br />
The initial step is to compile the list of properties and their corresponding levels, in descending<br />
order of importance, which, <strong>for</strong> example in the case of a product related search, would be those<br />
features considered necessary to produce that product.<br />
Compiling the list of properties<br />
The list may be drawn up in a number of ways:-<br />
1. Manually, using the ‘append’, ‘insert’ and ’delete’ buttons from the toolbar:<br />
- append<br />
- insert<br />
- delete<br />
Until one property has been added, only the ‘append’ button is operational. Pressing the ‘append’ or<br />
the ‘insert’ button will produce a scrollable list from which the user should select a property, to delete<br />
a property highlight the relevant property and press the ‘delete’ button.<br />
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2. Reading in a previously saved file, using the ‘from file’ button, this may additionally include<br />
corresponding saved property levels. Files are saved to the user directory, and selecting this button<br />
will produce the following window with a scrollable list of files, from which the user may make their<br />
selection.<br />
3. By restoring, via the ‘end-use related’ button, a list of properties, and corresponding levels, that<br />
have been predefined as necessary <strong>for</strong> a particular product (end-use). These may have either been<br />
defined by an expert, the system default criteria, or by the user, user customised criteria, <strong>for</strong> a<br />
particular end-use. Selecting the end-use button will produce a scrollable list <strong>for</strong> the user to select<br />
from, as shown here:-<br />
The user should then select the end-use of interest from this list; where an ‘s’ <strong>for</strong> system or a ‘u’ <strong>for</strong><br />
user flag a particular end-use this denotes that an end-use criteria has been defined. In the above<br />
example, both system and user defined criteria have been defined <strong>for</strong> ‘agricultural implements’. A ‘
4. Prime Properties - selecting the ‘prime properties’ button, will read in a list of properties,<br />
without defined levels, that are considered to be a set of key properties by the user and may be<br />
defined through the setup option from the menu bar, as described earlier. A default list is provided.<br />
Properties should be ordered roughly in order of importance and will be numbered as such.<br />
Alternative properties may be set by clicking on the ‘or’, which appears next to a property when<br />
highlighted; this option may be useful, <strong>for</strong> example, where the user is interested in the durability of<br />
a timber, the obvious property to consider being ‘natural durability’ as a ‘key’ property but if a<br />
species failed under this consideration it may become acceptable if treated with a preservative, so<br />
the ease with which preservative can be used would become a factor; <strong>for</strong> the purpose of an<br />
evaluation the user would then, list ‘natural durability’ as the ‘key’ property, with very durable and<br />
durable, say, set as the required minimum levels, and directly under it, as an ‘or’, ‘amenability to<br />
preservation (heartwood)’, with the levels permeable and moderately resistant set. Any number of<br />
alternatives may be set and these will be considered in turn.<br />
Once a list of properties has been compiled by any of the a<strong>for</strong>ementioned methods, it may be<br />
edited using the ‘append’, ‘insert’ and ‘delete’ buttons; the ‘delete all’ button will clear the screen<br />
of all properties and allow the user to start again. Having compiled a list, then selecting to read in a<br />
list from file, end-use criteria or the prime properties will overwrite the original list.<br />
Setting the property levels<br />
The level of each property can be set up or altered, either manually or from data <strong>for</strong> a particular<br />
species.<br />
1. To set or edit levels manually, highlight the relevant property, either by using the up or down<br />
arrows from the toolbar or by using the mouse to click directly on the property. The appropriate<br />
property levels will then be displayed, to select or deselect a level simply click on the relevant check<br />
box, in the screen shot above the levels ‘permeable’ and ‘moderately resistant’ have been set<br />
manually <strong>for</strong> the property ‘amenability to preservation (heartwood)’, note how the check boxes appear<br />
crossed <strong>for</strong> those two levels. The property has also been set as an alternative property notice the ‘or’<br />
in front of the property name.<br />
2. The user may set the levels from a ‘donor species’, which is defined as a species used to set<br />
minimum search values <strong>for</strong> property levels when per<strong>for</strong>ming a search by multiple properties. This<br />
facility can be useful when trying to find and compare species with similar properties. For<br />
example, if the user wishes to find alternatives to a particular species, setting that species as the<br />
donor species will enable the search process to look <strong>for</strong> species with similar property levels.<br />
Selecting the ‘from data’ button will access the following window:<br />
27
From this window the user should select which of the properties the levels should be set <strong>for</strong>: the<br />
current property only, all existing properties or <strong>for</strong> all future properties. Having made a selection<br />
pressing ‘OK’ will access a select a species screen, if a species has already been set and the user<br />
wishes to change it pressing ‘Select species’ will also produce the following screen:-<br />
The user should then select a species from the scrollable list of species names. Pressing the<br />
‘Benchmark species’ button will limit the list to the benchmark species, set through the setup<br />
option from the menu bar, pressing ‘All Species’ will return the full list. To select a species, either<br />
double click on it or highlight and press the ‘Select’ button.<br />
Once the donor species has been set, the user will be returned to the initial criteria definition<br />
screen, the levels <strong>for</strong> the particular properties having been changed to correspond to the data <strong>for</strong><br />
that specific species, as recorded in the database.<br />
Where a property has had no levels set, or every level has been set, the number relating to that<br />
property will appear red. A search can not be carried out, where levels are being considered, if <strong>for</strong><br />
one particular property no levels have been set.<br />
The user may remove the consideration of property levels from a search, the results will then<br />
simply indicate the presence or absence of data.<br />
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The ‘level off’ button removes the levels<br />
the ‘level on’ button returns the levels<br />
Note that when no levels are under consideration ‘or’ properties are treated as key properties.<br />
Throughout the evaluation, the method of compiling both the list of properties and their levels is<br />
displayed.<br />
Printing the criteria<br />
Having completed the criteria, when the user is satisfied with the list of properties and<br />
corresponding levels, the user may choose to start the search, or to save or print the property<br />
criteria. Selecting the ‘print’ button, will prompt the user to confirm whether or not the property<br />
criteria should be output to a file (RESULTS.TXT).<br />
Saving the criteria<br />
Saving the criteria may be carried out be<strong>for</strong>e or after a search on returning to the property list<br />
screen. Leaving this section of the program without saving will cause the system to prompt the<br />
user to save search requirements. Selecting the ‘save criteria’ button will access the following<br />
window:-<br />
The user can then choose to save the property list as a user-customised ‘Enduse-related criteria’,<br />
where levels have been set, or to ‘File’, with or without set levels.<br />
Selecting to save as an enduse-related criteria prompts a further window, shown on the next page,<br />
with a scrollable list of all end-uses from which the user should select the end-use the criteria should<br />
be saved to. Where an ‘s’ proceeds an end-use, a system criteria has already been defined, and where<br />
a ‘u’ proceeds an end-use, a user customised enduse criteria has already been defined, which may be<br />
overwritten. A ‘
To remove a user-customised criteria, overwrite the particular end-use criteria with an empty criteria<br />
set.<br />
Selecting to save to file will prompt the user to specify a criteria file name (extension ‘.crt’) that<br />
will be saved to the <strong>Prospect</strong> User Directory.<br />
Starting the Search<br />
Once the criteria has been created the user should click on the ‘start search’ button, from the criteria<br />
definition screen, and will then be prompted to set the search range.<br />
The search range may be restricted by species and by distribution. The selection may be made by<br />
clicking on the following options: all species, benchmark species, a single genus chosen from a<br />
scrollable list or a single species, chosen from a scrollable list; and by distribution: all areas, a<br />
single country chosen from a scrollable list or a single region from a scrollable list. The user might,<br />
<strong>for</strong> example, only wish to consider species from Australasia in an evaluation.<br />
Setting the ‘Reference species’<br />
From the Search Range screen, the user may select a ‘Reference species’. The reference species,<br />
will then be displayed at the top of every screen of results, produced by the search, making it easier<br />
to relate and compare other species to this species of particular interest. If, <strong>for</strong> example, the user<br />
has set the property levels to that of one species, the ‘donor species’, setting the ‘reference species’<br />
as the same species will be particularly useful.<br />
To set a Reference species clicking on the appropriate check box will access the ‘Select a species’<br />
window:<br />
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From this screen, the user should select the required species from the scrollable list. Pressing the<br />
‘Benchmark species’ button will limit the list to the benchmark species, pressing ‘All species’ will<br />
return the full list. To select a species, either double click on it or highlight and press ‘Select’.<br />
When a ‘donor species’ has already been set that species will initially appear highlighted in the<br />
‘Reference species’ selection list.<br />
Having selected a reference species the user will be returned to the Search Range window, the<br />
selection will be displayed, and from here the tick button should be selected to initiate the search.<br />
Species Search Results<br />
The search results screen displays all species in the database, or in the specified search range, <strong>for</strong><br />
which it has some data (approximately ordered by proximity to the specified search criteria), the<br />
species are listed on the left of the screen and may span several screens. The results screen indicates<br />
the method by which both the properties and associated property levels were established. If the search<br />
criteria was end-use related an additional column will appear to the right of the screen headed<br />
‘known-market’, which shows the highest level at which each species is recorded as used <strong>for</strong> this<br />
purpose in the literature.<br />
In the example above, from the top of the display, it can be seen that the property list was created<br />
by reading in the ‘prime properties’ list and that the levels were set using a ‘donor species’, here<br />
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Hymenaea courbaril, which was then also set as the ‘Reference species’, note how it appears at the<br />
top of the screen and separated from the rest of the list.<br />
The column headed ‘property matches’ shows how each of the species fulfilled the timber property<br />
requirements. For every species, each selected property is represented by a coloured block or<br />
diamond (shown shaded in the guide), the ‘property match indicators’, which denote how the<br />
evaluated properties met the required minimum levels. The data <strong>for</strong> each species can fit the<br />
property requirements in four different ways, dependent on how the data entries related to the<br />
requested property levels. The property match indicator squares are shown in four colours (default<br />
shown shaded here), such that:-<br />
(light green)<br />
(dark green)<br />
(red)<br />
(grey)<br />
- property met the necessary requirements with unanimous opinion (all data entries in<br />
the required classes)<br />
- property met the necessary requirements but with variation in opinion (some but not<br />
all data entries in the required classes)<br />
- property failed to meet necessary requirements (no data entries in the required<br />
classes)<br />
- no data recorded <strong>for</strong> this property<br />
The colours of the match indicators may be altered through the setup option from the menu bar (see<br />
earlier section of the guide), a default is provided. Changing the selection will not alter an already<br />
present results display, the new colours will only come into operation on carrying out a new search.<br />
To view the colour key go to the setup option.<br />
For each requested feature the program will first check the ‘key’ property, and if it proves<br />
satisfactory, its level of suitability will be displayed through the appropriately coloured square; if<br />
the key property fails to meet the requirements or has no data, the program will check any<br />
alternative ‘or’ properties, that may have been specified, in turn. The first of these to appear<br />
satisfactorily will be indicated with an appropriately coloured diamond; the colour code being the<br />
same as <strong>for</strong> the ‘squares’.<br />
- alternative ‘or’ property, key property having failed.<br />
If, during the search, property levels were not under consideration, the results display will simply<br />
indicate the presence or absence of data <strong>for</strong> each property; alternative ‘or’ properties will be<br />
considered as ‘key’ properties. The display uses a circle symbol to indicate:<br />
(blue)<br />
- some data recorded <strong>for</strong> this property<br />
(grey)<br />
- no data recorded <strong>for</strong> this property<br />
The following display illustrates the same search as be<strong>for</strong>e but with no levels set:-<br />
32
From the species search results screen, the user may carry out a number of operations, using the<br />
picture button toolbar at the bottom of the screen.<br />
Move between species<br />
Using the arrow buttons, the user may move up and down between species on the screen, and ‘page’<br />
through the species list.<br />
Species Home Page<br />
Having highlighted a species, either directly using the mouse or via the arrow buttons, the user<br />
may access the Species Home Page, which displays all taxonomic and distribution data and a wood<br />
surface image, where available <strong>for</strong> that species; and provides access to the timber properties, enduses,<br />
species observations and user notebook <strong>for</strong> that particular species (see ‘Species Home Page’<br />
in the Search by species name section <strong>for</strong> an illustration and further details).<br />
Match Detail<br />
Match detail allows the user to examine the property matching process in detail, having<br />
highlighted the species of interest, the user may view, in detailed data <strong>for</strong>mat, the data assessed <strong>for</strong><br />
each property used in the search, and if property levels were considered, the degree to which the<br />
data met the required minimum values. Where levels have been set the appropriate descriptors will<br />
be displayed in blue with a ‘>’ after them. From the display the user may, as where detailed data is<br />
viewed (see Search by species name and Search by data content sections of the guide), access the<br />
reference sources, property observations, and definition. Data may be printed to file and via the<br />
arrow buttons the user may page through the properties making up the criteria.<br />
In the display illustrated above, the data <strong>for</strong> the density of Chlorocardium rodiaei can be seen to meet<br />
the necessary requirements but with a variation in opinion, some of the data entries fell within the<br />
required range but a small number of references recorded Chlorocardium to have a maximum density<br />
greater than the set requirements. The corresponding property match indicator would, there<strong>for</strong>e, have<br />
appeared dark green on the initial search results screen.<br />
33
Property overlay<br />
Via the ‘property overlay’ button (a light bulb shown illuminated) the user may access an overlay<br />
listing the properties used in the search, each property linking to the relevant ‘property match<br />
indicator’ square as shown below. To remove the property overlay, simply select the ‘property<br />
overlay’ button (now shown as an unlit light bulb).<br />
Species Comparison<br />
The species comparison button enables the user to make direct comparisons between two species<br />
from the initial species search results screen. Clicking on the ‘compare species’ button will lead<br />
the user to select the two species to be compared, via two further buttons, which will appear in<br />
place of the ‘compare species’ button.<br />
The user should highlight the first species name, directly using the mouse or through the up<br />
and down arrow buttons and then choose the ‘mark species’ button (a red tree marked with<br />
a ‘1’).<br />
The second species name should then be highlighted in the same manner and the ‘mark<br />
species’ button (now shown blue and marked with a ‘2’) chosen.<br />
The data <strong>for</strong> each species are then visually compared <strong>for</strong> each of the specified search properties, in<br />
turn. The display takes the <strong>for</strong>m of two sets of horizontal ‘bar’ graphs indicating the number of data<br />
entries <strong>for</strong> each descriptor <strong>for</strong> both of the selected species. Data recorded under specific conditions are<br />
shown in appropriate colours. The requested search levels are displayed in blue with a ‘>’ after them.<br />
34
The following illustration shows a comparison between Hymenaea courbaril and Gonystylus<br />
bancanus, the property under consideration being ‘modulus of elasticity/bending stiffness’. The<br />
number of data entries <strong>for</strong> each descriptor is shown under the appropriate species, and as conditions<br />
have been recorded colour codes are used, in the example, there were 11 data entries stating that the<br />
modulus of elasticity is medium <strong>for</strong> Hymenaea, of which five were recorded under green conditions<br />
and six under 12% to 15% m.c.<br />
The arrow buttons can be used to move through the selected properties, the property definition<br />
may be viewed and the comparison, <strong>for</strong> the set of properties, printed to file; the ‘exit’ button will<br />
return the user to the species search results screen.<br />
Print<br />
Selecting the ‘print’ button from the species search results screen, will print the current screen of<br />
results and associated property criteria to file (RESULTS.TXT), the user will be asked to confirm<br />
this. Each screen of species displayed can be printed separately, with subsequent screen<br />
concatenated on the page. Printing the results of an evaluation from the Search by multiple<br />
properties section of the program will show:-<br />
· the manner in which the property list and levels were drawn up<br />
· the requested properties and their desired levels<br />
· the actual evaluation with the colour-coded symbols represented by printable characters<br />
preceded by an interpretation of those characters.<br />
35
A page of output from a multiple properties search is shown here, the property list having been<br />
drawn up by reading in the prime properties and the levels set from a donor species Hymenaea<br />
courbaril, which was also set to be the reference species.<br />
================================================================================<br />
Species search evaluation<br />
properties based on prime list, levels based on H. courbaril<br />
================================================================================<br />
1 density (kg/m3) 400-499 basic 480- 599 air-dry<br />
or 500-599 basic 600- 719 air-dry<br />
or 600-699 basic 720- 839 air-dry<br />
or 700-799 basic 840- 959 air-dry<br />
or 800-899 basic 960-1079 air-dry<br />
2 bole length (m) 10 -
--------------------------------------------------------------------------------<br />
property assessment indicators:<br />
O property met the necessary requirements with unanimous opinion<br />
o property met the necessary requirements, but variation in opinion<br />
x property failed to meet necessary requirements<br />
· no data recorded <strong>for</strong> this property<br />
-------------------------------------------------------------------------------<br />
property<br />
species name<br />
matches<br />
-------------------------------------------------------------------------------<br />
Hymenaea courbaril<br />
OOOOOooOOoOOOOO<br />
--------------------------------------------------------------------------------<br />
Byrsonima spicata<br />
OOOOoOOOxoOOOoO<br />
Brachystegia spici<strong>for</strong>mis<br />
OoOOOOOoOxOOOOx<br />
Berlinia grandiflora<br />
OoOOoooOOxOOOOo<br />
Quercus robur<br />
OOoOoooOOxOOOOo<br />
Betula alleghaniensis<br />
OOOOOooooxOoOoo<br />
Pentacme contorta<br />
OOOOoOOOxOOOOOo<br />
Patagonula americana<br />
OOOOoOOOxOOOOoO<br />
Lagerstroemia speciosa<br />
OoOooOOOOxOOOoO<br />
Gilbertiodendron dewevrei<br />
OoOOoooOOxOOOoO<br />
Albizia versicolor<br />
OoOooOOOOxOOOoO<br />
Dipteryx odorata<br />
oOOOOOOOO·OOxOo<br />
Ekebergia capensis<br />
OoOOOOOoxOOOOOO<br />
Staudtia stipitata<br />
oOOoOooOOxOOOOo<br />
Balanocarpus heimii<br />
OooOoOOOOxOOooo<br />
Afzelia quanzensis<br />
OoOooOOOOxoOOOo<br />
Parashorea stellata<br />
OOOooooOOxOOOOO<br />
Terminalia catappa<br />
OOOoOo·ooOOOOoo<br />
Pygeum africanum<br />
oOOOooOoOxOOOOO<br />
Casuarina litorea<br />
OoOOoooOOxOOooo<br />
Help<br />
From the results screen, context-sensitive help is available, via the ‘help’ button.<br />
Exit<br />
The ‘exit’ button will return the user to the initial criteria definition screen.<br />
Once returned to the criteria definition screen, the property list and associated levels are still<br />
displayed on screen and may be edited or the user may clear and build a new set of properties and<br />
levels, to initiate another search.<br />
Exiting from the criteria definition screen will return the user to the Main Menu; if the current criteria<br />
set has not been saved the user will be prompted to save be<strong>for</strong>e exiting, see earlier in this section <strong>for</strong><br />
more detail on saving to end-use or file.<br />
37
5.4 Potential End-Uses <strong>for</strong> a Species<br />
The second evaluation section can be used to evaluate the suitability of potential end-uses <strong>for</strong> one<br />
particular species. The end-use criteria, sets of properties and associated levels considered<br />
necessary <strong>for</strong> a particular product, held in the system and created by the user, are used in<br />
comparison to the species property data to establish which products the species could produce.<br />
Search Details<br />
The user must first specify a species of interest either by botanical name or by vernacular name;<br />
clicking on ‘Species name (by botanical name)’ will produce a scrollable list from which the user<br />
can select a species.<br />
Clicking on ‘Species name (by vernacular name)’ will prompt the user to enter the vernacular name<br />
(or any part of the it), this may produce a selection of names, with the associated botanical name, from<br />
which the user should then select by double clicking.<br />
Secondly, the user should select whether the ‘system default’ end-use criteria, those criteria predefined<br />
in the system, or the ‘user-defined’ end-use criteria, those defined by the user, either in the<br />
Search by multiple properties section of the program or in this section, should be used to evaluate<br />
38
the species. Only those end-uses that have defined criteria can be considered in the search, when<br />
user-defined criteria are under consideration, system defined criteria will be used where no userdefined<br />
exist <strong>for</strong> a particular end-use and vice versa.<br />
The search criteria may be viewed, edited or created at this stage by clicking on the ‘Check<br />
criteria?’ check box. The Criteria Definition screen, as in the previous section, will then be<br />
displayed.<br />
The picture buttons from the toolbar can be used, in exactly the same way as in the Search by multiple<br />
properties section (see previous section of the <strong>Guide</strong> <strong>for</strong> exact details), to create property sets and<br />
associated levels.<br />
Properties may be compiled:-<br />
· manually using the ‘append’, ‘insert’ and ‘delete’ buttons<br />
· by reading in previously saved file (with or without associated levels)<br />
· by restoring a predefined end-use related criteria, defined by the system or the user (with<br />
associated levels)<br />
· by reading in the prime properties (with no associated levels)<br />
The associated levels can then be set (where necessary):-<br />
· manually, by clicking on relevant check boxes<br />
· from a ‘donor species’, using the property data <strong>for</strong> a particular species to set the levels <strong>for</strong> the<br />
selected properties<br />
Exactly as in the previous section, properties should be ordered roughly in order of importance,<br />
and will be numbered as such. Where a property has no associated levels set, the property number<br />
will appear red. Alternative ‘or’ properties may also be set as in the previous section.<br />
The property lists and associated levels can be saved to file or as ‘user-defined’ enduse criteria. If a<br />
user criteria <strong>for</strong> a particular end-use already exists this may be overwritten. If a property list has<br />
been created and not saved, exiting this screen will prompt the user to do so. Property sets may<br />
also, as in the previous section, be printed to file (RESULTS.TXT) from this screen. However, in<br />
this section a search may not be initiated from here and the only criteria sets that will be<br />
considered in the evaluation are the end-use related criteria.<br />
39
End-use criteria<br />
If the user simply wishes to view predefined end-use criteria, the ‘end-use related’ button will, as<br />
in the previous section, produce a list of all end-uses, from which the user may select, by<br />
highlighting, the relevant end-use and clicking on the ‘select’ button; those end-uses flagged by an<br />
‘s’ having a predefined system criteria and those flagged by a ‘u’, a user criteria.<br />
Pressing the ‘exit’ button, from the criteria definition screen, will return the user to the Enduse Search<br />
Details screen from where the Potential end-uses <strong>for</strong> a species search may be initiated, via the tick<br />
button.<br />
Potential End-Uses Search Results<br />
The search results are displayed in a similar manner to the Search by multiple properties results,<br />
with the end-uses under assessment (as opposed to species under assessment <strong>for</strong> one particular<br />
criteria set in the previous section) displayed roughly in order of potential. End-use names are<br />
displayed on the left of the screen, with a column, to the left of this list, headed ‘sys/user criteria’,<br />
showing which type of criteria was used to evaluate each end-use. If user-defined assessment<br />
criteria have been requested, as in the above example, <strong>for</strong> each end-use the program will try to use<br />
the ‘user-defined’ property requirements, but where this does not exist will use the system defined<br />
criteria, and vice versa.<br />
40
Also, an additional column is displayed, to the right of the screen, headed ‘known market<br />
(literature)’, as in the Search by multiple properties section where an end-use has been considered,<br />
showing the highest known level of use, recorded in the literature <strong>for</strong> each product, in relation to<br />
the particular species, and enables a comparison to be made between the assessment and the<br />
known degree of use. Degrees of use being defined as ‘export’, known to be sold on commercial<br />
markets; ‘local’, known to be sold in local markets; ‘unknown’, reported used, but the extent of use<br />
unknown; and ‘-’, no record of use.<br />
The particular species under consideration, is named by botanical name above the results, and where<br />
the species was identified by vernacular name this is also displayed at the top of the screen. In the<br />
example, the species was chosen by vernacular name ‘gum-anime tree’, the botanical name being<br />
Hymenaea courbaril.<br />
The column headed ‘property matches’ shows how the particular species fulfilled the timber<br />
property requirements <strong>for</strong> each of the end-uses. For every product the selected property is<br />
represented by a ‘property match indicator’, a coloured block or diamond (shown shaded in the<br />
guide), denoting how the evaluated properties met the required minimum levels. The data <strong>for</strong> the<br />
species can fit the property requirements in four different ways, dependent on how the data entries<br />
related to the requested property levels. The property match indicators are shown in four colours<br />
(default shown shaded here), such that:<br />
(light green)<br />
(dark green)<br />
(red)<br />
(grey)<br />
- property met the necessary requirements with unanimous opinion (all data entries in<br />
the required classes)<br />
- property met the necessary requirements but with variation in opinion (some but not<br />
all data entries in the required classes)<br />
- property failed to meet necessary requirements (no data entries in the required<br />
classes)<br />
- no data recorded <strong>for</strong> this property<br />
The colours of the match indicators may be altered through the setup option from the menu bar, a<br />
default is provided. Changing the selection will not alter an already present results display, the new<br />
colours will only come into operation on carrying out a new search. To view the colour key go to<br />
the setup option.<br />
For each requested feature the program will first check the ‘key’ property, and if it proves<br />
satisfactory, its level of suitability will be displayed through the appropriately coloured square; if<br />
the key property fails to meet the requirements or has no data, the program will check any<br />
alternative ‘or’ properties, that may have been specified, in turn. The first of these to appear<br />
satisfactorily will be indicated with an appropriately coloured diamond; the colour code being the<br />
same as <strong>for</strong> the ‘squares’.<br />
- alternative ‘or’ property, key property having failed.<br />
From the Potential end-uses search results screen, the user may carry out a number of operations,<br />
using the picture button toolbar at the bottom of the screen.<br />
Move between end-uses<br />
Using the arrow buttons, the user may move up and down between end-uses displayed on screen,<br />
and page through the end-uses listed. Highlighting an end-use, either with the arrow buttons or by<br />
clicking directly on it using the mouse, will enable the user to view further details relating to that<br />
criteria.<br />
41
Species Home Page<br />
Via the ‘Species Home Page’ button, the user may access the Species Home Page, which displays all<br />
taxonomic and distribution data and a wood surface image, where available, <strong>for</strong> the particular species,<br />
and provides access to the timber properties, end-uses, species observations and user notebook <strong>for</strong> that<br />
particular species (see Species Home Page in the Search by species name section <strong>for</strong> an illustration<br />
and further details).<br />
Match Detail<br />
The ‘match detail’ button allows the user to examine the property matching process in detail,<br />
having highlighted the end-use of interest, the user may view, in detailed data <strong>for</strong>mat, the data<br />
assessed <strong>for</strong> each property used in the search, and the degree to which the data met the required<br />
minimum values. The appropriate levels set <strong>for</strong> the search displayed in blue and flagged by a ‘>’<br />
(see the previous section <strong>for</strong> an illustration). From the Match Detail display the user may as,<br />
wherever detailed data is viewed (see Search by species name and Search by data content sections<br />
of the guide) access the reference sources, property observations and definition. The user should<br />
use the arrow buttons to page through the properties, and may print property matches to a file<br />
(RESULTS.TXT), having specified print options.<br />
Property overlay<br />
Via the ‘property overlay’ button (shown as an illuminated light bulb), the user may access an<br />
overlay listing the properties used to create each of the end-use criteria; each property name<br />
linking to the appropriate property match indicator and shown in the corresponding colour. In the<br />
illustration below, the overlay identifies the properties used in the evaluation of ‘furniture: chairs’<br />
as a potential product of Hymenaea courbaril, the colours of the property match indicators and<br />
appropriate property name indicating how the species met the minimum property requirements <strong>for</strong><br />
that particular end-use.<br />
To remove the property match overlay, simply click on the ‘property overlay’ button,<br />
(shown as an unlit light bulb, when the overlay is present).<br />
42
Print<br />
Selecting the ‘print’ button, from the Potential end-uses results screen, will print the current screen<br />
of results to file (RESULTS.TXT), the user will be asked to confirm this. Each screen of end-uses<br />
displayed can be printed separately with each subsequent screens concatenated on the page. The<br />
output of an evaluation from the Potential end-uses <strong>for</strong> a species section shows:<br />
· the actual evaluation with the colour coded symbols represented by printable characters,<br />
preceded by the interpretation of those characters<br />
· whether user or system criteria were used <strong>for</strong> each end-use<br />
· the level of use recorded in the literature <strong>for</strong> each end-use<br />
A page of output, <strong>for</strong> ‘gum-anime tree’, Hymenaea courbaril, the example used here, is shown<br />
below:-<br />
================================================================================<br />
Potential End-uses <strong>for</strong> gum-anime tree<br />
================================================================================<br />
property assessment indicators:<br />
O property met the necessary requirements with unanimous opinion<br />
o property met the necessary requirements, but variation in opinion<br />
x property failed to meet necessary requirements<br />
· no data recorded <strong>for</strong> this property<br />
--------------------------------------------------------------------------------<br />
sys/user user criteria<br />
property known market<br />
criteria end-use<br />
matches (literature)<br />
--------------------------------------------------------------------------------<br />
user furniture: general oo·oOoO··OOoOOox local<br />
user boats: fittings ooo·oOoo·OOoOO· -<br />
system cladding (external): agric./industrial ooOoOooo·Oox·O -<br />
system cladding (external): domestic ooOoOooo·Oox·O -<br />
system furniture: table/counter tops ooOO·oO·oooOOo -<br />
user furniture: cabinet work oo·oOoO··OOoOOo unspecified<br />
system house framing, carcassing oooo·ooooOx·oxo -<br />
system handles: wood working tools ooo·OoooO···OOO -<br />
system joinery (external): ground contact oOoOO·ooO···Oo -<br />
user furniture: laboratory & other bench tops oOo·oO·oooOOo· -<br />
system joinery (external): non-ground contact oOooO·ooO···oo -<br />
user furniture: chairs ooo·oo·Oo··oOOO -<br />
system mouldings, picture frames, etc. oo·ooo·oo··OOOo -<br />
system gates ooo·oo·OOO·Oo· -<br />
system tool handles: unspecified oooOOO··OOO· local<br />
user boats: decking ooo·oo·oo·xOoo· unspecified<br />
system construction: light oOooooo··oxo local<br />
user handles: axe, hammer oooOOO··OOO· -<br />
user agricultural implements ooo···ooo·ooOOO local<br />
system cladding (external): unspecified ooOoo·oxo·Oox· -<br />
system laminated products/beams oo·ooO·xo·OooOo -<br />
Help<br />
From the results screen pressing the ‘help’ button will access the context-sensitive help.<br />
Exit<br />
The ‘exit’ button will return the user to the initial End-uses search details screen, from where the user<br />
may start another search or exit back to the Main Menu.<br />
43
5.5 Summaries of Database Contents<br />
From the Main Menu, the fifth option examines the general content of the database, in terms of<br />
predefined static lists, species distribution and taxonomic material; as well as providing a pictorial<br />
catalogue of all wood surface images included in the database. In general this section lists the basic<br />
elements of the database, i.e. properties, end-uses, species etc., but does not show any timber<br />
in<strong>for</strong>mation.<br />
While in the Summaries of database contents section, the ‘System Status’ is displayed, this simply<br />
details the overall number of entries <strong>for</strong> species, synonyms, genera, families, vernacular names,<br />
timber properties, end-uses and references in the database.<br />
The display takes the <strong>for</strong>m of a menu bar at the top of the window with four sections of<br />
in<strong>for</strong>mation, namely properties/end-uses, distribution, taxonomy and images. Only one of these<br />
sub-menus can be active at any one time.<br />
Properties<br />
From the Properties sub-menu choosing the various options accesses the following lists of timber<br />
properties and end-uses:-<br />
all properties<br />
property groups<br />
properties in a given group<br />
descriptions of properties<br />
recorded end-uses<br />
a simple list of properties with relevant groups<br />
a simple list of groups<br />
a simple list of properties - having selected property<br />
group of interest from a scrollable list<br />
detailed descriptions of properties<br />
- having selected property range or group of interest<br />
a simple list of all end-uses, with an indication as to whether<br />
end-use related criteria have been defined <strong>for</strong> each end-use.<br />
44
Selecting ‘descriptions of properties’ invokes a further menu:<br />
Descriptions of properties<br />
The detail of how each property is recorded within the database can be shown by choosing<br />
‘descriptions of properties’.<br />
The following options <strong>for</strong> displaying details <strong>for</strong> any subset of the property list are available:<br />
all properties<br />
specific property group<br />
individual property<br />
describes all timber properties<br />
describes properties in a given group<br />
- having selected a group of interest from a scrollable list<br />
describes a specific property<br />
- having selected a particular property from a scrollable<br />
The description <strong>for</strong> each property displays the property name, the group the property belongs to,<br />
database structure and a definition. Under the heading ‘database structure’ are displayed the<br />
descriptors (levels) used to depict the property, and if relevant the possible conditions under which<br />
data were collected; generally, qualitative data are described by a list of possible descriptions and<br />
quantitative data by a range of size classes. Under the heading ‘definition and related in<strong>for</strong>mation’,<br />
a technical definition and any related in<strong>for</strong>mation are displayed; and if a quantitative property the<br />
exact values <strong>for</strong> the descriptors.<br />
In the following example, <strong>for</strong> ‘shrinkage - radial’, the display shows that the property belongs to<br />
the movement/shrinkage property group, that data can be recorded under 5 different descriptors,<br />
from very small to large, specifying which of 2 conditions, green to 12% m.c. or green to oven dry,<br />
the data items were collected under; a definition is provided and the exact values <strong>for</strong> the different<br />
descriptors specified.<br />
45
If the user has selected to view more than one property, the arrow buttons at the bottom of the screen<br />
may be used to page through the properties. Property definitions are available throughout the system,<br />
wherever detailed property data are presented and the ‘property definition’ button displayed.<br />
Where a simple list is displayed, <strong>for</strong> example having selecting ‘all properties’ (the resulting list<br />
illustrated below) in order to close it the user should select ‘File’ and then ‘close’ and to print the<br />
list to file (RESULTS.TXT) the user should select ‘File’ and then ‘print’.<br />
Distribution<br />
The second sub-menu describes the static list of countries and geographical regions used in the<br />
database and can also show the distribution of each species.<br />
countries<br />
geographical regions<br />
countries in a given region<br />
distribution of a given species<br />
species from a given country<br />
species from a given region<br />
a list of countries, with corresponding regions<br />
a list of geographical regions<br />
a list of countries in a specific region<br />
- having selected region of interest from scrollable list<br />
a list of countries, with corresponding regions, where a<br />
species grows - having selected a species of interest<br />
a list of species which grow in a specific country<br />
- having selected country of interest<br />
a list of species which grow in a specific region<br />
- having selected region of interest<br />
Selecting any one of these options will produce a list in similar <strong>for</strong>mat to the lists of properties<br />
described in the previous section.<br />
46
For example, selecting the option ‘Species from a given country’ will first produce a scrollable list of<br />
countries to select from:-<br />
Then, having chosen a particular country, say Australia, a list of all the species from that country<br />
in the database will be displayed, which can be printed to file or closed in the same way as the<br />
property lists in the previous section. The top of such a list is illustrated here:<br />
Taxonomy<br />
The third sub-menu describes the taxonomic details of the species in the database.<br />
families/genera<br />
species/synonyms<br />
vernacular names<br />
displays all details of family/genus hierarchy<br />
displays all or any subset of the recorded species names<br />
including any synonyms or misapplied names<br />
displays all or any subset of the trade/commercial names<br />
and common/local names, together with the botanical names<br />
of the species<br />
Selecting each of these invokes further menus.<br />
47
Families/genera<br />
all genera<br />
all families<br />
genera in a given family<br />
family of a given genus<br />
displays all genus names with corresponding family<br />
displays all family names<br />
displays all genera belonging to a specific family<br />
- having selected family of interest<br />
displays the family name of a specific genus<br />
- having selected genus of interest<br />
Species/synonyms<br />
all species (excl synonyms)<br />
all species (incl synonyms)<br />
species in a given genus<br />
species in a given family<br />
displays all primary species names stored in<br />
the database, with appropriate family, excluding<br />
those which are synonyms or misapplied names<br />
displays all recorded species names stored, with<br />
appropriate family, names including<br />
synonyms/misapplied names<br />
displays recorded species names (including<br />
synonyms/misapplied names) belonging to a<br />
specific genus - having selected genus of interest<br />
displays recorded species names (including<br />
synonyms/misapplied names) belonging to a<br />
specific family - having selected family of interest<br />
synonyms of a given species displays synonyms and misapplied names, with<br />
appropriate family of a specific species - having<br />
selected species of interest<br />
Vernacular names<br />
all vernacular names<br />
all trade names<br />
all common names<br />
displays all the vernacular names recorded in the database,<br />
and the botanical names of the species to which they relate<br />
displays all the trade/commercial names recorded, and the<br />
associated botanical names<br />
displays all the common/local names recorded, and<br />
the associated botanical names<br />
vernacular names of a given species<br />
displays the trade and common names of a specific<br />
species - having selected a species of interest<br />
species with a given vernacular name displays species with a trade or common name<br />
containing a given name - having entered a<br />
vernacular name of interest (either whole or part of<br />
the name may be entered)<br />
Displays are, as in the other summaries sections, in the <strong>for</strong>m of lists, which may be printed to file.<br />
48
For example, to view species with a particular vernacular name, firstly select ‘vernacular names’,<br />
the options described above are then displayed, choosing ‘species with a given vernacular name’,<br />
will prompt the user to enter a vernacular name (either whole or part of a name).<br />
If, <strong>for</strong> example, ‘iron’ was entered as the vernacular name the display would then list all vernacular<br />
names which include the text ‘iron’, along with details as to whether it was considered to be a trade<br />
or common name (with associated reference code number if common) and the botanical name it<br />
relates to. The illustration below show the beginning of such a list:-<br />
Images<br />
This section not only allows the user to browse through all the scanned wood surface images in the<br />
database, but also enables the direct comparison of wood surface images <strong>for</strong> up to four selected<br />
species. Selecting ‘Images’ will result in the following window displaying four images, each with<br />
a species name below them:-<br />
49
In order to select a species, highlight a popup bar (by clicking on one of the species names) and a<br />
scrollable list of all species names within the database will be displayed:-<br />
The user may then select from the scrollable list directly; pressing the first letter of the required<br />
species will take the list on to the correct alphabetical section of the list. To browse through the<br />
images press the up and down arrows (on the keyboard) while a popup bar is selected<br />
(highlighted).<br />
50
5.6 References<br />
From the Main Menu, the sixth option is the ‘References’ section, which allows the user to peruse<br />
the publication list independently of the data. It can also show references relating to specific species,<br />
properties, end-uses and/or countries.<br />
Each reference is described by the author(s), publication date, title and the journal or publisher, and<br />
is given a unique reference code number, which enables the user to identify the reference from<br />
which each item of data has been abstracted.<br />
Initially, the Reference Search screen displays all the references used in the abstraction of data in a<br />
scrollable list at the top of the screen. In order to select and view references of more particular<br />
interest a number of ways of restricting the displayed list are provided.<br />
1. By highlighting a particular reference in the scrollable publications list so as to view a single<br />
reference.<br />
2. By entering the reference code number (if known) in the ‘Reference code’ field, so as to view a<br />
single reference.<br />
3. By entering any combination of restrictions in the following fields, to view a list of references:<br />
i.) The Publication date - can restrict the list of references to those from a specific year or range of<br />
dates. The user should enter the earliest year of publication in the first box and press the enter key,<br />
and then the latest date in the ‘to’ box and press the enter key. The range of dates are inclusive, if the<br />
earlier date is entered but not a latest the search will assume from that date and if the first box and not<br />
the second is completed the search will assume up to that date. In order to search <strong>for</strong> one year enter<br />
the same year in each box.<br />
51
ii). by using the Free text search. Text may be entered (in upper or lower case, search is not case<br />
sensitive) in the following fields:- Author - any text within the author’s name, Title - any text<br />
contained within the reference’s title, Journal - any text contained within the Journal or Publisher’s<br />
name; the enter key should be pressed between entries.<br />
For example typing ‘smith’ in the author field as shown here and<br />
then pressing enter, will cause the scrollable list of species to<br />
display only those references with smith included in the author’s<br />
name as illustrated below:<br />
iii). by clicking on Select data range to the right of the screen under the Data Restrictions heading,<br />
which takes the user onto a further screen illustrated below, and enables references to be selected<br />
which relate to specific data.<br />
The reference list can be restricted here, by clicking on the relevant check boxes and selecting from<br />
scrollable lists, by range of properties of interest (none, all, a single property, the prime properties or<br />
any number of property groups) and/or end-uses of interest (none, all or a single end-use); and by the<br />
search range - by species by name (all species, the benchmark species, a single genus or a single<br />
species selected either by botanical name or by entering a vernacular name) and/or by species by<br />
distribution (all areas, a single country or a single region).<br />
In the example the user has restricted the search, by selecting the relevant options, to references that<br />
contain data on the prime properties and species that grow in Australia; when satisfied with the data<br />
restrictions clicking on the ‘search’ button (the tick button) will return the user to the initial screen<br />
where the relevant references will then be displayed within the scrollable publications list, and the<br />
search restrictions will be noted in the data restrictions box.<br />
From the initial Reference search screen the following can be undertaken by using the relevant<br />
buttons:<br />
52
Reset<br />
Having made any restrictions, by whatever method, the user may wish to return to the complete list<br />
of references, in order to do this the ‘reset’ button should be used to clear any restrictions made.<br />
View<br />
Once any required restrictions have been made to the list of selected references, to view a particular<br />
reference the user should either double click on that reference or highlight it and then click on the<br />
‘view’ button. To view all the selected references, choose the ‘ALL SELECTED REFERENCES’<br />
entry, at the top of the list.<br />
When viewing the selection, details displayed <strong>for</strong> each reference include: its code number, author(s),<br />
publication date, publication title, and the journal or publisher. The example below was selected<br />
from a search <strong>for</strong> ‘smith’ in the author field as described under ‘Free text search’, 10 references<br />
were found to include this text in the author field and the user has chosen to view ‘ALL<br />
SELECTED REFERENCES’ of which this is the fourth (Reference 4 of 10):-<br />
Having chosen to view a selection the user may page through the references using the arrow keys at<br />
the bottom of the window; the arrow at the extreme left will take the user to the first reference of a<br />
list, the second left facing arrow will take the user to the previous reference, and similarly with the<br />
right facing arrows, the inner right facing arrow will take the user on to the next reference and the<br />
furthest right arrow will take the user to the end of the list. Pressing the ‘exit’ button will take the user<br />
back to the initial search screen.<br />
Print<br />
From the initial screen, having made any required restrictions to the list of selected references, the<br />
‘print’ button will enable the user to print a selection of references to file (RESULTS.TXT).<br />
Help<br />
Context-sensitive help is available throughout the section via the ‘help’ button.<br />
Exit<br />
From the initial screen, the ‘exit’ button will take the user back to the Main Menu.<br />
5.7 Exit<br />
The final option from the Main Menu is Exit,<br />
53
6. Appendices<br />
Appendix 1: Technical Aspects of <strong>Prospect</strong><br />
Hardware<br />
The <strong>Prospect</strong> database was developed to make timber in<strong>for</strong>mation accessible to a wide range of<br />
users by making a portable and user-friendly package <strong>for</strong> use on af<strong>for</strong>dable computer equipment.<br />
The database has been designed to operate on IBM-compatible microcomputers running <strong>Windows</strong><br />
3.1 or <strong>Windows</strong> 95 and requires a minimum configuration of:<br />
· 486 processor or better (Pentium recommended)<br />
· 4Mb RAM (8 Mb or more recommended)<br />
· 24Mb of hard disk space (full version)<br />
· CD-ROM drive<br />
· colour VGA monitor (SVGA 256 colours recommended)<br />
· mouse or other pointing device<br />
Software<br />
The FoxPro package was chosen as the database management system to handle the in<strong>for</strong>mation <strong>for</strong><br />
<strong>Prospect</strong> <strong>for</strong> several reasons:<br />
It has flexible facilities <strong>for</strong> data presentation, file handling and menu control, together with a<br />
capacity to store and manage large amounts of data. It is also fast; with the vast wealth of<br />
in<strong>for</strong>mation that <strong>Prospect</strong> records, speed of operation was an essential consideration.<br />
Using the FoxPro Distribution Kit, a run-time version of the <strong>Prospect</strong> program can be produced so<br />
that is can be easily distributed to users at other sites without incurring copyright problems or royalty<br />
charges<br />
System default end-use related criteria - classifications<br />
In order to make some assessment of the potential uses of a timber, it is necessary to decide which<br />
qualities of the timber are most desirable, or indeed essential, <strong>for</strong> that product. The consultant on<br />
the project has had many years of experience in this field, and with his expert advice it has been<br />
possible to implement these judgements <strong>for</strong> end-uses recorded in <strong>Prospect</strong>.<br />
Based on the recorded timber properties and their descriptions, a list of required properties and<br />
their minimum acceptable levels has been built up <strong>for</strong> several end-uses. This involves simply<br />
indicating which descriptors are acceptable <strong>for</strong> each required property. The program makes<br />
provision <strong>for</strong> alternative or compensating properties to be specified. For example, where a timber<br />
is not naturally durable it may be acceptable if it was amenable to preservation treatment.<br />
The program attempts to display the species/use matches very approximately in descending order<br />
of suitability so that the user need only scan the first few screens of results. To do this it uses a<br />
very basic ‘scoring’ system.<br />
Each property in the list of required features is examined in turn. Should there be no satisfactory<br />
data <strong>for</strong> a ‘key’ property (i.e. either there are no data recorded or all data entries show it is an<br />
unacceptable feature) it will consider, in turn, data <strong>for</strong> any alternative properties if they have been<br />
specified. If an alternative property is satisfactory, it will be shown in the results but these will be<br />
scored slightly lower than a key feature.<br />
To per<strong>for</strong>m this assessment, the program examines the ‘summarised’ <strong>for</strong>m of the data. For any<br />
given end-use and species, the program looks at the total number of recorded data entries (x) <strong>for</strong><br />
each descriptor. There are four possible situations which may arise, each of which is given a score<br />
as follows:<br />
54
Situation Meaning Score<br />
(key<br />
property)<br />
All data entries (x) are in the<br />
range of required descriptors<br />
Some of the data entries (x) are in<br />
the range of descriptors<br />
Complete data match - all reference<br />
sources show property completely<br />
satisfactory<br />
partial data match - some reference<br />
sources show property satisfactory,<br />
but others indicate contradictory<br />
opinion<br />
Score<br />
(alternative<br />
property)<br />
10 8<br />
9 7<br />
There are no recorded data No in<strong>for</strong>mation to <strong>for</strong>m an opinion 0 0<br />
None of the data entries (x) are in<br />
the range of required descriptors<br />
Failed data match - all reference<br />
sources show property unsuitable<br />
-30 -30<br />
For each species, the scores <strong>for</strong> each property are totalled and recorded. In addition to this, each<br />
property is given a weighting according to its position in the property requirements list. The properties<br />
should be specified in order of importance; the weighting is allocated linearly with the first property<br />
given a high weighting and the last a low. This is so that the most essential features are stressed.<br />
As a final stage, a score is also given <strong>for</strong> the level of known use recorded in the published sources.<br />
This is only a small addition, mainly to provide distinction where only literature data are displayed.<br />
Scores are given as follows:<br />
Recorded level of use<br />
Score<br />
Available on commercial markets (i.e. exported) 3<br />
Available on local markets 2<br />
Used, but degree of use unknown 1<br />
No in<strong>for</strong>mation recorded 0<br />
The species or uses are then displayed in descending order of score. When potential end-uses <strong>for</strong> a<br />
given species are being assessed, the distinction between the most and least suitable is complicated by<br />
the fact that <strong>for</strong> each end-use a different set of property requirements is being considered. To<br />
overcome this, the score <strong>for</strong> each use is divided by the number of features being considered, i.e. the<br />
mean score per feature is used.<br />
55
Appendix 2: List of Timber Properties<br />
Characteristic Descriptors Details/Conditions Definition<br />
tree feature<br />
tree height (m) 0 -
Characteristic Descriptors Details/Conditions Definition<br />
deposits<br />
whitish deposits in vessels<br />
yellowish deposits in vessels<br />
stone/gum aggregates<br />
gum/resin exudation<br />
growth features of the wood gum/resin streaks<br />
latex or other ducts<br />
included phloem<br />
The occurrence of gums and<br />
mineral deposits in the structure<br />
of the wood.<br />
The occurrence of generally<br />
undesirable growth features of<br />
the wood.<br />
silica present<br />
slight<br />
moderate<br />
severe<br />
0.5%<br />
The extent of silica deposits in<br />
the heartwood.<br />
grain<br />
straight<br />
wavy<br />
spiral<br />
interlocked<br />
other<br />
The alignment of cells relative<br />
to the axis of the tree or the<br />
longitudinal edge of an<br />
individual piece of sawn timber.<br />
figure<br />
growth ring<br />
stripe<br />
ripple<br />
mottle<br />
dimple<br />
burr<br />
ray<br />
irregular colour<br />
other<br />
The distinctive ornamental<br />
markings on the longitudinal<br />
surface of wood as a result of<br />
the arrangement of its<br />
constituent tissues, irregular<br />
colouration, defects or the<br />
nature of the grain.<br />
figure (occurrence)<br />
very fine & distinct<br />
distinct<br />
weak<br />
variable<br />
The intrinsic quality of the<br />
figure.<br />
texture<br />
lustre<br />
fine<br />
fine/medium<br />
medium<br />
medium/coarse<br />
coarse<br />
pronounced<br />
lustrous<br />
slightly lustrous<br />
dull<br />
Structural characteristics of<br />
wood as revealed by touch or<br />
reaction to cutting tools.<br />
(Largely determined by<br />
distribution and size of the<br />
various cells).<br />
The reflective properties of cell<br />
walls be<strong>for</strong>e any finish is<br />
applied.<br />
toxicity<br />
non-toxic<br />
respiratory effects<br />
dermatitic effects<br />
poisonous<br />
unspecified toxicity<br />
A characteristic that provides an<br />
indication of the reactive<br />
effects which may arise when<br />
handling or working a wood.<br />
staining properties<br />
non-staining<br />
coloured water-soluble extract<br />
reacts with Fe to discolour wood<br />
other staining characteristics<br />
Extractives in wood which react,<br />
usually in the presence of water,<br />
to cause discolouration of the<br />
wood or adjacent materials.<br />
corrosive properties<br />
non-corrosive<br />
reacts with metals<br />
density (kg/m 3 ) 0-199 basic 0- 239 air-dry<br />
200-299 basic 240- 359 air-dry<br />
300-399 basic 360- 479 air-dry<br />
400-499 basic 480- 599 air-dry<br />
500-599 basic 600- 719 air-dry<br />
600-699 basic 720- 839 air-dry<br />
700-799 basic 840- 959 air-dry<br />
800-899 basic 960-1079 air-dry<br />
900-999 basic 1080-1199 air-dry<br />
>1000 basic >1200 air-dry<br />
movement in service<br />
shrinkage - radial<br />
shrinkage - tangential<br />
shrinkage - volumetric<br />
small<br />
medium<br />
large<br />
stable<br />
not stable/prone to move<br />
very small<br />
small<br />
moderate<br />
fairly large<br />
large<br />
very small<br />
small<br />
moderate<br />
fairly large<br />
large<br />
very small<br />
small<br />
moderate<br />
fairly large<br />
large<br />
movement/shrinkage characteristics<br />
4.5%<br />
conditions:<br />
experiment<br />
reputation<br />
(a)<br />
(b)<br />
up to 2% up to 3%<br />
<strong>2.1</strong>-2.5% 3.1-4.0%<br />
2.6-3.0% 4.1-5.0%<br />
3.1-3.5% 5.1-6.0%<br />
>3.5% >6.0%<br />
conditions:<br />
green to 12% m.c.(a)<br />
green to o.d. (b)<br />
(a)<br />
(b)<br />
up to 3% up to 5%<br />
3.1-4.0% 5.1-6.5%<br />
4.1-5.0% 6.6-8.0%<br />
5.1-6.0% 8.1-9.5%<br />
>6.0% >9.5%<br />
conditions:<br />
green to 12% m.c.(a)<br />
green to o.d. (b)<br />
(a)<br />
(b)<br />
up to 5% up to 8%<br />
5.1-6.5% 8.1-10.5%<br />
6.6-8.0% 10.6-13.0%<br />
8.1-9.5% 13.1-15.5%<br />
>9.5% >15.5%<br />
conditions:<br />
green to 12% m.c.(a)<br />
green to o.d. (b)<br />
The corrosive action when a<br />
timber comes into contact with<br />
metal, such as screws, nails,<br />
bolts and plates.<br />
The “air” dry density of wood at<br />
12-15% moisture content (kg/m 3 )<br />
related to basic density (ovendry<br />
weight, green volume).<br />
Movement records dimensional<br />
stability subsequent to drying.<br />
It is calculated as the sum of<br />
the percentage radial and<br />
tangential changes consequent<br />
upon a change in relative<br />
humidity from 90% to 60%.<br />
Shrinkage that occurs<br />
perpendicular to the growth<br />
rings, it is approximately<br />
proportional to moisture loss.<br />
Radial shrinkage is roughly half<br />
that of tangential shrinkage.<br />
Shrinkage that occurs<br />
perpendicular to the grain and<br />
parallel to the growth rings.<br />
Volumetric shrinkage is slightly<br />
less than the sum of axial,<br />
radial and tangential shrinkage.<br />
mechanical characteristics<br />
57
Characteristic Descriptors Details/Conditions Definition<br />
very low<br />
(a)<br />
(b)<br />
low<br />
85<br />
maximum crushing strength<br />
(parallel to grain)<br />
modulus of rupture/<br />
bending strength<br />
modulus of elasticity/<br />
bending stiffness<br />
toughness - total work<br />
toughness - work to maximum<br />
load<br />
toughness - hammer drop<br />
toughness - pendulum<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
(a)<br />
(b)<br />
175<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
(a)<br />
(b)<br />
20.0<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
0.440<br />
(a)<br />
(b)<br />
0.220<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
1.60<br />
71.2<br />
The maximum compressive strength<br />
of the specimen parallel to the<br />
grain.<br />
The highest stresses in the<br />
outermost fibres of the wood when<br />
the beam breaks under the<br />
influence of a load.<br />
The linear relationship between<br />
stress and strain within the<br />
elastic range of a material,<br />
providing an indication of<br />
stiffness.<br />
The energy required to cause<br />
complete failure in a beam when<br />
the load is applied rapidly.<br />
Work to maximum load represents<br />
the ability of the specimen to<br />
absorb shock with some permanent<br />
de<strong>for</strong>mation.<br />
A hammer of a given weight is<br />
dropped on a beam from<br />
successively increasing heights<br />
until rupture occurs. The height<br />
of the maximum drop that causes<br />
failure represents the ability of<br />
wood to absorb shocks that cause<br />
failure beyond the proportional<br />
limit.<br />
A pendulum weight is<br />
progressively raised and released<br />
until it causes failure.<br />
hardness (Janka side grain) very soft<br />
soft<br />
medium<br />
hard<br />
very hard<br />
(a)<br />
(b)<br />
12000<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
The load required to imbed a<br />
11.3mm diameter hardened steel<br />
ball into the sample surface to<br />
one half the diameter of the<br />
ball.<br />
shear(parallel to grain)<br />
very low<br />
low<br />
medium<br />
high<br />
very high<br />
(a)<br />
(b)<br />
22.0<br />
The measure of the resistance of<br />
the timber to shearing, tests<br />
being made in both the tangential<br />
and radial plane.<br />
conditions:<br />
green<br />
(a)<br />
12% to 15% m.c. (b)<br />
natural durability<br />
very durable<br />
durable<br />
moderately durable<br />
non durable<br />
perishable<br />
wood staining fungal attack resistant<br />
sapwood susceptible<br />
heartwood susceptible<br />
Pinworm attack (ambrosia unusual or absent<br />
beetle)<br />
commonly present<br />
present in standing tree<br />
attack of felled log<br />
occurrence in heartwood<br />
Powder post attack (Lyctid resistantsusceptible<br />
& Bostrychid)<br />
durability characteristics<br />
(a) (b) (c)<br />
years years av. dry wt. loss %<br />
>25 >10 nil or negligible<br />
15-
Characteristic Descriptors Details/Conditions Definition<br />
termite attack (Isoptera) resistantmoderately<br />
resistantsusceptible<br />
Marine borer attack<br />
amenability to preservation<br />
(heartwood)<br />
amenability to preservation<br />
(sapwood)<br />
drying (rate)<br />
drying (ease)<br />
kiln drying rate(green to<br />
12% m.c.)<br />
resistantmoderately<br />
resistantsusceptible<br />
permeable<br />
moderately resistant<br />
resistant<br />
extremely resistant<br />
permeable<br />
moderately resistant<br />
resistant<br />
extremely resistant<br />
fast<br />
moderate<br />
slow<br />
easy<br />
moderate<br />
difficult<br />
variable<br />
rapid<br />
fairly rapid<br />
rather slow<br />
slow<br />
kiln schedule UK=A US=T2D4/T2D3 Fr=1<br />
UK=B US=T2C2/T2C1 Fr=2<br />
UK=C US=T3C2/T3C1 Fr=3<br />
UK=D US=T3D2/T3C1 -<br />
UK=E US=T6D2/T3D1 Fr=5<br />
UK=F US=T6D4/T3D3 Fr=6<br />
UK=G US=T8B3/T5B1 -<br />
UK=H US=T10D4S/T8D3S Fr=7<br />
UK=J US=T10D5S/T8D4S Fr=4<br />
UK=K US=T13C4S/T11D3S -<br />
UK=L US=T14C6S/T12C5S -<br />
UK=M - -<br />
drying degrade - surface<br />
checking<br />
drying degrade - end<br />
splitting<br />
none<br />
slight<br />
moderate<br />
severe<br />
none<br />
slight<br />
moderate<br />
severe<br />
conditions:<br />
field tes<br />
laboratory test<br />
observation/reputation<br />
conditions:<br />
salt water test<br />
observation/reputation<br />
tropical waters<br />
temperate waters<br />
permeability characteristics<br />
complete penetration by preservative<br />
lateral penetration 6-18mm<br />
lateral penetration 3-6mm<br />
effectively untreatable<br />
complete penetration by preservative<br />
lateral penetration 6-18mm<br />
lateral penetration 3-6mm<br />
effectively untreatable<br />
drying characteristics<br />
conditions:<br />
air drying<br />
kiln drying<br />
conditions:<br />
air drying<br />
kiln drying<br />
(a) (b) (c)<br />
84<br />
conditions:<br />
up to 32mm thickness (a)<br />
33 to 63mm thickness (b)<br />
>63mm thickness (c)<br />
Damage caused by insects of the<br />
Order Isoptera.<br />
Damage caused in marine or<br />
brackish water by marine molluscs<br />
and marine crustaceans.<br />
The extent to which heartwood can<br />
be impregnated with preservatives<br />
under pressure to protect against<br />
fungal, insect or marine attack.<br />
The extent to which sapwood can<br />
be impregnated with preservatives<br />
under pressure to protect against<br />
fungal, insect or marine attack.<br />
The rate at which timber dries<br />
from a green condition.<br />
The ease or difficulty with which<br />
timber can be dried from a green<br />
condition.<br />
The time in days to kiln dry<br />
timber from green to 12% moisture<br />
content.<br />
Equivalent kiln schedules used in<br />
the U.K. (United Kingdom), U.S.<br />
(United States of America), and<br />
Fr (France).<br />
Separation of wood fibres along<br />
the grain <strong>for</strong>ming a crack or<br />
fissure that does not penetrate<br />
through the timber from one<br />
surface to the other.<br />
Split at the end of a log or<br />
piece.<br />
drying degrade -<br />
collapse/honeycomb<br />
drying degrade - cup<br />
none<br />
slight<br />
moderate<br />
severe<br />
none<br />
slight<br />
moderate<br />
severe<br />
Collapse is the flattening or<br />
buckling of cells during drying<br />
which become manifest in<br />
excessive or uneven shrinkage.<br />
Honeycomb is the separation of<br />
the fibres in the interior of a<br />
piece induced by drying stresses.<br />
Curvature of a piece of timber<br />
across the width of the face.<br />
drying degrade - spring/bow none<br />
slight<br />
moderate<br />
severe<br />
drying degrade - twist/warp none<br />
slight<br />
moderate<br />
severe<br />
Bow: curvature of a piece of<br />
timber lengthwise in a plane<br />
normal to the edge, Spring:<br />
curvature of a piece of timber<br />
lengthwise in a plane normal to<br />
the face.<br />
Spiral distortion of a piece of<br />
timber lengthwise.<br />
drying degrade - knots<br />
splits/loosening<br />
none<br />
slight<br />
moderate<br />
severe<br />
The splitting or loosening of<br />
knots during drying.<br />
resin/gum exudation on<br />
drying<br />
absent<br />
present<br />
Movement of mobile extractives<br />
(gums and resins) which occur<br />
when timber is dried as ambient<br />
temperatures increase.<br />
sawing - general (green)<br />
easy<br />
moderate<br />
difficult<br />
variable<br />
sawing characteristics<br />
The ease or difficulty with which<br />
a timber can be sawn when green.<br />
sawing - general (dry)<br />
easy<br />
moderate<br />
difficult<br />
variable<br />
The ease or difficulty with which<br />
a timber can be sawn when “air”<br />
dry (12-15% moisture content).<br />
59
Characteristic Descriptors Details/Conditions Definition<br />
mild<br />
moderate<br />
severe<br />
sawing - blunting effect<br />
(green)<br />
The effect of a timber on the<br />
per<strong>for</strong>mance of a saw when the<br />
timber is green.<br />
sawing - blunting effect<br />
(dry)<br />
mild<br />
moderate<br />
severe<br />
The effect of a timber on the<br />
per<strong>for</strong>mance of a saw when the<br />
timber is dry.<br />
machining - general<br />
easy<br />
moderate<br />
difficult<br />
variable<br />
machining - blunting effect slight<br />
moderate<br />
fairly severe<br />
severe<br />
variable<br />
machining characteristics<br />
The ease or difficulty with which<br />
a timber can be machined.<br />
The effect of a timber on the<br />
per<strong>for</strong>mance of a machine when the<br />
timber is processed.<br />
planing (ease)<br />
planing (finish)<br />
mortising (ease)<br />
mortising (finish)<br />
moulding (ease)<br />
moulding (finish)<br />
turning (ease)<br />
turning (finish)<br />
boring<br />
recessing & routing (ease)<br />
easy<br />
moderate<br />
difficult<br />
good<br />
satisfactory<br />
poor<br />
easy<br />
moderate<br />
difficult<br />
good<br />
satisfactory<br />
poor<br />
easy<br />
moderate<br />
difficult<br />
good<br />
satisfactory<br />
poor<br />
easy<br />
moderate<br />
difficult<br />
good<br />
satisfactory<br />
poor<br />
easy<br />
moderate<br />
difficult<br />
easy<br />
moderate<br />
difficult<br />
recessing & routing (finish) good<br />
satisfactory<br />
poor<br />
steam bending<br />
very good<br />
good<br />
moderate<br />
poor<br />
very poor<br />
750<br />
conditions:<br />
radius of curvature supported<br />
radius of curvature not supported<br />
The ease or difficulty with which<br />
a timber can be machined planed.<br />
The quality of finish when a<br />
timber is planed.<br />
The ease or difficulty with which<br />
a mortise can be cut in a timber<br />
either by hand or with a machine.<br />
The quality of finish when a<br />
timber is mortised.<br />
The ease or difficulty with which<br />
a timber can be shaped.<br />
The quality of finish when a<br />
timber is moulded.<br />
The ease or difficulty with which<br />
a timber can be machined on a<br />
lathe.<br />
The quality of finish when a<br />
timber is machined on a lathe.<br />
The ease or difficulty with which<br />
a timber can be bored<br />
perpendicular to the grain.<br />
The ease or difficulty with which<br />
a timber can be slotted, rebated<br />
or routed.<br />
The finish achieved when a timber<br />
is slotted, rebated, or routed.<br />
The curvature to which a 1 inch<br />
(25mm) thick sample may be steam<br />
bent with an expectation of a 5%<br />
failure rate.<br />
nailing (ease)<br />
easy<br />
difficult<br />
possible if prebored<br />
fastening characteristics<br />
The ease or difficulty of nailing<br />
a timber.<br />
nailing (hold)<br />
good<br />
satisfactory<br />
poor<br />
The tenacity with which a timber<br />
holds a nail.<br />
screwing (ease)<br />
easy<br />
difficult<br />
possible if prebored<br />
The ease or difficulty of<br />
screwing a timber.<br />
screwing (hold)<br />
good<br />
satisfactory<br />
poor<br />
The tenacity with which a timber<br />
holds a screw.<br />
resistance to splitting<br />
(nail & screw)<br />
excellent<br />
good<br />
fair<br />
poor<br />
very poor<br />
The resistance of a timber to<br />
splitting when nailed or screwed.<br />
gluing (solid wood)<br />
easy<br />
moderate<br />
difficult<br />
surfacing characteristics<br />
The ease or difficulty with which<br />
a timber can be glued.<br />
finishing - general<br />
good<br />
satisfactory<br />
poor<br />
The general quality of the<br />
finished surface.<br />
sanding (ease)<br />
easy<br />
moderate<br />
difficult<br />
The ease or difficulty with which<br />
a timber can be finished using a<br />
paper or cloth backed abrasive.<br />
60
Characteristic Descriptors Details/Conditions Definition<br />
sanding (finish)<br />
good<br />
satisfactory<br />
poor<br />
The quality of the surface finish<br />
obtained when using a paper or<br />
cloth backed abrasive.<br />
staining<br />
painting<br />
good<br />
satisfactory<br />
poor<br />
good<br />
satisfactory<br />
poor<br />
conditions: requires filling<br />
conditions: requires filling<br />
The ease with which a timber can<br />
be uni<strong>for</strong>mly stained, using<br />
either a water or spirit based<br />
stain, and the quality of the<br />
resulting stained surface.<br />
The ease with which a timber can<br />
be painted and the quality of the<br />
finished surface.<br />
varnishing<br />
good<br />
satisfactory<br />
poor<br />
conditions: requires filling<br />
The ease with which a timber can<br />
be varnished and the quality of<br />
the finished surface.<br />
polishing<br />
good<br />
satisfactory<br />
poor<br />
conditions: requires filling<br />
The ease with which a timber can<br />
be polished, e.g. French<br />
polished, and the quality of the<br />
finished surface.<br />
veneer - bolt preparation<br />
veneer- ease of cutting<br />
veneer - drying degrade<br />
veneer - gluing<br />
steaming required<br />
no steaming needed<br />
easy<br />
moderately easy<br />
difficult<br />
no degrade - dries flat/no split<br />
slight/moderate - buckles/splits<br />
moderate/severe - collapse +b/s<br />
good<br />
variable<br />
difficult<br />
veneer production characteristics<br />
conditions:<br />
rotary cutting<br />
slicing<br />
conditions:<br />
uf resin<br />
pf resin<br />
other resin<br />
Treatment of a timber in order<br />
<strong>for</strong> it to produce an acceptable<br />
veneer.<br />
The ease or difficulty with which<br />
a bolt or flitch of timber can be<br />
peeled or sliced.<br />
The extent of degrade, typically<br />
splits and distortion, of a<br />
veneer on drying.<br />
The ease or difficulty with which<br />
a veneer of a timber can be glued<br />
and the resulting tenacity of the<br />
bond.<br />
61
Appendix 3: List of End-Uses<br />
agricultural implements<br />
artificial limbs<br />
axles<br />
bakers items<br />
baskets<br />
battery separators<br />
bearings, cogs, pulleys, brake blocks<br />
beehives<br />
boats: building (general)<br />
boats: decking<br />
boats: fittings<br />
boats: framing<br />
boats: masts / flag masts<br />
boats: masts/spars (laminated)<br />
boats: masts/spars (single pole)<br />
boats: planking<br />
boxes, crates, pallets, packing cases<br />
bridges: unspecified<br />
brushbacks<br />
bungs, stoppers, plugs<br />
canoes<br />
carving<br />
charcoal<br />
chemical derivatives<br />
cladding (external): agric./industrial<br />
cladding (external): domestic<br />
cladding (external): unspecified<br />
coffins<br />
combs<br />
compressed wood<br />
construction: heavy<br />
construction: hydraulic<br />
construction: light<br />
cooperage: slack<br />
cooperage: tight<br />
cooperage: unspecified<br />
decking<br />
doors: unspecified<br />
draining boards<br />
drawing boards<br />
fencing: paling<br />
fencing: posts/stakes<br />
fencing: rails<br />
fencing: unspecified<br />
fibre building board/hardboard<br />
floats & lifebelts<br />
flooring: commercial heavy traffic<br />
flooring: commercial normal traffic<br />
flooring: domestic light traffic<br />
flooring: general<br />
flooring: industrial heavy traffic<br />
flooring: industrial light traffic<br />
food containers<br />
footwear<br />
fuelwood/briquettes<br />
furniture: cabinet work<br />
furniture: chairs<br />
furniture: general<br />
furniture: laboratory & other bench tops<br />
furniture: table/counter tops<br />
furniture: upholstered furniture<br />
gates<br />
gums, resins, tannins, oils<br />
handles: axe, hammer<br />
handles: broom, brush<br />
handles: cutlery/knife<br />
handles: unspecified<br />
handles: wood working tools<br />
house framing, carcassing<br />
insulation<br />
joinery (external): ground contact<br />
joinery (external): non-ground contact<br />
joinery (external): unspecified<br />
joinery (general): internal & external<br />
joinery (internal)<br />
ladders: rungs<br />
ladders: stiles<br />
ladders: unspecified<br />
laminated products/beams<br />
lasts, shoe/boot<br />
liquid fuel<br />
manicure sticks<br />
matches: boxes<br />
matches: splints<br />
mathematical instruments, rulers<br />
millwork<br />
mining timber, pitprops<br />
model making<br />
mouldings, picture frames, etc.<br />
musical instruments: percussion<br />
musical instruments: piano/organ parts<br />
musical instruments: strings<br />
musical instruments: unspecified<br />
musical instruments: wood wind<br />
nails, treenails, screws<br />
oars, paddles<br />
panelling<br />
particleboard/chipboard<br />
patterns<br />
pencils<br />
picking sticks<br />
piers: unspecified<br />
piling, groynes<br />
plywood corestock<br />
plywood: core (laminboard, blockboard)<br />
plywood: general<br />
plywood: veneer (exterior)<br />
plywood: veneer (interior)<br />
plywood: veneer (marine)<br />
poles: scaffolding<br />
poles: shunting<br />
poles: telegraph, transmission<br />
printers blocks<br />
pulp/paper<br />
rifle furniture<br />
rollers, mangles<br />
roof trusses: agricultural/industrial<br />
roof trusses: domestic<br />
roof trusses: unspecified<br />
ropes & fibres<br />
scaffold boards<br />
shingles, shakes<br />
shuttering (concrete)<br />
sleepers, cross ties<br />
sports items: archery bows<br />
sports items: baseball bats<br />
sports items: billiard cues<br />
sports items: cricket bats<br />
sports items: fishing rods<br />
sports items: golf club heads<br />
sports items: golf club shafts<br />
sports items: hockey sticks<br />
sports items: lacrosse sticks<br />
sports items: polo sticks<br />
sports items: skis<br />
sports items: tennis rackets<br />
sports items: unspecified<br />
steps (sides/treads)<br />
structural beams: unspecified<br />
structures: agricultural<br />
structures: domestic<br />
structures: freshwater<br />
structures: industrial<br />
structures: marine<br />
textile bobbins, shuttles, cotton reels<br />
textile machinery<br />
tobacco pipes<br />
tool handles: unspecified<br />
tools: mallets<br />
tools: planes<br />
tools: spirit levels<br />
toothpicks<br />
toys<br />
turnery: architectural & furniture<br />
turnery: dairy & kitchen<br />
turnery: ornamental<br />
turnery: unspecified<br />
vats, tanks<br />
vehicles: decking/flooring<br />
vehicles: framing<br />
vehicles: sidings, cab timber, etc.<br />
veneer: decorative<br />
veneer: general purpose<br />
veneer: unspecified<br />
waferboard<br />
walking sticks<br />
water associated products: unspecified<br />
water cooling towers<br />
well construction<br />
wharves: unspecified<br />
wheels: rims<br />
wheels: spokes<br />
wood flour<br />
wood wool<br />
yokes<br />
descriptors:<br />
used commercially/exported<br />
used locally<br />
used, but extent unknown<br />
known to be used and exported <strong>for</strong> this application<br />
known to be used locally <strong>for</strong> this application<br />
known to have been used <strong>for</strong> this application but extent of use unknown<br />
62
Appendix 4: List of countries/geographical regions<br />
Australasia<br />
Australia<br />
New Zealand<br />
Papua New Guinea<br />
West Irian<br />
Central America<br />
Belize<br />
Costa Rica<br />
El Salvador<br />
Guatemala<br />
Honduras<br />
Mexico<br />
Nicaragua<br />
Panama<br />
Central Southern Africa<br />
Angola<br />
Malawi<br />
Mozambique<br />
Zambia<br />
Zimbabwe<br />
East Africa<br />
Djibouti<br />
Ethiopia<br />
Kenya<br />
Somalia<br />
Tanzania<br />
Uganda<br />
East Asia<br />
China<br />
Japan<br />
North Korea<br />
South Korea<br />
Taiwan<br />
Equatorial Africa<br />
Burundi<br />
Cameroon<br />
Central African Republic<br />
Chad<br />
Congo<br />
Equatorial Guinea<br />
Gabon<br />
Rwanda<br />
Zaire<br />
Indian Ocean<br />
Comoro Islands<br />
Madagascar<br />
Maldives<br />
Mauritius<br />
Reunion<br />
Seychelles<br />
Middle Europe<br />
Austria<br />
Belgium<br />
Czech Republic<br />
Germany<br />
Hungary<br />
Luxembourg<br />
Netherlands<br />
Poland<br />
Slovakia<br />
Switzerland<br />
North Africa<br />
Algeria<br />
Egypt<br />
Libya<br />
Morocco<br />
Sudan<br />
Tunisia<br />
Western Sahara<br />
North America<br />
Canada<br />
U.S.A.<br />
North Atlantic<br />
Bermuda<br />
Canary Islands<br />
Cape Verde Islands<br />
Madeira<br />
Northern Europe<br />
Denmark<br />
Finland<br />
Great Britain<br />
Iceland<br />
Ireland<br />
Norway<br />
Sweden<br />
Pacific<br />
Fiji<br />
French Polynesia<br />
Hawaii<br />
New Caledonia<br />
Norfolk Island<br />
Solomon Islands<br />
Tonga<br />
Vanuatu<br />
Western Samoa<br />
South America<br />
Argentina<br />
Bolivia<br />
Brazil<br />
Chile<br />
Colombia<br />
Ecuador<br />
French Guiana<br />
Guyana<br />
Paraguay<br />
Peru<br />
Surinam<br />
Uruguay<br />
Venezuela<br />
South Eastern Europe<br />
Albania<br />
Bosnia<br />
Bulgaria<br />
Croatia<br />
Greece<br />
Italy<br />
Macedonia<br />
Romania<br />
Serbia<br />
Slovenia<br />
South Western Europe<br />
France<br />
Portugal<br />
Spain<br />
South East Asia<br />
Andaman Islands<br />
Borneo<br />
Brunei<br />
Burma<br />
Cambodia<br />
Indonesia<br />
Laos<br />
Malaysia<br />
Philippines<br />
Sabah<br />
Sarawak<br />
Sumatra<br />
Thailand<br />
Vietnam<br />
Southern Africa<br />
Botswana<br />
Lesotho<br />
Namibia<br />
South Africa<br />
Swaziland<br />
Southern Asia<br />
Afghanistan<br />
Bangladesh<br />
Bhutan<br />
India<br />
Nepal<br />
Pakistan<br />
Sri Lanka<br />
West Africa<br />
Benin<br />
Burkina<br />
Gambia<br />
Ghana<br />
Guinea<br />
Guinea-Bissau<br />
Ivory Coast<br />
Liberia<br />
Mali<br />
Mauritania<br />
Niger<br />
Nigeria<br />
Sao Tom‚ & Principe<br />
Senegal<br />
Sierra Leone<br />
Togo<br />
West Indies<br />
Antigua<br />
Bahamas<br />
Barbados<br />
Cuba<br />
Dominica<br />
Dominican Rep.<br />
Grenada<br />
Guadeloupe<br />
Haiti<br />
Jamaica<br />
Martinique<br />
Montserrat<br />
Netherlands Antilles<br />
Puerto Rico<br />
St. Kitts, Nevis & Anguilla<br />
St. Lucia<br />
St. Vincent<br />
Trinidad & Tobago<br />
Virgin Islands<br />
Western Asia<br />
Bahrain<br />
Iran<br />
Iraq<br />
Israel<br />
Jordan<br />
Kuwait<br />
Lebanon<br />
Oman<br />
Qatar<br />
Saudi Arabia<br />
South Yemen<br />
Syria<br />
Turkey<br />
United Arab Emirates<br />
Yemen<br />
63
Appendix 5: List of Species (All species, excluding synonyms and misapplied names)<br />
q a ‘w’ after the species name indicates that conservation status data <strong>for</strong> that species is available from the<br />
World Conservation Monitoring Centre.<br />
q a ‘~’ in the species name indicates that the data came from plantation grown timber.<br />
World Conservation Monitoring Centre<br />
WCMC provides in<strong>for</strong>mation services on the conservation and sustainable use of species and ecosystems.<br />
The in<strong>for</strong>mation on plants comes from wide ranging sources, including The Species Survival Commission<br />
of the IUCN - World Conservation Union and The Nature Conservancy (USA), National Botanical<br />
Institute (South Africa) and CSIRO (Australia). An in<strong>for</strong>mation service providing details relevant to the<br />
status and conservation of the threatened tree species of the world and their potential <strong>for</strong> sustainable<br />
utilization will be available in electronic and hard copy <strong>for</strong>m in 1998.<br />
Species appearing on <strong>Prospect</strong> were compared to those species found on the World Conservation<br />
Monitoring Centre Plants Database on the 26th of November, 1996 and those found to be in common at<br />
that time are those that appear flagged in the following species list. The WCMC database is updated<br />
continually and so other species may now be in common with those appearing on <strong>Prospect</strong>. To obtain more<br />
in<strong>for</strong>mation relating to WCMC and the flagged species contact:-<br />
The In<strong>for</strong>mation Officer,<br />
World Conservation Monitoring Centre,<br />
219 Huntingdon Road,<br />
Cambridge,<br />
CB3 0DL, U.K.<br />
Tel: +44 (0)1223 277314<br />
Fax: +44 (0)1223 277136<br />
E-mail: info@wcmc.org.uk<br />
<strong>for</strong> more in<strong>for</strong>mation on WCMC please go to:<br />
http://www.wcmc.org.uk<br />
or http://www.unep-wcmc.org/<strong>for</strong>est/homepage.htm<br />
64
Abelia triflora Br.<br />
Abies alba Mill.<br />
w<br />
Alseis yucatanensis Standley<br />
Alseodaphne semecarpifolia Nees<br />
w<br />
Abies amabilis Forb.<br />
Alstonia congensis Engl.<br />
w<br />
Abies balsamea Mill.<br />
w Alstonia scholaris (L.) R.Br.<br />
w<br />
Abies grandis Lindl.<br />
w Altingia excelsa Nor.<br />
w<br />
Abies procera Rehd.<br />
w Alvaradoa amorphoides Liebm.<br />
Acacia aneura F.Muell<br />
Amaioua corymbosa H.B.K.<br />
w<br />
Acacia arabica Willd.<br />
Amanoa grandiflora Muell.Arg.<br />
w<br />
Acacia auriculi<strong>for</strong>mis~<br />
Amblygonocarpus andongensis<br />
w<br />
Acacia catechu Willd.<br />
w Amburana cearensis (Fr.Allem.) A.C.Smith.<br />
w<br />
Acacia confusa Merr.<br />
Amoora cucullata Roxb.<br />
w<br />
Acacia mangium~ Willd.<br />
Amoora wallichii King<br />
Acacia mearnsii De Wild.<br />
w Ampelocera hottlei (Standl.) Standl.<br />
Acacia melanoxylon R.Br.<br />
w Amphimas ferrugineus Pierre ex Pellegr.<br />
Acacia melanoxylon~ R.Br.<br />
Amphimas pterocarpoides Harms<br />
Acacia polyacantha Willd.<br />
Amyris balsamifera L.<br />
w<br />
Acacia richii A.Gray<br />
w Amyris elemifera L.<br />
Acanthosyris falcata Griseb.<br />
Acer catalpifolium Rehd.<br />
w<br />
Amyris simplicifolia Karst.<br />
Anacardium excelsum (Bert & Balb) Skeels<br />
w<br />
Acer cultratum Wall.<br />
Anacardium occidentale L.<br />
w<br />
Acer pseudoplatanus L.<br />
w Anacardium occidentale~ L.<br />
Acer rubrum L.<br />
Anadenanthera macrocarpa (Benth.) Brenan<br />
w<br />
Acer saccharum Marsh.<br />
w Andira coriacea Puller<br />
w<br />
Achras zapota Linn.<br />
Andira inermis (H.B.K.) (Wright) D.C.<br />
w<br />
Acioa barteri Engl.<br />
w Andira surinamensis (Bondt) Splitg. ex Pulle<br />
w<br />
Ackama paniculata Engl.<br />
Androstachys johnsonii Prain<br />
w<br />
Acnistus arborescens Schl.<br />
Angelesia splendens Korth.<br />
w<br />
Acrocarpus fraxinifolius Arn.<br />
w Aniba ovalifolia Mez<br />
Acrocarpus fraxinifolius~ Arn.<br />
Aningeria adolfi-friederici Robyns & Gilbert<br />
w<br />
Acronychia porteri Hook. F.<br />
w Aningeria altissima (A.Chev.) Aubr. & Pellegr.<br />
Adansonia digitata L.<br />
w Anisophyllea laurina R.Br.<br />
Adenanthera pavonina L.<br />
w Anisoptera costata Korth.<br />
w<br />
Adenaria floribunda H.B.K.<br />
w Anisoptera curtisii Dyer ex King<br />
w<br />
Adina microcephala (Del.) Hiern.<br />
w Annona glabra L.<br />
w<br />
Adinandra lamponga Miq.<br />
w Annona squamosa L.<br />
w<br />
Aegiceras floridum Roem. & Schult.<br />
w Anogeissus acuminata Wall.<br />
Aegiceras majus Gaertn.<br />
Anogeissus leiocarpus (DC.) Guill. & Perr.<br />
Aegle marmelos Correa<br />
Anopyxis klaineana (Pierre) Engl.<br />
w<br />
Aesculus hippocastanum L.<br />
w Anthocephalus chinensis (Lam.) A.Rich. ex Walp. w<br />
Aesculus turbinata Bl.<br />
Anthocephalus chinensis~ (Lam.) A.Rich ex Walp.<br />
Aextoxicon punctatum Ruiz & Pav.<br />
w Antiaris africana Engl.<br />
w<br />
Afrocrania volkensii (Harms) Hutch<br />
w Antiaris spp.<br />
Afzelia africana Pers.<br />
Antidesma ghaesembilla Gaertn.<br />
Afzelia quanzensis Welw.<br />
w Antrocaryon micraster A.Chev. & Guill.<br />
w<br />
Afzelia spp.<br />
Apeiba aspera Aubl.<br />
Agathis alba Foxw.<br />
Apeiba tibourbou Aubl.<br />
w<br />
Agathis australis Steud.<br />
w Aphanamixis rohituka Pierre<br />
Agathis microstachya Bail et White<br />
w Aphananthe philippinensis Planch.<br />
Agathis palmerstonii F.v.M.<br />
Apodytes dimidiata E.Mey ex Bernh.<br />
w<br />
Agathis robusta F.M.Baill.<br />
Aporrhiza talbotii Bak.f<br />
Agathis robusta~ F.M.Bail.<br />
Aporusa aurea Hook. f.<br />
w<br />
Agathis vitiensis Benth et Hook<br />
w Aporusa maingayi Hook. f.<br />
w<br />
Aglaia odoratissima Bl.<br />
w Aporusa nigricans Hook. f.<br />
w<br />
Agonandra brasiliensis Benth. & Hook. F.<br />
w Apuleia leiocarpa (Vog.) Macbride<br />
Agrostistachys borneensis Becc.<br />
w Aquilaria malaccensis Lam.<br />
w<br />
Ailanthus altissima Saingle<br />
w Aralidium pinnatifidum Miq.<br />
w<br />
Ailanthus excelsa Roxb.<br />
Araucaria angustifolia O.Ktze.<br />
w<br />
Alangium chinense (Lour.) Harms<br />
w Araucaria angustifolia~ O.Ktze<br />
Albizia adianthifolia (Schum.) W.Wight<br />
Araucaria araucana K.Koch.<br />
w<br />
Albizia antunesiana Harms<br />
Araucaria cunninghamii~ Sweet.<br />
Albizia ferruginea (Guill. & Perr.) Benth.<br />
Araucaria hunsteinii~ K.Schum<br />
Albizia gummifera (Gmel.) C.A.Sm. Arbutus unedo L. w<br />
Albizia lebbeck (L.) Benth. w Ardisia lanceolata Roxb. w<br />
Albizia odoratissima (L.F.) Benth. Aromadendron elegans Bl. w<br />
Albizia spp.<br />
Arthrophyllum diversifolium Blume<br />
Albizia versicolor Welw. ex Oliv. w Artocarpus altilis (Parkinson) Fosberg<br />
Albizia zygia (DC.) J.F.Macbr. Artocarpus bracteata Hook. f w<br />
Aleurites <strong>for</strong>dii Hemsl.<br />
Artocarpus gomeziana Wall.<br />
Aleurites moluccana (L.) Willd. w Aspidosperma album (Vahl) R.Ben ex P. w<br />
Alexa imperatricis (Schomb.) Baill. w Aspidosperma megalocarpon Mull. Arg<br />
Alibertia edulis A.Rich. w Aspidosperma peroba S.da Gama.<br />
Allanblackia floribunda A.Chev.<br />
Aspidosperma quebracho-blanco Schl.<br />
Allanblackia stuhlmannii Engl. w Asteriastigma macrocarpa Bedd. w<br />
Allophylus abyssinicus (Hochst.) Radlk. w Asteropeia rhopaloides Bak.<br />
Alnus glutinosa Gaertn. w Astronium fraxinifolium Schott. w<br />
Alnus rubra Bong. Astronium graveolens Jacq. w<br />
Alphitonia philippinensis Braid. Astronium le-cointei Ducke w<br />
Alphitonia zizyphoides A.Gray w Atamisquea emarginata Miers<br />
65
Atherosperma moschatum Labill.<br />
Bucida buceras L.<br />
Aucoumea klaineana Pierre<br />
w Bucklandia populnea R.Br.<br />
w<br />
Autranella congolensis (De Wild.) A.Chev.<br />
Bulnesia arborea Engl.<br />
w<br />
Averrhoa bilimbi L.<br />
Bumelia obtusifolia R.& Sch.<br />
Averrhoa carambola L.<br />
Burkea africana Hook.<br />
Avicennia nitida Jacq<br />
w Bursera simaruba (L.) Sarg.<br />
Azadirachta indica A.Juss.<br />
w Bussea occidentalis Hutch.<br />
Azadirachta indica~ A.Juss.<br />
Butea monosperma (Lamk.) Taub.<br />
Baccaurea motleyana Muell.Arg.<br />
w Butea superba Roxb.<br />
Bagassa guianensis Aubl.<br />
w Buxus sempervirens L.<br />
w<br />
Baikiaea insignis Benth.<br />
w Byrsonima coriacea (Sw.) DC.<br />
Baikiaea plurijuga Harms<br />
Byrsonima crassifolia (L.) H.B.K.<br />
Baillonella toxisperma Pierre<br />
w Byrsonima spicata (Cav.) DC.<br />
Balanites aegyptiaca (L.) Del.<br />
w Cabralea cangerana Sald.<br />
Balanocarpus heimii King<br />
Cabralea oblongifoliola C.DC.<br />
Balfourodendron riedelianum Engl.<br />
w Cadaba trifoliata W.& A.<br />
Balsamodendron mukul Hook. ex Stocks<br />
Caesalpinia coriaria (Jacq.) Willd.<br />
Banara guianensis Aubl.<br />
Caesalpinia granadillo Pittier<br />
Baphia nitida Lodd.<br />
Caesalpinia sappan L.<br />
w<br />
Baphia pubescens Hook. f.<br />
Calatola costaricensis Standl.<br />
Barringtonia acutangula Gaertn.<br />
Caldcluvia paniculata Don<br />
w<br />
Barringtonia scortechinii King<br />
Calliandra guildingii Benth.<br />
Barringtonia speciosa Forst.<br />
Callicarpa arborea Roxb.<br />
Bastardiopsis densiflora Hassl.<br />
Callitris columellaris~ F.Muell.<br />
Beilschmiedia kweo (Mildbr.) Robyns & Wilczek w Calodendrum capense (L.f.) Thunb.<br />
Beilschmiedia mannii (Meissn.) Benth. & Hook. f.<br />
Caloncoba brevipes Gilg<br />
Beilschmiedia spp.<br />
Calophyllum brasiliense Camb.<br />
w<br />
Beilschmiedia tawa (A.Cunn.) Kirk<br />
Calophyllum costatum F.M.Bail.<br />
Bellucia costaricensis Cogn.ex Th.Dur. et Pitt.<br />
Calophyllum kajewskii A.C. Smith<br />
w<br />
Belotia panamensis Pitt.<br />
Calophyllum leucocarpum A.C.Smith<br />
w<br />
Berlinia auriculata Benth.<br />
Calophyllum vitiense Turr.<br />
w<br />
Berlinia bracteosa Benth.<br />
Calpocalyx brevibracteatus Harms<br />
Berlinia grandiflora (Vahl) Hutch. & Dalz.<br />
Calycolpus glaber (Benth.) Berg<br />
Berrya cordifolia (Willd.) Burret<br />
w Calycophyllum candidissimum (Vahl) DC.<br />
Bersama abyssinica Fres.<br />
Calycophyllum spruceanum (Benth.) Hook<br />
w<br />
Bertholletia excelsa Berg.<br />
w Calyptranthes pallens Griseb.<br />
Bertiera guianensis Aubl.<br />
Calyptranthes zuzygium (L.) Sw.<br />
w<br />
Betula alleghaniensis Britt.<br />
Calyptrella cucullata Triana<br />
Betula alnoides Ham.<br />
Campnosperma auriculata (Bl.) Hook. f.<br />
w<br />
Betula papyrifera Marsh.<br />
w Campnospermum panamensis Standl.<br />
Betula pendula<br />
w Camptostemon philippinense (Vidal) Beccari<br />
Betula pubescens Ehrh.<br />
w Canangium odoratum (Lam.) Baill.<br />
Billia columbiana Planch. & Lind.<br />
Canarium euphyllum Kurz<br />
Bischofia javanica Blume<br />
w Canarium schweinfurthii Engl.<br />
w<br />
Bixa orellana L.<br />
Canella winterana (L.) Gaertn.<br />
w<br />
Blastemanthus grandiflorus Spruce<br />
Canotia holacantha Torr.<br />
Blepharocarya involucrigera F.Muell. w Canthium rubrocostatum Robyns w<br />
Blighia sapida Koenig w Capparis cynophallophora L.<br />
Blighia unijugata Bak.<br />
Carallia calycina Thw.<br />
Boehmeria rugulosa Wedd. w Carapa grandiflora Sprague w<br />
Bombacopsis quinata (Jacq.) Dugand w Carapa guianensis Aubl. w<br />
Bombacopsis quinata~ (Jacq.) Dugand<br />
Carapa procera DC.<br />
Bombacopsis sepium Pitt.<br />
Carapa slateri Standl.<br />
Bombax ceiba L.<br />
Cardwellia sublimis F.Muell.<br />
Bonyunia aquatica Ducke Careya arborea Roxb. w<br />
Boschia griffithii Mast.<br />
Cariniana excelsa Casar.<br />
Bouea burmanica Griff. Cariniana legalis (Mart.) Kuntze w<br />
Bouea macrophylla Griff. w Cariniana pyri<strong>for</strong>mis Miers. w<br />
Bourreria ovata Miers<br />
Carissa spp.<br />
Bowdichia nitida Spruce ex Benth. w Carpinus betulus L. w<br />
Brachylaena hutchinsii Hutch. w Carpodiptera cubensis Griseb.<br />
Brachystegia cynometroides Harms<br />
Carya spp. (true hickory)<br />
Brachystegia eurycoma Harms Caryocar costaricense Donn.Sm. w<br />
Brachystegia mildbraedii Harms Caryocar glabrum Pers. w<br />
Brachystegia spici<strong>for</strong>mis Benth. Caryocar villosum Pers. w<br />
Brassaiopsis hainla Seem. Casearia battiscombei R.E.Fries w<br />
Bravaisia integerrima Standl. w Casearia dinklagei Gilg<br />
Bridelia micrantha (Hochst.) Baill. w Casearia engleri Gilg. w<br />
Brosimum alicastrum Sw. Cassia nodosa (Roxb.) K & S.Larsen w<br />
Brosimum caloxylon Standl. w Cassia siamea Lamk. w<br />
Brosimum costaricanum Liebm.<br />
Cassia siamea~ Lamk.<br />
Brosimum paraense Hub.<br />
Cassia timoriensis DC.<br />
Brosimum utile (HBK) Pittier Cassine buchananii Loes. w<br />
Broussonetia papyrifera Vent.<br />
Cassine crocea O.Ktze<br />
Brya ebenus DC.<br />
Cassipourea afzelii (Oliv.) Alston<br />
Buchanania lancifolia Roxb.<br />
Cassipourea elliptica Poir.<br />
Buchanania lanzan Spreng. w Cassipourea malosana (Bak.) Alston w<br />
Buchenavia capitata (Vahl) Eichl. w Cassipourea verticillata N.E.Br.<br />
66
Castanea dentata Borkh.<br />
w Citrus medica L.<br />
w<br />
Castanea sativa Mill.<br />
w Clarisia racemosa R.& P.<br />
Castanopsis cuspidata Schott<br />
Clathrotropis brachypetala Kleinh.<br />
w<br />
Castanopsis junghuhnii (Miq.) Hayata<br />
Clathrotropis macrocarpa Ducke<br />
w<br />
Castanopsis kawakamii Hayata<br />
w Cleistanthus collinus Benth.<br />
w<br />
Castanopsis sumatrana A.DC.<br />
Cleistanthus myrianthus Kurz<br />
w<br />
Castanospermum australe Cunn. & Fraser<br />
Cleistopholis glauca Pierre ex Engl. & Diels<br />
Castela coccinea Griseb.<br />
Cleistopholis patens (Benth.) Engl. & Diels.<br />
w<br />
Castilla elastica Cerv.<br />
w Clerodendrum disparifolium Bl.<br />
w<br />
Castilla fallax Cook<br />
w Clethra lanata Mart. & Gal.<br />
Casuarina equisetifolia Forst.<br />
w Clidemia naevula (Naud.) Triana<br />
Casuarina equisetifolia~ Forst.<br />
Clusia rosea Jacq.<br />
w<br />
Casuarina litorea L.<br />
Cneorum trimerum (Urb.) Chod.<br />
Casuarina torulosa Dryand. ex Ait.<br />
Cochlospermum orinoccense Steud.<br />
Catalpa longissima Jacq.<br />
Coelocaryon oxycarpum Stapf<br />
Catostemma commune Sand.<br />
w Coelocaryon preussii Warb.<br />
w<br />
Catostemma fragrans Benth.<br />
w Coelostegia griffithii Benth.<br />
w<br />
Cavanillesia platanifolia H.B.K.<br />
Cola acuminata (P.Beauv.) Schott & Endl.<br />
Cecropia juranyana A.Rich.<br />
Cola spp.<br />
Cecropia obtusifolia Bertol.<br />
Colophospermum mopane J.Leonard<br />
Cecropia peltata L.<br />
w Colubrina arborescens (Mill.) Sarg.<br />
Cedrela fissilis Vell.<br />
w Colubrina cubensis (Jacq.) Brongn.<br />
w<br />
Cedrela odorata L.<br />
w Colubrina reclinata (L'Her.) Brongn.<br />
Cedrela odorata~ L.<br />
Columbia floribunda Kurz<br />
Cedrelinga catanae<strong>for</strong>mis Ducke<br />
w Combretum binderianum Kotschy<br />
w<br />
Ceiba occidentalis Burk.<br />
w Combretum lamprocarpum Diels<br />
Ceiba pentandra (L.) Gaertn.<br />
w Combretum schumannii Engl.<br />
w<br />
Ceiba samauma Schum.<br />
w Compsoneura sprucei (A.DC.) Warb.<br />
Celtis adolfi-friderici Engl.<br />
w Condalia lineata A.Gray<br />
Celtis africana Burm. f.<br />
w Condalia obovata Hook.<br />
Celtis australis L.<br />
w Conocarpus erectus L.<br />
w<br />
Celtis durandii Engl. w Conopharyngia durissima Stapf<br />
Celtis mildbraedii Engl. w Conostegia xalapensis (Bonpl.) D.Don<br />
Celtis occidentalis L.<br />
Copaifera mildbraedii Harms<br />
Celtis philippensis Blanco w Copaifera panamensis (Britton) Standley w<br />
Celtis prantlii Priemer ex Engl.<br />
Cordia africana Lam.<br />
Celtis zenkeri Engl. w Cordia alliodora Oken w<br />
Centrolobium paraense Tul.<br />
Cordia alliodora~ Oken.<br />
Centrolobium patinense Pittier<br />
Cordia caffra Sond.<br />
Centronia excelsa (Bonpl.) Triana Cordia dichotoma Forst. f. w<br />
Cephalosphaera usambarensis (Warb.) Warb. Cordia dodecandra DC. w<br />
Ceratonia siliqua L. Cordia gerascanthus L. w<br />
Ceratopetalum apetalum D.Don<br />
Cordia goeldiana Hub.<br />
Cerbera odollam Gaertn. w Cordia millenii Bak. w<br />
Cercidiphyllum japonicum S.& Z. w Cordia obliqua Willd. w<br />
Cercidium praecox (R. & P.) Harms Cordia platythyrsa Baker w<br />
Cercis canadensis L. w Cordia spp. (African)<br />
Ceriops tagal C.B.Rob. w Cordia trichotoma Vell. ex Steud.<br />
Cervantesia colombiana A.C.Smith Cordyla africana Lour. w<br />
Cestrum panamense Standl.<br />
Cornus macrophylla Wall.<br />
Chaetocarpus castanocarpus Thw.<br />
Cornus peruviana Macbride<br />
Chamaecyparis lawsoniana Parl. w Cosmocalyx spectabilis Standley<br />
Chamaecyparis nootkatensis Spach. w Cotylelobium malayanum V.Sl. w<br />
Chilopsis linearis P.DC. Coula edulis Baill. w<br />
Chlorocardium rodiaei (Schomb.) J.G. Rohwer w Couma macrocarpa B.R. w<br />
Chlorophora regia A.Chev. w Coumarouna oleifera (Benth.) Taub.<br />
Chlorophora tinctoria (L.) Gaud. Couratari guianensis Aubl. w<br />
Chloroxylon swietenia (B.C.) w Couratari panamensis Standley w<br />
Chorisia insignis H.B.K. w Couroupita darienensis Pittier<br />
Chorisia speciosa St Hill. w Couroupita odoratissima Seem.<br />
Christiania africana DC. Coutarea hexandra K.Schum. w<br />
Chrysochlamys membranacea Tr. & Pl.<br />
Craibiodendron shanicum W.W.Smith<br />
Chrysophyllum albidum G.Don w Crataegus oxyacantha L.<br />
Chrysophyllum cainito L.<br />
Cratoxylon arborescens (Vahl) Bl.<br />
Chrysophyllum olivi<strong>for</strong>me L. Crescentia cujete L. w<br />
Chrysophyllum perpulchrum Mildr. w Crinodendron tucumanum Lillo w<br />
Chrysophyllum sanguinolentum (Pierre) Monach. Croton argyratus Bl. w<br />
Chukrasia tabularis A.Juss. w Croton glabellus Linn. w<br />
Chytroma idatimon Miers<br />
Croton macrostachyus Hochst. ex Rich.<br />
Cinchona ledgeriana Moens ex Trimen<br />
Croton megalocarpus Hutch.<br />
Cinnamomum camphora Nees. & Eberm.<br />
Croton oblongifolius Roxb.<br />
Cinnamomum iners Reinw.<br />
Crudia obliqua Griseb.<br />
Cinnamomum parthenoxylon Meissn. w Crypteronia paniculata Blume. w<br />
Cipadessa fruticosa Bl.<br />
Cryptocarya chinensis Hemsl.<br />
Citharexylum caudatum L. Cryptomeria japonica D.Don. w<br />
Citharexylum fruticosum L.<br />
Ctenolophon englerianus Mildbr.<br />
Citharexylum macradenium Greenm.<br />
Ctenolophon grandifolius Oliv.<br />
Citrus aurantium L. Cuervea kappleriana (Miq.) A.C.Smith w<br />
67
Cullenia exarillata A.Robyns<br />
Diospyros xanthochlamys Gurke<br />
Cunonia capensis L.<br />
Dipholis salicifolia (L) ADC.<br />
Cupressus lusitanica Mill.<br />
w Diphysa robinioides Benth.<br />
w<br />
Cupressus lusitanica~ Mill.<br />
Diplodiscus paniculatus Turczaninow<br />
w<br />
Cupressus macrocarpa Hartw.<br />
w Diplorhynchus condylocarpon (Muell. Arg.) Pichon<br />
Curtisia faginea Ait.<br />
Diplotropis martiusii Benth.<br />
w<br />
Cussonia arborea Hochst. ex A.Rich.<br />
Diplotropis purpurea (Rich.) Amsh.<br />
Cyclobalanopsis gilva Oerst.<br />
Dipterocarpus rotundifolius Foxworthy<br />
w<br />
Cyclobalanopsis morii (Hayata) Hayata<br />
Dipterocarpus tuberculatus Roxb.<br />
w<br />
Cylicodiscus gabunensis (Taub.) Harms<br />
w Dipterodendron costaricense Radlk.<br />
Cynometra alexandri C.H.Wright<br />
Dipteryx odorata Willd.<br />
w<br />
Cynometra insularis A.C. Smith<br />
w Discoglypremna caloneura (Pax) Prain<br />
w<br />
Cynometra megalophylla Harms<br />
Discophora panamensis Standley<br />
w<br />
Cynometra polyandra Roxb. Distemonanthus benthamianus Baill. w<br />
Cynometra ramiflora L. w Distylium racemosum S. & Z. w<br />
Cyrilla racemiflora L. Doerpfeldia cubensis Urb. w<br />
Dacrydium cupressinum Sol. Dombeya goetzenii K.Schum w<br />
Dacrydium elatum Wall. w Dorstenia kameruniana Engl.<br />
Dacryodes buettneri (Engl.) J.H.Lam. w Doryphora sassafras Endl. w<br />
Dacryodes edulis (G.Don) H.J.Lam Dracontomelon mangiferum Blume w<br />
Dacryodes excelsa Vahl. w Drimys granatensis L. f.<br />
Dacryodes igaganga Aubr. & Pell. w Dryobalanops aromatica Gaertn. f.<br />
Dactylocladus stenostachys Oliv.<br />
Drypetes brownii Standl.<br />
Dalbergia cearensis Ducke w Drypetes diversifolia Krug & Urb.<br />
Dalbergia frutescens Britton w Drypetes lateriflora (Sw.) Krug & Urb.<br />
Dalbergia latifolia Roxb.<br />
Drypetes principum (Muell.Arg.) Hutch.<br />
Dalbergia melanoxylon Guill. & Perr. w Duabanga grandiflora (Roxb. ex DC.) Walp.<br />
Dalbergia nigra Fr.Allem. w Duboisia myoporoides R.Br.<br />
Dalbergia oliveri Gamble w Dyera costulata Hook. f. w<br />
Dalbergia retusa Hemsl. w Dysoxylum fraseranum Benth.<br />
Dalbergia sissoo DC. w Dysoxylum pilosum A.C. Smith<br />
Dalbergia sissoo~ DC. Dysoxylum richii C.DC w<br />
Dalbergia stevensonii Standl.<br />
Ehretia acuminata R.Br.<br />
Daniellia klainei A.Chev.<br />
Ehretia anacuna (Berl.) Johnston<br />
Daniellia ogea (Harms) Holland w Ehretia cymosa Thonn.<br />
Daniellia oliveri (Rolfe) Hutch. & Dalziel Ehretia tinifolia L.<br />
Daniellia thurifera Bennett w Ekebergia capensis Sparrm.<br />
Daphnandra micrantha Benth. Ekebergia rueppelliana (Fresen) A.Rich w<br />
Daphniphyllum lancifolium Hook.<br />
Ekmanianthe actinophylla (Gris.) Urb.<br />
Daphnopsis macrophylla Gilg Elaeocarpus floribundus Bl. w<br />
Daphnopsis philippiana Krug & Urban w Elateriospermum tapos Bl.<br />
Dehaasia curtisii Gamble Embothrium coccineum Forst. w<br />
Delonix regia (Hook.)Raf. w Enallagma latifolia (Mill.) Sm. w<br />
Dendropanax arboreus L. w Enantia chlorantha Oliv.<br />
Deplanchea bancana V.Steenis w Endiandra palmerstoni (F.M.Bail.) C.T.White w<br />
Dermatocalyx parviflora Oerst. Endospermum macrophyllum Pax et Hoffm. w<br />
Desbordesia glaucescens (Engl.) Van Tiegh. Endospermum malaccense Muell.Arg. w<br />
Desmostachys vogelii Stapf<br />
Engelhardtia <strong>for</strong>mosana Hayata<br />
Detarium senegalense J.Gmelin w Engelhardtia nudiflora Hook.<br />
Dialium dinklagei Harms. w Engelhardtia pterocarpa (Oerst.) Standl. w<br />
Dialium guianense Willd.<br />
Engelhardtia roxburghiana Lindl.<br />
Dialium spp. Engelhardtia spicata Bl. w<br />
Dialyanthera otoba Warb. Enicosanthum fuscum (King) Airy-Shaw. w<br />
Dichrostachys glomerata (Forsk.) Chiov. Entada abyssinica Steud. ex A.Rich. w<br />
Dicorynia guianensis Amsh.<br />
Entandrophragma angolense (Welw.) C.DC.<br />
Didelotia brevipaniculata J.Leon. w Entandrophragma candollei Harms w<br />
Didymopanax morototoni (Aubl) Dene et Planch. Entandrophragma cylindricum Sprague w<br />
Dillenia reticulata King w Entandrophragma utile (Dawe & Sprague) Sprague w<br />
Dimorphocalyx malayanus Hook. Enterolobium cyclocarpum (Jacq.) Griseb. w<br />
Dinizia excelsa Ducke Enterolobium schomburgkii Benth. w<br />
Diospyros abyssinica (Hiern.) F.White w Eperua falcata Aubl.<br />
Diospyros atropurpurea Gurke Eperua grandiflora (Aubl.) Benth. w<br />
Diospyros batocana Hiern w Eperua jenmannii Oliv. w<br />
Diospyros burmanica Kurz<br />
Erblichia odorata Seem.<br />
Diospyros confertiflora (Hiern) Bakh. w Eremophila mitchellii Benth.<br />
Diospyros crassiflora Hiern. w Erinocarpus nimmoanus Grah. w<br />
Diospyros ehretioides Wall. Eriobotrya bengalensis Hook. f.<br />
Diospyros ferrea (Willd.) Bakh. w Eriolaena candollei Wall.<br />
Diospyros gabunensis Gurke<br />
Eriolaena quinquelocularis Wight<br />
Diospyros insculpta Hutch. & Dalz.<br />
Eriolaena spectabilis Planch.<br />
Diospyros kaki L. f. Erisma uncinatum Warm. w<br />
Diospyros kamerunensis Gurke w Erithalis fruticosa L.<br />
Diospyros mannii Hiern w Ervatamia corymbosa King & Gamble<br />
Diospyros marmorata Parker w Erythrina berteroana Urb.<br />
Diospyros mespili<strong>for</strong>mis (Hochst.) ex A.DC. w Erythrina glauca Willd. w<br />
Diospyros sanza-minika (A. Chev.) w Erythrina mildbraedii Harms<br />
Diospyros spp.<br />
Erythrophleum africanum (Benth.) Harms<br />
Diospyros thomasii Hutch. & Dalz. Erythrophleum guineense G.Don w<br />
68
Erythrophleum ivorense A.Chev.<br />
Erythrophleum suaveolens (Guill. & Perr.) Brenan<br />
Erythroxylum mannii Oliv.<br />
Escallonia myrtillioides L.<br />
Eschweilera amara (Aubl.) Ndz.<br />
Eschweilera longpipes Miers<br />
Eschweilera odora (Poepp.) Miers<br />
Eschweilera sagotiana Miers<br />
Eschweilera subglandulosa Miers.<br />
Esenbeckia alata (Karst. & Tr.) Tr. & Pl.<br />
Esenbeckia atata Pitt.<br />
Esenbeckia pilocarpoides H.B.K.<br />
Esenbeckia spp.<br />
Eucalyptus botryoides Sm.<br />
Eucalyptus calophylla R.Br.<br />
Eucalyptus camaldulensis Dehn.<br />
Eucalyptus camaldulensis~ Dehn.<br />
Eucalyptus citriodora Hook<br />
Eucalyptus citriodora~ Hook.<br />
Eucalyptus corymbosa Sm.<br />
Eucalyptus deglupta Bl.<br />
Eucalyptus deglupta~ Bl.<br />
Eucalyptus delegatensis R.T. Bak.<br />
Eucalyptus diversicolor F.v.M.<br />
Eucalyptus globulus Labill.<br />
Eucalyptus globulus~ Labill.<br />
Eucalyptus grandis Maid.<br />
Eucalyptus grandis~ Maid.<br />
Eucalyptus maculata Hook.<br />
Eucalyptus maidenii F.Muell.<br />
Eucalyptus marginata Sm.<br />
Eucalyptus melliodora A.Cunn.<br />
Eucalyptus microcarpa Maiden<br />
Eucalyptus microcorys F.Muell.<br />
Eucalyptus obliqua L.Herit.<br />
Eucalyptus obliqua~ L.Herit.<br />
Eucalyptus paniculata Sm.<br />
Eucalyptus pilularis Smith<br />
Eucalyptus regnans~ F.Muell.<br />
Eucalyptus resinfera Sm.<br />
Eucalyptus robusta Sm.<br />
Eucalyptus robusta~ Sm.<br />
Eucalyptus saligna Smith<br />
Eucalyptus saligna~ Smith<br />
Eucalyptus tereticornis Sm<br />
Eucalyptus tereticornis~ Sm.<br />
Eucalyptus viminalis Labill.<br />
Eucalyptus wandoo Blakely<br />
Euclea lanceolata E.Mey.<br />
Eucryphia cordifolia Cav.<br />
Eucryphia lucida Druce<br />
Eugenia axillaris (Sw.) Willd.<br />
Eugenia confusa DC.<br />
Euphorbia tirucalli L.<br />
Euroschinus falcatus Hook. f.<br />
Eusideroxylon zwageri T. & B.<br />
Euxylophora paraensis Hub.<br />
Evodia glabra Blume<br />
Excoecaria agallocha L.<br />
Exocarpos latifolia R.Br.<br />
Exostema caribaeum (Jacq.) R. & S.<br />
Fagara amaniensis Engl.<br />
Fagara brieyi Vermoesen & Gilbert<br />
Fagara flava Krug & Urb.<br />
Fagara heitzii Aubrev. & Pellegr.<br />
Fagara leprieurii Engl.<br />
Fagaropsis angolensis (Engl.) Dale<br />
Fagraea fragrans Roxb.<br />
Fagraea gigantea Ridl.<br />
Fagraea gracilipes A.Gray<br />
Fagus grandifolia Ehrh.<br />
Fagus sylvatica L.<br />
Faidherbia albida (Del.) A.Chev.<br />
Faramea occidentalis (L.) A.Rich.<br />
Faurea macnaughtonii Phill.<br />
Faurea saligna Harv.<br />
Ficalhoa laurifolia Hiern.<br />
Ficus aurea Nutt.<br />
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Ficus glabrata H.B. & K.<br />
Ficus glaucescens Miq.<br />
Ficus laevigata Vahl<br />
Fillaeopsis discophora Harms<br />
Fitzroya cupressiodes Johnst.<br />
Flacourtia cataphracta Roxb.<br />
Flindersia brayleyana F.Muell.<br />
Forestiera acuminata Poir.<br />
Fraxinus americana L.<br />
Fraxinus excelsior L.<br />
Fraxinus nigra Marsh.<br />
Fraxinus pennsylvanica Marsh.<br />
Funtumia africana (Benth.) Stapf<br />
Gallesia integrifolia (Spreng.) Harms.<br />
Gallesia scorododendrum Casar.<br />
Gambeya africana Pierre<br />
Gambeya lacourtiana (De Wild.) Aubr. & Pell.<br />
Gamblea ciliata Clarke<br />
Ganua motleyana Pierre<br />
Garcinia cowa Roxb.<br />
Garcinia gerrardii Harv.<br />
Garcinia kola Heckel<br />
Garcinia myrtifolia A.C.Smith<br />
Gardenia coronaria Ham.<br />
Gardenia latifolia Ait.<br />
Gavarretia terminalis Baill.<br />
Geissois benthami F.Muell.<br />
Genipa americana L.<br />
Gevuina avellana Mol.<br />
Gilbertiodendron dewevrei J.Leonard<br />
Gironniera nervosa Planch.<br />
Gironniera reticulata Thw.<br />
Glandonia macrocarpa Gris.<br />
Gliricidia sepium (Jacq.) Walp.<br />
Gluta elegans (Wall.) Hook. f.<br />
Gmelina arborea Roxb.<br />
Gmelina arborea~ Roxb.<br />
Goethalsia meiantha (D.Sm.) Burret<br />
Gomidesia lindeniana Berg.<br />
Gonioma kamassi (Eckl.) E.Mey.<br />
Goniothalamus griffithii Hook. f. & Th.<br />
Gonocaryum calleryanum (Baill.) Becc.<br />
Gonystylus bancanus (Miq.) Kurz<br />
Gonystylus macrophyllus (Miq.) A.Shaw.<br />
Gonystylus punctatus A.C.Smith<br />
Gordonia papuana Kobuski<br />
Gossweilerodendron balsamiferum (Verm.) Harms<br />
Gossypiospermum praecox (Gris.) P.Wils.<br />
Goupia glabra Aubl.<br />
Grevillea robusta A.Cunn.<br />
Grewia microcos L.<br />
Grias fendleri Seem.<br />
Grislea secunda Loefl.<br />
Guaiacum officinale L.<br />
Guaiacum sanctum L.<br />
Guarea cedrata (A.Chev.) Pell.<br />
Guarea glabra Vahl.<br />
Guarea thompsonii Sprague & Hutch.<br />
Guarea trichilioides L.<br />
Guazuma ulmifolia Lam.<br />
Guettarda combsii Urb.<br />
Guibourtia arnoldiana (De Wild.& Th.Dur.) J.Leonard<br />
Guibourtia coleosperma (Benth.) J.Leonard<br />
Guibourtia demeusei (Harms) J.Leonard<br />
Guibourtia ehie (A.Chev.) J.Leon.<br />
Guibourtia pelligriniana J.Leonard<br />
Guibourtia spp.<br />
Guibourtia tessmannii (Harms) J.Leonard<br />
Guilandina echinata (Lam.) Spreng.<br />
Gymnacranthera farquhariana Warb<br />
Gymnanthes lucida Sw.<br />
Gynocardia odorata R.Br.<br />
Gynotroches axillaris Bl.<br />
Haematoxylum campechianum L.<br />
Hagenia abyssinica (Bruce) J.F.Gmel.<br />
Haldina cordifolia (Roxb.) Ridsd.<br />
Hal<strong>for</strong>dia scleroxyloa F.Muell.<br />
Hallea ledermannii B.Verd.<br />
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69
Hallea stipulosa Leroy.<br />
Halleria lucida L.<br />
Haloxylon ammodendron Boiss.<br />
Hannoa klaineana Pierre & Engl.<br />
Haplolobus floribundus (K.Sch.) H.J.Lam<br />
Haplormosia monophylla (Harms) Harms<br />
Hardwickia binata Roxb.<br />
Harungana madagascarensis Lam. ex Poir.<br />
Hasseltiopsis dioica (Benth.) Sleumer<br />
Heinsia crinata (Afzel.) G.Taylor<br />
Heisteria macrophylla Oerst.<br />
Heisteria parvifolia Smith<br />
Helicostylis latifolia Pittier<br />
Helicostylis tomentosa Mac.<br />
Helietta cuspidata (Engl.) Chod. & Hassl.<br />
Heliocarpus popayanensis H.B.K.<br />
Heritiera javanica (Blume) Katerm.<br />
Heritiera littoralis (Dryand.) Ait.<br />
Heritiera macrophylla Wall.<br />
Heritiera ornithocephala Kosterm.<br />
Heritiera utilis (Sprague) Sprague<br />
Hernandia guianensis Aubl.<br />
Hernandia ovigera L.<br />
Hernandia sonora L.<br />
Heterophragma adenophyllum Seem.<br />
Heterotrichum cymosum (Wendl.) Urb.<br />
Hevea brasiliensis Muell. Arg.<br />
Hevea brasiliensis~ Muell. Arg.<br />
Hevea guyanensis Aubl.<br />
Heynea trijuga Roxb.<br />
Hibiscus elatus Sw.<br />
Hibiscus floccosus Mast.<br />
Hibiscus macrophyllus Roxb.<br />
Hibiscus mutabilis Linn.<br />
Hibiscus tiliaceus L.<br />
Hieronyma alchorneoides Fr. AU.<br />
Hieronyma laxiflora M.Arg.<br />
Himatanthus articulata (Vahl) Woodson<br />
Hippomane mancinella L.<br />
Hippophae rhamnoides L.<br />
Hippophae salicifolia Don<br />
Holigarna helferi Hook. f.<br />
Holoptelea grandis (Hutch.) Mildbr.<br />
Holoptelea integrifolia (Roxb.) Planch.<br />
Holopyxidium jarana (Huber) Ducke.<br />
Homalium angustistipulatum Keay<br />
Homalium aylmeri Hutch. & Dalz.<br />
Homalium foetidum (Roxb.) Benth<br />
Homalium letestui Pellegr.<br />
Homalium longifolium Benth.<br />
Homalium tomentosum Benth.<br />
Homalium zeylanicum Benth.<br />
Hopea beccariana Burck.<br />
Hopea ferrea Lanessan<br />
Hopea odorata Roxb.<br />
Hopea papuana Diels.<br />
Humboldtia bourdilloni Prain<br />
Humiria balsamifera (Aubl.) St. Hil.<br />
Humiria floribunda Mart.<br />
Humiria procera Little<br />
Hunteria corymbosa Roxb.<br />
Hura crepitans L.<br />
Hydnocarpus alpina Wight.<br />
Hydnocarpus castanea Hook.f. & Thoms.<br />
Hymenaea courbaril Linn<br />
Hymenodictyon excelsum (Roxb) Wall.<br />
Hymenolobium excelsum Ducke<br />
Hymenostegia afzelii Harms.<br />
Hypelate trifoiata Sw.<br />
Ichthyomethia piscipula (L.) Hitchcock<br />
Ilex aquilifolium L.<br />
Ilex belizensis Lundell<br />
Ilex casiquiarensis Loes.<br />
Ilex cymosa Bl.<br />
Ilex mitis (L.) Radlk.<br />
Ilex panamensis Standley<br />
Ilex paraguensis St. Hil.<br />
Ilex repanda Griseb.<br />
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Ilex sideroxyloides Griseb.<br />
Inga alba Willd.<br />
Inga edulis Mart.<br />
Intsia bijuga (Cole BR.) O.Ktze.<br />
Intsia palembanica Miq.<br />
Intsia retusa (Kurz) Merr<br />
Irvingia gabonensis Baillon<br />
Irvingia grandifolia Engl.<br />
Irvingia oliveri Pierre<br />
Iryanthera lancifolia Ducke<br />
Isoberlinia scheffleri (Harms) Greenway<br />
Isoberlinia tomentosa Craib & Stapf.<br />
Isolona campanulata Engl. & Diels<br />
Isoptera borneensis Schieff<br />
Ixora arborea Roxb ex Sm.<br />
Jacaranda copaia (Aubl.) D.Don<br />
Jacaranda rhombifolia G.F.W. Mey.<br />
Jackiopsis ornata Wall.<br />
Jacquinia keyensis Mez<br />
Joannesia heveoides Ducke.<br />
Jodina rhombifolia Hook. & Arn.<br />
Juglans mandshurica Maxim.<br />
Juglans w nigra L.<br />
Juglans w regia L.<br />
Juglans sieboldiana Maxim.<br />
Julbernardia globiflora (Benth.) Troupin<br />
Julbernardia pellegriniana Troupin<br />
Juniperus procera Hochst.<br />
Kalopanax pictus Nakai<br />
Kandelia rheedii W. & A.<br />
Kermadecia vitiensis Turr.<br />
Khaya anthotheca (Welw.) C.DC.<br />
Khaya grandifoliola C.DC.<br />
Khaya ivorensis A.Chev.<br />
Khaya nyasica Stapf. ex E.G. Baker<br />
Khaya senegalensis (Desr.) A.Juss.<br />
Khaya spp.<br />
Kigelia pinnata (Jacq.) DC.<br />
Kiggelaria africana L.<br />
Kirkia acuminata Oliv.<br />
Klainedoxa gabonensis Pierre ex Engl.<br />
Kleinhovia hospita L.<br />
Knema furfuracea Warb.<br />
Koompassia excelsa (Becc) Taub.<br />
Koompassia malaccensis Maing. ex Benth.<br />
Krugiodendron ferreum (Vahl) Urb.<br />
Kurrimia paniculata Wall<br />
Kurrimia pulcherrima Wall<br />
Kydia calycina Roxb.<br />
Lachnopylis floribunda (Benth.) C.A.Sm.<br />
Lacistema aggregatum (Berg) Rusby<br />
Laetia procera (Poepp & Endl.) Eichl.<br />
Lagerstroemia calyculata Kurz<br />
Lagerstroemia hypoleuca Kurz<br />
Lagerstroemia speciosa (L.) Pers.<br />
Lagerstroemia subcostata Loehne<br />
Lagerstroemia tomentosa Presl.<br />
Lagetta lintearia Lam<br />
Laguncularia racemosa (L.) Gaertn.<br />
Lannea coromandelica (Houtt.) Merrill<br />
Lannea kerstingii Engl. & Krause<br />
Lannea welwitschii (Hiern.) Engl.<br />
Lansium domesticum Jack<br />
Laplacea fruticosa (Schrad.) Kobuski<br />
Larix decidua Mill.<br />
Larix larcinia Koch.<br />
Larix leptolepis Gord.<br />
Larix occidentalis Nutt.<br />
Laurelia sempervirens (R. & P.) Tul.<br />
Laurelia serrata Bert.<br />
Lecythis paraensis (Huber) Ducke<br />
Leucaena glauca (L) Benth<br />
Leucaena trichodes (Jacq) Benth.<br />
Libocedrus decurrens Torr.<br />
Licania buxiflora Sandw.<br />
Licania densiflora Kleinh.<br />
Licania heteromorpha Benth.<br />
Licania hypoleouca Benth<br />
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70
Licania macrophylla Benth.<br />
Licania micrantha Miq.<br />
Licania mollis Benth.<br />
Licania persaudii Fanshawe & Maguire<br />
Licania platypus Kuntze.<br />
Licania ternatensis Hook. f.<br />
Licania venosa Rusby.<br />
Licaria canella (Meissn) Kosterm.<br />
Licaria triandra (Sw) Kostem<br />
Liquidambar styraciflua Linn.<br />
Liriodendron tulipfera L.<br />
Lithocarpus megalophylla Rehd.<br />
Lithraea molleoides (Vell) Engl.<br />
Litsea sebifera Pers.<br />
Lonchocarpus castilloi Standley<br />
Lonchocarpus hedyosmus Miq.<br />
Lophira alata Banks ex Gaertn.<br />
Lophira spp.<br />
Lophopetalum littorale Kurz<br />
Lophopetalum maingayi Ridl<br />
Lophopetalum wallichii Kurz<br />
Lovoa swynnertonii Bak f<br />
Lovoa trichilioides Harms<br />
Loxopterygium sagotii Hook f.<br />
Luehea divaricata Mart<br />
Lumnitzera coccinea W et A<br />
Lysiloma bahamensis Benth<br />
Lysiloma latisliqua (L) Benth<br />
Maba cooperi Hutchinson & Dalziel<br />
Macaranga conglomerata Brenan<br />
Macaranga kilimandsharica Pax.<br />
Macaranga puncticulata Gage<br />
Macoubea guianensis Aubl.<br />
Macrolobium acaciaefolium Benth<br />
Macropanax oreophilum Miq.<br />
Madhuca latifolia (Roxb.) McBride<br />
Madhuca malaccensis H.J.Lam<br />
Madhuca tomentosa H.J.Lam<br />
Madhuca utilis (Ridl.) H.J.Lam<br />
Maesa ramentacea A.DC.<br />
Maesopsis eminii Engl.<br />
Maesopsis eminii~ Engl.<br />
Malacantha alnifolia (Baker) Pierre.<br />
Malache scabra B.Vog.<br />
Mallotus macrostachyus Muell.Arg.<br />
Mallotus muticus (Muell. Arg.) Airy Shaw<br />
Mallotus penangensis Muell.Arg.<br />
Mallotus philippinensis Muell. Arg.<br />
Mammea africana Sabine (G.Don)<br />
Mangifera foetida Lour.<br />
Mangifera indicata Linn.<br />
Manglietia <strong>for</strong>diana Oliv<br />
Manihot glaziovii Muell Arg<br />
Manilkara bidentata (A.Dc) Chev.<br />
Manilkara cuneifolia Dubard.<br />
Manilkara kauki Dubard<br />
Manilkara lacera Dubard.<br />
Manilkara littoralis (Kurz) Dub<br />
Manilkara zapota (L) V. Royen<br />
Mansonia altissima A. Chev.<br />
Mansonia gagei J.R.Drumm.<br />
Mappia racemosa Jacq.<br />
Mareya micrantha (Benth) Muell.Arg.<br />
Marila grandiflora Griseb.<br />
Markhamia hildebrandtii (Baker) Sprague<br />
Markhamia platycalyx Sprague<br />
Marmaroxylon racemosum Killip<br />
Marquesia macroura Gilg<br />
Matayba scrobiculata (HBK) Radlk.<br />
Mauria birringo Tul.<br />
Meiogyne virgata Miq.<br />
Melaleuca quinquenervia (Cav.) S.T.Blake<br />
Melanorrhoea torquata King<br />
Melanoxylon brauna Schott<br />
Melia azedarach Linn.<br />
Melia composita Willd<br />
Memecylon afzelii G.Don.<br />
Memecylon edule Roxb.<br />
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Mesua ferrea L.<br />
Metopium brownei (Jacq) Urban.<br />
Metrosideros collina A.Gray<br />
Metrosideros robusta A Cinn<br />
Mezilauris itauba (Meissn.) Taub.<br />
Mezzetia leptopoda Oliv<br />
Michelia champaca Linn<br />
Michelia <strong>for</strong>mosana Masamume<br />
Miconia argentia Swartz<br />
Microberlinia bisulcata A. Chev.<br />
Microberlinia brazzavillensis A. Chev<br />
Microdesmis puberula Hook f. ex Planch<br />
Micromelum pubescens Bl<br />
Mildbraediodendron excelsum Harms<br />
Milicia excelsa (Welw.) C.C. Berg<br />
Millettia laurentii de Wild<br />
Millettia pendula Benth<br />
Millettia rhodantha Baili<br />
Millettia stuhlmannii Taub.<br />
Mimusops dariensis Pitt<br />
Mimusops jaimiqui (C.Wright) Dub.<br />
Minquartia guianensis Aubl<br />
Mitragyna parvifolia (Roxb) Korth.<br />
Mitragyna rubrostipulacea Havill<br />
Monodora myristica Dunal<br />
Monopetalanthus heitzii pellegr.<br />
Monopetalanthus letestui Pellegr.<br />
Monotes kerstingii Gilg.<br />
Mora excelsa Benth.<br />
Mora gonggrijpii (Kleinh) Sandw<br />
Mora megistosperma (Pittier) Britt & Rose<br />
Morelia senegalensis A.Rich<br />
Moringa oleifera Lamk.<br />
Morus alba L.<br />
Morus celtidifolia H.B.K<br />
Morus lactea Mildbr<br />
Morus laevigata Wall<br />
Morus mezozygia (Stapf.)<br />
Mosquitoxylum jamaicense K & Urb.<br />
Mouriri parvifolia Benth<br />
Mouriri pseudo-geminata Pittier<br />
Musanga cecropioides R.Br.<br />
Myrianthus libericus Rendle<br />
Myrianthus serratus (Trecul) Benth & Hook f.<br />
Myrica cerifera L.<br />
Myristica castaneaefolia A.Gray<br />
Myristica chartacea Gillespie<br />
Myrocarpus fastigiatus Fr All.<br />
Myrospermum frutescens Jacq<br />
Myroxylon balsamum (L) Harms<br />
Myrsine capitellata Wall.<br />
Napoleonaea vogelii Hook. & Planch.<br />
Nauclea diderrichii (De Wild. ex Th. Dur.) Merr. w<br />
Nauclea junghuhnii (Miq.) Merr.<br />
Nauclea maingayi Hook. f.<br />
Nauclea pobeguinii (Pellegr.) Petit<br />
Naucleopsis macrophylla Miq.<br />
Necepsia afzelii Prain<br />
Neesia synandra Mast.<br />
Neoboutonia macrocalyx Pax<br />
Neonauclea peduncularis Merrill<br />
Nephelium longana Camb.<br />
Nesogordonia papaverifera (A.Chev.) R.Capuron<br />
Newtonia buchananii (Bak.) Gilb. & Bout.<br />
Newtonia paucijuga (Harms) Brenan<br />
Niemeyera prunifera F.Muell.<br />
Norrisia malaccensis Gardn.<br />
Nothofagus dombeyi Blume<br />
Nothofagus menziesii Oerst.<br />
Nothofagus moorei (F.Muell.) Krasser<br />
Nothofagus procera (P. & E.) Oerst.<br />
Nothofagus truncata (Colenso) Cockayne<br />
Nothopegia colebrookiana Bl.<br />
Nuxia floribunda Benth.<br />
Nyctanthes arbor-tristis Linn.<br />
Nycticalanthus speciosus Ducke<br />
Nyssa aquatica L.<br />
Ochanostachys amentacea Masters<br />
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71
Ochna arborea Burch. ex DC.<br />
Ochna holstii Engl.<br />
Ochna wallichii Planch.<br />
Ochroma lagopus Sw.<br />
Ochthocosmus africanus Hook. f.<br />
Ocotea barcellensis Mez<br />
Ocotea bullata E.Mey.<br />
Ocotea canaliculata (Rich) Mez.<br />
Ocotea coriacea (Sw.) Britt.<br />
Ocotea leucoxylon Gomez de la Maza<br />
Ocotea porosa L. Barroso<br />
Ocotea puberula Nees<br />
Ocotea rubra Mez.<br />
Ocotea usambarensis Engl.<br />
Ocotea wachenheimii R.Benoist<br />
Octoknema borealis Hutch. & Dalz.<br />
Octomeles sumatrana Miq.<br />
Odyendea zimmermannii Engl.<br />
Oldfieldia africana Benth. & Hook. f.<br />
Olea capensis L.<br />
Olea ferruginea Royle<br />
Olea hochstetteri (A.Chev.) Bak.<br />
Olea welwitschii (Knobl.) Gilg & Schell.<br />
Olinia cymosa Thunb.<br />
Olinia usambarensis Gilg<br />
Olmedia aspera R & P<br />
Omphalocarpum elatum Miers.<br />
Omphalocarpum procerum P. de Beaux<br />
Ongokea gore (Hua) Pierre<br />
Orites excelsa R.Br.<br />
Oroxylum indicum Benth<br />
Osyris compressa (Berg) A.DC.<br />
Ougenia dalbergioides Benth<br />
Oxandra lanceolata (Sw) Baill<br />
Oxystigma oxyphyllum (Harms) J.Leonard<br />
Pachira aquatica Aubl.<br />
Pachira insignis Sw.<br />
Pachyanthus cubensis A. Rich.<br />
Pachypodanthium staudtii (Engl. & Diels) Engl.<br />
Pahudia cochinchinensis Pierre ex Laness.<br />
Pajanelia rheedii D.C.<br />
Palaquium fidjiense Pierre ex Dubard<br />
Palaquium galactoxylum (F.Muell) H.J.Lam<br />
Palaquium hornei (Hartog ex Baker) Dubard<br />
Pangium edule Reinw.<br />
Parahancornea amapa (Huber) Ducke<br />
Paramacherium schomburgkii (Benth.) Ducke<br />
Parartocarpus triandrus J.J.Smith<br />
Parartocarpus venenosus (Zoll.& Mor.) Becc.<br />
Paraserianthes falcataria L.<br />
Paraserianthes falcataria~ L.<br />
Parashorea lucida (Miq.) Kurz<br />
Parashorea plicata Brandis<br />
Parashorea stellata Kurz<br />
Parastemon urophyllus A.DC.<br />
Paratecoma peroba (Record) Kuhlm.<br />
Paratrophis glabra (Merrill) v.Steenis<br />
Parinari campestris Aublet<br />
Parinari excelsa Sabine<br />
Parinari goetzeniana Engl.<br />
Parinari insularum A.Gray<br />
Parinarium griffithianum Benth.<br />
Parishia insignis Hook. f.<br />
Parkia bicolor A.Chev.<br />
Parkia filicoidea Welw. ex Oliv.<br />
Parkia javanica (Lam.) Merr.<br />
Parkinsonia aculeata L.<br />
Paropsia vareci<strong>for</strong>mis Mast.<br />
Patagonula americana L.<br />
Paulownia tomentosa (Thunb.) Steud.<br />
Pausinystalia lane-poolei Hutch.<br />
Payena lucida A.DC.<br />
Pelliciera rhizophorae Planch. & Triana<br />
Peltogyne porphyrocardia Griseb.<br />
Peltogyne pubescens Benth.<br />
Peltogyne venosa Benth.<br />
Peltophorum dasyrachis Kurz ex Bak.<br />
Pentace burmanica Kurz<br />
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Pentace triptera Mast.<br />
Pentaclethra macroloba (Willd.) Kuntze<br />
Pentaclethra macrophylla Benth.<br />
Pentacme contorta Merr. & Rolfe.<br />
Pentadesma butyracea Sabine<br />
Pentaphylax arborea Ridley<br />
Pentaspadon motleyi Hook. f.<br />
Perebea laevigata Standl.<br />
Pericopsis angolensis (Baker) van Meeuwen<br />
Pericopsis elata (Harms) van Meeuwen<br />
Pericopsis mooniana Thw.<br />
Pericopsis spp.<br />
Peronema canescens Jack.<br />
Persea americana Mill<br />
Persea caerulea (Ruiz et Pavon) Mez.<br />
Persea lingue Nees.<br />
Petersianthus macrocarpus (P.Beauv.) Liben<br />
Petitia domingensis Jacq.<br />
Phoebe porphyria (Gris) Mez<br />
Phyllanthus discoideus (Baill.) Mull. Arg.<br />
Phyllostylon brasiliensis Cap.<br />
Picea abies Karst.<br />
Picea engelmanii Engelm.<br />
Picea glauca Voss.<br />
Picea mariana B.S.P.<br />
Picea rubens Sarg.<br />
Picea sitchensis Carr.<br />
Picramnia pentandra Sw.<br />
Picrasma quassioides Benn<br />
Pinus banksiana Lamb.<br />
Pinus caribaea Morelet<br />
Pinus caribaea~ Morelet<br />
Pinus contorta Dougl.<br />
Pinus elliottii~ Engelm.<br />
Pinus kesiya Royle ex Gord.<br />
Pinus kesiya~ Royle ex Gord.<br />
Pinus lambertiana Dougl.<br />
Pinus merkusii~ Jungh & de Vr.<br />
Pinus monticola Dougl. ex Lamb.<br />
Pinus nigra Arn.<br />
Pinus oocarpa Schiede<br />
Pinus oocarpa~ Schiede<br />
Pinus palustris Mill.<br />
Pinus patula~ Schiede & Deppe<br />
Pinus pinaster Ait.<br />
Pinus ponderosa Laws.<br />
Pinus radiata D.Don<br />
Pinus radiata~ D.Don.<br />
Pinus resinosa Ait.<br />
Pinus strobus L.<br />
Pinus sylvestris L.<br />
Pinus taeda~ Linn.<br />
Piptadenia rigida Benth<br />
Piptadeniastrum africanum (Hook. f.) Brenan<br />
Piratinera guianensis Aubl.<br />
Piscidia communis (Blake) I.M. Johnst.<br />
Pistacia chinensis Bunge<br />
Pithecellobium arboreum Urb.<br />
Pithecellobium dulce (Roxb) Benth.<br />
Pithecellobium jupunba (Willd.) Urb.<br />
Pittoniotis trichantha Gris<br />
Planchonia papuana Knuth.<br />
Platanus hybrida<br />
Platanus occidentalis L.<br />
Plathymenia reticulata Benth<br />
Platonia insignis Mart.<br />
Platylophus trifoliatus D.Don<br />
Platymiscium pinnatum (Jacq) Dugand<br />
Platymiscium trinitatis Benth<br />
Platypodium elegans<br />
Plumeria sucuuba R. Spruce.<br />
Podocarpus dacrydioides A.Rich.<br />
Podocarpus ensiculus Melv.<br />
Podocarpus ferrugineus D.Don.<br />
Podocarpus gracilior Pilg.<br />
Podocarpus guatemalensis Standl.<br />
Podocarpus hallii Kirk.<br />
Podocarpus milanjianus Rendle<br />
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72
Podocarpus spicata R.BR.<br />
Podocarpus totara G.Benn<br />
Podocarpus usambarensis Pilg.<br />
Poeciloneuron indicum Bedd.<br />
Poga oleosa Pierre<br />
Polyalthia oliveri Engl. & Diels<br />
Polyscias ferruginea Harm<br />
Polyscias kikuyuensis Summ.<br />
Pometia pinnata Jacobs<br />
Pongamia pinnata (Linn) Pierre<br />
Populus deltiodes Marsh.<br />
Populus tremuloides Mich.<br />
Poulsenia armata (Miq.) Standl.<br />
Pouteria micropholis (Pierre) Baehni<br />
Premna angolensis Gurke<br />
Premna maxima T.C.E. Fries<br />
Prioria copaifera Gris<br />
Prosopis africana (Guill. & Perr.) Taubert<br />
Prosopis juliflora (Sw.) DC.<br />
Protium crenatum Sandwith<br />
Protium decandrum (Aublet) Marchand<br />
Protomegabaria stapfiana Hutch<br />
Prunus avium L.<br />
Prunus serotina Ehrh.<br />
Pseudocedrela kotschyi Harms<br />
Pseudosamanea guachapele Harms.<br />
Pseudosindora palustris Sym<br />
Pseudospondias microcarpa Engl.<br />
Pseudotsuga menziesii Franco.<br />
Psidium guajava L.<br />
Ptaeroxylon obliquum Radlk.<br />
Pteleopsis hylodendron (Mildbr.)<br />
Pteleopsis myrtifolia Engl. et Diels<br />
Pterocarpus angolensis D.C.<br />
Pterocarpus antunesii (Taub) Harms<br />
Pterocarpus dalbergioides Roxb.<br />
Pterocarpus macrocarpus Kurz.<br />
Pterocarpus officinalis Jacq.<br />
Pterocarpus soyauxii Taub.<br />
Pterogyne nitens Tul<br />
Pterospermum acerifolium Willd<br />
Pycnanthus angolensis (Welw) Warb<br />
Pygeum africanum Hook f.<br />
Pyrus communis L.<br />
Qualea rosea Aubl.<br />
Quararibea asterolepis Pittier<br />
Quassia amara L.<br />
Quassia indica (Gaertn.) Nooteboom<br />
Quercus cerris L.<br />
Quercus dentata Thunb.<br />
Quercus ilex L.<br />
Quercus petraea Liebl.<br />
Quercus robur L.<br />
Quercus rubra L.<br />
Randia cochinchinensis (Lour.) Merrill<br />
Randia exaltata Griff.<br />
Randia scortechinii King & Gamble<br />
Rapanea guianensis Aubl.<br />
Rapanea laetevirens Mez<br />
Rapanea melanophleos Mez<br />
Rapanea rhododendroides (Gilg.) Mez.<br />
Raputia magnifica Engl.<br />
Recordoxylon amazonicum Ducke<br />
Reynosia septentrionalis Urb.<br />
Rhabdodendron macrophyllum (Spruce) Huber<br />
Rheedia edulus Planch. & Triana<br />
Rhizophora apiculata Bl.<br />
Rhizophora mangle Linn.<br />
Rhodamnia cinerea Jack<br />
Rhodamnia trinervia Blume<br />
Rhodoleia teysmannii Miq.<br />
Rhus cotinus L.<br />
Rhus semialata Murray<br />
Rhus succedanea L.<br />
Rhus typhina Torn.<br />
Rhus wallichii Hook. f.<br />
Ribes glaciale Wall.<br />
Ricinodendron heudolottii (Baill) Pierre<br />
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Ricinodendron rautanenii Schinz.<br />
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Robinia pseudoacacia Linn.<br />
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Sabinea florida (Vahl) DC.<br />
Saccopetalum unguiculatum C.E.C. Fischer<br />
Sacoglottis gabonensis (Baill.) Urb.<br />
Sacoglottis obovata Urb.<br />
Sageraea ellptica Hook. f. & Thomas<br />
Sageretia oppositifolia Brongn.<br />
Sagotia racemosa Baill.<br />
Salix alba L.<br />
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Salix fragilis L.<br />
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Samanea saman (Jacq.) Merrill.<br />
Sandoricum indicum Cav.<br />
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Santalum album L.<br />
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Sapindus detergens Roxb.<br />
Sapindus drummondii Hook. & Arn.<br />
Sapindus saponaria L.<br />
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Sapium aucuparium Jacq.<br />
Sapium baccatum Roxb.<br />
Sapium ellipticum (Hochst.) Pax<br />
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Sapium insigne Benth.<br />
Schefflera paraensis Huber Apud Ducke<br />
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Schima noronhae Reinw.<br />
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Schinopsis balanse Engl.<br />
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Schinopsis lorentzii (Gris.) Engl.<br />
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Schizolobium parahybum (Vell.) Blake<br />
Schizomeria ovata D.Don<br />
Schleichera oleosa (Lour) Okan.<br />
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Schrebera alata (Hochst) Welw.<br />
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Schrebera arborea Chev.<br />
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Sclerocarya birrea (A.Rich.) Hochst.<br />
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Sclerolobium melinonii Harms<br />
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Scorodocarpus borneensis (Bail) Becc<br />
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Scottellia coriacea A.Chev<br />
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Scyphocephalium mannii (Benth) Warb.<br />
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Scytopetalum tieghemii Hutch. et Dalz.<br />
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Sebestena sebestena (L) Britton<br />
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Sequoia sempervirens Endl.<br />
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Serianthes melanesica Fosberg var. Melanesica<br />
Shorea balanocarpoides Sym<br />
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Shorea kunstleri King.<br />
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Shorea negrosensis Foxw.<br />
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Shorea polysperma Merr.<br />
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Shorea robusta Gaertn f<br />
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Shorea siamensis Miq<br />
Sideroxylon foetidissimum Jacq.<br />
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Simarouba amara Aubl.<br />
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Simarouba glauca DC.<br />
Siphonodon australis Benth.<br />
Siphonodon celastrineus Griff.<br />
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Spirostachys africana Sond<br />
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Spondias mombin L.<br />
Spondias pinnata (Linn.F.) Kurz<br />
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Staudtia kamerunensis Warb.<br />
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Staudtia stipitata Warb.<br />
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Sterculia apetala Karst.<br />
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Sterculia caribaea R.Brown<br />
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Sterculia oblonga Mast.<br />
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Sterculia pruriens (Aublet) Schumann<br />
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Sterculia quinqueloba (Garcke) K.Schum<br />
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Sterculia rhinopetala K.Schum.<br />
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Sterculia rugosa R.Brown<br />
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Stereospermum chelonoides (Linn F) DC<br />
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Stereospermum kunthianum Cham.<br />
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Strephonema pseudocola A Chev.<br />
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Strombosia glaucescens Engl.<br />
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Strombosia grandifolia Hook f ex Benth<br />
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Strombosia javanica Blume<br />
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Strombosia pustulata Oliv.<br />
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Strombosia scheffleri Engl.<br />
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Strychnos nux-vomica Linn.<br />
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Swartzia bannia Sandw.<br />
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Swartzia fistuloides Harms.<br />
Swartzia leiocalycina Benth . w<br />
Swartzia madagascariensis<br />
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Swietenia macrophylla King<br />
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Swietenia macrophylla~ King<br />
Swietenia mahagoni Jacq.<br />
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73
Swintonia floribunda Griff<br />
Swintonia schwenkii Teysm.<br />
Swintonia spicifera Hook f<br />
Symphonia globulifera L.f.<br />
Syncarpia glomulifera (Sm) Niedenzu<br />
Syncarpia hillii Bailey<br />
Syzygium cordatum Hochst.<br />
Syzygium guineense (Willd.) DC<br />
Tabebuia Donnell-Smithii J.N.Rose<br />
Tabebuia guayacan Hemsl.<br />
Tabebuia heterophylla (DC.) Britton<br />
Tabebuia insignis (Miq.) Sandw.<br />
Tabebuia rosea (Bertol.) DC.<br />
Tabebuia serratifolia Vahl.<br />
Tabebuia stenocalyx Sprague & Stapf.<br />
Tabernaemontana arborea Rose<br />
Tabernaemontana citrifolia L.<br />
Talauma sambuensis Pittier<br />
Tamarindus indica L.<br />
Tambourissa thouvenotii P.Dang.<br />
Tapirira guianensis Aubl.<br />
Taralea oppositifolia Aubl.<br />
Taxodium distichum Rich.<br />
Taxus baccata L.<br />
Teclea nobilis Del.<br />
Tecoma stans (L.) H.B.K.<br />
Tectona grandis Linn.f.<br />
Tectona grandis~ Linn.F.<br />
Terminalia aemula Diels.<br />
Terminalia amazonia (Gmel) Ecell.<br />
Terminalia bialata Steudel<br />
Terminalia brassii Excell<br />
Terminalia catappa Linn<br />
Terminalia chebula (Gaertn) Retz<br />
Terminalia ivorensis A. Chev.<br />
Terminalia paniculata W.& A.<br />
Terminalia procera Roxb.<br />
Terminalia prunioides Laws.<br />
Terminalia superba Engl. and Diels.<br />
Terminalia tomentosa W et A<br />
Tessmannia africana (Harms)<br />
Tessmannia anomala (Micheli) Harms.<br />
Testulea gabonensis Pellegr.<br />
Tetraberlinia bifoliolata (Harms)<br />
Tetraberlinia tubmaniana J.Leonard<br />
Tetractomia roxburghii Hook F<br />
Tetragastris balsamifera (Sw.) Kuntze<br />
Tetrameles nudiflora R.Br. ex Benn<br />
Tetramerista glabra Miq.<br />
Tetrapleura tetraptera (Schum. & Thonn) Taub.<br />
Theobroma bernouillii Pittier.<br />
Theobroma subicanum Mart.<br />
Thespesia populnea (L) Soland ex Correa<br />
Thuja occidentalis L.<br />
Thuja plicata Lamb<br />
Tieghemella africana H.Chev w<br />
Tieghemella heckelii Hutch. et Dalz<br />
Tilia americana L.<br />
Timonius wallichianus Valet<br />
Toona ciliata M.J. Roem.<br />
Toona ciliata~ M.J. Roem.<br />
Tourne<strong>for</strong>tia argentea Linn.<br />
Trachylobium verrucosum Oliv<br />
Trema micrantha (L) Blume.<br />
Trema orientalis (Linn) Bl.<br />
Trewia nudiflora Linn.<br />
Tricalysia singularis K Schum.<br />
Trichadenia philippinensis Merr.<br />
Trichilia emetica Vahl.<br />
Trichilia havanensis Jacq<br />
Trichilia hirta L.<br />
Trigonobalanus verticillatus Forman<br />
Trilepisium madagascariense DC.<br />
Triplaris surinamensis Cham.<br />
Triplochiton scleroxylon K. Schum<br />
Tristania conferta R.Br.<br />
Trochodendron aralioides Sieb. et Zucc.<br />
Trophis racemosa (L) Urb.<br />
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Tsuga canadensis Carr.<br />
Tsuga heterophylla Sarg.<br />
Turraeanthus africanus (Welw. ex C.DC.) Pelergry<br />
Uapaca guineensis (Don) Muell.Arg.<br />
Uapaca kirkana Muell.Arg.<br />
Ulmus mexicana Planch.<br />
Ungnadia speciosa Endl.<br />
Unona latifolia Hook. f. & Th.<br />
Upuna borneensis Sym.<br />
Urophyllum corymbosum Korth.<br />
Vaccinium leschenaultii Wight<br />
Vallesia glabra (Cav.) Link<br />
Vangueriopsis discolor Robyns<br />
Vatairea lundellii (Standl.) Killip.<br />
Vataireopsis araroba (Aguiar) Ducke<br />
Vateria indica L.<br />
Vatica cinerea King<br />
Vatica heteroptera Symington<br />
Vatica stapfiana (King) V.Sl.<br />
Ventilago madraspatana Gaertn.<br />
Vepris lanceolata (Lam.) G.Don<br />
Vernonia arborea Ham.<br />
Villebrunea integrifolia Gaud.<br />
Virgilia divaricata Adamson<br />
Virola bicuhyba (Schott) Warb.<br />
Virola koschnyi Warb<br />
Virola melinonii (Benoit) A.C. Smith<br />
Virola sebifera Aubl.<br />
Virola surinamensis (Rol) Warb<br />
Vitex cofassus Reinw.<br />
Vitex divaricata Sw.<br />
Vitex doniana Sweet.<br />
Vitex gaumeri Greenm.<br />
Vitex quinata Will.<br />
Vochysia guianensis Aubl.<br />
Vochysia hondurensis Sprague.<br />
Vochysia lanceolta Staf.<br />
Vochysia surinamensis Stafl.<br />
Vochysia tetraphylla DC.<br />
Vouacapoua americana Aubl.<br />
Wallaceodendron celebicum Koord.<br />
Wallenia laurifolia (Jacq.) Sw.<br />
Walsura villosa Wall.<br />
Waltheria americana L.<br />
Warburgia ugandensis Sprague<br />
Warscewiczia coccinea (Vahl) Klotsch<br />
Weinmannia trichosperma Cav.<br />
Wendlandia tinctoria DC.<br />
Wercklea insignis Pitt. & Stand.<br />
Wightia gigantea Wall.<br />
Wormia pulchella Jack<br />
Wrightia tinctoria R.Br.<br />
Wrightia tomentosa R. & Sch.<br />
Xanthophyllum flavescens Roxb.<br />
Ximenia americana L<br />
Xylia xylocarpa (Roxb.) Taub.<br />
Xylopia parviflora (A.Rich.) Benth.<br />
Xylopia parvifolia Hook. f. & Th.<br />
Xylopia quintasii Engl. & Diels<br />
Xymalos monospora (Harv.) Baill.<br />
Zanthoxylum elephantiasis McFad.<br />
Zanthoxylum fagara (L) Sarg.<br />
Zanthoxylum gillettii (De Wild.) Waterman<br />
Zanthoxylum martinicense (Lam.) DC.<br />
Zelkova <strong>for</strong>mosana Hayata<br />
Zelkova serrata Makino<br />
Zinowiewia integerrima Turcz.<br />
Ziziphus jujuba Lamk.<br />
Zollernia paraensis Hub.<br />
Zuelania guidonia (Sw.) Britt. & Millsp.<br />
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