# Natural History Observations on a Warty Frog:Callulina dawida (Amphibia: Brevicipitidae) in the Taita Hills, Kenya

Authors: Patrick K. Malonza
Journal: ISRN Zoology
 (2012)

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## Abstract

Amphibian populations are declining throughout the world, but most of the susceptible species possess particular biological attributes. Understanding these traits plus the environmental factors responsible for declines greatly aids conservation prioritization and planning. This paper examines the natural history observations and ecological characteristics ofCallulina dawida, a frog endemic to the montane forests of the Taita Hills, Kenya. Sampling was accomplished by use of standardized pitfall trapping, transects, and time-limited searches. Mean monthly temperature and elevation significantly influenced the species distribution and abundance but mean monthly rainfall did not. The species was rare or absent during the cold season and its abundance increased with elevation. Breeding occurred during the long dry season (June to October) with juveniles being abundant between January and March. Available evidence shows that this species deposits a cluster of large yolk-rich eggs on the forest floor with maternal care and direct development. Its occurrence only within highly fragmented indigenous forests makes the species worth listing as critically endangered. To conserve this species, all remaining indigenous forest fragments including those communally or privately owned should be preserved and connected through planting of indigenous trees along stream valleys. In addition, the exotic tree plantations should be replaced with indigenous trees to restore the species habitat.


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## Body

## 1. Introduction

Amphibians are more susceptible to changes in the local environment than other vertebrates [1, 2] because of their permeable skin that absorbs water and oxygen, and their lives depend on clean environmental resources.Almost a third of known amphibian species worldwide are already threatened by a combination of habitat loss, climate change, ultraviolet radiation, diseases, pathogens, global warming, overexploitation, pet trade, environmental pollution, and invasive species [2, 7].Habitat loss and fragmentation [8, 9] are the major causes of the observed global amphibian population declines [3, 10, 11] and is most prevalent in species-rich tropical regions [12]. Among the highly fragmented and threatened habitats is the east African montane forests of the Eastern Arc Mountains (EAM); with the Taita Hills forests being the most fragmented and threatened [13, 14]. Animal populations within such isolated small fragments are ecologically vulnerable to genetic loss due to inbreeding and genetic drift via “bottlenecks” and “founders’ effects” [3, 15, 16].The rate at which amphibian species are declining as a result of human activities is of significant concern to ecologists and conservation biologists [17]. Amphibian extinction risks and population declines are taxonomically nonrandom [2, 18], indicating that certain species biological attributes influence susceptibility to decline. Such traits include large size, low fecundity, being rainforest endemic specialists, breeding in streams, narrow habitat tolerances, restricted range, living at high altitude and low vagility [3, 18, 19]. Understanding these particular biological traits is important in species conservation management and planning [18, 20].Despite the exceptionally high amphibian diversity and abundance in many ecosystems, some amphibian species are occasionally misrepresented in biodiversity estimates because of their secretive nature, nocturnal habits, and small ranges or because of a general lack of understanding of their life histories [7]. Knowledge on the life history of many amphibians is limited and for some even the most basic biological data are lacking [21]. The brevicipitids (Breviceps, Balebreviceps, Probreviceps, Callulina,and Spelaeophryne) range from south Africa through east Africa to the Bale Mountains of Ethiopia [22]. They are typically cryptic and spend much of their time in soil or leaf litter [23], a behavior that partly accounts for the paucity of life history information. Many brevicipitids exhibit some form of parental care. There are reports of females found in burrows with a clutch of eggs in Probreviceps [23, 24]. Probrevicepsis the sister genus to Callulina [25]. The genus Callulina is endemic to the EAM forests of Tanzania and Kenya. The species Callulina kreffti Nieden, 1911, was for close to a century assumed to be the only species in the entire EAM. The first to be described as distinct species was Callulina kisiwamsitu, De Sá et al. 2004, which is endemic to west Usambara Mountains [26]. Recent taxonomic review has found that Callulina kreffti is endemic to the east Usambara Mountains. Following this revelation four more species have recently been formally described: the Taita Hills Callulina dawidaLoader et al. 2009; North Pare Callulina laphaniLoader et al. 2010; two species from South Pare Mountains: Callulina shengenaandCallulina stanleyiLoader et al. 2010. This shows that it is likely that many of the remaining mountain forest blocks may have more than one species. For example three forms from the Nguru Mountains are thought to be distinct new species [27]. Together with these all the other forms from the other forest blocks such as Nguru, Kanga, Ukaguru, Rubeho, Uluguru, Mahenge, and Udzungwa most likely represent undescribed species [28].While currently taxonomists are describing new forms from this genus, little information exists on their life history characteristics such as breeding and other habits that can be used to enhance their conservation management plans. What is known is that species in this genus are mainly forest dwellers, good climbers, and lay eggs that are presumed to develop directly into young frogs [23].Herein I provide additional information on the natural history of one of the warty frogsCallulina dawida,by examining its ecological and breeding characteristics. The aim of this study was to get a better understanding of the species’ behavioural characteristics that can aid conservation efforts. My specific objectives were to investigate whether: (1) Callulina dawida is a forest dwelling species; (2) the distribution and abundance of this frog is independent of mean monthly temperature, rainfall and elevation; (3) the frogs’ eggs are terrestrially deposited anywhere in the forest; (4) the frog is a good climber and terrestrially moves widely within the forest


## 2. Materials and Methods

### 2.1. Study Site

Callulina dawida were studied in fragmented forests of the Taita Hills (Dawida, Mbololo, Sagalla, and Kasigau) mountain blocks. The Taita Hills lie between 38°20′ East and 3°25′ South, in southeastern Kenya. Sampling was done in selected sites of indigenous forests, exotic plantations and farms at varying elevation and disturbance gradients (see the Appendix).


### 2.2. Sampling

Data collection was conducted over a period of 30 months (December 2004 to March 2008). Sampling was accomplished by use of standardized night transect walks and pitfall trapping for quantitative data. Thirty transects were rectangular in shape totaling 600 m standard similar to that used in previous studies [29, 30]. All Callulina dawida individuals observed within 1 m on either side and above the transect path were recorded. Sampling of each transect was repeated every week. The traps consisted of Y-shaped drift fence (30 cm high polythene paper supported with wooden pegs) array with segments of 5 m length in association with four pitfall traps (10 liter plastic buckets) flush with the ground [31]. Three trap sets were set in each site for five days (trapping sessions) after which they were closed and reopened after one week. In total, there were 15 trapping sites. Checking of the traps was done once every morning not later than 7:30 am o’clock morning. Day time one person hour time-limited searches similar to the procedure described by Karns [32] and opportunistic visual encounter surveys generated qualitative data mainly on species habits.To study movement, capture-mark-recapture was done beginning in September 2006 in Ngangao, Chawia, and Mwachora, and later in Fururu, Ndiwenyi, and Vuria forests. Captured frogs were marked by inserting numbered alpha-numeric tags (VIAlpha, northwest Marine, USA) subcutaneously on the ventral surface of the thigh and released for later identity after recapture. A Pesola spring balance (Max. 60 g) was used to take body mass (to the nearest 1 g) while snout-vent length (SVL) was measured using a ruler (to the nearest 1 mm). Age classes were defined using SVL size ranges. Voucher specimens were processed and are deposited at the National Museums of Kenya, Nairobi—NMK Herpetology reference collection (see the Appendix).To study the species breeding habits, nests were searched and when found they were marked and monitored until all the eggs hatched.


### 2.3. Statistical Analyses

All quantitative analyses used data from traps as transect data were not sufficiently productive in terms of number of individuals recorded. One samplet-test was used to test the variation in frog abundance among the forest fragments. Nonparametric Spearman Rank Correlation was used to test the influence of temperature and rainfall on abundance. Chi-square was used to test monthly age group variation in abundance and to test whether abundance was associated with altitude. Data were analyzed with STATISTICA 6.0 [33].


## 2.1. Study Site

Callulina dawida were studied in fragmented forests of the Taita Hills (Dawida, Mbololo, Sagalla, and Kasigau) mountain blocks. The Taita Hills lie between 38°20′ East and 3°25′ South, in southeastern Kenya. Sampling was done in selected sites of indigenous forests, exotic plantations and farms at varying elevation and disturbance gradients (see the Appendix).


## 2.2. Sampling

Data collection was conducted over a period of 30 months (December 2004 to March 2008). Sampling was accomplished by use of standardized night transect walks and pitfall trapping for quantitative data. Thirty transects were rectangular in shape totaling 600 m standard similar to that used in previous studies [29, 30]. All Callulina dawida individuals observed within 1 m on either side and above the transect path were recorded. Sampling of each transect was repeated every week. The traps consisted of Y-shaped drift fence (30 cm high polythene paper supported with wooden pegs) array with segments of 5 m length in association with four pitfall traps (10 liter plastic buckets) flush with the ground [31]. Three trap sets were set in each site for five days (trapping sessions) after which they were closed and reopened after one week. In total, there were 15 trapping sites. Checking of the traps was done once every morning not later than 7:30 am o’clock morning. Day time one person hour time-limited searches similar to the procedure described by Karns [32] and opportunistic visual encounter surveys generated qualitative data mainly on species habits.To study movement, capture-mark-recapture was done beginning in September 2006 in Ngangao, Chawia, and Mwachora, and later in Fururu, Ndiwenyi, and Vuria forests. Captured frogs were marked by inserting numbered alpha-numeric tags (VIAlpha, northwest Marine, USA) subcutaneously on the ventral surface of the thigh and released for later identity after recapture. A Pesola spring balance (Max. 60 g) was used to take body mass (to the nearest 1 g) while snout-vent length (SVL) was measured using a ruler (to the nearest 1 mm). Age classes were defined using SVL size ranges. Voucher specimens were processed and are deposited at the National Museums of Kenya, Nairobi—NMK Herpetology reference collection (see the Appendix).To study the species breeding habits, nests were searched and when found they were marked and monitored until all the eggs hatched.


## 2.3. Statistical Analyses

All quantitative analyses used data from traps as transect data were not sufficiently productive in terms of number of individuals recorded. One samplet-test was used to test the variation in frog abundance among the forest fragments. Nonparametric Spearman Rank Correlation was used to test the influence of temperature and rainfall on abundance. Chi-square was used to test monthly age group variation in abundance and to test whether abundance was associated with altitude. Data were analyzed with STATISTICA 6.0 [33].


## 3. Results

### 3.1. Species Diagnosis

Callulina  dawida is a medium sized frog in which females can reach 55 mm and males 35 mm (Figure 1). The toes of the hind feet are arranged in two opposable groups, with the fourth and fifth together, pointing backward when walking on the forest floor. The skin is warty and dorsal adult color is variable from light brown, grey, dark brown, orange to yellowish. In terms of coloration there is no well-marked sexual dimorphism. Using SVL, the frog population was grouped into three age groups: juveniles (<20 mm), Subadults (20–30 mm) and adults >30 mm).Figure 1
A life photograph ofCallulina dawida in the wild in Ngangao forest P. Malonza.


### 3.2. Population and Habitat Characteristics

From December 2004 until March 2008, 101 individuals were recorded. Twenty-one individual frogs were recorded in traps and seven in transects (Table3). The majority of the rest were from time-limited searches or opportunistic visual encounter surveys and leaf-litter sampling. Thirty three individuals were marked with three recaptures. The SVL of the largest adult and the smallest juvenile recorded in this study were 55 mm and 9 mm, respectively. Characteristically, frogs were found in microhabitats such as on or under leaf litter, or debris and within decomposing logs, tree stems and or bark.Callulina dawida was only found in indigenous forest fragments above an altitude of 1400 m in the Dawida and Mbololo mountain blocks and not in the Sagalla or Kasigau blocks. No individuals were found in typical farmland or exotic plantation habitats.


### 3.3. Distribution and Abundance

There was a discernable monthly age group variation in distribution and abundance (χ2=20.31, d.f.=2, n=12, P=0.00004). While adults could be caught in most months of the year; most of the juveniles were trapped in January and February (Table 2). The mean number of individuals trapped in the four forest fragments differed (one sample t-test; t=4.17, d.f.=3, n=4, P=0.025). Consequently, a high number of individuals were recorded in Ngangao as compared to the other three forests (Mwachora, Chawia, Mbololo).


### 3.4. Influence of Rainfall, Temperature, and Altitude

Spearman Rank Correlation showed thatCallulina  dawida abundance was positively influenced by mean monthly temperature (t=2.39, P=0.037, R=0.60, n=12) and there was no effect of rainfall in the data set (t=1.499, P=0.166, R=0.28, n=12). Therefore individuals are commonly recorded during the warm months of January to March and August to October and less during the cold months of June and July. They are also few to none during the peak rainy seasons in April and November/December (Table 2). The results also demonstrate a clear association between altitude and abundance (χ2=8.0, d.f.=2, n=4, P<0.018). Hence the species is most abundant in the high altitude Ngangao forest fragment (Table 1).Table 1
The number ofCallulina dawidaindividuals captured and recorded from transects in different study sites. In parentheses are total number of trapping sessions and transect walks. Provided also are some characteristics of the sites; area (ha) and approximate maximum elevation (m).
SiteSizeElevationTrapsTransectsIndigenous forestsNgangao192195211 (141)1 (18)Chawia5016254 (146)0 (17)Mwachora316504 (131)0 (17)Macha31700—0 (15)Boma0.251460—0 (18)Mbololo22017792 (123)6 (21)Sagalla315000 (132)0 (15)Kasigau2016450 (32)0 (19)Table 2
Monthly abundance records of juvenile and adultCallulina  dawida in traps.
MonthJuvenilesSubadultsAdultsJanuary500February411March101April001May011June000July000August010September011October011November000December001Table 3
Distribution of Taita warty frog (Callulina dawida) recorded in different forest fragments showing life snout-vent length (SVL) and body weight (Wt), age group, recording date, recording method, and comments. Indigenous forests sizes in parentheses is as follows: Ngangao (92 ha), Chawia (50 ha), Mwachora (4 ha), Ndiwenyi (3 ha), Fururu (12 ha), Boma (0.25 ha), Makandenyi patch (negligible), Kiangungu patch (negligible), Vuria (1 ha), and Mbololo (220 ha). The 18 preserved specimens are shown with NMK catalogue numbers.
SpecimenSVL (mm)Wt (g)Age groupSiteDateMethodComments1457.1FemaleFururu16/12/2004Visual encounter surveyPreserved: NMK-A42662363.7FemaleKiangungu16/12/2004Visual encounter surveyPreserved: NMK-A42673302.5MaleNgangao28/12/2004Visual encounter surveyPreserved: NMK-A4268/14291.8SubadultNgangao28/12/2004Visual encounter surveyPreserved: NMK-A4268/2540.68—FemaleNgangao20/04/2005Pitfall trapPreserved: NMK-A4343643.118.26FemaleChawia25/04/2005Time-limited searchPreserved: NMK-A4344/17302.59MaleChawia26/04/2005Leaf litter searchPreserved: NMK-A4344/2815—JuvenileMbololo29/03/2006Pitfall trapPreserved: NMK-A45749190.6JuvenileMbololo03/04/2006Night transect walkPreserved: NMK-A4582/110200.79SubadultMbololo03/04/2006Night transect walkPreserved: NMK-A4582/211190.63JuvenileMbololo03/04/2006Night transect walkPreserved: NMK-A4582/31231—MaleNgangao07/04/2006Time-limited searchReleased1335—FemaleNgangao21/12/2005Pitfall trapPreserved: NMK-A44921410—JuvenileNgangao06/01/2006Pitfall trapReleased1510—JuvenileNgangao17/01/2006Pitfall trapReleased1645—FemaleNgangao24/01/2006Visual encounter surveyReleased1740—FemaleNgangao10/02/2006Pitfall trapReleased1814—JuvenileNgangao21/02/2006Pitfall trapPreserved: NMK-A45941911—JuvenileNgangao21/02/2006Pitfall trapReleased2015—JuvenileNgangao22/02/2006Pitfall trapReleased2112—JuvenileNgangao22/02/2006Pitfall trapReleased2234—MaleNgangao20/03/2006Pitfall trapPreserved: NMK-A45902340—FemaleNgangao20/03/2006Funnel trap against drift fenceReleased24——AdultNgangao20/03/2006Visual encounter surveyDisappeared before capture25292SubadultVuria16/04/2006Visual encounter surveyReleased2612—JuvenileMwachora05/01/2006Pitfall trapReleased2714—JuvenileMwachora06/01/2006Pitfall trapReleased2815—JuvenileMwachora17/01/2006Pitfall trapReleased2921—SubadultMwachora14/03/2006Pitfall trapPreserved: NMK-A4624309—JuvenileFururu06/12/2005Visual encounter surveyPreserved: NMK-A44163150—FemaleChawia07/02/2006Leaf litter searchReleased3238—FemaleChawia22/02/2006Leaf litter searchReleased3321—SubadultChawia08/03/2006Leaf litter searchReleased3446—FemaleBoma10/05/2006Time-limited searchPreserved: NMK-A46453545—FemaleMbololo05/05/2006Pitfall trapPreserved: NMK-A46843625—SubadultMbololo30/05/2006Time-limited searchReleased3733—MaleBoma03/07/2006Time-limited searchReleased3851—FemaleBoma03/07/2006Time-limited searchReleased39——adultNgangao26/06/2006Time-limited searchReleased4020—SubadultNgangao30/05/2006Pitfall trapReleased41——AdultMakandenyiMarch 2006Visual encounter surveyReleased4230—MaleChawia08/08/2006Pitfall trapReleased4333—MaleNgangao14/08/2006Time-limited searchReleased4434—MaleChawia20/09/2006Pitfall trapReleased4530—MaleChawia20/09/2006Pitfall trapReleased4620—SubadultNgangao25/09/2006Patch samplingRecaptured on 01/04/2007; SVL 42 mm47447FemaleNgangao27/09/2006Patch samplingReleased48221.25SubadultNgangaoOctober 2006Patch samplingReleased49211.25SubadultNgangaoOctober 2006Patch samplingReleased5035—FemaleChawia11/10/2006Patch samplingReleased5127—SubadultChawia28/10/2006Pitfall trapReleased5232—MaleChawia29/10/2006Pitfall trapReleased53436.5FemaleNgangao02/11/2006Time-limited searchReleased54353FemaleNgangao2/11/2006Time-limited searchRecaptured on 02/05/2007; SVL 48 mm, wt 9 g55302MaleNgangao02/11/2006Night transect walkReleased56456FemaleNgangao03/11/2006Time-limited searchReleased5730—MaleMbololo05/12/2006Night transect walkReleased5835—FemaleMbololo05/12/2006Night transect walkReleased5946—FemaleMbololo06/12/2006Time-limited searchReleased6055—FemaleMbololo08/12/2006Time-limited searchReleased6143—FemaleNdiwenyi03/04/2007Time-limited searchReleased6240—FemaleFururu05/04/2007Time-limited searchReleased6329—SubadultNdiwenyi05/04/2007Time-limited searchReleased6446—FemaleVuria11/05/2007Time-limited searchReleased6545—FemaleNdiwenyi28/05/2007Time-limited searchReleased6648—FemaleNgangao02/05/2007Time-limited searchReleased674312FemaleMwachora04/05/2007Time-limited searchReleased68489.5FemaleMbololo17/05/2007Time-limited searchRecaptured on 09/12/2007, SVL 48 mm694811FemaleNgangao09/06/2007Time-limited searchReleased70406.5FemaleNgangao09/06/2008Time-limited searchReleased71262SubadultNgangao09/06/2009Time-limited searchReleased7247—FemaleVuria23/06/2007Time-limited searchReleased7350—FemaleVuria24/06/2007Time-limited searchReleased7430—MaleVuria24/06/2007Time-limited searchReleased7547—FemaleVuria25/06/2007Time-limited searchReleased7655—FemaleVuria25/06/2007Time-limited searchReleased7752—FemaleVuria25/06/2007Time-limited searchReleased7833—MaleVuria25/06/2007Time-limited searchReleased7950—FemaleVuria26/06/2007Time-limited searchReleased8030—MaleVuria26/06/2007Time-limited searchReleased8112—JuvenileVuria26/06/2007Time-limited searchReleased8230—MaleMwachora14/08/2007Time-limited searchReleased83457.5FemaleFururu12/11/2007Time-limited searchReleased: female sitting on 30–40 egg clutch84489FemaleNgangao08/10/2007Time-limited searchReleased85458FemaleNgangao28/10/2008Time-limited searchReleased86456FemaleChawia30/10/2007Time-limited searchReleased87478.5FemaleChawia03/12/2007Time-limited searchReleased884712FemaleNgangao05/12/2007Time-limited searchReleased89407.5FemaleNgangao05/12/2007Time-limited searchReleased90507FemaleMwachora17/12/2007Time-limited searchReleased91202SubadultNgangao6/01/2008Time-limited searchReleased9246—FemaleMbololo18/02/2008Time-limited searchReleased9345—FemaleMbololo22/02/2008Time-limited searchReleased9440—FemaleMbololo25/02/2008Time-limited searchReleased95498.5FemaleMwachora26/02/2008Time-limited searchReleased96508FemaleMwachora14/03/2008Time-limited searchReleased9742—FemaleVuria20/03/2008Time-limited searchReleased9845—FemaleVuria20/03/2008Time-limited searchReleased9922—SubadultVuria20/03/2008Time-limited searchReleased10040—FemaleVuria21/03/2008Time-limited searchReleased10155—FemaleVuria23/03/2008Time-limited searchReleased


### 3.5. Breeding and Other Behavioral Characteristics

Results from time-limited searches showed thatCallulina dawida breeds during the long dry season which runs from June to October. In July and August a strong three note trilling call was heard from males in several forests. On 12 September 2007 in Fururu forest a female (45 mm, 7.5 g) was found on leaf litter sitting on a clutch of 30–40 eggs (2-mm diameter egg capsule) bound together (Figure 2). When displaced she returned to sit on the eggs. The female was then visited on 21 November 2007 and found on the same state until 29 November when only 6 eggs remained with the female still sitting on them. It was observed that the eggs hatch directly into froglets which immediately leave the nest. Once all the eggs have hatched the mother leaves the nest. The smallest juvenile (9 mm) recorded was found on 6 December; 2005 perched on grass within a forest site in Fururu infested with army ants Dorylus molestusGerstäcker, 1859. Callulina  dawida are good climbers and on several occasions in Vuria forest individuals were found perched higher than 1 m on tree stems. Callulina  dawida is normally solitary although on two occasions in Mbololo forest during night transect walks two individuals were found within a meter of one another. One of the adults which had been found perched on a sloping dry thin branch about 30 cm off the ground, was subsequently found on the same site and position the following night. On the forest floor the frog mainly walks but can also make short hops. When disturbed; while walking it tends to become immobile, inflating itself or freezing before proceeding. Information gathered from three marked and recaptured individuals indicates that the species movement is limited: (a) An individual of 20 mm had moved about 25 m after 8 months with a new SVL of 42 mm. (b) An adult of 35 mm was recaptured about 7 m away having increased in SVL to 48 mm after 7 months. (c) An adult of 48 mm was recaptured about 30 m away after 7 months with no change in body length.Figure 2
ACallulina dawida egg mass (clutch) in a ground nest and a displaced female walking away (Oliver Mwakio).


## 3.1. Species Diagnosis

Callulina  dawida is a medium sized frog in which females can reach 55 mm and males 35 mm (Figure 1). The toes of the hind feet are arranged in two opposable groups, with the fourth and fifth together, pointing backward when walking on the forest floor. The skin is warty and dorsal adult color is variable from light brown, grey, dark brown, orange to yellowish. In terms of coloration there is no well-marked sexual dimorphism. Using SVL, the frog population was grouped into three age groups: juveniles (<20 mm), Subadults (20–30 mm) and adults >30 mm).Figure 1
A life photograph ofCallulina dawida in the wild in Ngangao forest P. Malonza.


## 3.2. Population and Habitat Characteristics

From December 2004 until March 2008, 101 individuals were recorded. Twenty-one individual frogs were recorded in traps and seven in transects (Table3). The majority of the rest were from time-limited searches or opportunistic visual encounter surveys and leaf-litter sampling. Thirty three individuals were marked with three recaptures. The SVL of the largest adult and the smallest juvenile recorded in this study were 55 mm and 9 mm, respectively. Characteristically, frogs were found in microhabitats such as on or under leaf litter, or debris and within decomposing logs, tree stems and or bark.Callulina dawida was only found in indigenous forest fragments above an altitude of 1400 m in the Dawida and Mbololo mountain blocks and not in the Sagalla or Kasigau blocks. No individuals were found in typical farmland or exotic plantation habitats.


## 3.3. Distribution and Abundance

There was a discernable monthly age group variation in distribution and abundance (χ2=20.31, d.f.=2, n=12, P=0.00004). While adults could be caught in most months of the year; most of the juveniles were trapped in January and February (Table 2). The mean number of individuals trapped in the four forest fragments differed (one sample t-test; t=4.17, d.f.=3, n=4, P=0.025). Consequently, a high number of individuals were recorded in Ngangao as compared to the other three forests (Mwachora, Chawia, Mbololo).


## 3.4. Influence of Rainfall, Temperature, and Altitude

Spearman Rank Correlation showed thatCallulina  dawida abundance was positively influenced by mean monthly temperature (t=2.39, P=0.037, R=0.60, n=12) and there was no effect of rainfall in the data set (t=1.499, P=0.166, R=0.28, n=12). Therefore individuals are commonly recorded during the warm months of January to March and August to October and less during the cold months of June and July. They are also few to none during the peak rainy seasons in April and November/December (Table 2). The results also demonstrate a clear association between altitude and abundance (χ2=8.0, d.f.=2, n=4, P<0.018). Hence the species is most abundant in the high altitude Ngangao forest fragment (Table 1).Table 1
The number ofCallulina dawidaindividuals captured and recorded from transects in different study sites. In parentheses are total number of trapping sessions and transect walks. Provided also are some characteristics of the sites; area (ha) and approximate maximum elevation (m).
SiteSizeElevationTrapsTransectsIndigenous forestsNgangao192195211 (141)1 (18)Chawia5016254 (146)0 (17)Mwachora316504 (131)0 (17)Macha31700—0 (15)Boma0.251460—0 (18)Mbololo22017792 (123)6 (21)Sagalla315000 (132)0 (15)Kasigau2016450 (32)0 (19)Table 2
Monthly abundance records of juvenile and adultCallulina  dawida in traps.
MonthJuvenilesSubadultsAdultsJanuary500February411March101April001May011June000July000August010September011October011November000December001Table 3
Distribution of Taita warty frog (Callulina dawida) recorded in different forest fragments showing life snout-vent length (SVL) and body weight (Wt), age group, recording date, recording method, and comments. Indigenous forests sizes in parentheses is as follows: Ngangao (92 ha), Chawia (50 ha), Mwachora (4 ha), Ndiwenyi (3 ha), Fururu (12 ha), Boma (0.25 ha), Makandenyi patch (negligible), Kiangungu patch (negligible), Vuria (1 ha), and Mbololo (220 ha). The 18 preserved specimens are shown with NMK catalogue numbers.
SpecimenSVL (mm)Wt (g)Age groupSiteDateMethodComments1457.1FemaleFururu16/12/2004Visual encounter surveyPreserved: NMK-A42662363.7FemaleKiangungu16/12/2004Visual encounter surveyPreserved: NMK-A42673302.5MaleNgangao28/12/2004Visual encounter surveyPreserved: NMK-A4268/14291.8SubadultNgangao28/12/2004Visual encounter surveyPreserved: NMK-A4268/2540.68—FemaleNgangao20/04/2005Pitfall trapPreserved: NMK-A4343643.118.26FemaleChawia25/04/2005Time-limited searchPreserved: NMK-A4344/17302.59MaleChawia26/04/2005Leaf litter searchPreserved: NMK-A4344/2815—JuvenileMbololo29/03/2006Pitfall trapPreserved: NMK-A45749190.6JuvenileMbololo03/04/2006Night transect walkPreserved: NMK-A4582/110200.79SubadultMbololo03/04/2006Night transect walkPreserved: NMK-A4582/211190.63JuvenileMbololo03/04/2006Night transect walkPreserved: NMK-A4582/31231—MaleNgangao07/04/2006Time-limited searchReleased1335—FemaleNgangao21/12/2005Pitfall trapPreserved: NMK-A44921410—JuvenileNgangao06/01/2006Pitfall trapReleased1510—JuvenileNgangao17/01/2006Pitfall trapReleased1645—FemaleNgangao24/01/2006Visual encounter surveyReleased1740—FemaleNgangao10/02/2006Pitfall trapReleased1814—JuvenileNgangao21/02/2006Pitfall trapPreserved: NMK-A45941911—JuvenileNgangao21/02/2006Pitfall trapReleased2015—JuvenileNgangao22/02/2006Pitfall trapReleased2112—JuvenileNgangao22/02/2006Pitfall trapReleased2234—MaleNgangao20/03/2006Pitfall trapPreserved: NMK-A45902340—FemaleNgangao20/03/2006Funnel trap against drift fenceReleased24——AdultNgangao20/03/2006Visual encounter surveyDisappeared before capture25292SubadultVuria16/04/2006Visual encounter surveyReleased2612—JuvenileMwachora05/01/2006Pitfall trapReleased2714—JuvenileMwachora06/01/2006Pitfall trapReleased2815—JuvenileMwachora17/01/2006Pitfall trapReleased2921—SubadultMwachora14/03/2006Pitfall trapPreserved: NMK-A4624309—JuvenileFururu06/12/2005Visual encounter surveyPreserved: NMK-A44163150—FemaleChawia07/02/2006Leaf litter searchReleased3238—FemaleChawia22/02/2006Leaf litter searchReleased3321—SubadultChawia08/03/2006Leaf litter searchReleased3446—FemaleBoma10/05/2006Time-limited searchPreserved: NMK-A46453545—FemaleMbololo05/05/2006Pitfall trapPreserved: NMK-A46843625—SubadultMbololo30/05/2006Time-limited searchReleased3733—MaleBoma03/07/2006Time-limited searchReleased3851—FemaleBoma03/07/2006Time-limited searchReleased39——adultNgangao26/06/2006Time-limited searchReleased4020—SubadultNgangao30/05/2006Pitfall trapReleased41——AdultMakandenyiMarch 2006Visual encounter surveyReleased4230—MaleChawia08/08/2006Pitfall trapReleased4333—MaleNgangao14/08/2006Time-limited searchReleased4434—MaleChawia20/09/2006Pitfall trapReleased4530—MaleChawia20/09/2006Pitfall trapReleased4620—SubadultNgangao25/09/2006Patch samplingRecaptured on 01/04/2007; SVL 42 mm47447FemaleNgangao27/09/2006Patch samplingReleased48221.25SubadultNgangaoOctober 2006Patch samplingReleased49211.25SubadultNgangaoOctober 2006Patch samplingReleased5035—FemaleChawia11/10/2006Patch samplingReleased5127—SubadultChawia28/10/2006Pitfall trapReleased5232—MaleChawia29/10/2006Pitfall trapReleased53436.5FemaleNgangao02/11/2006Time-limited searchReleased54353FemaleNgangao2/11/2006Time-limited searchRecaptured on 02/05/2007; SVL 48 mm, wt 9 g55302MaleNgangao02/11/2006Night transect walkReleased56456FemaleNgangao03/11/2006Time-limited searchReleased5730—MaleMbololo05/12/2006Night transect walkReleased5835—FemaleMbololo05/12/2006Night transect walkReleased5946—FemaleMbololo06/12/2006Time-limited searchReleased6055—FemaleMbololo08/12/2006Time-limited searchReleased6143—FemaleNdiwenyi03/04/2007Time-limited searchReleased6240—FemaleFururu05/04/2007Time-limited searchReleased6329—SubadultNdiwenyi05/04/2007Time-limited searchReleased6446—FemaleVuria11/05/2007Time-limited searchReleased6545—FemaleNdiwenyi28/05/2007Time-limited searchReleased6648—FemaleNgangao02/05/2007Time-limited searchReleased674312FemaleMwachora04/05/2007Time-limited searchReleased68489.5FemaleMbololo17/05/2007Time-limited searchRecaptured on 09/12/2007, SVL 48 mm694811FemaleNgangao09/06/2007Time-limited searchReleased70406.5FemaleNgangao09/06/2008Time-limited searchReleased71262SubadultNgangao09/06/2009Time-limited searchReleased7247—FemaleVuria23/06/2007Time-limited searchReleased7350—FemaleVuria24/06/2007Time-limited searchReleased7430—MaleVuria24/06/2007Time-limited searchReleased7547—FemaleVuria25/06/2007Time-limited searchReleased7655—FemaleVuria25/06/2007Time-limited searchReleased7752—FemaleVuria25/06/2007Time-limited searchReleased7833—MaleVuria25/06/2007Time-limited searchReleased7950—FemaleVuria26/06/2007Time-limited searchReleased8030—MaleVuria26/06/2007Time-limited searchReleased8112—JuvenileVuria26/06/2007Time-limited searchReleased8230—MaleMwachora14/08/2007Time-limited searchReleased83457.5FemaleFururu12/11/2007Time-limited searchReleased: female sitting on 30–40 egg clutch84489FemaleNgangao08/10/2007Time-limited searchReleased85458FemaleNgangao28/10/2008Time-limited searchReleased86456FemaleChawia30/10/2007Time-limited searchReleased87478.5FemaleChawia03/12/2007Time-limited searchReleased884712FemaleNgangao05/12/2007Time-limited searchReleased89407.5FemaleNgangao05/12/2007Time-limited searchReleased90507FemaleMwachora17/12/2007Time-limited searchReleased91202SubadultNgangao6/01/2008Time-limited searchReleased9246—FemaleMbololo18/02/2008Time-limited searchReleased9345—FemaleMbololo22/02/2008Time-limited searchReleased9440—FemaleMbololo25/02/2008Time-limited searchReleased95498.5FemaleMwachora26/02/2008Time-limited searchReleased96508FemaleMwachora14/03/2008Time-limited searchReleased9742—FemaleVuria20/03/2008Time-limited searchReleased9845—FemaleVuria20/03/2008Time-limited searchReleased9922—SubadultVuria20/03/2008Time-limited searchReleased10040—FemaleVuria21/03/2008Time-limited searchReleased10155—FemaleVuria23/03/2008Time-limited searchReleased


## 3.5. Breeding and Other Behavioral Characteristics

Results from time-limited searches showed thatCallulina dawida breeds during the long dry season which runs from June to October. In July and August a strong three note trilling call was heard from males in several forests. On 12 September 2007 in Fururu forest a female (45 mm, 7.5 g) was found on leaf litter sitting on a clutch of 30–40 eggs (2-mm diameter egg capsule) bound together (Figure 2). When displaced she returned to sit on the eggs. The female was then visited on 21 November 2007 and found on the same state until 29 November when only 6 eggs remained with the female still sitting on them. It was observed that the eggs hatch directly into froglets which immediately leave the nest. Once all the eggs have hatched the mother leaves the nest. The smallest juvenile (9 mm) recorded was found on 6 December; 2005 perched on grass within a forest site in Fururu infested with army ants Dorylus molestusGerstäcker, 1859. Callulina  dawida are good climbers and on several occasions in Vuria forest individuals were found perched higher than 1 m on tree stems. Callulina  dawida is normally solitary although on two occasions in Mbololo forest during night transect walks two individuals were found within a meter of one another. One of the adults which had been found perched on a sloping dry thin branch about 30 cm off the ground, was subsequently found on the same site and position the following night. On the forest floor the frog mainly walks but can also make short hops. When disturbed; while walking it tends to become immobile, inflating itself or freezing before proceeding. Information gathered from three marked and recaptured individuals indicates that the species movement is limited: (a) An individual of 20 mm had moved about 25 m after 8 months with a new SVL of 42 mm. (b) An adult of 35 mm was recaptured about 7 m away having increased in SVL to 48 mm after 7 months. (c) An adult of 48 mm was recaptured about 30 m away after 7 months with no change in body length.Figure 2
ACallulina dawida egg mass (clutch) in a ground nest and a displaced female walking away (Oliver Mwakio).


## 4. Discussion

Callulina  dawida is a high-elevation species occurring in indigenous forest fragments above 1400 m within Dawida and Mbololo blocks of the Taita Hills [28]. These fragments range from <1 ha to 220 ha [34]. It is absent in typical farmland and plantation habitats as well as the isolated indigenous forest fragments on Kasigau Mountain and Sagalla Hill. Results on monthly distribution showed age group variation in abundance, which for juveniles reflects the time of their recruitment. This means after hatching around November it is in January and February when they are grown-up enough to move around and become easily detected.Movement is limited in this species justifying its survival in tiny forest patches though continued population viability within such small isolated patches is questionable due to the associated ecological and genetic problems [3, 15, 16]. Ngangao forest had the highest number of individuals captured in traps. This suggests that it has a combination of ideal habitat characteristics suitable for the occurrence of this species. Also there is less human disturbance than in Mwachora and Chawia. The high density of individuals in small fragments such as Vuria forest which is at the highest altitude could be because of a combination of factors. It could be due to the fact that the habitat is ideal and the dispersal area is small and there is low disturbance because of inaccessibility of the forest to humans as well as less predation and competition from other species.The abundance of theCallulina  dawida is influenced by temperature with more individuals being recorded during the warm months of the year in the Taita Hills [35]. This coincides with the periods of moderate to high temperatures and humidity. No individuals were recorded in July which is the coldest month in the Taita Hills [36, 37]. These observations concur with other studies that have shown that temperature affects amphibian populations through its effects on growth and development [38]. It was also found that more individuals were recorded in high altitude forests of Ngangao in traps and Vuria in time-limited searches than those on lower elevations. Extrinsic factors such as temperature, rainfall, and altitude are interrelated [38–41] and affect the biology of amphibians and hence their abundance [42]. In particular, studies have found that altitude and its relation with temperature has negative effects on amphibian population [40]. A study on Mount Kupe in Cameroon found that species that do not depend on water for breeding (direct developers like Callulina  dawida) were more abundant on high altitudes than the open water breeders [43]. Previous studies have generally found that rainfall and temperature directly affect food availability which in turn affects amphibian populations through growth and development and these factors relate to elevation [38–41]. Other studies have found rainfall to be the most important abiotic factor influencing tropical anuran reproduction by affecting and regulating the timing and length of breeding season in open (water) site breeders [21].Callulina  dawida start breeding with calls mainly during the long dry season from around July. The call is a fast repeated “brrr brr brr…” [44]. Then egg clutch is deposited on leaf litter nests in September and the mother broods them for three months until November, a relatively long developmental period as expected at high elevations [38]. While a clutch of 30–40 capsulated eggs was found, it was only 6 that were found towards the end of the incubation. This means that eggs hatch at different times and the young ones immediately leave the nest site. Elsewhere in another brevicipitid (Probreviceps macrodactylus macrodactylus), Müller et al. [45] found a clutch of 32 eggs including 21 infertile jelly-filled capsulated eggs laid during the dry season. They suggested that infertile jelly-filled egg capsules prevent the fertile eggs from desiccation during the dry period. This form of parental care is not new as it has been recorded in other brevicipitids, for example, Probreviceps  uluguruensis,  Probreviceps macrodactylus loveridgei [23] and Probreviceps rhodesianus [24]. These results also show that Callulina  dawida, like other brevicipitids, deposit relatively small clutches of large yolk-rich eggs that are buffered by infertile jelly-filled egg capsules. My findings concurs with others that have shown that direct developing montane species produce relatively small clutches of large yolk-rich eggs and exhibit increased parental care [41].Growth and development inCallulina dawida is fast attaining sexual maturity within eight months. This rapid attainment of a reproductive size is expected in tropical areas where temperatures are high, allowing anurans to grow throughout the year [38, 42].


### 4.1. Conservation and Management Strategy

The species is restricted to severely fragmented indigenous forests and I conclude that its extent of occurrence, area of occupancy, and habitat quality will continue to decline. A combination of these factors makes the species eligible for listing in the critically endangered (CR) category B 1a&b (i, ii, iii, iv) [46]. To ensure a comprehensive protection of Callulina  dawida maintenance or step-up efforts for all currently known indigenous forest fragments is paramount. I strongly recommend promotion of local initiatives that encourage planting indigenous plant species over exotics and preservation of private or community sacred forest groves including maintenance of potential habitat corridors (e.g., riverine forests) that connect existing forest fragments. I also support habitat restoration programmes that involve careful replacement of exotic tree plantations with native trees.


## 4.1. Conservation and Management Strategy

The species is restricted to severely fragmented indigenous forests and I conclude that its extent of occurrence, area of occupancy, and habitat quality will continue to decline. A combination of these factors makes the species eligible for listing in the critically endangered (CR) category B 1a&b (i, ii, iii, iv) [46]. To ensure a comprehensive protection of Callulina  dawida maintenance or step-up efforts for all currently known indigenous forest fragments is paramount. I strongly recommend promotion of local initiatives that encourage planting indigenous plant species over exotics and preservation of private or community sacred forest groves including maintenance of potential habitat corridors (e.g., riverine forests) that connect existing forest fragments. I also support habitat restoration programmes that involve careful replacement of exotic tree plantations with native trees.



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*Source: 212491-2012-03-15.xml*