Chairman Dr. R. Morandini (Italy) Vice-Chairman Dr. F. Ng (Malaysia)
Australia | Dr.J.W. Turnbull | Alternate | Australia |
Division of Forest Research | Mr. J.C. Doran | ||
CSIRO | Division of Forest Research | ||
P.O. Box 4008 | CSIRO | ||
Canberra A.C.T. 2600 | P.O. Box 4008 | ||
Canberra A.C.T. 2600 | |||
Brazil | Dr. M. Ferreira | Alternate | Chile |
IPEF/ESALO | Sr. R. Delmastro | ||
Caixa Postal No. 9 | Universidad Austral de Chile | ||
Piracicaba, Sao Paulo State 13400 | Casilla 567 UACH | ||
Valdivia | |||
Canada | Dr. C.W. Yeatman | Alternate | Canada |
Canadian Forestry Service | Dr. E.K. Morgenstern | ||
Petawawa National Forestry Institute | Faculty of Forestry | ||
Chalk River | University of New Brunswick | ||
Ontario KOJ 1JO | Fredericton N.B. | ||
China | Dr. Pan Chih-Kang | Alternate | China |
The Arboretum | Dr. Z.S. Zhu | ||
Chinese Academy of Forestry | Forest Research Institute | ||
Wan Shou Shan | Kwangtung Province | ||
Beijing | Sha Ho | ||
Kwangchow | |||
Denmark | Mr. H. Keiding | Alternate | Denmark |
Arboretet | Mr. H. Barner | ||
DK - 2970 Hørsholm | Stattskovenes Planteavlsstation | ||
DK - 3050 Humlebaek | |||
Finland | Dr. M. Hagman | Alternate | Sweden |
Forest Research Institute | Mr. P. Krutzsch | ||
Forest Tree Breeding Station | Skogsstyrelsen | ||
SF - 01590 Maisala | S - 55183 Jököping | ||
France | M. M. Corbasson | Alternate | France |
Centre technique forestier tropical | M. C. Cossalter | ||
45bis Avenue de la Belle Gabrielle | Centre technique forestier tropical | ||
F-94130 Nogent-sur-Marne | 45bis Avenue de la Belle Gabrielle | ||
F-94130 Nogent-sur-Marne | |||
Honduras | Sr. O. Ochoa M. | Alternate | Guatemala |
Banco de Semillas | Sr. O. Vinicio | ||
Escuela Nacional de Ciencias Forestales | Banco de Semillas Forestales | ||
Corporación Hondureña de Desarrollo Forestal | Instituto Nacional Forestal | ||
Siguatepeque, Comayagua | 7a Avenida 7-00, zona 13 | ||
Ciudad de Guatemala | |||
India | Mr. R. C. Ghosh | Alternate | India |
3 Bengali Library Road | I.F.S. Madan Gopal | ||
Dehra Dun - 248001 U.P. | Coordinator | ||
Indo-Danish project on Seed Procurement and Tree Improvement | |||
Indian Forest Service | |||
State Forest Department Buildings | |||
Saifabad | |||
Hyderabad 500 004 A.P. | |||
Italy | Dr. R. Morandini | Alternate | Greece |
Istituto Sperimentale per la Selvicoltura | Prof. C.P. Panetsos | ||
I-52100 Arezzo | Laboratory of Forest Genetics | ||
School of Agriculture and Forestry | |||
Aristotelian University | |||
Thessaloniki | |||
Kenya | Mr. J. A. Odera | Alternate | Malawi |
Kenya Forest Department | Mr. R.S.W. Nkonja | ||
P.O. Box 74 | Department of Forestry | ||
Kikuyu | Forestry Research Institute of Malawi | ||
P.O. Box 270 | |||
Zomba | |||
Malaysia | Dr. F. Ng | Alternate | Thailand |
Forest Research Institute | Dr. S. Bhumibhamon | ||
Kepong, Selangor | Faculty of Forestry | ||
Kasetsart University | |||
Bangkok 10903 | |||
Mexico | Ing. F. Patiño V. | Alternate | Mexico |
Instituto Nacional de Investigaciones Forestales | Ing. L.J. Maldonado A. | ||
Centro de Investigaciones Forestales del Noreste | |||
Av. Progreso, 5 | |||
Coyoacán 21 D.F. | Instituto Nacional de Investigaciones Forestales | ||
A.P. 150 | |||
Saltillo, Coahuola 25260 | |||
Nigeria | Mr. G.O.A. Ojo | Alternate | Ivory Coast |
Forestry Research Institute of Nigeria | M. K. Diabate | ||
Centre technique forestier tropical | |||
P.M.B. 5054 | |||
Ibadan | B.P. 8033 | ||
Abidjan | |||
United Kingdom | Mr. R. H. Kemp | Alternate | United Kingdom |
Overseas Development Administration | Mr. P.J. Wood | ||
Commonwealth Forestry Institute | |||
Eland House | |||
Stag Place | University of Oxford | ||
London SW1E 5DH | South Parks Road | ||
OX1 3RB Oxford |
FAO PANEL OF EXPERTS ON FOREST GENE RESOURCES
Fifth Session
Rome 8 – 11 December 1981
Opening of the Meeting
Election of Chairman and Vice-Chairman
Adoption of Agenda
Progress since 4th Session of Panel (March 1977)
Other international activities
Summarized review of Global Programme for the Improved Use of Forest Genetic Resources
Revision of priorities for future action
Species priorities (Group Work)
Summary recommendations on regional, operational and species priorities
Proposals for FAO Regular Programme activities
Proposals for other projects
Miscellaneous
Other business
Institute | Amount (US$) | Purpose |
US Forest Tree Seed Centre, Macon | 2 000 | Seed of N. American species for developing countries |
ENGREF1, France | 3 000 | Frost-hardy Eucalyptus species |
CFI2, U.K. | 8 000 | Central American conifers and hardwoods |
Office of Forests, Papua New Guinea | 5 000 | Araucaria, Eucalyptus and Acacia species |
CSIRO3, Australia | 7 000 | Eucalyptus and Acacia species |
8 000 | ||
CTFT4, France | 8 000 | West African hardwoods |
Forest Dept., Nicaragua | 5 000 | P.caribaea, P. oocarpa for conservation/evaluation |
Forest Dept., Belize | 1 800 | P. caribaea, P. oocarpa for conservation/evaluation |
COHDEFOR5, Honduras | 5 000 | P. caribaea, P. oocarpa for conservation/evaluation |
Forest Dept., Indonesia | 3 500 | Tropical Acacia species |
INIF6, Mexico | 8 000 | Dry area Prosopis & Atriplex sp. |
CONAF7, Chile | 8 700 | Dry area Prosopis, Acacia and Atriplex species |
INFOR8, Peru | 5 000 | Dry area Prosopis & Capparis sp. |
Agr.Res.Centre, P.D.R. Yemen | 5 000 | Dry area Prosopis & Acacia sp. |
Forestry Res. Inst., Sudan | 3 000 | Dry area Acacia species |
CNRF9, Senegal | 7 000 | Dry area Acacia species |
Land Development Authority, Israel | 3 000 | Dry area Acacia species |
TOTAL | US$96 000 |
1 Ecole Nationale du Genie Rural des Eaux et des Forêts, Nancy
2 Commonwealth Forestry Institute, Oxford
3 Commonwealth Scientific and Industrial Research Organization, Canberra
4 Centre Technique Forestier Tropical, Nogent-sur-Marne
5 Corporación Hondureña de Desarrollo Forestal, Siguatepeque
6 Instituto Nacional de Investigaciones Forestales, Mexico City
7 Corporación Nacional Forestal, Santiago
8 Instituto Nacional Forestal y de Fauna, Lima
9 Centre National de Recherches Forestières, Dakar
1966/67 | 1968/69 | 1970/71 | 1972/73 | 1974/75 | 1976/77 | 1978/79 | 1980/81 | 1982/83 | |
SEED PROCUREMENT | |||||||||
FRI & CSIRO, Canberra, Australia (Eucalypts, Araucaria, Acacia, P. radiata) | 10 000 | 13 000 | 10 000 | 10 000 | 15 000 | 15 000 | 18 000 | 15 000 | ( 9 500) |
CFI, Oxford, UK (Central Am. Pines & hardwoods) | 15 000 | 15 000 | 3 000 | 5 000 | 8 000 | ( 2 000) | |||
INIF, Mexico (Pinus spp. dry area spp.) | 5 000 | 5 000 | 10 000 | 5 000 | 10 000 | 8 000 | (10 000) | ||
IUFRO (N. Am. Conifers) | 1 200 | 5 000 | 1 000 | ||||||
UNDP/FAO/Brazil (Araucaria) | 8 000 | 3 000 | |||||||
FRI, Nigeria (Tropical hardwoods) | 2 500 | 2 500 | 3 000 | 5 000 | |||||
CTFT, France (Tropical hardwoods, incl. arid zone Acacia species) | 2 500 | 5 000 | 3 000 | 5 000 | 8 000 | ( 7 000) | |||
Ist. Sper. Selvicoltura, Arezzo, Italy (Mediterranean conifers) | 5000 | 3000 | 1500 | ||||||
Seed Centre, Macon, USA (cost of seed for developing countries) | 500 | 1 000 | 1 000 | 2 000 | 2 000 | ( 2 000) | |||
Office of Forests, Papua New Guinea (Eucalyptus, Acacia, Araucaria & Casuarina) | 5000 | 5 000 | 5 000 | (12 000) | |||||
Danish/FAO Forest Tree Seed Centre, Humlebaek (Gmelina) | 5 0001 | ||||||||
F.D., Nicaragua (P. caribaea) | 3 500 | 5 000 | |||||||
BANSEFOR, Guatemala (P.caribaea, P. oocarpa, P. strobus var. chiapensis) | 2 8001 | ||||||||
Fiji Pine Commission (P. caribaea) | 3 000 | ( 500) | |||||||
Queensland F.D. (P. caribaea seed/scion supply) | 1 000 | ||||||||
ENGREF, France (frost-hardy Eucalypts) | 3 000 | ||||||||
F.D., Belize (Tropical pines) | 1 800 | ||||||||
COHDEFOR, Honduras (Tropical pines) | 5 000 | ||||||||
F.D., Indonesia (Tropical Acacia spp.) | 3 5001 | ( 1 500) | |||||||
CONAF, Chile (dry area spp.) | 8 700 | (12 000) | |||||||
INFOR, Peru (dry area spp.) | 5 000 | ( 9 000) | |||||||
Agric.Res.Centre, P.D.R Yemen (dry area spp.) | 5 000 | ( 5 000)4 | |||||||
F.R.I, Sudan (dry area Acacia spp.) | 3 000 | ( 4 000)4 | |||||||
CNRF, Senegal (dry area Acacia spp.) | 7 000 | (10 000) | |||||||
Land Dev. Authority, Israel (dry area Acacia spp.) | 3 000 | ( 2 000) | |||||||
F.R.I., India | ( 5 000)4 | ||||||||
F.D., Pakistan | |||||||||
Miscellaneous | 1 500 | ( 1 500)4 | |||||||
SUB-TOTAL | 10 000 | 14 500 | 36 200 | 51 500 | 40 000 | 35 000 | 64 300 | 96 000 | (93 000)4 |
EX SITU CONSERVATION STANDS | |||||||||
F.R.I., Nigeria | 5 000 | ||||||||
OCF, Congo | 5 000 | 2 000 | |||||||
SUB-TOTAL | 10 000 | 2 000 | |||||||
DISSEMIN. OF INFORMATION | |||||||||
Forest Genetic Resources Inform. | 16 000 | 17 500 | 38 000 | 42 000 | 34 000 | (34 000) | |||
Methodology of Conservation (FP;MISC/75/8) | 10 000 | 7 000 | |||||||
SUB-TOTAL | 16 000 | 17 500 | 48 000 | 49 000 | 34 000 | (34 000) | |||
MEETINGS | |||||||||
FAO Panel of Experts on Forest Gene Resources | 10 000 | 9 000 | 14 000 | 19 000 | 67 000 | ||||
3rd World Consultation on Forest Tree Breeding | 58 000 | 4 000 | |||||||
SUB-TOTAL | 10 000 | 9 000 | 14 000 | 77 000 | 4 000 | 67 000 | |||
CONSULTANCIES | 15 000 | 31 000 | (29 300) | ||||||
HQ.STAFF, DIRECT COSTS 2 3 | 5 000 | 10 000 | 16 000 | 35 000 | 25 000 | 64 000 | 60 000 | 60 000 | (112 752) |
TOTAL (approximate) | 15 000 | 34 500 | 61 200 | 102 500 | 96 500 | 234 000 | 210 300 | 257 000 | (269 052) |
1 Carried forward (in part or fully) to following biennium
(1981)
Species | Pinus caribaea var. hondurensis | Pinus oocarpa | Eucalyptus tereticornis | Eucalyptus camaldulensis | ||||||||
Provenance | Alamicamba | Los Limones | Poptun | Mountain Pine Ridge | Yukul | Bonete | Cooktown | Mt.Carnet | Petford | Katherine | Gibb River | TOTAL |
Country | Area, ha 1 | |||||||||||
Congo | 16.4(20)2 | 20.0(20) | 8.2(10) | 10.1(10) | 20.1(20) | 20.0(20) | 9.1(10) | 9.8(10) | - | - | - | 113.7(120) |
Ivory Coast | 7.0(10) | - | 8.0(10) | 9.4(10) | 9.0(10) | - | - | - | - | - | - | 33.4(40) |
Kenya | - | 7.5(10) | - | - | - | - | - | - | - | - | - | 7.5(10) |
Nigeria | 1.4(20) | 8.0(20) | - | 14.7(30) | 30.5(30) | 18.4(0) | 1.6(0) | 3.0(0) | 2.6(10) | 1.4(10) | - | 81.6(120) |
Zambia | - | - | - | 20.0(20) | 10.0(10) | 20.0(20) | 19.0(10) | 11.0(10) | - | - | - | 80.0(70) |
Thailand | 10.2(20) | 12.6(20) | 10.1(10) | 14.9(20) | 18.7(20) | - | - | - | 22.0(10) | - | 24.9(10) | 113.4(110) |
India3 | (10) | (10) | (10) | (10) | (10) | (10) | - | - | - | - | - | (60) |
TOTAL AREA (31.12.80) | 35.0(80) | 48.1(80) | 26.3(40) | 69.1(100) | 88.3(100) | 58.4(50) | 29.7(20) | 23.8(20) | 24.6(20) | 1.4(10) | 24.9(10) | 429.6(530) |
2 Numbers in parenthesis indicate area originally planned.
3 Joined the project only in 1980.
COUNTRY | SPECIES | OBSERVATIONS |
Australia | Eucalyptus camaldulensis Dehnh.1 | 11 new provenances collected for project with special emphasis on arid zones |
E. microtheca F.Muell. 1 | 73 seedlots, grouped into 21 “provenance groups” for first-stage evaluation according to climatic conditions. | |
Acacia aneura F.Muell. ex. Benth. | 5 provenances collected by early 1980 | |
Chile | Acacia caven Mol. | |
Atriplex repanda Phil. | ||
Prosopis tamarugo F. Philippi | ||
Prosopis spp. (“Algarrobo”) | May include several species. P. atacamensis, P. silicuastrum, P. chilensis, P. burkartii | |
India | Acacia nilotica (L.) Willd. ex Del. | ssp. indica/var.vediana var. jaquamontii var. cupressiformis |
A. senegal (L.) Willd. | “Land Race” | |
A. tortilis Hayne | “Land Race”; according to some sources may in fact be A.raddiana Savi. | |
Prosopis cineraria (L.)Druce (syn. P. spicigera L.) | ||
Israel | Acacia albida Del. | |
A. raddiana Savi (syn. A. tortilis (Forsk) Hayne ssp. raddiana (Savi) Brenan | ||
A. tortilis Hayne (syn. A. tortilis (Forsk) Hayne ssp. tortilis (Hayne) Brenan | ||
Mexico | Acacia berlandieri | |
A. farnesiana | ||
Atriplex canescens | ||
Cercidium spp. | ||
Prosopis spp. (“Mezquite”) | May include several species, P. juliflora; P. glandulosa, P. alba, P. torreyana | |
Pakistan | Acacia nilotica | |
A. senegal | “Land Race” | |
Prosopis cineraria | ||
Peru | Prosopis spp. (“Algarrobo”) | May include several species, P. chilensis, P. limensis, P. juliflora |
Senegal | Acacia albida Del. | |
A. nilotica (L.) Willd. ex. Del. var. adansonii | ||
A. raddiana Savi | ||
A. senegal (L.) Willd. | ||
A. tortilis Hayne | ||
Sudan | Acacia nilotica (L.) Willd. ex. Del. | ssp. nilotica ssp. tomentosa ssp. adstringes |
Acacia tortilis | ||
PDR Yemen | Prosopis cineraria (L.) Druce | |
Acacia nilotica (L.) Willd. ex Del. | “Land Race” | |
A. senegal (L.) Willd. | ||
A. tortilis Hayne |
1 Collections completed and distributed for evaluation.
Lists of species endangered in parts or the whole of their range are given in this Appendix. They come from various sources. The species listed by the Panel (Appendix 7.1) consist mainly of species of known or potential value for social or economic use, whereas the other lists include taxonomic species whether or not they are of known value. The Panel list (7.1) includes species which are not endangered as species but contain valuable endangered populations.
7.1 SPECIES LISTED AT THE 5TH SESSION OF THE FAO PANEL OF EXPERTS ON FOREST GENE RESOURCES
Abies guatemalensis
A. nebrodiensis
A. numidica
Acacia albida
A. caven
A. tortilis subsp. tortilis
A. tortilis subsp. raddiana
Adenanthera macrocarpa
Alnus jorullensis
Aniba duckei
Araucaria angustifolia
A. cumminghamii
A. hunsteinii
Aspidosperma polyneuron
Astronium urundeuva
Atriplex repanda
Balfourodendron riedelianum
Bertholetia excelsa
Bombacopsis quinata
Brachylaena hutchinsii
Caesalpinia dalei
Cedrela fissilis
C. odorata
Cedrus libani
Cercidiphyllum japonicum
Chlorophora excelsa
Cordia milleni
Cupressus atlantica
C. dupreziana
Dalbergia nigra
Didymopanax morototoni
Diospyros hemiteles
Dipteryx alata
Entandrophragna angolense
Esenbeckia leiocarpa
Eucalyptus deglupta
E. globulus subsp. globulus
Fagus longipetiolata
Gigasiphon macrosiphon
Glyptostrobus pensilis
Gossweilerodendron balsamiferum
Gymnostemon zaizou
Ilex paraguaiensis
Irvingia gabonensis
Joannesia princeps
Juniperus bermudiana
Juniperus procera
Khaya senegalensis
Liquidambar styraciflua
Lovoa swynnertonii
Machaerium villosum
Mimosa caesalpinifolia
Mimosa verrucosa
Nesogordonia papaverifera
Ocotea porosa
Pericopsis elata
Pinus armandii var. ahamiana
P. eldarica
P. koraiensis
P. patula subsp. tecunumanii (syn. P. tecunumanii)
P. pentaphylla
P. pseudostrobus
P. radiata
Piptadenia peregrina
Platanus orientalis
Plathymenia foliosa
Populus ilicifolia
Prosopis cineraria
Pseudotsuga gaussenii
P. sinensis
Pterogyne nitens
Schinopsis brasiliensis
Stuhlmannia moavi
Tabebuia impetiginosa
Taiwania cryptomerioides
T. flousiana
Tectona hamiltoniana
T. philippinensis
Ulmus wallichiana
Vepris glandulosa (syn. Tecleopsis glandulosa)
Zeyheria tuberculosa
7.2 TREE SPECIES OR SPECIES WITH POTENTIAL IN FORESTRY ACTIVITIES INCLUDED IN THE IUCN RED DATA BOOK (1978) 1
Categories used in the Red Data Book: | |
(Ex) | Extinct |
A category used for species not found after repeated searches of known and likely areas. | |
(E) | Endangered |
Taxa in danger of extinction and whose survival is unlikely if the causal factors continue operating. | |
Included are taxa whose numbers have been reduced to a critical level or whose habitats have been so drastically reduced that they are deemed to be in immediate danger of extinction. | |
(V) | Vulnerable |
Taxa believed likely to move into the endangered category in the near future if the causal factors continue operating. | |
Included are taxa of which most or all the populations are decreasing because of over-exploitation, extensive destruction of habitat or other environmental disturbance; taxa with populations that have been seriously depleted and whose ultimate security is not yet assured; and taxa with populations that are still abundant but are under threat from serious adverse factors througout their range. | |
(R) | Rare |
Taxa with small world populations that are not at present endangered or vulnerable but are at risk. | |
These taxa are usually localized within restricted geographical areas or habitats or are thinly scattered over a more extensive range. | |
Note: | The Endangered and Vulnerable categories may include, temporarily, taxa whose populations are beginning to recover as a result of remedial action, but whose recovery is insufficient to justify their transfer to another category. |
Species
Acacia aphylla Maslin (E)
Acacia peuce F. Muell. (V)
Achyranthes mangarevica Suesseng. (Ex/E)
Ailanthus fordii Nooteboom (R)
Arbutus canariensis Veillard ex Duhamel (V)
Badua crassa A.DC. (E)
Betula uber (Ashe) Fernald (E)
Camellia crapnelliana Tutcher (E)
Camellia granthamiana
Casuarina fibrosa C.A. Gardner (E)
Ceratonia sp. nov. (E)
Cladrastis lutea (Michaux f.) C. Koch (V)
Cordyline kaspar W.R.B. Oliver (R)
Cupressus dupreziana A. Camus (E)
Cupressus macrocarpa Hartweg (E)
Dendrosicyos socotranus Balf.F. (V)
Diospyros hemiteles 3 B.K. Richardson
Dirachma socotrana Schweinf. (E)
Dorstenia gigas Schweinf.
Dracaena draco (L.) L. (V in wild)
Dracaena ombet Kotschy & Peyr. (V/E)
Drypetes caustica (Frapp. ex Cordem.) Airy Shaw (E)
Elliottia racemosa Muhlenberg ex Elliott (E)
Eucalyptus argophloia Blakely (E. in wild)
Eucalyptus carnabyi Blakely & Steedman (E)
Eucalyptus crenulata Blakely & Beuzev (E)
Eucalyptus curtisii Blakely & C.T. White (V)
Eucalyptus froggatti Blakely (E)
Eucalyptus rhodantha Blakely & Steedman (E)
Eucalyptus steedmanii C.A. Gardner (Ex in wild)
Euphorbia wakefieldii N.E. Brown (E)
Franklinia alatamaha Marshall (Ex in wild)
Freziera forerorum A. Gentry, ined. (in press) (E)
Gigasiphomnacrosiphon (Harms) Brenan (R/E)
Heritiera longipetiolata Kanehira (E)
Hibiscadelphus giffardianus Rock (E)
Hibiscadelphus wilderianus Rock (Ex)
Idiospermum australiense (Diels) S.T. Blake (V)
Juniperus bermudiana L. (V)
Lebronnecia kokioides Fosberg (R)
Medusagyne oppositifolia Baker (E)
Neowawraea phyllanthoides Rock (E)
Olea laperrinei Battand. & Trabut (V)
Persea theobromifolia A. Gentry (E)
Pittosporum dallii Cheeseman (E)
Prunus gravesii Small (E)
Punica protopunica Balf. f. (E)
Salix silicicola Raup (R)
Santalum fernandezianum F. Phil. (Ex)
Serianthes nelsonii Merr. (E)
Sophora fernandeziana (Phil.) Skottsb. (V)
Sophora masafuerana (Phil.) Skottsb. (E)
Sophora toromiro (Phil.) Skottsb. (Ex in wild)
Tetrataxis salicifolia (Thouars ex Tul.) Baker (E)
Trochetia erythroxylon (G. Forster) Benth. (E)
Ulmus wallichiana Planchon (E)
Vateria seychellarum Dyer (E)
Vepris glandulosa (Hoyle & Leakey) Kokwaro (E)
Zanthoxylum paniculatum Balf. f. (E)
7.3 ENDANGERED SPECIES, VARIOUS REFERENCES
7.3a Eucalyptus species of highly restricted occurrence and endangered or potentially endangered 1
Eucalyptus acies
E. alpina
E. approximans spp. approximans
E. aquilina
E. archeri
E. argophloia
E. badjensis
E. baeuerlenii
E. bakeri
E. barberi
E. beardiana **
E. benthamii
E. brockwayi
E. burdettiana
E. burgessiana
E. caesia
E. calcicola
E. camfieldii
E. cneorifolia
E. conglomerata
E. cordata
E. coronata
E. crenulata
E. cupularis*
E. curtisii
E. dendromorpha
E. desmondensis
E. ficifolia
E. fitzgeraldii*
E. froggattii
E. georgei**
E. gregsoniana
E. halophila**
E. imlayensis**
E. insularis
E. johnsoniana**
E. kartzoffiana
E. kitsoniana
E. kruseana
E. lane-poolei
E. lansdowneana spp. lansdowneana*
E. largeana
E. luehmanniana
E. megacornuta
E. michaeliana
E. mitchelliana
E. morrisbyi
E. neglecta
E. nigra*
E. olsenii
E. paliformis
E. parvifolia
E. pendens
E. pulverulenta
E. pumila
E. remota
E. rhodantha
E. risdonii
E. rummeryi
E. saxatilis
E. scoparia
E. sepulcralis
E. squamosa
E. steedmanii
E. stenostoma
E. stogtei
E. stowardii*
E. sturgissiana
E. tetrapleura
E. triflora
E. woodwardii
E. xanthonema*
E. yarraensis
* Distribution not adequately known and in Eucalyptus nigra taxonomic boundaries are not clear.
** Species newly described and the distribution not adequately known.
7.3b Species listed in Plant Conservation Bulletin (IUCN) 1
Acacia tortilis
Albizia arunachalensis
A. gamblei
Betula utilis
Beilschmiedia pseudomicropora
Cupressus sempervirens
Dipthysa robinoides
Inocarpus edulis
Juniperus macropoda
J. phoenica
Lecythis ampla
Myroxylon balsamuem
Pericopsis elata
Pinus halepensis
P. strobus var. chiapensis
Pistacia atlantica
Platanus wrightii
Salix goodingii
Stipa tenacissima
Symplocos latiflora
S. oligandra
S. sessilis
S. coynadense
Trochetiopsis spp.
1 Plant Conservation Bulletin 2 (1982) pp. 1–9
7.3c Indian Species in Danger of Extinction or Depletion 2
Albizia arunachalensis
A. gamblei
Beilschmiedia pseudomicropora
Diospyros cacharensis
Dysoxyhun reticulatum
Gaultheria seshagiriana
Gymnocladus assamicus
Lithocarpus kamengensis
Luculia grandifolia
Mitrephora harae
Pinus bhutanica
Populus gamblei
Radermachera sinica
Rhododendron dalhousiae
R. tawangensis
Salix bhutanensis
Symaplocos glauca
Syzygium assamicum
2 Indian Forester 107 (11) - 1981, pp. 712–724
7.3d Threatened Plants Committee, IUCN Species Survival Commission 3
Abies guatemalensis
A. nebrodensis
Araucaria araucana
Basiloxylon excelsum
Batocarpus costaricensis
Caryocar costaricense
Celtis aetnensis
Cynometra hemitomophylla
Engelhardtia pterocarpa
Fitzroya cupressoides
Guaiacum sanctum
Guarea longipetiola
Pilgerodendron uviferum
Podocarpus costalis
Podocarpus parlatorei
Quercus copeyensis
Swietenia humilis
Tachigalia versicolor
Vantanea barbourii
7.3e Rare and Endangered Tree Species in Mexico 1
Abies concolor (Cord et Glend) Hopes.
Abies guatemalensis Rehder
Bursera aloexylon Gray
Carpinus caroliniana Walt.
Cedrela odorata L.
Ceiba pentandra (L) Gaerth.
Cercis canadensis Linn
Chirantodendron pentadactylon Larreat
Cordia alliodora (Ruiz et Pav) Cham.
Cordia eleagnoides D.C.
Cornus disciflora D.C.
Cupressus benthami Endl.
Cupressus forbesii Jepson
Cupressus guadalupensis S. Wats
Fagus mexicana Martínez
Juniperus californica Carr.
Juníperus deppeana var. pachyphlaea (Torr.) Martínez
Juniperus standleyi Steyermark
Libocedrus decurrens Torr.
Olneya tesota Gray
Ostrya virginiana C. Koch,
Picea chihuahuana Martínez
Picea mexicana Martínez
Pinus attenuata Lemm
Pinus contorta var. latifolia Engelm
Pinus coulteri Don
Pinus culminicola Andressen et Beaman
Pinus jeffreyi Murr
Pinus maximartinezii Rzedowski
Pinus monophylla Torr.
Pinus muricata D.Don
Pinus radiata var. binata Don
Pinus rzedowski Madrigal et Caballero
Pinus strobus var. chiapensis Mart.
Podocarpus matudae
Podocarpus reikei
Pseudotsuga (various species)
Swietenia macrophylla King
Swietenia humilis Zucc
Taxus globosa Schlecht
Tilia mexicana Schlecht
1 Tables provided by F. Patiño V., Mexico
7.3f Notes on East African Species Considered Endangered or Vulnerable 1
1. Cordia milleni (Boraginaceae)
A forest tree with spreading crown. Timber is popular for furniture and cabinet making. It occurs in Uganda, Burundi, Congo and Western Kenya. In Uganda and Kenya it is the target of heavy felling. Its natural regeneration is poor.
2. Caesalpinia dalei (Caesalpiniaceae)
A spreading buttressed tree. This species has only been recorded in Kwale district Kenya, from an area now intensively cultivated. Feared extinct.
3. Gigasiphon macrosiphon (Caesalpiniaceae)
A tree 6–20 m high with large beautiful flowers with potential for ornamental planting. Occurs in very few localities, on Mrima Hill, Southern Coast, Kenya, and in Southern province in Tanzania.
4. Stuhlmannia moavi (Caesalpiniceae)
A tree of moderate size - 9 m. So far recorded from Pangani district in Tanzania (Muwanja, Mkororro and Wachanga).
5. Brachylaena hutchinsii (Muhugu) (Compositae)
A tall dioecious tree, resistant to termites and borers which in the past was used for sleepers, flooring blocks, but is now used extensively for wood carvings. The species occurs in localized areas in East Africa. In Kenya it occurs in the highlands and in the coastal belt; in Tanzania - Usambara steppe, and in the coast lowlands; while it is rare in Uganda, occurring in South Busoga. In Kenya much of the B. hutchinsii habitat has gone to settlement while the remaining trees are now facing increasingly heavy felling. Logs are highly priced for wood carvings.
6. Lovoa swynnertonii (Kilimanjaro mahogany) (Meliaceae)
A forest tree with first class quality timber. In Kenya occurring in Meru forest, East of Mt. Kenya, and in the forest on Mrima hill at the coast. In Uganda it occurs in Mengo, Ankole and Toro; while in Tanzania it occurs in Rau Forest Reserve (Kilimanjaro) and Kaigi (Bukoba). It is sparsely distributed within its range with uncertain natural regeneration potential.
7. Chlorophora excelsa (Mvule) (Moraceae)
A large deciduous tree occurring in forests and savannas, it enjoys great importance in the timber trade. In the region, mvule occurs around Lake Victoria and in hills of coastal district. (Also occurs elsewhere in tropical Africa). Today mvule has been exterminated in most of the coastal forests in Kenya. The number of trees in western Kenya has been considerably reduced. Here the trees are outside the forest reserve. Cutting has been uncontrolled and exploitation is very heavy. The situation has worsened following expansion in intensive agriculture and land consolidation. Natural regeneration is poor and artificial regeneration handicapped by gall fly damage. The same fate is facing the mvule stands in Busoga district of Uganda.
8. Tecleopsis glandulosa - Vepris glandulosa (Rutaceae)
A medium sized forest tree originally reported from central Kenya, growing in association with cape chestnut and Olea hochsterii. It was feared in the sixties that this species had completely disappeared from Kiambu forest but repeated searches in the seventies revealed that there were still less than forty individuals in the Muguga forest reserve.
Regeneration of T. glandulosa is poor and prospects for its artificial regeneration are uncertain. This is the only record of T. glandulosa in East Africa. The species also occurs in Ethiopia, C. Africa, Mozambique and South Africa.
9. Entandrophragma angolense (Budongo Mahogany) (Meliaceae)
A very large deciduous tree with first class timber, considered to be the best cabinet wood of the East African Meliaceae. E. angolense also occur in Angola. The timber is exported widely. Experience in East Africa shows that this species is the target of heavy exploitation. It regeneration is poor.
10. Populus ilicifolia (Salicaceae)
Tall deciduous riparian tree in Kenya restricted to Tana, Athi and Uaso Nyiro river basins. In Tanzania it occurs in Ruvu river systems.
It is feared that the development of storage dams along the Tana and Athi river basins and the irrigation network radiating from Uaso nyiro may alter dry weather flow over substantial lengths of the water course and hence affect the P. ilicifolia forests. Unless the forests are given legal protection, the entire vegetation is bound to be progressively cleared by the new settlers.
1 Information provided by J.A. Odera, kenya.