The Extinction of Endemic Species by a Program of Biological Control!

The Extinction of Endemic Species by a Program of Biological Control!

Pacific Science (1984), vol. 38, no. 2 © 1984 by the University of Hawaii Press. All rights reserved The Extinction of Endemic Species by a Program of Biological Control! BRYA N CLARKE,2 JAM ES MURRAY,3 AND MICHAEL S. JOHNSON4 ABSTRACT: Land snails ofthe genus Partula, inhabiting the high islands ofthe Pacific Ocean, have provided exceptional opportunities for studies oil the origin and differentiation ofspecies: The endemic taxa ofMoorea, in French Polynesia, have been particularly well studied. In an attempt to control the numbers of the giant African snail, Achatina fulica, which is an agricultural pest, a carnivorous snail, Euglandina rosea; has been introduced into Moorea. It is spreading across the island at the rate ofabout 1.2 km per year, eliminating the endemic Partula. One species is aiready extinct in the wild; and extrapolating the rate ofspread ofEzigltmdina , it is expected that all the remaining taxa (possibly excepting P. exigua) will be eliminated by 1986-1987. Euglandina has been introduced into many other oceanic.islands, and it appears that more than a hundred endemic species are at risk . These observa­ tions point to a serious danger in programs of " biological control." SINCE THE TIM E OF DARWiN, the endemic Polynesia, by an introduced molluscan pre­ species of oceanic islands have held a special dator (Euglandina rosea (Ferussacj), interest for students of evolution. The cla ssic studies ofCrampton (1932) and Archipelagos of volcanic origin, such as the later investigations (Murray and Clarke 1980, Galapagos and H awaiian islands, are natural Murray, Johnson , and Clarke 1982) have laboratories in which the phenomena ofspeci­ shown that these snails provide exceptional ation can be studied (Lack 1947, Carson and opportunities for study of the origin and dif­ Y60n 1982). The fauna and flora of such is­ ferentiation of species. Their unique combi­ lands are, however, unusually susceptible to nation of ovoviviparity, low mobility, short the introduction of competitors, parasites, generation tim e, ease of cu lture in the labo­ and predators. ratory, and extensive genetic po lymorphism In thi s paper we report the progressive ex­ (at both the morphological and molecular tinction of land sna ils (genus Partulai , en­ levels) make th em almost idea l mat erial for demic to the island of Moorea in French the study of ecological and evolutionary genetics. Their loss is not merely a tragedy for stu ­ dents ofgenetics, it is also a wattling about the I Manu script accepted 10 January 1984. potentially devastating effects of some pro­ 2 Museum National d'Histoire Nat urelle et Ecole gra ms in " biological control"; and it exem­ Pratique des Hautes Etudes en Polynesie Francaise, plifies a threat to more than a hundred other Centre de l'Environnernent de Moorea, B.P. 12, Moo rea, species. Because the Partula of Moorea ha ve French Polynesia. Permanent address: University of Nottingham, Department of Genetics, University Park , been mapped in great detail, we ar e able to Nottingham NG 7 2RD , England. document rather precisely the progress of 3 Museum National d'Histoire Naturelle et Ecole extinction. Pratique des Hautes Etudes en Polynesie Francaise, Centre de l'Environnement de Moorea, B.P. 12, Moorea, French Polynesia. Permanent address: University of Virginia, Department of Biology,Charlottesville, Virginia 22901. 4 University of Western Australia, Department of Zoology, Nedlands, Western Australia 6009. 98 PACIFIC SCIENCE, Volume 38, April 1984 FIGURE I. The island of Moorea, showing the principal topographical features. Pacific Ocean. The island is volcanic in origin, and P. mirabilis Crampton). Their status as and its age is approximately 1.2 million years good biological species is, however, in ques­ (Jackson 1976). It is about 12km in diameter, tion because each, at some point on the island, and its highest peak rises to 1207 m. Nine gives evidence of hybridization or intergra­ other peaks exceed 700m (Figure 1). dation with another. For example, P. tohiveana Crampton (1932) and Crampton and tohiveana and P. suturalis are the sympatric Cooke (1953) described eleven species of terminal elements of a ring-species including Partula, all endemic to the island. Two of P. tohiveana olympia. The pattern is such that, these (Partula solitaria Crampton and Partula potentially at least, genes could flow from any diaphana Crampton and Cooke) have since one "species" to any other (with the possible been relegated to the genus Samoana (Kondo exception of P. mooreana). Nonetheless, at 1973). Of the remaining nine, one (P. den- any particular place as many as four of the droica Crampton) is clearly a geographical taxa may coexist without interbreeding. race of P. suturalis Pfeiffer and another (P. When they do so, they are clearly distinct in olympia Crampton) a geographical race of P. genetics, morphology, ecology, and behavior tohiveana Crampton (Clarke and Murray (Johnson, Clarke, and Murray 1977, Murray 1969,Murray and Clarke I980).-The number .. and ~Clarke ~1980, MurraY,Johnson, _and of Partula "species" is thus reduced to seven Clarke 1982). (P. taeniata Morch, P. exigua Crampton, P. The geographical ranges of the taxa prior to suturalis Pfeiffer, P. tohiveana Crampton, P. the introduction of Euglandina are shown in aurantia Crampton, P. mooreana Hartman, Figure 2 (pages 99 and 100). II i ...:Z Extinction of Endemic Species-CLARKE, MURRAY, AND JOHNSON 99 FIGURE 2. The ranges of the different species of Partu/a on Moorea prior to the introduction of Eug/andina rosea : (A) Partu/a taeniata (N = P. taeniata nuc/eo/a, Sp = P. t. spadicea, St = P. t. strio/ata, Si = P. t. simu/ans , E = P. t. e/ongata); (B) Partu/a ex igua (E) and P. mirabi/is (M); (C) Partu/a suturalis (V = P . suturalis vexi//um , S = P. s. strigosa, D = P. s. dendroica); (D) Partu/a mooreana (M), P. tohiveana (0), and P. aurantia (A). Extinction of Endemic Species- CLARKE, M URRAY, AND JOHNSON 101 THE INTRODUCTION OF Achatina AND TH E EFFECT OF Euglandina ON Achatina Euglandina The decline in the numbers of A chatina The giant African snail, Achatina fulica fulica on Moorea since 1978:-1979 cannot Bowdich, is well known as an agricultural pest rigorously be ascribed to the effects of (Mead 1961, 1979). It was introduced into Euglandina rosea. Living Achatina are still to Tahiti (by someone who wished to breed it for be found in the territories occupied by Eug­ food) in 1967 and spread rapidly to the other landina, and the decline in the number ofAcha­ islands in the archipelago. Its numbers in­ tina has been ob served in parts of the island creased in Moorea to such an extent that the not yet reached by the carnivore, for example snails invaded human dwellings, and on one Aareo Valley and Vaihiiaiia Valley. Further­ occasion two wheelbarrow-loads of snails more, a similar decline has occurred on the were taken from the walls of a single house (R. island of Huahine, to which E. rosea ha s not Brosious, pers. comm.). Because Achatina, yet been introduced (Pointier and Blanc 1982). unlike Partula , eats living plants, it caused great damage to crops and gardens. The num­ bers ofA .fulica apparently reached a peak on THE EF FECT OF Euglandina ON Partula Moorea in 1978, and thereafter declined. The cause of this decline is unknown (see below), Although the role of Euglandina in control­ but the very large numbers of empty un­ ling Achatina is doubtful, there is unfortu- broken shells found all over the island suggest .nately no doubt at all about its effects on an epidemic disease (or perhap s predation by Partula . It consume s them with great effi­ land planarian s; see Mead 1979: 70). Living ciency. Four individuals of P. taeniata were Achatina are still common on Moorea, and put in a plastic lunch-box with a single E. still cause damage to crops, but the scale of rosea. Within 24 hours they had all been the problem has greatly diminished . eaten, leaving four empty shells. Euglandina .rosea was introduced into During our field studies in 1982·we were Tahiti and Moorea in an attempt at the unable, with one exception discussed below , " biological control" of Achatina fulica. to find any Partula in the territories now oc­ Euglandina rosea, which is native to Florida cupied by Euglandina rosea. Our 1982 surveys and centralAmerica, is a carnivorous mollusc specifically included localities (in Paparoa, that preys upon other land snails. Although it Mouaputa, Faamaariri, and Puutu Valleys) certainly eat s Achatina, there is, as far as we that had yielded large samples of Partula in know, little evidence that it is an effective 1967 and 1980. Four species (P. aurantia, P. agent ofcontrol (Mead 1979). Nevertheless, it suturalis, P. tohiveana, and P. taeniata ) seem has been widely recommended for this pur­ to have been entirely eliminated from the pose by departments ofagri culture in various northeast ofthe island . Partula aurantia, which countries. It is still so recommended by the was restricted to this area (see Figure 2), must South Pacific Commission. now be considered extinct in the wild state Euglandina rosea was introduced into (the only living examples being tho se kept Moorea, with the approval of the Service de alive by James Murray in the laboratory). The L'Economie Rurale and the Division de subspecies P. taeniata striolata is also, we be­ Recherche Agronomique, at the orange plan­ lieve, extinct. tation of M. Nardi in Paopao on 16 March Th e single exception is Partula exigua. Thi s 1977 (J. L. Reboul, pers. comm.). It spread taxon is restricted to the northeast (see Figure into the adjoining for ests, and by 1980 its 2), although it is closely related to P.

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