Review of Gene Movement by Bats and Birds and Its Potential Significance for Eucalypt Plantation Forestry
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44 Gene movement by bats and birds Review of gene movement by bats and birds and its potential significance for eucalypt plantation forestry S.G. Southerton1,2, P. Birt3, J. Porter4 and H.A. Ford5 1CSIRO Division of Forestry and Forest Products, PO Box E4008, Kingston ACT 2600, Australia 2Email: [email protected] 3PO Box 108, Bellbowrie, Queensland 4070, Australia 43 Bougainvillea Ave, Indooroopilly, Queensland 4068, Australia 5Zoology, University of New England, Armidale, NSW 2351, Australia Revised manuscript received 30 May 2003 Summary Pollen-carrying vectors are the principal agents of gene movement in eucalypt forests. Eucalypt flowers produce abundant nectar Pollen- and/or nectar-feeding lorikeets and bats and nectar-feeding and pollen and hence attract numerous visitors, especially insects honeyeaters, while less frequent visitors to eucalypt flowers than and birds. Insects vastly outnumber all other floral visitors and insects, may make a unique contribution to eucalypt population undoubtedly play a major role in pollen movement (House 1997). structure because of their capacity to move pollen large distances. While birds and bats are less frequently recorded visitors to Birds and bats may travel upwards of 50 km day–1 during feeding, eucalypt flowers than insects, some species are dependent on and further during migration or feeding bouts over several days. flowers for food. These have the capacity to transport pollen over Limited data suggest that they carry viable pollen. Several much greater distances than insects. In this paper we examine the eucalypts have adaptations favouring bird pollinators, while some foraging behaviour, and feeding and migratory movements, of species, particularly Corymbia spp., have adaptations commonly birds and bats that feed on eucalypt flowers. We investigate their found among plants pollinated by bats and other nocturnal visitors. capacity to move pollen in native eucalypt forests and consider Bats may have the capacity to carry viable pollen over greater the effect of this movement on the genetic diversity of native distances than birds. We suggest that the effect of pollen transfer forests and its significance for native forests in the new plantation by birds and bats on the genetic structure of widespread eucalypt environment. species is potentially greatest in fragmented forests where these animals can traverse gaps of several kilometres between Eucalypts are preferential outcrossers discontinuous stands. Greater understanding of pollen movement by birds and bats in natural eucalypt forest is a prerequisite to The breeding system of eucalypts has been reviewed previously understanding the potential for gene movement from commercial by Pryor (1976), Moran and Bell (1983), Eldridge et al. (1993), eucalypt plantations into native forests. and Potts and Wiltshire (1997). Eucalypts preferentially outcross but are capable of self-fertilisation, although subsequent seed set Keywords: forest ecology; geographical distribution; geographical dispersal; gene flow; nectar; pollen; pollinators; pollination; animal is usually severely reduced compared with that resulting from behaviour; feeding behaviour; forest management; birds; Chiroptera; outcrossing (Eldridge et al. 1993; Potts and Wiltshire 1997). Pteropodidae; eucalypts Progeny derived from selfing frequently suffer from severe inbreeding depression (James and Kennington 1993; Hardner and Introduction Potts 1995) and would not be expected to contribute to future generations, as the outcrossed progeny will be favoured by natural At the current rate of establishment, eucalypt plantations will soon selection (Skabo et al. 1998). Natural eucalypt populations occupy a larger proportion of the total Australian plantation estate frequently exhibit high outcrossing rates, with mature trees than softwoods (National Plantation Inventory 2000). This trend showing higher than expected levels of heterozygosity (Moran promises to reduce the overall environmental effect of commercial and Bell 1983; Potts and Wiltshire 1997). forestry in Australia by shifting many harvesting operations from Other factors which may facilitate outcrossing in eucalypts include native forests to highly productive plantations. However, there delayed receptivity of the stigma until several days after pollen are ecological issues that arise when plantations contain non-local shed (protandry), bending away of anthers from the style (Potts provenances or planting stock with reduced genetic diversity — and Wiltshire 1997), stylar extension (Moncur and Boland 1989) such as seedlings from breeding programs or selected clones. The and prolonged pollen viability (Griffin 1989). Higher rates of plantation revolution in Australian eucalypt forestry has drawn outcrossing have been associated with mass-flowering species attention to the potential for gene movement from plantation (James and Kennington 1993) and higher numbers and densities species to related interfertile species in adjacent forests (Wardell- of flowering trees (Sampson et al. 1995). Delayed production of Johnson et al. 1997). The prospect of clonal eucalypt plantations nectar in Eucalyptus melliodora until after the stigma becomes and transgenic eucalypts will focus increased attention on gene receptive may also favour outcrossing (Moncur and Boland 1989). movement in eucalypt plantations. Australian Forestry 2004 Vol. 67, No. 1 pp. 44–53 45 Seed and pollen dispersal in natural eucalypt forests has evolved to maximise the likelihood of gene flow between populations. Eucalypt seed is generally dispersed by wind, with the distance travelled being related to tree height, wind velocity and seed weight Birds may be more important cross-pollinators of eucalypts if (Cremer 1977). Several Corymbia and a small number of insect visitation is suppressed by cool conditions in the early Eucalyptus species have true seed wings suitable for wind dispersal morning or by flowering in winter (Hopper 1981). Eucalyptus (Boland et al. 1980). Dispersal in animal droppings does not occur, globulus flowers during the often cold, wet and windy spring although many birds eat eucalypt seed, because the seed does not weather in Tasmania — conditions that reduce insect activity survive passage through the alimentary canal of mammals and (Hingston and Potts 1998). Additionally, of the numerous insects birds (Joseph 1986). Inadvertent dispersal of Corymbia torelliana that visit the flowers, few make contact with the stigma of the seed attached to the sticky bodies of native bees has been reported large E. globulus flower. over distances of up to 300 m (Wallace and Trueman 1995). The Many eucalypts have small, white and open, cup-shaped flowers capacity for long-distance dispersal of seed or fruits by birds, that may produce modest amounts of nectar (Paton and Ford 1977) floods (e.g. E. camaldulensis), storms, or in fire updraughts was and their attractiveness to birds may vary. For instance, New recognised by Kirkpatrick (1977). Parrots are rather messy eaters England stringybark (E. caliginosa) flowers regularly and is a and could disperse seed from eucalypt fruits over distances of major nectar source for honeyeaters in some years, but appears to several hundred metres as they fly from feeding sites. be ignored in others (H.A. Ford pers. obs.). This means that short- Pollen is likely to be the major vehicle of gene movement in term studies may underestimate the visitation rate by birds. Other eucalypts. Virtually all eucalypts produce sticky pollen, a eucalypts produce copious nectar and are particularly popular with characteristic that is believed to prevent wind from being an birds (E. cosmophylla, E. leucoxylon, E. sideroxylon: Paton and effective agent of dispersal (Eldridge et al. 1993). There is, Ford 1977; Paton 1982a; Franklin et al. 1989; Oliver 2000). however, likely to be some movement of pollen during high winds The flowers of some eucalypts possess several characteristics over unknown distances. Two red gums, E. tereticornis and found to be common amongst ‘bat-pollinated’ plants (Faegri and E. blakelyi, are the only species (Pryor 1976) known to produce van der Pjil 1971; McCoy 1990; P. Birt unpubl. data). Several dry pollen, but the importance of wind pollination with these species produce larger volumes of nectar at night and display species is not known. An important barrier to gene flow via pollen anthesis predominantly at night, suggesting they are capable of is asynchronous flowering of trees of the same species or related attracting nocturnal pollinators (McCoy 1990; P. Birt unpubl. species capable of hybridisation. data). Many Corymbia and some Eucalyptus species develop large Pollen viability under field conditions is poorly understood in terminal clumps of white flowers, which may facilitate detection eucalypts. Isolated reports suggest viability is retained for at least at night by bats. Similar floral features have been observed in several days (Griffin 1989). If this characteristic is widespread in other ‘bat-pollinated’ plants (Woodside and Pyke 1995; Vieira the Eucalyptus and Corymbia genera, pollinator movements over and Decarvalhookano 1996; Slauson 2000). several days or during nomadic or migratory movements may be significant. Pollen transfer between vectors visiting flowers, during Pollen- and nectar-feeding parrots allopreening in the case of birds or between bees in the hive, may increase the effective distance of pollen movement. There are seven lorikeet species in two genera (Trichoglossus and Glossopsitta)