Table 6
FOREST GENETIC RESOURCES PRIORITIES (BY REGION, SPECIES AND OPERATION)
| 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 albus | 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 nyacica | 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 | |
| Entandrophragna angelense | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | selection for resistance to shoot borer of utmost importance | |
Entandrophragna cylindrious | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | " " " " " | |
| Entandrophragna utile | 1 | - | 1 | 1 | 1 | 2 | 1 | 2 | 1 | 1 | 1 | " " " " " | |
| Gymnostemon saizou | 1 | - | - | - | - | 1 | - | - | - | - | - | (E) in Ivory Coast | |
| Juniperus procera | 2 | - | - | - | - | 3 | - | - | - | - | - | conserve as part of ecosystem | |
| Khaya anthotheca | 1 | - | 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 emirii | 2 | - | - | - | 2 | - | - | - | - | - | 2 | important in Uganda | |
| Mitragyna ciliata | 2 | 2 | 2 | 2 | 2 | 1 | 2 | 2 | 2 | 2 | 2 | locally important in W. Africa | |
| Manclea diderrichii | 2 | 2 | 2 | 2 | 2 | 1 | 2 | 2 | 2 | 2 | 2 | " " " " | |
Perioopsis elata (syn. Afrormcsia 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 wind breaks, 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 | |||||
| Eucalyptus drepanophylla | 2 | 3 | 2 | 3 | |||||||||
| E. dunnii | 1 | 2 | 1 | 2 | 1 | 1 | 1 | ||||||
| E. exserta | 2 | 2 | 2 | ||||||||||
| E. fibrosa spp. fibrosa | 2 | 2 | |||||||||||
| E. fastigata | 1 | 1 | 2 | 1 | 2 | 3 | 2 | 3 | |||||
| E. gamophylla | 3 | 2 | 2 | 2 | 3 | oil production | |||||||