| Operation | Importance rating | Operational priority rating | Remarks | ||||||||||
| Exploration | Evaluation | Conservation | Utilisation | ||||||||||
| Species | Wood Production | Other Purposes | Botanical | Genecological | Collection for Testing | Testing (Provenance Trials) | In Situ | Collection for Conservation | Storage as Seed etc. | Ex Situ in Artificial Stands | Use of Bulk Supplies | Individual Selection and Breeding | |
| 7. (b) South-East Asia | |||||||||||||
Acacia nilotica | 1 | - | - | - | - | 1 | - | - | 2 | - | - | for soil protection and range management in arid zone | |
Acacia senegal | 1 | - | - | - | - | 2 | - | - | 1 | - | - | " " " " | |
Albizia falcata | 2 | - | 2 | 2 | 2 | - | - | - | - | - | - | important for pulp | |
Anthocephalus cadamba (syn. A. chinensis) | 3 | - | 3 | 3 | 3 | - | - | - | - | - | - | proved difficult to grow in monoculture (India) | |
Araucaria cunninghamii | 1 | - | 1 | 1 | 1 | 3 | - | - | - | 2 | 2 | ||
Araucaria hunsteinii | 1 | - | 1 | 1 | 1 | 3 | - | - | - | 2 | 2 | ||
Azadirachta indica | 1 | - | 1 | 1 | 1 | 2 | - | - | 1 | 1 | 2 | ||
Bamboo spp. | 1 | 1 | 1 | - | - | - | 1 | - | - | - | - | - | sporadic flowering habit may endanger regeneration |
Bischofia javanica | 3 | - | 3 | 3 | 3 | 3 | - | - | - | - | - | ||
Bombax ceiba | 1 | - | - | 2 | 2 | - | - | - | - | - | 1 | ||
Dalbergia latifolia | 1 | - | - | - | - | 1 | 1 | - | 1 | - | - | ||
Dalbergia sissoo | 1 | - | 1 | 1 | 1 | - | - | - | 2 | - | 2 | v. promising N. India and Pakistan | |
Dipterocarpus spp. | 1 | - | - | - | - | 1 | 1 | 1 | - | - | - | needs research on seed storage | |
Eucalyptus deglupta | 1 | - | 1 | 1 | 1 | 2 | 1 | - | 1 | - | 2 | ||
Eucalyptus urophylla | 1 | - | 1 | 2 | 1 | - | - | - | 1 | 2 | 3 | ||
Gmelina arborea | 1 | - | 1 | 1 | 1 | 2 | 2 | 2 | 2 | 1 | 1 | needs research on seed storage | |
Pinus kesiya (syn. khasya, insularis) | 1 | - | 2 | 1 | 1 | 2 | - | - | 1 | 1 | 1 | ||
Pinus merkusii/ merkusiana | 1 | - | 2 | 1 | 1 | - | 1 | - | 1 | - | 1 | ||
Santalum album | 2 | - | - | - | - | - | - | - | - | - | 2 | high priority parts of S. India | |
Tectona grandis | 1 | - | 2 | 1 | 1 | 1 | - | - | 1 | 2 | 1 | ||
Toona ciliata | 3 | - | 3 | - | - | - | - | - | - | - | - | ||
Toona serrata | 3 | - | 3 | - | - | - | - | - | - | - | - | ||
| 8. Africa | |||||||||||||
Acacia albida | 1 | - | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | important for soil protection and range management in arid zones, also for gum, tannin or fodder production | |
Acacia nilotica | 1 | - | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
Acacia senegal | 1 | - | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
Acacia tortilis | 1 | - | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
Alluaudia procera | 2 | - | - | - | - | 1 | - | - | - | - | - | (E) in Madagascar | |
Aucoumea klaineana | 1 | - | 1 | 1 | - | 1 | - | - | 1 | - | 2 | (E) of great local importance to some W. African countries | |
Brachylaena hutchinsii | 2 | - | - | - | - | 1 | - | - | - | - | - | (E) in part of range | |
Burtt-davya nyasica | 3 | 3 | - | - | - | - | - | - | - | - | - | ||
Chlorophora excelsa | 1 | 2 | 1 | - | - | 3 | 1 | 3 | 1 | 1 | 1 | selection for resistance to gall of utmost importance | |
Chlorophora regia | 1 | 2 | 1 | - | - | 3 | 1 | 3 | 1 | 1 | 1 | ||
Diospyros spp. | 1 | - | - | - | - | 1 | - | - | 1 | - | - | for ebony wood | |
Entandrophragma angolense | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | selection for resistance to shoot borer of utmost importance | |
Entandrophragma cylindricum | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | " " " " " | |
Entandrophragma utile | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | " " " " " | |
Gymnostemon zaizou | 1 | - | - | - | - | 1 | - | - | - | - | - | (E) in Ivory Coast | |
Juniperus procera | 2 | - | - | - | - | 3 | - | - | - | - | - | conserve as part of ecosystem | |
Khaya anthotheca | 1 | - | 1 | 1 | 1 | - | - | - | - | - | - | selection for resistance to shoot borer of utmost importance | |
Khaya grandifoliola | 1 | - | 1 | 1 | 1 | 1 | - | - | - | - | - | " " " " " | |
Khaya ivorensis | 1 | - | 1 | 1 | 1 | - | - | - | - | - | - | " " " " " | |
Khaya nyasica | 2 | - | - | - | - | 2 | - | - | - | - | - | " " " " " | |
Khaya senegalensis | 1 | - | 2 | 2 | 2 | 1 | - | - | - | 3 | - | (E) in northern part of range | |
Maesopsis eminii | 2 | - | - | - | 2 | - | - | - | - | - | 2 | important in Uganda | |
Mitragyna ciliata | 2 | 2 | 2 | 2 | 2 | 1 | 2 | 2 | 2 | 2 | 2 | locally important in W. Africa | |
Nauclea diderrichii | 2 | 2 | 2 | 2 | 2 | 1 | 2 | 2 | 2 | 2 | 2 | " " " " | |
Pericopsis elata (syn. Afrormosia elata) | 2 | 2 | 2 | 2 | 2 | 1 | 1 | 1 | 1 | - | - | (E) | |
Pterocarpus angolensis | 2 | - | - | - | - | 2 | - | - | - | - | - | ||
Pterygota macrocarpa | 3 | - | - | - | - | 2 | - | - | 2 | - | - | ||
Terminalia ivorensis | 1 | - | 1 | - | - | - | - | - | 1 | 1 | 1 | ||
Terminalia superba | 1 | - | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
Triplochiton scleroxylon | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 1 | ||
Turraeanthus africana | 1 | 2 | 2 | 2 | 2 | 1 | 2 | 2 | 2 | 2 | 2 | locally important in W. Africa | |
Widdringtonia whytei | 2 | - | - | - | - | 3 | - | - | - | - | - | conserve as part of ecosystem | |
| 9. Australia | |||||||||||||
Acacia binervata | 2 | 2 | 2 | ||||||||||
Acacia cyanophylla | 3 | 1 | 2 | 2 | 2 | 2 | coastal shelter and salt tolerance | ||||||
Acacia elata | 2 | 2 | 2 | ||||||||||
Acacia peuce | 2 | 2 | 2 | 2 | 2 | 1 | 2 | Limited distribution, use in v. arid areas | |||||
Acacia pruinocarpa | 3 | 2 | 3 | 3 | |||||||||
Acacia salicina | 2 | 2 | 2 | 2 | 2 | 2 | shelter in arid zones with high pH | ||||||
Araucaria cunninghamii | 1 | 1 | 1 | 1 | 3 | 2 | 2 | selection and breeding in Australia | |||||
Callitris glauca | 1 | 3 | 3 | 3 | |||||||||
Callitris intratropica | 1 | 2 | 2 | 3 | 2 | ||||||||
Casuarina decaisneana | 2 | 2 | 2 | 3 | 3 | use for shelter in arid zones | |||||||
Casuarina glauca | 3 | 3 | 3 | use for coastal windbreaks | |||||||||
Eucalyptus acmenioides | 1 | 2 | 2 | 2 | |||||||||
E. alba | 2 | 2 | 2 | 3 | 3 | 2 | |||||||
E. argophloia | 2 | 2 | 1 | 1 | |||||||||
E. astringens | 1 | 2 | 2 | 2 | 1 | 2 | tannin production | ||||||
E. bicostata | 1 | 1 | 1 | 1 | 1 | 2 | 1 | 3 | |||||
E. botryoides | 1 | 3 | 1 | 1 | 2 | 3 | 2 | use for coastal windbreaks, sand fixation | |||||
E. brassiana | 2 | 2 | 2 | 2 | 2 | 3 | |||||||
E. brevifolia | 3 | 1 | 1 | 2 | use for shelter in arid zones | ||||||||
E. brockwayi | 1 | 3 | 2 | 3 | 2 | ||||||||
E. camaldulensis | 1 | 1 | 1 | 2 | 1 | 1 | 3 | 1 | 1 | ||||
E. cambageana | 2 | 2 | 2 | ||||||||||
E. citriodora | 1 | 1 | 2 | 1 | 1 | 3 | 1 | 2 | use for oil production | ||||
E. cladocalyx | 2 | 2 | 2 | 3 | 2 | 2 | 3 | 3 | use for windbreaks | ||||
E. cloeziana | 1 | 1 | 1 | 2 | 3 | 3 | 2 | 2 | |||||
E. crebra | 1 | 2 | 2 | 2 | 3 | ||||||||
E. cypellocarpa | 1 | 2 | 2 | 2 | 3 | ||||||||
E. dalrympleana | 1 | 3 | 2 | 2 | 2 | 3 | 1 | 1 | |||||
E. deanei | 1 | 2 | 2 | 1 | 2 | 3 | 1 | 1 | |||||
E. delegatensis | 1 | 2 | 2 | 2 | 2 | 2 | |||||||
E. dives var. “C” | 1 | 1 | 2 | 2 | 1 | 3 | 1 | oil production | |||||
