There are probably more illegal ivory items for sale in Egypt than anywhere else in Africa. The author visited the main tourist centres of Cairo, Luxor and Aswan in late 1998 and counted over 21,000 ivory items for sale. Most of the ivory has come from elephants hunted illegally in Central and West Africa. Traders still transport the raw tusks, by truck and on camels, through Sudan across the desert into Egypt. Since the 1990 CITES ban on the international commercial ivory trade, Egypt, a member state, has prohibited not only the import and export of ivory but domestic trade as well. Ivory sales continue openly, however, in the markets and hotels, and new ivory items are still being made. The main buyers are from France, Italy, Spain and Latin America. The Egyptian Government must enforce its legislation against this ivory trade to reduce the serious elephant poaching in the Central African Republic, the Democratic Republic of Congo and Sudan.

The history of the endemic rodents of the Galápagos Islands began with the discovery of the first Galápagos rice rat species by Charles Darwin in 1835 and the last species was described as recently as 1980. Unfortunately, of the seven described species known to occur in the islands during the past 150 years, only two were known to be extant to 1995. Since then, two expeditions to the Galápagos Islands have been conducted to survey endemic rodent populations. The first confirmed the existence of a small endemic rice rat, Nesoryzomys fernandinae, on Fernandina, known previously only from owl pellet remains found in 1979. In 1997, an expedition to Santiago revealed a population of the larger rice rat N. swarthi, a species collected alive only once in 1906 and considered extinct in all recent literature on the Galápagos Islands. Survey efforts on Santa Cruz resulted only in the collection of introduced rodent species (Rattus rattus, R. norvegicus and Mus musculus). The extant species of native rodents in the Galápagos Islands now number four: N. narboroughi and N. fernandinae on Fernandina; N. swarthi on Santiago; and Oryzomys bauri on Santa Fe. Three species are found on islands where no introduced rodents or cats occur, whereas only one (N. swarthi) co-exists with R. rattusand M. musculus. Nesoryzomys darwini and N. indefessus on Santa Cruz and O. galapagoensis on San Cristóbal are still considered extinct. Strategies for conservation should include monitoring islands for introduced rodents and cats, development of emergency plans in the event of introductions, and captive management.

The Dominican Republic faces multiple threats to biodiversity. A list of native species of amphibians and reptiles (excluding sea turtles) is presented. Some may have become extinct recently, substantial populations of others have been extirpated, some have greatly reduced numbers, and others appear to be rare or have restricted ranges. Most of the 13 taxa listed are relatively large, vulnerable to human exploitation or introduced predators, and/or have limited distributions and specific habitat requirements. To be listed, evidence must exist that: (1) populations are dwindling, (2) the range is shrinking, or (3) a species must be vulnerable to exploitation and historically rare. Two iguanas (Cyclura cornuta, C. ricordii), two turtles (Trachemys decorata, T. stejnegeri vicina), and one crocodilian (Crocodylus acutus) have been exploited extensively and have long been recognized as threatened or endangered. The ranges of Cyclura ricordii and T. decorata are very localized and the previously widespread ranges of the others have shrunk or become fragmented. A toad (Bufo fluviaticus), a large galliwasp (Celestus anelpistus), and a snake (Alsophis melanichnus) have not been collected recently. Only a few specimens of another galliwasp (C. carraui) and a dwarf gecko (Sphaerodactylus cochranae) have been taken recently. In addition, extensive portions of the habitats of these species have been severely altered. Three other snakes (Alsophis anomalus, laltris agyrtes, I. dorsalis) are rare and may never have been common. Their size and habits render them vulnerable to predation by the introduced mongoose and to decimation by humans who fear and dislike them.

Przewalski's gazelle Procapra przewalskii is endemic to China and is classified as Critically Endangered by IUCN—The World Conservation Union. Historically, the species occurred in parts of the provinces of Gansu, Inner Mongolia, Ningxia and Qinghai but now appears to be restricted to three populations around Qinghai Lake. These three populations— Bird Island, Hudong–Ketu and Yuanzhe—have all declined since 1988. The populations have been monitored since 1994 and the smallest, on Bird Island, appears to be on the brink of extinction, with only seven individuals being recorded in 1998. In the same year, the Hudong–Ketu population comprised 56 individuals (29.4 per cent males, 50 per cent females and 21 per cent juveniles) and the Yuanzhe population 51 individuals (29.4 per cent males, 43.1 per cent females and 27.5 per cent juveniles). The causes of the declines vary for each population but include loss of habitat as a result of desertification, poaching and, possibly, wolf predation. Human activity and high juvenile mortality are major threats to the continued survival of the gazelle. Conservation measures proposed are: (i) the establishment of a special reserve for Przewalski's gazelle; (ii) a study of the wolf-gazelle relationship and control of the number of wolves if necessary; (iii) a search for remnant populations of Przewalski's gazelle in other regions in their historical range and the identification of suitable sites for translocation and establishment of new populations.

The forests of the Kilum-Ijim area, around Mount Oku in West Cameroon, are the largest remaining patch of montane forest in West Africa, and the highest in altitude. This important habitat harbours endemic species of both animals and plants but is surrounded by a high density of human settlements: c. 300,000 people live within a day's walk of the forest, which covers only 200 sq km. BirdLife International and the Ministry of the Environment and Forestry, Government of Cameroon, are currently operating the Kilum-Ijim Forest Project, with the overall goal of conserving representative areas of the Cameroon montane forest biome in the long-term. The purpose of the project is toensure that the biodiversity, extent and ecological processes of the Kilum-Ijim Forest are maintained and that the forest is used sustainably by the local communities. The existence of a small Sphagnum community and associated wetland plant species was discovered in 1997 on the summit of Mount Oku, at 2900 m. This site is of extremely high conservation importance because several plant species endemic to the Kilum-Ijim area have been recorded there. In addition, it is the highest Sphagnum bog and the source of the highest stream in West Africa.

A spring (1999) census was conducted of great bustards Otis tarda in north-western Morocco, where a poorly known population of this species occurs. Sixty-four birds were seen in four distinct areas. Adult males were seen displaying at three of these areas, indicating that they are probably traditional lek sites. No adult males were observed in the fourth area and its status as a lek site is uncertain. Two further sites were visited but no birds were seen. Two lst-year males were seen with their mothers, demonstrating successful breeding in 1998. We argue that the small number of birds, a population sex ratio of 1:3.3 in favour of females, evidence for a range contraction, and probable isolation from other great bustard populations mean that this population is now extremely endangered and will decline to extinction unless conservation measures are implemented immediately.