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EMU Vol. 91, 164-171, 1991 O Royal Australasian Ornithologists Union 1991 0158-4197/91/03164 + 7 $2.00 Received 25-6-1990, accepted 9-11-1990 Anti-predator Behaviour in the Bell Miner Manorina melanophrys Aldo Poiani Department of Zoology, La Trobe University, Bundoora, Vic. 3083 Summary: Data on anti-predator and anti-competitor behaviour in the Bell Miner Manorina rnelanophrys were collected opportunistically during two breeding seasons at Healesville, south-eastem Victoria, and show that: (a) nest predators were mobbed by more Bell Miners than were competitors; (b) in general, nest predators were mobbed by more birds within a dense than within a less dense colony; (c) this difference in the mobbing response between colonies does not appear to lead to an increase in reproductive success in dense colonies; (d) intruders were mobbed by more birds early than late in the season; and (e) potential nest predators were mobbed by slightly more Bell Miners than were competitors when an active nest was close by. Mobbing behaviour in the Bell Miner may decrease the risks to individuals engaged in anti-predator defence and helpers' involvement in mobbing may benefit breeders through the 'dilution' of those risks. Introduction Miner. Swainson (1970) reported that 3-12 birds participated in a distraction display against a human intruder at an active nest. Smith & Robertson (1978) showed that small intruders (presumably potential competitors) are pursued by a single Bell Miner, often beyond the boundaries of its territory, while potential nest predators such as currawongs Strepera spp., Laughing Kookaburras Dace10 novaguineae and ravens Corvus spp. are mobbed by up to 12 birds from more than one breeding unit. Clarke (1984) confirmed observations made by Smith & Robertson (1978) that bird species which forage in the understorey are not attacked, while a Laughing Kookaburra was mobbed by a group of nine Bell Miners from more than one breeding unit. Here I present field observations on mobbing and other anti-predator behaviour and on attacks against potential competitors by the Bell Miner. My aim was to test whether the number of Bell Miners engaged in an attack against any intruder (predator or competitor) varied according to intrinsic and extrinsic factors such as how dangerous was the intruder for the Bell Miners and the period of the breeding season. Anti-predator behaviour in birds can take the form of either attack (Curio 1975) or distraction display (Armstrong 1956) by a single individual, or mobbing by more than one bird of the same or different species (Curio 1978). The pattern of anti-predator behaviour is affected by the kind of predator being mobbed, the season (e.g. breeding vs non-breeding), the period within the season (e.g. early vs late), the spatial distribution of potential mobbers with respect to the predator (e.g. colonial vs non-colonial species), the developmental stage of the nest contents (when attacks or displays are part of the nest defence) among others (Curio et al. 1978; Shalter 1978; Robinson 1985; Zimmermann & Curio 1988). The participants in anti-predator defence may accrue benefits in terms of enhanced present and/or future fitness by evicting a predator from their breeding areas or territories (Curio 1978). However, they are also running risks (of injury or death) which represent the costs of the anti-predator behaviour (Curio & Regelmann 1985; see also Montgomery & Weatherhead 1988). Even though Hennessy (1986) has recently questioned the costs of anti-predator defence, both direct and indirect evidence in its favour are increasing (Curio & Regelmann 1986; Poiani & Yorke 1989; see Sordahl 1990 for a recent review). The Bell Miner Manorina melanophrys is a cooperatively breeding, multi-brooded honeyeater that lives in loose colonies of variable sizes (Smith & Robertson 1978; Clarke 1988). There have been few studies of mobbing and other anti-predator behaviour in the Bell Methods Data were collected opportunistically during a study of a population of Bell Miners in the Sir Colin Mackenzie Zoological Park at Healesville, 60 km east of Melbourne, between November 1988 and April 1990, which covered nearly two breeding seasons (August to April at Healesville). The observations suffer from two major biases. First, a predator's or competitor's intrusion into the Bell Poiani: Bell Miner Anti-predator Behawour 165 Miners' territory may not have been noticed unless the intruder was mobbed or otherwise chased away. The presence of raptors, however, was generally evident to the observer even when they elicited no response from the Bell Miners. Second, the effort to record anti-predator behaviour was spread unevenly through the breeding season. Hence, the data were analysed for two periods, early-mid and late season, instead of month by month. A predator (or competitor) may perceive the intensity of the mobbing response in many ways. For instance, it may be perceived as more intense if many of the potentially available mobbers actually attack the predator. Once the mobbing group has formed, a predator may perceive a further increase in the intensity of mobbing as the mobbers get closer or increase the frequency of swoops, and/or the frequency of alarm calls. In this study I measured the intensity of the mobbing response only by the number of mobbers engaged in the attack. For each occasion on which one or more Bell Miners attacked an intruder (whether a predator or competitor) data were recorded for the following six variables and their effects analysed: (a) period of the breeding season (early-mid or late); (b) density of the colony where the event occurred (dense or sparse); (c) number of Bell Miners involved in the attack; (d) whether the intruder was flying or perched; (e) whether the attack took place within 15 m of an active nest; and (f) identity of the intruder. Unless otherwise specified data were analysed by a two-way Analysis of Variance to examine differences between means. A d(x + 0.5) transformation of data was used to make the variance independent of the mean. Statistical analyses follow Sokal & Rohlf (1981) and Conover (1980), tests are all one-tailed; means standard deviations are given throughout. + Results Table 1 lists the intruding species considered in the present study, classified according to their potential relationship with the Bell Miners, i.e. nest predators, predators of adult birds and competitors. Competitors had feeding habits similar to those of Bell Miners, a high probability of being harassed by Bell Miners (Smith & Robertson 1978; Loyn et al. 1983), and a positive response towards a Bell Miner's abandonment of a former territory (Clarke 1984). Period of the breeding season The breeding season of the Bell Miner at Healesville Table 1 Potential predators and competitors of Bell Miners considered in this study. Species Common name Family (a) POTENTIAL NEST PREDATORS Gymnorhina tibicen Australian Magpie Cracticidae Strepera graculina Pied Currawong Cracticidae Cracticus torquaius Grey Butcherbird Cracticidae Corvus coronoides Australian Raven Cowidae Dace10 novaeguineae Laughing Kookaburra Alcedinidae Varanus varius Lace Monitor Varanidae Antechinus stuartii Stuart's Antechinus Dasyuridae (b) POTENTIAL PREDATORS OF ADULT BIRDS Accipiter cirrhocephalus Collared Sparrowhawk Accipitridae A. fasciatus BrownGoshawk Accipitridae Aquila audax Wedge-tailed Eagle Accipitridae Falco longipennis Australian Hobby Falconidae (c) POTENTIAL COMPETITORS Alisterus scapularis King Parrot Psittacidae Platycercus eximius Eastern Rosella Platycercidae F elegans Crimson Rosella Platycercidae Anthochaera carunculata Red Wattlebird Meliphagidae extended from August to April. The frequency distribution of nests built showed a maximum between November and February, while virtually no nests were built between May and July. The sample sizes for early and mid-season separately were small, so I compared the data for the period August to February with data from the late season (March to April). Data from the 1988-89 and the 1989-90 breeding seasons were pooled in order to increase the sample size. The number of mobbers in the early-mid and late season was compared. Colony density did not have an independent effect on the number of Bell Miners attacking any of the three kinds of intruders considered (Tables 2 & 3), while the time of the breeding season had an independent effect only for Pied Currawongs (P < 0.01, Table 3b), mobbed by more Bell Miners in the early-mid periods of the season. Also a marginally significant interaction between colony density and season is shown for the Pied Currawongs (Table 3b) with the difference between early-mid and late season being greater in the sparse colony than in the dense colony. When all intruders are considered together (Table 3d), time during the breeding season is the only factor statis- EMU Vol. 91, 1991 166 Table 2 The number of Bell Miners mobbing Laughing Kookaburras, Pied Currawongs and competitors at different colony density and at different times of the breeding season. Data shown are mean f s.d. (sample size). Early-mid season Late season (a) LAUGHING KOOKABURRA Table 3 Two-way Analysis of Variance for the effect of time during the breeding season and colony density on the number of Bell Miners mobbing Laughing Kookaburras, Pied Currawongs and psittaciform competitors. Source of variation d.f. M.S. F P (a) LAUGHING KOOKABURRA Sparse colony 1.84f1.14(13) 1.88f1.36 (9) Colony dens~ty 1 0.23 3.38 > 0.05 Dense colony 2.92 f 2.69 (13) 2.00 f 1.80 (9) Stage of the BS1 1 0.14 2.05 > 0.10 0.13 1.91 > 0.10 Two-way interaction colony density x stage of BS (b) PlED CURRAWONG Sparse colony 3.44 f 1.42 (9) 1.66 f 2.08 (3) Dense colony 3.44 f 2.65 (9) 2.33 f 0.57 (3) (c) PSllTAClFORM COMPETITORS Residual (b) PlED CURRAWONG 1 0.00 0.00 > 0.75 1 0.72 12.00 c 0.001"* 2.00 f 1.41 (7) 1.OO f 0.00 (2) Stage of the BS Dense colony 2.14 f2.19 (7) 1.50 f 0.70 (2) Two-way interaction colony density x stage of BS Sparse colony 2.37 f 1.44 (29) Dense colony 2.89 2.52 (29) + 0.068 Colony dens~ty Sparse colony (d) LAUGHING KOOKABURRAS, PlED CURRAWONGS AND PSITTACIFORM COMPETITORS 1 172 Residual 1 92 0.19 3.16 0.10 > P >0.05 0.06 1.71 f 1.38 (14) (c) PSITTACIFORM COMPETITORS 2.00f 1.46 (14) Colony density 1 0.00 0.00 > 0.75 Stage of the BS 1 0.11 1.83 >0.10 1 0.03 0.50 > 0.25 68 0.06 tically significant, indicating that more mobbers participated in anti-predator attacks in the early-mid than in the late season. Effect of colony density Data were recorded within two zones (A and B) of the Park, with zone A occupied by denser colonies than zone B. Nests of different females in zone A were built closer to each other than in zone B (Mann-Whitney Utest T I = 9.11, n = 21, m = 16, P < 0.001, Conover 1980). Females in zone A tended to have more attendants at nests with chicks 2-5 days old than females of zone B (2, = 5.5 f 4.0 v s fB = 3.6 f 1.2 attendantsJnest); Mann-Whitney U-test T I = 1.23, n = 6, m = 6, 0.11 > P > 0.10. Only attendants accumulated during the first two hours of observation were included in order to keep the observation effort constant. None of the attendants considered was included in more than one nest. The number of Bell Miners engaged in each attack against an intruder was compared between zones for the early-mid and late parts of the breeding season. All the effects of colony density and kind of intruder plus the interaction are significant ( P c 0.01, Tables 4a & 5a). This indicates that both predators and competitors were mobbed by more Bell Miners in a dense colony than in Two-way interaction colony density x stage of BS Res~dual d) LAUGHING KOOKABURRAS, PlED CURRAWONGS AND PSITACIFORM COMPETITORS Colony density Stage of the BS Two-way mteraction colony density x stage of BS Residual > 0.10 1 1 0.15 0.80 2.14 11.42 < 0.01" 1 0.00 0.00 > 0.75 340 0.07 a less dense one. In this case all the species included in Table 1 were considered. Nest predators were mobbed by more Bell Miners than were competitors, and competitors were mobbed more intensely when intruding into a sparse colony whereas nest predators were mobbed more intensely in a dense colony. However, the percentage of nests lost by predation was greater in the denser colony than in the less dense one (41.2%, 68 nests laid in vs 30.0%, 60 nests laid in) but this difference is not significant (G test for independence: Gad,= 1.70, P > 0.10). Mobbing vs attack by a single bird The frequencies of mobbing episodes and attacks by a Poiani: Bell Miner Anti-predator Behaviour 167 Table 4 The effect of: (a) colony density; (b) intruder perched or flying; and (c) vicinity of an active nest on the number of Bell Miners mobbing nest predators and competitors. Data shown are mean f s.d. (sample size). Nest predator Table 5 Analysis of Variance for effects of: (a) colony density; (b) intruder perched or flying; and (c) vicinity of active nest on the number of Bell Miners mobbing nest predators and competitors. Source of variation d.f. MS. F P Competitor (a) COLONY DENSITY (a) COLONY DENSITY Dense 3.40 f 3.27 (42) 1.38 It 1.57 (18) Sparse 2.09 f 1.42 (42) 1.55 k 1 .09 (18) (b) INTRUDER PERCHED OR FLYING Colony density 1 0.83 Kmd of intrude 1 3.29 1 0.97 476 0.07 Two-way interaction colony density x kind of intruder Perched 2.23 f 1.37 (21) 2.00 ? 1.58 (9) Residual Flying 1.66 f 1.49 (21) 1.OO ? 0.70 ( 9) (b) INTRUDER PERCHED OR FLYING (c) VICINITY OF ACTIVE NEST Close to nest (2 15 m) 3.88 f 4.37 (18) Farfromnest(>15m) 2.61f2.14(18) 1.46 ? 1.68 (15) 1.66?1.11 (15) single bird were compared for nest predators and competitors using a Binomial test. Nest predators were more frequently mobbed than attacked by a single bird: 55 instances vs 23 instances (P < 0.05) while there was no difference for competitors: 15 vs 14 (P > 0.05). Effect of the intruder's behaviour I compared the number of mobbers engaged in attacks against flying or perching intruders (nest predators or competitors). Intruders were mobbed more intensely when they perched than when they flew through the colony (P < 0.01, Tables 4b & 5b). This trend is not affected by the kind of intruder (nest predators or competitors, interaction: P > 0.05, Table 5b). Effect of the vicinity of an active nest The numbers of mobbers engaged in attacks against intruders more or less than 15 m from an active nest were compared. This was the distance that an avian predator might perch in a tree just above a nest in the understorey. Nest vicinity by itself did not have an effect on the number of mobbers (P > 0.05, Table 4c & 5c). However, an almost significant interaction between the two factors suggests that the difference in the number of Bell Miners mobbing nest predators and competitors was slightly greater when an active nest was close by than when the nest was far away (Table 5c). Kind of potential predator Predators were divided into: (a) predators of adult birds (e.g. raptors); (b) avian predators of nests (e.g. curra- Perched or flying 1 0.84 Kind of intruder 1 0.31 Two-way interaction perched1 flying x kind of intruder 1 0.00 Residual 0.04 236 (c) VICINITY OF ACTIVE NEST Vicinity 1 0.00 Kind of intruder 1 2.68 1 0.39 260 0.11 Two-way interaction vicinity x kind of intruder Residual wongs); and (c) terrestrial predators of nests (e.g. monitor lizards). I did not carry out statistical analysis for raptors and terrestrial predators of nests since for the former the Bell Miners' behaviour was invariable and for the latter I had insufficient data. It was possible to carry out a one-way Analysis of Variance (with unequal sample sizes) for some of the avian predators of nests. Potential avian predators of nests were mobbed by an average of 2.73 Bell Miners (range 1-15) while raptors were never mobbed. I recorded 18 instances in which a raptor intruded into a colony, especially flying at or below the level of the canopy, but on only one occasion I recorded a Brown Goshawk being dive-bombed (once) by a single Bell Miner. The Goshawk was perching about 20 m from the ground. In all other cases the Bell Miners uttered an alarm call in chorus until the raptor was out of sight. They did not call if the raptor was flying well above the canopy nor when a Wedgetailed Eagle flew level with the top of the canopy on 11 March 1990. There was no significant difference in the number of EMU Vol. 91. 1991 168 Table 6 One-way Analysis of Variance for the effect of the nest predator's species (Laughing Kookaburra, Pied Currawong and Australian Raven) on the number of Bell Miners engaged in mobbing. F = 0.65, P > 0.50 ,,,, Species of predator Mean k s.d. (sample size) Australian Raven 7.30 f 5.50 (3) Laughing Kookaburra 2.13 f 1.79 (52) Pied Currawong 4.25 ? 5.33 (28) mobbers engaged in attacks against Laughing Kookaburras, Pied Currawongs and ravens (one-way Analysis of Variance. Table 6. P > 0.50). Not all terrestrial predators of nests were mobbed in the same way. Stuart's Antechinus Antechinus stuartii were attacked by four (n = 1 observation) or one (n = 2) Bell Miners. These attacks occurred when it was climbing a tree very close (0.3 and 2 m) to an active nest. I observed anti-predator behaviour against a Lace Monitor Varanus varius only once. The encounter did not occur close to an active nest. Two Bell Miners perched about 2 m from the ground as the Lace Monitor was passing below them. The birds then uttered an alarm call but did not leave the bush they were perching on. When a human approached a nest with nestlings a variable number of Bell Miners (5-20) usually surrounded the intruder and performed broken-wing displays while uttering loud distress calls. I was once repeatedly attacked by a female Bell Miner while measuring a nestling; she swooped so resolutely and close that I was able to catch her with an entomological net! This happened inside the zoo area of the Park where Bell Miners may be more habituated to human presence. Discussion It has been suggested that the intensity of mobbing against potential nest predators (here measured as the number of birds engaged in mobbing) will vary as the breeding season progresses because late in the season the probability of renesting decreases (Carlisle 1982; Winkler 1987). Decreased renesting with time occurs in the Bell Miner population at Healesville where the birds show a humpback distribution of nesting activity with a maximum between November and February and virtually no nests built between May and July. This contrasts with the findings of Clarke (1988) who showed that Bell Miners can nest year-round in the more coastal site of Janefield, near Melbourne. The higher seasonality of Bell Miners at Healesville may be explained by the different annual precipitation regimes in the two sites: 1000 mm at Healesville vs 691 mm at Melbourne. For a bird such as the Bell Miner which lives in loose colonies (sensu Dow 1975), an additional factor may complicate the possible effects of time in the season on anti-predator behaviour. It might be expected that as the breeding season comes to an end, colonial birds would suffer relatively more from increased competition for food than from nest predation (Haas 1985), assuming (a) that the bird has a limited amount of time to allocate to either anti-predator or anti-competitor attacks; (b) that costs of foraging increase towards the end of the breeding season; and (c) that there is a tradeoff between benefits accruing to the bird through the current reproductive event and the probability of the bird's survival during the non-breeding season. Unfortunately, we lack data to test the above assumptions for Bell Miners, although the non-breeding season at Healesville may indicate that assumptions (b) and (c) may hold true for this population. In which case competitors should be mobbed more intensely late in the season (especially in the dense colony) while predators should be mobbed more intensely in the early-mid season. My data do not support this prediction. Although Bell Miners mobbed Pied Currawongs more intensely in the early-mid season within a dense colony a able 2b), Laughing Kookaburras and psittaciform competitors were mobbed as intensely early or late in the season, within a dense or a sparse colony (Table 2a,c). This trend was also valid if we consider that the number of active nests in the colony was greater in the early-mid season in the dense colony (unpubl. data). In general, intruders were mobbed more intensely in a dense than in a less dense colony (Table 4). Coloniality may have increased the efficiency of anti-predator defence (e.g. through an increased recruitment of mobbers) and it might therefore increase reproductive success (Gotmark & Anderson 1984; Shields 1984; Robinson 1985; Raveling 1989). Nest predators (all species from Table 1) were mobbed more intensely in a dense colony and more than competitors (Table 4). However, the increased number of mobbers within dense colonies did not coincide with a decreased rate of predation upon nests and preliminary data suggest that the percentage of nests lost by predation was slightly greater in the denser colony than in the less dense one although this difference was not significant (see Results, 'Effect of Poiani: Bell Miner Anti-predator Behaviour colony density'). This lack of coincidence might be due to denser colonies attracting more predators because of their vicinity to the zoo area, although the kinds of predators were similar in both dense and sparse zones. Increased mobbing in the denser zone might have had an effect in deterring predators if we consider that if that level of mobbing had not occurred, predation might have been even higher. Therefore, mobbers in dense colonies may be making the best of a bad job. Nevertheless, they still do slightly worse than birds in sparse colonies in terms of nest failures. In comparison to competitors, nest predators were more likely to be mobbed than to be chased by a single bird (P < 0.005). But if we consider that predator species are the same all over Healesville and that the addition of one or two extra mobbers (which is the average unit size difference between zones A and B, see above) to a mobbing group composed of 3-4 individuals (unit size at B) lacks a significant effect as a deterrent to those predators (at least within the limits of colony density differences considered in this study), why should that extra bird join an already 'efficient' mobbing group? In other words, although it is possible that the difference between one and more than one mobber was significant in terms of nest protection, if the efficiency of anti-predator defence reached a saturation point at a mobbing group size of 3-4 individuals, what was the functional reason for an extra bird increasing the mobbing group up to 5 or 6 individuals? One possibility is that the addition of one or more mobbers in the denser colonies decreased the frequency of visits by each predator (Curio 1978) but, as those colonies might also be visited by more predators, the effects of mobbing on nest success were relatively small. On the other hand, evidence is increasing that attacks against predators can be dangerous for the mobbers (Curio & Regelmann 1986); even nest predators such as Laughing Kookaburras can represent a risk for adult Bell Miners in some circumstances (Poiani & Yorke 1989). Mobbing in Bell Miners may be a result of a strategy to minimise the risks to individuals engaged in anti-predator attacks (Curio 1978). This hypothesis is supported by the fact that competitors, less dangerous to adult Bell Miners than predators, are attacked by a single bird more than they are mobbed. Smith & Robertson (1978) also observed that potential competitors of Bell Miners are attacked by single birds while potential nest predators are mobbed. Since the Bell Miner is a cooperatively breeding bird, the recruitment of helpers during mobbing might 169 be a cost the helpers pay to be allowed to remain in the parental territory (Gaston 1978, Emlen 1982, Hunter 1985). The parents may benefit through the 'dilution effect' of mobbing (Curio 1978). However, an effect of group mobbing on the reproductive success of breeders cannot be ruled out since we do not know whether mobbing by a pair of solitary breeders is less successful than mobbing by breeders plus one or more helpers. The perils that Bell Miners face during anti-predator defence are clearly shown when we compare their responses towards nest predators and raptors. Raptors were never mobbed while nest predators were mobbed by an average of three birds. In addition, intruders were mobbed more intensely when they were perched than when they were flying (Table 4b). On the other hand, small Stuart's Antechinus were fiercely attacked by one or more Bell Miners, while large Monitor Lizards and humans were not approached closely. This contrasts with mobbing behaviour of the Noisy Miner Manorina melanocephala which has been observed mobbing Monitor Lizards at close range (Dow 1975). Laughing Kookaburras, Pied Currawongs and Australian Ravens are known nest predators of Bell Miners (Falconer 1984; Poiani 1991) and, as they are roughly the same size, it is not surprising that they are mobbed with similar intensity (Table 6). The vicinity of an active nest was another variable which affected mobbing behaviour. Bell Miners tended to mob nest predators more intensely than competitors when a nest was close by (0.10 > P > 0.05), suggesting that they do not chiefly rely on nest concealment to escape nest predators (Zimmermann & Curio 1988). This is not surprising since the great activity of birds (breeders and helpers) provisioning chicks is likely to make the nest more easily located by predators (see also Dow 1977). This was further supported by observations of brooding females leaving the nest immediately after other Bell Miners uttered an alarm call (e.g. in the presence of Pied Currawongs), instead of crouching in the nest. It is possible that those breeding females left the nest to join the mobbing group. Mobbing behaviour has been studied in other cooperatively breeding species. As in the Bell Miner, raptors are not mobbed by the Florida Scrub Jay Aphelocoma c. coerulescens (Francis et al. 1989), and cooperative breeding appears to be a factor enhancing the intensity of the mobbing response in both the Scrub Jay and the Mexican Jay Aphelocoma ultramarina (Cully & Ligon 1976). Other aspects of mobbing behaviour important in cooperative breeders are the effect of kinship on the risk 170 taken during mobbing (Payne et al. 1988), effect of age, sex and social status (Payne et al. 1985; Francis et al. 1989), and the occurrence of specialised anti-predator behaviours such as the 'sentinel system' of the Florida Scrub Jay (McGowan & Woolfenden 1989). Acknowledgements I am very grateful to R.A. Zann, A.A. Martin, M.F. Clarke, E. Curio, K. Rogers and E. Russell for their very helpful comments and criticisms which greatly improved the manuscript. Many thanks also to my wife Marisa for her very valuable help in the field and constant encouragement. This work was financed by the Department of Zoology, La Trobe University, the Sir Colin Mackenzie Zoological Park and the M.A. Ingram Trust. References Amstrong, E.A. 1956. Distraction display and the human predator. Ibis 98,641-654. Campbell, K.G. & Moore, K.M. 1957. An investigation of the food of the Bell Bird Manorina melanophrys Latham. Proceedings of the Zoological Society of New South Wales 1955-59,72-73. Carlisle, R.T. 1982. Brood success in variable environments: implications for parental care allocation. Animal Behaviour 30, 824-836. Clarke, M.F. 1984. Interspecific aggression within the genus Manorina. Emu 84, 113-115. Clarke, M.F. 1988. The reproductive behaviour of the Bell Miner Manorina melanophrys. Emu 88, 88-100. Conover, W.J. 1980. Practical nonparametric statistics. John Wiley & Sons, New York. Cully, J.F.Jr. & Ligon, J.D. 1976. Comparative mobbing behavior of Scrub and Mexican Jays. Auk 93, 116-125. Curio, E. 1975. The functional organization of anti-predator behaviour in the Pied Flycatcher: a study of avian visual perception. Animal Behaviour 23, 1-115. Curio, E. 1978. The adaptive significance of avian mobbing. I Teleonomic hypotheses and predictions. Zeitschrift fur Tierpsychologie 48, 175-183. Curio, E. & Regelmann, K. 1985. The behavioural dynamics of Great Tit (Parus major) approaching a predator. Zeitschrift fur Tierpsychologie 69, 3-18. Curio,E. & Regelmann,K. 1986. Predator harassment implies a real deadly risk: a reply to Hennessy. Ethology 72.75-78. Curio, E., Emst, U. & Vieth, W. 1978. The adaptive significance of avian mobbing. I1 Cultural transmission of enemy recognition in blackbirds: effectiveness and some constraints. Zeitschrift fur Tierpsychologie 48, 184-202. EMU Vol. 91, 1991 Dow, D.D. 1975. Displays of the honeyeater Manorina melanocephala. Zeitschrift fur Tierpsychologie 38, 7096. Dow, D.D. 1977. Reproductive behavior of the Noisy Miner, a communally breeding honeyeater. Living Bird 16, 163185. Emlen, S.T. 1982. The evolution of helping. I An ecological constraints model. American Naturalist 119, 29-39. Falconer, P. 1984. Grey Currawong robs Bell Miner nest. Bird Observer 629,57. Francis, A.M., Hailman, J.P. & Woolfenden, G.E. 1989. Mobbing by Florida Scrub Jays: behaviour, sexual asymmetry, role of helpers and ontogeny. Animal Behaviour 38,795-816. Gaston, A.J. 1978. The evolution of group territorial behavior and cooperative breeding. American Naturalist 112, 1091-1100. Gotmark,F. & Andersson, M. 1984. Colonial breeding reduces nest predation in the Common Gull (Larus canus). Animal Behaviour 32,485-492. Haas,V. 1985. Colonial and single breeding in Fieldfares, Turdus pilaris L.: a comparison of nesting success in early and late broods. Behavioral Ecology and Sociobiology 16, 119-124. Hennessy, D.F. 1986. On the deadly risk of predator harassment. Ethology 72,72-74. Hunter, L.A. 1985. The effects of helpers in cooperatively breeding Purple Gallinules. Behavioral Ecology and Sociobiology 18, 147-153. Loyn, R.H., Runnals, R.G., Forward, G.Y. & Tyers, J. 1983. Territorial Bell Miners and other birds affecting populations of insect prey. Science 221, 1411-1413. McGowan, K.J. & Woolfenden, G.E. 1989. A sentinel system in the Florida Scrub Jay. Animal Behaviour 37, 1000- 1006. Montgomerie, R.D. & Weatherhead, P.J. 1988. Risks and rewards of nest defence by parent birds. Quarterly Review of Biology 63, 167-187. Payne, R.B., Payne, L.L. & Rowley, I. 1985. Splendid Wren Malurus splendens response to cuckoos: an experimental test of social organization in a communal bird. Behaviour 94, 108-127. Payne, R.B., Payne, L.L. & Rowley, I. 1988. Kinship and nest defence in cooperative birds: Splendid Fairy-wrens, Malurus splendens. Animal Behaviour 36,939-941. Poiani, A. & Yorke, M. 1989. Predator harassment: more evidence on the deadly risk. Ethology 83,167-169. Poiani, A. 1991. Laughing Kookaburra robs Bell Miner nest. Corella. Raveling, D.G. 1989. Nest-predation rates in relation to colony size of Black Brant. Journal of Wildlife Management. 53, 87-90. Robinson, S.K. 1985. Coloniality in the Yellow-rumped Cacique as a defense against nest predators. Auk 102, 506-5 19. Poiani: Bell Miner Anti-predator Behaviour Shalter, M.D. 1978. Effect of spatial context on the mobbing reaction of Pied Flycatcher to a predator model. Animal Behaviour 26, 1219-1221. Shields, W.M. 1984. Barn Swallow mobbing: self-defence, collateral kin defence, group defence, or parental care? Animal Behaviour 32, 132-148. Smith, A.J. & Robertson, B.I. 1978. Social organization of Bell Miners. Emu 78, 169-178. Sokal, R.S. & Rohlf, F.J. 1981. Biometry, 2nd edn. Freeman, Chicago. 171 Sordahl, T.A. 1990. The risks of avian mobbing and distraction behavior: an anecdotal review. Wilson Bulletin 102, 349-352. Swainson, G.W. 1970. Distraction display in the Bell Miner. Emu 70,199. Winkler, D.W. 1987. A general model for parental care. American Naturalist 130,526-543. Zimmermann, U. & Curio, E. 1988. Two conflicting needs affecting predator mobbing by Great Tits, Parus major. Animal Behaviour 36,926-932. 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