Vocal behavior of Crested Guineafowl (Guttera edouardi) based on visual and sound playback surveys in the Umhlanga Lagoon Nature Reserve, KwaZulu-Natal province, South Africa
© van Niekerk. 2015
Received: 8 December 2014
Accepted: 26 May 2015
Published: 21 July 2015
Generally speaking, playbacks were often ineffective to determine the group sizes of birds since mainly males from leks responded. This limitation has not been tested properly for flocking birds such as Crested Guineafowl (Guttera edouardi) with the view to use it as a counting method. The aims of the study reported in this paper were (1) to describe the calls of Crested Guineafowl in a social context; (2) to interpret calls in an evolutionary context; and (3) to demonstrate that playbacks can be used to locate and count Crested Guineafowl in small isolated forests.
The vocal behavior of Crested Guineafowl was observed during a survey conducted in the Umhlanga Lagoon Nature Reserve (KwaZulu-Natal, South Africa) from November 2010 to June 2012. Transect line observations and sound playback methods were used.
The behavioral context and structure of calls were described. The eight calls described for Crested Guineafowl were produced mainly to unite flock members in the dense understory, where visibility was poor, and to repel intruders. When not disturbed, Crested Guineafowl were quiet and only made soft contact calls.
The high rate of call back and the fact that flocks invariably approach the source of the call en masse, shows that field researchers are able to assess the population size of Crested Guineafowl with sound playbacks along a transect. The value of playbacks as a conservation tool is assessed.
The Crested Guineafowl (Guttera edouardi) is one of the least scientifically studied galliforms in southern Africa (Madge and McGowan 2002; Little and Crowe 2011). Published papers have concentrated on the viability of this species in forest patches of different sizes (Lawes et al. 2006), evolution (Crowe 1978), adaptive morphological variation of Crested Guineafowl and Helmeted Guineafowl (Numida meleagris) (Crowe 1979) and some diet studies (Wilson 1965; Hill 1974). Maier (1982) analyzed the vocal characteristics of Helmeted Guineafowl in captivity, and identified six sound groups, but the vocal behavior of Crested Guineafowl has not been described.
The Hawaan Forest (35 ha) and Umhlanga Lagoon Nature Reserve (ULNR, 20 ha) at Umhlanga (Kwazulu-Natal province, South Africa) are forested enclaves between high-density human settlements and tourism facilities (e.g. hotels), and the forests are visited by thousands of tourists annually. No Crested Guineafowl populations exist south of these forests (Little and Crowe 2011). In light of alien plant invasion and the demand for residential space, basic information on the Crested Guineafowl’s ecology is crucial to conserve these birds in these forests (Sutherland et al. 2004; Rasaru 2007; Little and Crowe 2011). Crested Guineafowl live in closely knitted flocks with dominant birds initiating foraging direction (JH van Niekerk, personal observations). This is similar to Helmeted Guineafowl where males lead the flock (van Niekerk 2010a).
A basic description of sounds is important for identifying species, use in bio-acoustic monitoring with automated sound techniques and for phylogenetic studies (Sutherland et al. 2004; Brandes 2008; van Niekerk 2013). In forests where visibility is low, sound playbacks can be used to improve monitoring accuracy (e.g. population trends). Playbacks can be used for line transect or point transect surveys; this could be especially suitable for dense forests, where observation routes are often limited to clearings (Sutherland et al. 2004). However, playbacks were ineffective to determine the group sizes of birds such as the Red-crested Korhaans (Lophotis ruficrista), since mainly males from leks responded (van Niekerk 2014). This limitation has not been tested properly for flocking birds such as Crested Guineafowl with the view to use it as a counting method (Little and Crowe 2011).
Playbacks could have a negative effect on the behavior of birds, for instance by diverting them from other activities such as breeding or causing habituation (Lima and Roper 2009). The latter would introduce bias into a follow-up study (Harris and Haskell 2013). In order to use sound playbacks as an ethical conservation tool, it is important to assess the effect of playback on Crested Guineafowl and establish a protocol (Harris and Haskell 2013). The aims of the study reported in this paper were (1) to describe the calls of Crested Guineafowl in a social context; (2) to interpret calls in an evolutionary context; and (3) to demonstrate that playbacks can be used to locate and count Crested Guineafowl in small isolated forests.
The forest (~7 ha) in the ULNR (20 ha) (S29.710028 E31.094438) was chosen for field work. A patch of mangrove and the Umhlanga Lagoon form the northern boundary, a high traffic volume dual-carriage tar road (width 25 m) forms the western boundary that separates the Hawaan Forest and the ULNR, and there is a wetland on the eastern boundary and a hotel on the southern boundary. Rain falls mainly during summer, and the average rainfall is about 989 mm per annum (Mucina and Rutherford 2006). The vegetation is KwaZulu-Natal Coastal Belt with subtropical coastal forests (Mucina and Rutherford 2006). Indigenous trees include the Coastal Red Milkwood (Mimusops caffra), Climbing Raisin (Grewia caffra), Red Milkwood (M. obovata), Zulu Cherry-orange (Teclea gerrardii), Natal Fig (Ficus natalensis), White Stinkwood (Celtis africana) and White Mangrove (Avicennia marina).
The 460 m-long footpath (~2.5 m wide) through the centre of the ULNR forest, used daily by the public, was a convenient clearing from which playbacks and observations were conducted. This habitat mainly included the regular occurrence of old trees (primary canopy trees) of about 50–200 cm tree trunk diameter, 30–40 m apart and about 20–30 m high interspersed with immature understory trees with a tree trunk diameter of about 20–70 mm on relatively flat ground with patches of thick bushes under the canopy.
The footpath was traversed three or four times per month on separate days, from November 2010 to June 2012; (1) to record group sizes and general behavior and (2) to study the sounds in a social context. To prevent possible habituation, playbacks were limited to 1 day per month (Catchpole and Slater 2008). Each survey, whether playback was done or not, lasted approximately 30 min. Playbacks (recorder) were directed at birds that were seen or heard but also at 30 m intervals along the transect without seeing or hearing guineafowl (“blind calling”).
For the playbacks, two typical alarm calls (two exemplars) were recorded and played through a Sony ICD-PX820 recorder (call volume of ~80 dB). One call was pre-recorded at the site and another was copied from a collection recorded by Gibbon (2003). The location of this recording is unknown. The sampling rate was 44.10 kHz. To prevent possible habituation the exemplars were alternated between visits (Catchpole and Slater 2008). Each playback lasted 30 s and was conducted 100 cm above ground level; the flat microphone faced the direction in which the birds were located. Visibility (0–1 m above ground level) was limited to 5 to 40 m on either side of the foot path.
As a pilot study, on three occasions during playback interactions with guineafowl, their own alarm calls that were freshly recorded, were played back immediately twice (totalling six playbacks) and in all cases the birds also responded behaviorally as expected (described later) to their own calls. By also playing the two calls intended for this survey, similar responses were observed. These tests were conducted to ensure that the behavioral effects described in this paper were not peculiar to two calls only. During the pilot study the birds responded to the playback from a distance of 40 m and invariably approached the source. A measuring tape was used. The recorded playbacks were also used in the Hawaan Forest and similarly the birds responded with sound and approached the source.
The recording distances of the responding birds varied from 2 to 15 m (estimated). When the birds approached the playback device, they were not exposed to more than one sound playback (lasting 30 s) and they were not exposed to the recordings or the researcher for more than 5 min. Sounds were described as soft (40–60 dB) or loud (>60 dB) determined with a Lutron (SL-4013) sound level meter. Spectrograms of recordings were visualised to identify and eliminate background noise from bird sounds. Before and after playback, and during trips when playbacks were not conducted, the observer devoted 10 min on entering or leaving the forest to record any spontaneous guineafowl sounds. Interviews were conducted with the following people who worked in two forests on a regular basis during the past 10 years: P. Carnegie (tour guide), B. Njcamu (tour guide), D. Mguni (Ezemvelo KwaZulu-Natal Wildlife) and S. Ngcobo (security guard). The purposes of these interviews were mainly to estimate the number of flocks in the study area and the general sizes of the flocks during each visit and to compare this with the results of this current survey.
Flocking behavior and flock sizes
The mean flock size from November 2010 to December 2011 was 5.78 (n = 39, range = 2–8, SD = 1.44) with an insignificant mean monthly flock size variation (χ 2 = 1.20, df = 9, p = 0.998). A larger flock of ~30 birds was observed in the adjacent Hawaan forest. Only one flock occupied the small forest during the past 10 years. During November 2011 the flock broke up into two smaller units of which one was a pair. The two sub-groups of the flock were observed in the forest apart from one another on five occasions (12.8 % or 5 out of 39 observations). During pair-formation the female followed the male over a fairly large area (5 ha or more) and she was actively courtship-fed. She either took a piece of food from his beak or he pointed with his beak where she should peck. While this occurred, he stood close by, typically with his crop area protruding forward, but no sounds were audible. Importantly, no offspring were observed during this survey or during the previous five years [B. Njcamu (tour guide), D. Mguni (Ezemvelo KwaZulu-Natal Wildlife) and S. Ngcobo (security guard) personal communication].
The birds responded to both playback exemplars. The sounds of Crested Guineafowl were categorised into four sound groups:
Spectrogram measurements selected to compare the frequencies (Hz) of basic syllables comprising the different calls of Crested Guineafowl
Frequency 95 %
Number of exemplars (n)
Number of months sampled
Frequency 5 %
Number of exemplars (n)
Number of months sampled
Number of exemplars (n)
Number of months sampled
Rate (syllables /second)
Number of exemplars (n)
Number of months sampled
Phrase size (syllables/bout)
Number of exemplars (n)
Number of months sampled
There were at least four variations of the alarm call: (1) the phrase consisted mostly of a repetition of syllables (n = 12) (Fig. 2a); (2) the syllable often started with a tonal element (n = 3) (Fig. 1b); (3) some syllables had a strong nasal quality (similar to Fig. 2a) (n = 5) and (4) alarm syllables were sometimes interspersed with loose-standing tonal syllables (Fig. 2c) (n = 3). The phrases containing the (calm notes) tonal element/syllable invariably followed an initial spell of frantic alarm calls.
Responses to playbacks
Generally speaking, when Crested Guineafowl were relatively far away (say 20 m) from humans and not interpreting the presence of humans as intruding (such as a sudden encounter at close range), they were heard producing soft tremolo contacts sounds. Calls were never heard on the perimeter of the forest (out in the open). The footpath was traversed on 142 occasions (71 times in one direction and 71 times back) and the guineafowl flock was visually located on 39 occasions (27.46 %). Playbacks were conducted during 20 of these visual encounters; the birds responded 19 (95 %) times with callbacks, and all the members of the flock emerged and became visible. This made it possible to count all the birds. During six of the occasions on which guineafowl were called up with playbacks, they were again observed on return, after 10 to 15 min, foraging about 20 to 30 m from where they were initially located, and producing soft tremolo sounds.
The mean group size (mean = 6.55, range = 4–7, SD = 0.9, n = 19) of Crested Guineafowl counted following playback was significantly larger than the mean group size of Crested Guineafowl counted when playback was not used (mean = 5.25, range = 2–7, SD = 1.68, n = 20) (ANOVA: F = 8.52, df1,36, p = 0.006). Blind calling, when no guineafowl were observed, was done on 30 occasions during a 6-month period. On these occasions, vocal responses were elicited three times (10 %), and the flock revealed itself and could be counted.
The replication of four guineafowl alarm calls, (mean; ~80.25 kHz at source), were audible to one human up to 50–60 m from the source (recorder) in the forest. At a distance of 50 m the dB of the calls were < 45 dB and not traceable on spectrographs.
Discussion and conclusions
Crested Guineafowl lived a relatively quiet flock life and mostly made contact sounds only. There is some evidence to suggest that Crested Guineafowl calls were not audible further than 50–60 m from the source, and they were certainly never heard on the perimeter of the forest. This is unlike galliform species in grasslands, such as Orange River Francolins (Scleroptila levaillantoides), which make territorial calls, and Helmeted Guineafowl females, which make repeated “buckwheat” calls during summer: both are often heard over distances of 100 to 120 m (van Niekerk 2010a; JH van Niekerk unpublished). Predators would be able to approach much closer in forests, and such close encounters leave little room for escape. Living in flocks in dense vegetation could be a physical handicap for large birds such as Crested Guineafowl, and so a silent lifestyle probably compensates for this disadvantage.
Eight Crested Guineafowl calls were described. However, since no offspring were present, it is expected that this repertoire size would be larger. Furthermore, a close-up survey, such as the one done on Helmeted Guineafowl in captivity (Maier 1982) may well reveal finer variations within the four sound groups (Table 1). African galliforms have small repertoires. Eight or nine calls were reported for Crested Guineafowl, while six were reported for Orange River Francolin (van Niekerk 2012), seven for Crested Francolin (Ortygornis sephaena) (van Niekerk 2010b), four calls for Coqui Francolin (Peliperdix coqui) (JH van Niekerk unpublished) and six to eight for Spurfowls Pternistis spp. (Madge and McGowan 2002; van Niekerk 2013). However, the variation in the alarm call of Crested Guineafowl was not found in the alarm calls of spurfowls or francolins. The calm tonal calls between the alarm clucks of Crested Guineafowl were possibly “acknowledgement calls” by members in response to the signalling calls from other flock members. This appears to be a trait of highly sociable galliforms that was absent among francolins and spurfowls, which mostly live singly or in family groups for part of the year.
Adaptive nature of calls
The alarm call of Crested Guineafowl possessed the lowest frequency of all the calls (Table 1). This is regarded as an adaptation, since low frequencies with longer wavelengths propagate better than high frequencies through forests (Catchpole and Slater 2008). Since this is a warning call, or a call that keeps members in contact with one another, it is indeed expected that this call will travel relatively un-attenuated and reach the recipients as a clear signal.
When staccato calls were produced by Crested Guineafowl the threat of an intruder (e.g. attack by an eagle) was more intense than in the case of alarm calls (Fig. 3), as they comprised rapidly produced syllables which probably exacerbated intruder confusion (Kroodsma and Miller 1982; Slabbekoorn et al. 2002). The high frequencies of staccato calls were possibly produced to confuse nearby intruders, since these frequencies bounce off objects such as tree bark and leaves, making it difficult to identify the location of the calling guineafowl in dense vegetation (Catchpole and Slater 2008). However, these high frequencies might also be used as a cue by conspecifics to assess the distance between separated birds in dense vegetation.
The purpose of the Crested Guineafowl’s rhythmic call (Fig. 4) was to bring together dispersed members separated by a distance of about 5 to 10 m. It may also be a duet between flock members, but this possibility requires further study. The purpose of the tremolo and twit calls was to keep the flock together as a close-knit group during foraging. These soft calls were inwardly orientated towards members in the flock. Therefore, it was expected that high or low frequencies to gauge distance or to reach isolated birds would not be part of the acoustic properties of contact calls (Table 1, Fig. 5).
Comparison with Helmeted Guineafowl
The calls of Crested and Helmeted Guineafowl are structurally and functionally similar (Maier 1982). Helmeted Guineafowl also utter (1) a single-syllabled alarm cluck similar to Fig. 2 (also see Little and Crowe 2011); (2) a staccato call when they are confronted by predators (similar to Fig. 3); (3) tremolos, which are narrow frequency bandwidth contact calls (similar to Fig. 5); and (4) soft twit syllables with narrow frequency bandwidth which are responses to strange noises (e.g. the clicking of a camera) similar to Fig. 5. Importantly, detailed studies are required to compare the frequencies, rate and strophe lengths of calls uttered by both species as these are expected to differ given the respective habitats of these birds. Helmeted Guineafowl live in savannah bushveld and open grasslands.
The “buckwheat” iambus call emitted by Helmeted Guineafowl females was absent in Crested Guineafowl; conversely, the complex rhythmic diversion call sound of Crested Guineafowl (Fig. 4) is absent in Helmeted Guineafowl. Iambus calls by Helmeted Guineafowl females are loud and travel quite far. A call of this nature in the Crested Guineafowls’ repertoire would be counter-productive to their secretive lifestyle. On the other hand, the rhythmic call of Crested Guineafowl is probably unnecessary for Helmeted Guineafowl, which lives out in the open, since the birds readily have more visual contact in order to re-unite after being dispersed by a predator.
Traditionally, the usefulness of playbacks for counting birds was dependent on the variation in response rate by members of a population. Some birds may not respond to playbacks for various reasons such as habituation and lead to inaccurate estimates from season to season (Gregory et al. 2004). Conversely, the high response rate and the fact that Crested Guineafowl approach the source in flocks, makes playbacks a reliable tool to count and determine the flock size trends in isolated forests without the intervention of trapping and marking (Lawes et al. 2006). More specifically, playbacks (alarm calls) can be used to locate and count Crested Guineafowl at point transects or along a continuous transect in dense forests where clearings are often limited to narrow roads or paths (Sutherland et al. 2004; Ward and Schlossberg 2004; Mota and Depraz 2004). However, a call of ~80 dB probably did not elicit any response beyond 60 m, owing to the attenuation of sound in dense forests; this could explain the fact that only 10 % of all blind calls elicited responses from the flock. The implication is that to search for Crested Guineafowl, one would have to do playbacks at about 50 m intervals in any direction in the forest to cover all possible guineafowl. Conveniently, unlike other birds such as the Red-crested Korhaan (van Niekerk 2014), during the survey it was not just a male that responded, but normally a dominant male with the rest of the flock calling and joining the dominant bird, as a result of which they were all visible for counting.
Playback had no apparent negative effect on the group cohesion or presence of guineafowl. The birds responded to playbacks every month with the exception of a single occasion. In fact, on six occasions the birds were called up with playbacks and when the observer returned along the same transect 10 to 15 min later, the birds were still foraging in one group in the same general area, about 20 to 30 m from where they were initially located. A 30-second playback to Crested Guineafowl can be safely conducted to visually locate birds one day per month. No guineafowl should be exposed to repeated playbacks and the observer for more than 5 min. This will prevent the habituation that was found in the case of the Orange River Francolin, where playbacks were conducted weekly (cf. van Niekerk 2012). Calls are often amplified to elicit responses from birds but care must be taken not to disturb breeding activity (Kroodsma and Miller 1982; Sutherland et al. 2004; Lawes et al. 2006). The protocol followed in this survey must be seen as baseline but more regular playbacks may also be non-intrusive. Finally, more tests are required especially since this study did not cover any breeding activities or when offspring were present.
I thank Ann Elizabeth Jones for assistance during field work.
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