Rediscovery of the “terrible hairy fly”, Mormotomyia hirsuta Austen (Diptera: Mormotomyiidae), in Eastern Kenya, with Notes on Biology, Natural History, and Genetic Variation of the Ukasi Hill Population

ABSTRACT Sixty-two years since last observed alive, Mormotomyia hirsuta Austen, the “terrible hairy fly”, was found inside and outside a large, cave-like cleft boulder at the summit of Ukasi Hill in eastern Kenya, the type locality of the species. Adults were observed climbing the walls of the boulder and walking on thick layers of bat guano, in which larvae and puparia were also discovered. Large numbers of M. hirsuta were observed on and at the base of the northern side of the boulder, which at the time of capture experienced continuous shade during daylight hours. Only three individuals were observed at the southern opening, exposed to direct sunlight and hot, dry conditions. A collection of vertebrate bones and skulls from layers of guano both inside and outside the cleft revealed several vertebrate associates, including two species of Chiroptera, Chaerephon cf. bivittatus (Heuglin) and Tadarida aegyptiaca (E. Geoffroy), which are probably the two major guano-producing species responsible for the larval breeding medium. Male-biased sexual size dimorphism was pronounced in adult M. hirsuta, with seven body-part measurements, including legs, larger by 33–61 % in males than females. Males demonstrated isometric growth while female growth was allometric. In contrast to males, female head and thorax lengths did not increase proportionally with leg length. Estimates of genetic diversity in the Ukasi population show higher than expected allelic diversity and indicate possible gene flow and frequent population bottlenecks. To promote the conservation of this endangered species, a joint effort has been initiated between the International Centre of Insect Physiology and Ecology, Nairobi and the National Museums of Kenya, Nairobi, to gazette the Ukasi hill area as a protected site.


INTRODUCTION
cimens collected at Ukasi (as Ukazzi) in 1933 by Major Harry Barron Sharpe, then racterized by its presumed association with bat guano, its greatly reduced and dysmore closely resembles a solfugid, at least when living and ambulant. Until 1948, two specimens deposited in the Natural History Museum, London remained the only known examples of this extraordinary species. In December 1948, following heavy rainfall, the species was again collected, this time in large numbers, by Victor Gurner Logan van Someren (1896-1976 (van Emden 1950). This collection, which included numerous specimens of adult females, larvae and puparia, was made at the type locality (Ukasi), apparently from the same large, split boulder at which Sharpe collected the original series (van Someren 1994). Van Emden's (1950) description of the adult female and the immature stages, and his views on the phylogenetic position of the family, were based on this material. In the 62 years since the species was last collected, numerous efforts to relocate it at the type locality have been unsuccessful.
Mormotomyia hirsuta bizarre-looking, with a vernacular name that, although somewhat hyperbolic, provides a relatively accurate physical description (Mormotomyia hirsuta = the frightful [hairy] he only representative of the dipterous family Mormotomyiidae M. hirsuta is currently considered the rarest type locality. In addition, although van Emden (1950) reported that larvae were guanobious, and that adults occurred on the rock face inside the cleft, no additional behavioural details were known. Of particular interest is whether the relationship of M. hirsuta with Chiroptera extends beyond larval nutrition alone, to adult phoresy. It is also not known whether other populations exist in similar habitats, or whether Ukasi Hill represents the only (relict) site. Finally, in the light of the contradictory evidence presented by morphological character states of both the larval and adult stages, the this has generated diverse opinions regarding the phylogenetic position of the family & Engel 2005; McAlpine 2007). Advances in molecular phylogeny (Yeates et al. 2007), held promise that the phylogenetic position of Mormotomyiidae within the Diptera could be resolved; a promise, however, that awaited freshly-collected specimens.
made with the noted Kenyan botanist Quentin Luke, who not only knew of the site but was also able to provide GPS coordinates. In July 2008, a short visit to Ukasi (the currently accepted spelling of the area name), was made by one of us (RSC) and colleagues from the National Museum of Natural History (Washington DC, USA) and Iziko South African Museum (Cape Town, RSA) in an attempt to relocate the type lo-Someren's personal observations. Attempts to locate living examples of M. hirsuta were unsuccessful at that time, however, possibly as this visit coincided with Kenya's dry season. Two years later, in November-December 2010, a further expedition was conducted to the site, coinciding with Kenya's short rainy season; the period during which van expedition and follow-up expeditions in February and April 2011. Preliminary data are presented on male-biased sexual size dimorphism and allometric growth of females. Additionally, a list of cleft-inhabiting vertebrate associates of Mormotomyia is evidence of recent genetic bottlenecks, the estimation of effective population size, and the potential existence of additional populations, through the development and chondrial cytochrome oxidase I gene.
Details of larval and puparial morphology are presented elsewhere (Kirk-Spriggs et al. 2011), and molecular data bearing on the phylogenetic placement of Mormotomyiidae within the Diptera will also be presented elsewhere (Wiegmann et al. in prep.).

Site description and visits
Ukasi Hill lies in the immediate vicinity of Ukasi town, approximately midway on the Thika-Garissa road, and the hill and boulder where M. hirsuta was discovered are easily visible from the road. The boulder is positioned at the summit of the hill and is located at 0.81713°S:38.54225°E, at an elevation of 720 m (Fig. 1). The boulder is approx. 20-25 m in height, with a cleft running from top to bottom and more or less north-south, effectively splitting it in two (Figs 2, 3). Additionally, several small, der (Figs 2,4,5). The area is generally hot and very dry, offering only marginal opportunities for agriculture. The vegetation is dry scrub with trees (Greenway 1973), with patches of Acacia/Commiphora woodland with Aloe, Boscia, Maerua, and Sansevieria spp. on the sides and base of the hill. Ukasi lies within the south-eastern branch of the Sahel that reaches as far south as northern Tanzania (Coe 1999).
r -1 December 2011) the weather was hot and dry, but local inhabitants informed us that heavy rains had occurred in the area approximately two weeks previously. It was anticipated that there would be a need to simulate rainfall and the transportation of 120 litres of water to the top of the hill was arranged. This A second expedition was made to the site on 8-9 February 2010 to gather rock samples for geological characterization of the boulder and to explore within the large deposits spilling from the cleft on the north and south sides of the boulder, and up to three meters within the southern opening of the cleft, were examined. Penetration of the northern opening of the cleft was possible to about two-thirds of the length of the entire cleft (see below), over which distance guano was examined for evidence of associates.
A third expedition was conducted on 21 April 2011, when the long rains would normally have begun. Although light rain had fallen in the Ukasi region a few days earlier, the area was hot and dry when visited. Conditions within the large cleft were examined on the northern and southern sides. Evidence of the presence of Mormotomyia and of fresh bat activity was sought within the large cleft and on the ground outside the boulder, encompassing its entire perimeter.

Body measurements
Fifteen individuals of each sex were selected from specimens that had been collected live and held for 2-3 days before being killed by freezing. The largest and smallest specimen of each sex were chosen, while other individuals were selected randomly. Overall body length was not determined due to abdominal shrinkage. Two measurements (as indicated in Figs 6, 7) were taken using easily determined points of reference on the lateral side of the thorax and head. On the thoracic pleura a line was measured (A) from the dorsolateral edge of the anterior of the pronotum to the hindmost articulation of the hind coxa with the thorax. On the head a line was measured (B) stretching from the ventrolateral edge of the cheek to the vertex. A dorsal head measurement (C) was taken from the anterior edge of the frontal plate (easily visible) to the vertex (Fig. 8). Thoracic length (D) (not illustrated here), was measured along the dorsal midline from the anterior edge of the pronotum to the apex of the scutellum. The three right legs of each specimen were removed (when available) and were placed were determined. Overall tarsal length was determined by summing the lengths of individually measured tarsomeres 1-5. Wings were not measured as these were too All measurements were made using ® LAS EZ software, version 1.5.0, on calibrated digital images captured on a ® Leica EZ4D binocular microscope. With the exception of female hind legs, lengths of body parts were distributed normally. Two-sample t-tests were undertaken to compare lengths of female and male body parts, except for hind legs, for which the non-parametric Mann-Whitney U-test was applied. To determine whether body part measurements of males and females were proportionally stable over regression model and the slopes of the lines of Log-Log plots examined (Futuyma 1986). In proportional (isometric) growth the slope approximates 1.0, while allometric growth is indicated when the slope deviates substantially from it; hypermetric when slope >1 and hypometeric when <1 (Shingleton et al. 2007).

Geology
Rock shards were chipped off the cleft boulder and submitted to the Geology Laboratory, University of Nairobi, for petrographic and mineralogical analysis. Standard and atomic absorption spectrometry.
Haplotype diversity, nucleotide diversity per site, and the average number of nucsoftware (Librado & Rozas 2009). The programme TCS v1.21 (Clement et al. 2000), which follows the method outlined by Templeton et al. (1992), was used to determine haplotype network was constructed with the connection limit between nodes calculated at 93 %.
Microsatellite development ® BioSpec-® Roche 454 A total of 441,628 reads were obtained with an average read length of 363 bp. Using were screened for di-, tri-, and tetranucleotide repeats using default settings within the program. Primers were designed using the PRIMER3 software (Rozen & Skaletsky 2000), implemented within the MSATCOMMANDER program, and tagged with a were chosen to be within a 100 to 450 bp range (including M13 tag), within an optimal annealing temperature of 59°C (range 57-63°C), an optimal GC content of ~50 %, low levels of self-or pair-complementarity, and a maximum stability (DG) of 8.0 (Faircloth region for primer design: 2,749 di-, 10,766 tri-, and 864 tetra-nucleotide microsatellites with at least 6, 4, and 4 repeats, respectively. Of these, a total of 40 primer pairs were selected for testing (16 di-, 19 tri-, and 5 tetra-nucleotides). Primer pairs were optimized using 5 individual M. hirsuta in order to minimize DNA depletion but maximize the likelihood of detecting polymorphism. Polymerase PCR buffer, 1.75 mM MgCL 2, 100 mM dNTP's, 1 pmol primer, ~20 ng DNA template, 0.5U Taq DNA polymerase (Apex), and ddH 2 pair was end-labelled with an M13F-29/IRD700 or 800 IRDye tag (Li-Cor Inc). PCR cycling conditions were comprised of an initial denaturation stage of 3 minutes at 95°C, followed by 28 cycles consisting of 30s denaturation at 95°C, 30s at optimal annealing temperature of 59°C, and 30s extension at 72°C, carried out using a Multistop solution (95 % formamide, 20 mm EDTA, bromophenol blue) was added to to loading onto a 25 cm 6 % polyacrylamide gel. Results were analyzed using the GENEPROFILER software (Scanalytics, Inc).
Unambigious PCR fragments within the expected size range exhibiting polymor-M. hirsuta as described above, and screened at these loci.
Genetic data analysis MICROCHECKER v2.2.3 software (Van Oosterhout et al. 2004) was used to assess the likelihood that null alleles, scoring error, and large allele dropout were evident at any locus screened. Basic summary population statistics (allelic diversity, expected and observed heterozygosity) were calculated using the Genetic Data Analysis (GDA) v1.1 software (Lewis & Zaykin 2002). Tests for departures from Hardy-Weinberg F IS , which measures departures from random mating within a population. The null expectation is zero and positive values can indicate two or more demes within the sampled organisms. It can also be an artefact caused by technical problems in detecting heterozygotes. It complements F ST , departures from random mating among populations or demes. F IT , the correlation of alleles in individuals sampled from a metapopulation, is F IT =(1-F IS )(1-F ST ). Given the uncertainty that additional populations exist, F IS and F IT may be interchangeable, however in light of the results, for this manuscript F IS will be used.

Population bottleneck analysis
Following a recent, severe reduction in a population's effective size (i.e., a genetic bottleneck), a characteristic genetic signature of an excess in heterozygosity may be observed at selectively neutral genetic markers, such as microsatellite loci. This occurs because allelic richness declines faster than heterozygosity due to the loss of rare alleles that contribute little to the overall heterozygosity (Cornuet & Luikart 1996). To examine the possibility of the occurrence of a recent population genetic bottleneck, statistical tests, suggested by Luikart et al. (1998), which are implemented in the program BOTTLENECK v1.2.01 (Cornuet & Luikart 1996). As microsatellite loci are unlikely to strictly follow the stepwise mutation model, analysis was run assuming Model (TPM). The latter was run assuming 70 % single-step mutations.

Effective population size
The effective population size (N e in an idealized population that would show the same amount of dispersion of allele pulation under consideration. It is important to note that N e is usually considerably smaller than the absolute population size (N population's ability to respond to microevolutionary forces, such as genetic drift and bottlenecks. Given the inability to accurately determine the census size of the N e were derived following statistical procedures developed for application when only single samples are available. These estimates were generated using the recently-developed approximate Bayesian computation method, implemented in the software ONeSAMP v1.2 (Tallmon et al. 2008) (http://genomics.jun.alaska.edu). When running this program, we used priors of a minimum effective population size of 2, and a maximum effective population size of 2000. While previous methods employing one-sample estimators have proven imprecise or biased (Waples 1991; England et al. 2006), this method has yielded accurate results of effective population size in a vertebrate species following the screening of a comparable number of individuals and microsatellite loci (Tallmon et al. 2008).

Natural history and biology
Living adults of Mormotomyia hirsuta late afternoon of 30 November 2010 the base of the boulder on its northern side was examined. Movements and calls of bats could be heard from within one or more of a thick layer in a small depression at the base of the boulder directly beneath the M. hirsuta were immediately observed scurrying over the guano and along the face of the boulder beneath the crack guano deposit. The surface of the guano deposit was strewn with ca 80-100 dead adults, which presumably had recently emerged, but were unable to access the crack or the large cleft. Live adults were placed in plastic containers containing moist, ab-sorbent paper or into 96 % ethanol for later molecular analysis. Some specimens were also preserved in 75 % ethanol. Larvae and puparia of M. hirsuta were collected from guano, and their treatment is described in Kirk-Spriggs et al. (2011). The following morning the expedition returned to the site at ca 10 am, the day rethe previous day. Although they were not systematically counted, it is estimated that approximately 600-800 live M. hirsuta crack. Short digital movies were captured of adults walking rapidly along the rock surface. 1 The base and inside of the main cleft on the south-facing side of the boulder were also investigated. The opening on that side was considerably wider than that on the north side and allowed relatively easy human access. Thick accumulations of bat guano were also observed there, spilling from the cleft opening, but as this face was in the cleft. Dry guano samples taken at this site later revealed empty puparia, indicating active breeding during favourably wet conditions. The opening of the main cleft on the north side could not be accessed as it was blocked with live and dead trees. However, copious amounts of guano that had been washed out of the main northern opening were searched for adult and immature stages of Mormotomyia, without success.
Characteristics of the boulder and the inside of the main cleft During the second expedition rock shards were chipped off the boulder near the site of the northern and southern openings into the main cleft. The samples are parageneisses with nearly identical mineralogical content (Table 1), and are similar to the Quartz-Felspar-Biotite paragranulites that Wright (1964) recorded from the Ukasi area. The cleft was easily entered on its southern side (Fig. 11), but after a few metres further progress was blocked by a large rock that had fallen from above. In order to enter the northern opening, dead wood blocking the entrance was removed. Inside the inner walls. These were arranged in such a way as to resemble a rising staircase and it was possible to proceed upwards into the cleft for about half its entire length (

Vertebrate associates
To collect evidence of cleft-associated Chiroptera and other vertebrates, guano was closely examined at sites where this had washed out of the cleft, immediately within there were collected inside the cleft, except for the hyrax remains and a single bat skull that were located only 2-3 metres outside the northern opening of the main cleft. Two species of bat, Chaerephon cf. bivittatus (Heuglin) and Tadarida aegyptiaca (E. 3-18). A complete list of the vertebrate species collected is provided in Table 2. During two of the three expeditions to Ukasi, baboons were observed around the boulder. Although evidence of baboon activity is regularly observed in caves, there was no evidence of baboon activity within the cleft. The source of the guano that produced Mormotomyia During the third visit to Ukasi there was no evidence of Mormotomyia. However, same area in a semicircular formation. Some guano fell from this crack while we were observing it, making it clear that bat activity within the crack, or simple gravity, is responsible for at least some of the accumulation on the ground beneath it. Fresh guano was also found just within the opening of the main cleft on its southern side where including within the northern length of the main cleft.
Sexual dimorphism in size of adult characters For all body part measurements, M. hirsuta males were considerably and statistically larger than females, the percentage difference in length ranging from 33-61 % (Table 3). Although overall lengths were not routinely determined, due to abdominal shrinkage, overall body size (excluding legs) of the two largest males was measured. The lengths of these two specimens were 8.96 and 9.26 mm respectively.   (Figs 21, 22), indicating that growth of males was isometric; that is, larger males retained the same proportional size among body parts and leg lengths as smaller individuals. For females, however, the relationship between much lower than 1.0, the expected value for isometric growth (Figs 19, 20). These data sensu Shingleton et al. 2007); individuals with longer legs did not have larger heads and thoraces. Rather, growth appeared to be constrained in these two body parts.
Due to the possibility that these loci may result in anomalous results, these were reallelic diversity and observed heterozygosity appeared moderate (allelic diversity range 3-9, average 6.31; observed heterozygosity range 0.208-0.875 average 0.638) P = < the positive F IS P =0.003), indicating inbreeding within the population. Bottleneck analysis revealed evidence for  are displayed as ovals. Circles represent haplotypes not sampled. Genbank accession numbers for haplotypes A through F are

The van Someren 1948 collection of Mormotomyia
The details of the 1948 collection of M. hirsuta probably differ slightly from the account offered by van Emden (1950). That paper refers only to V.G.L. van Someren using the opportunity of a trip to that part of Kenya to visit Ukasi Hill in the "… 1950: 121). However, the 1948 collection may owe more to chance than to purpose, and to two van Somerens, rather than one. In a letter dated 5 September 1994, G.R. Cunningham van Someren writes (van Someren 1994) that he accompanied his father in the area around Bura along the Tana River, south of Garissa. Heavy rain fell during the trip, and while returning to Nairobi the younger van Someren became unwell, the nearby hill, and V.G.L. van Someren recognized the rock as that previously pointed numbers on and near bat guano. It was also noted in the same correspondence that dual collection was not indicated on the specimen labels.

Natural history and biology
Conditions during the 2010 collection sides of the boulder during the 2010 expedition. Constant daytime shade helped maintain a favourable humidity gradient for larval development within the thick layer of guano that had accumulated outside the northern rock face. In contrast, guano immediately outside and within the larger southern opening was exposed to direct sunlight and very dry conditions, and this location appeared much less favourable for  the northern and southern openings of the main cleft. Rainfall also provides the humid conditions necessary for larval development and is probably the major cue for the hatching of Mormotomyia eggs.
Vertebrate associates of Mormotomyia Microscopic examination of guano pellets collected at the site revealed that these were exclusively composed of insect fragments. The two species of Chiroptera here regarded as the source of guano in the cleft at Ukasi, T. aegyptiaca and C. cf. bivittatus, are closely-related insectivorous species. Until recently, Chaerephon Dobson was regarded as a subgenus of Tadarida Tadarida aegyptiaca is a widespread species, ranging throughout the drier parts of tropical Africa, northern Africa, the Middle East and southern Africa (Kingdon 1984a). In contrast, the distribution of C. cf. bivittatus is more restricted, the species occurring from Ethiopia to Zambia in eastern and central Africa (Kingdon 1984a).
Heterohyrax brucei (Gray) (Procaviidae) the Small-toothed Rock Hyrax, is known from the drier parts of Kenya. Hyrax droppings were concentrated on one of the rock outside the cleft under rock overhangs. The single hyrax skull was located in a layer of bat guano approximately two metres outside the opening of the cleft. Both the Fringe-tailed Gerbil, Gerbilliscus (Taterona) robustus (Cretzschmar) (Muridae) and the Spectacled Elephant Shrew, Elephantulus cf. rufescens (Peters) (Macroscelididae) commonly occur in the drier parts of East Africa, with the former also extending across the Sahel to the Atlantic coast (Kingdon 1984a, b). Elephantulus rufescens commonly utilizes species of the dry-habitat succulent plants Aloe and Sansevieria for shelter and nesting (Kingdon 1984a), and both plants are common on Ukasi Hill. Neither E. rufescens nor G. robustus are particularly associated with caves. The presence of their skulls probably results from predator activity (if so, gerbils were the most common for invertebrates, possibly Mormotomyia. Similarly, one can only speculate on the presence of the bathyergid bones and the Quelea skulls. The Taita Falcon, Falco fasciinucha Reichenow & Neumann (Falconidae), was known to nest on Ukasi Hill (van Someren 1994) and this small raptor preys on birds (Zimmerman et al. 1996), perhaps including the common Q. quelea. Interestingly, starlings (possibly the Red-wing Starling, Onychognathus morio (L.) (Sturnidae)) were also observed within the cleft during the 1948 visit by the van Sobones and feathers we collected. In his 1994 correspondence he recalls his observations Sexual size dimorphism Sexual size dimorphism is common in insects, but females are usually the larger sex (Darwin 1871), size in females normally being positively correlated with fecundity.
Documented size dimorphism favouring males has, however, been described in many species. Increased male body size can result from sexual selection by females, with smaller males (Goldsmith 1987;Goldsmith & Alcock 1993), or in securing resources that make females more receptive to mating (Thornhill 1981). For some species, larger matings of previously uninseminated females, while smaller males having similar copulatory histories lose this ability, presumably because the latter's smaller volume of sperm has been exhausted (Cook 1992). A larger male may prevent access to a female by standing above her, behaviour Bonduriansky (2006) reported for the Australian Telostylinus angusticollis (Enderlein), the males of which enclose females within the span of their legs during copulation and oviposition. Larger males have (Tammaru et al. 1996).
It is curious that van Emden (1950) made no mention of size dimorphism in M. hirsuta Someren in 1948, on which material he [van Emden] made his observations, but did not indicate the sexes or number of specimens examined. It is possible he had too few to notice any obvious differences. Alternatively, specimens from this earlier collection may not have exhibited sexual size dimorphism. Environmental conditions at the site may have differed between 1948 and 2010, affecting growth. In any case, van Emden (1950) paid no attention to size in his paper, either absolute or relative.
It is impossible to know how the size of an individual male is determined by females or other males, but it is interesting to speculate on the function of the considerably longer, hair-like setae covering the greater part of the male (compare Figs 9 & 10). If the length of the setae increases proportionally to the size of an individual, then large males may appear larger still, lending them a further advantage if size is involved in sexual selection of males by females. Conversely, any increase in the perception of by predators, which often differentially prefer larger insects (Whitman & Vincent M. hirsuta is unknown. Its explanation depends on future in situ behavioural observations of live individuals.

Female allometry
In contrast to the males, females with longer legs do not have proportionally larger body parts (at least not the head and thorax). The hypothesis is suggested (subject to future testing on immobilized or freshly-killed females, prior to abdominal shrinkage), that an increase in female body size is limited to abdominal growth as an adaptation growth of the head and thorax is uncoupled from that of the abdomen and legs. If this hypothesis is correct, then, presumably, in conditions favourable to larval development after which the genetic and physiological mechanisms controlling growth of the imaginal discs for these body parts are inhibited (Shingleton et al. 2007), while those of the abdomen (and contents) continue to be active. Females with larger abdomens, but proportionately smaller heads and thoraces, would be produced.

Genetic variation within the Ukasi population
Despite the relatively small number of individuals available for molecular analysis, the genetic samples exhibited remarkable diversity at both the nuclear (allelic diversity and genetic heterozygosity) and mitochondrial (haplotype number and diversity) level. This is somewhat surprising given the nature of this population. Under an island model, it should be expected that a species would exhibit lower levels of genetic diversity compared to mainland populations of the same species (Frankham 1997). While the is available for direct genetic comparison. However, when compared to populations of other dispersal-limited invertebrates existing in relative, but not complete, isolation, diversity appears comparable (Crissman et al. 2010;Booth et al. are contradictory to those predicted, given the population's apparent instability, as indicated by the evidence for a recent genetic bottleneck, its ephemeral nature, and likely re-establishment from minimal numbers of breeding individuals following population crashes, as indicated by the low estimate of effective population size. These data therefore suggest either an extremely stable population of randomly breeding individuals living within the cleft and cracks of the boulder, or genetic exchange from neighbouring, as yet undetected, populations. The former hypothesis is not fully supported due to the relatively low estimates of N e that, as a result of the likelihood of overlapping generations, more accurately provides an estimate of the effective number of breeding individuals theoretically necessary to yield a population with comparable levels of genetic characteristics. As the mating system and reproductive output of this species become known, the estimates of N e genetic diversity of an isolated population over time. The latter hypothesis, however, mitochondrial analysis. At the mitochondrial level, we see moderate haplotype diversity, comparable to or greater than that observed in both island and mainland populations of other species (De La Rúa et al. 2001;Smith et al. 2006;McGaughran et al. predication, missing intermediate mtDNA haplotypes may exist in as yet undetected populations, or, alternatively, may have been lost from the gene-pool following recent genetic bottlenecks and/or population extinctions. It is, therefore, tempting to speculate the observed variation. Within the Ukasi population, genetic evidence also indicates the occurrence of inbreeding. This is not entirely unexpected following population re-establishment postbottleneck, however it may also indicate the presence of multiple demes or breeding homozygotes supports this theory. This apparent Wahlund effect is unlikely to result from the presence of null alleles, given that those loci with the genetic signature of possessing null alleles were removed prior to population genetic analysis. While this cannot be addressed further with the current data set, it is possible that this could arise through a number of population processes. These include niche/habitat partitioning, reproductive isolation between successive cohorts, or indeed, as suggested earlier, the occurrence of breeding individuals from other, as yet undetected, populations. Regardless of the population process responsible, the genetic estimate of effective population size suggests that the Ukasi population, whether founded from one or more groups, has resulted from a small number of individuals, supporting the positive F IS estimate. Empirical studies utilizing the one-sample method for effective population size estimation have proved the precision of this method (Maudet et al. 2002;Tallmon et al. (Waples 2006) have yielded comparable estimates (Aspi et al. 2009). We therefore do not doubt the current estimate generated, however we recognize that future studies incorporating additional samples, and temporal sampling, would prove valuable for At this time we can only speculate on possible modes of dispersal. Mormotomyia has none of the morphological adaptations for clinging onto bats' fur exhibited in other et al. 2011). It is unlikely, therefore, that adult Mormotomyia of captured, living bats. One possibility is that M. hirsuta eggs are transported with guano on the feet of birds. Seeds trapped in mud are known to be dispersed by birds in this way (Darwin 1872;van der Pijl 1969) and Mormotomyia eggs are probably capable of remaining dormant for extended periods (Kirk-Spriggs et al. 2011). The Mormotomyia and other of food. Given the supposed isolation of the species (for millennia) there would have been multiple opportunities for events such as this to have occurred, even if other po-As evidenced by the excess of heterozygosity observed at multiple loci following both the Sign and Wilcoxon tests, this population appears to have undergone a signiare only detectable for a short period following the decline, this reduction is likely to have occurred within the last 0.2 to 4.0 N e generations, where N e is the effective population size (Luikart & Cornuet 1998). If, in fact, this cave population is isolated, the long-term effect on this species' evolutionary potential could ultimately be detrimental (Frankham et al. 1999). The detection of a genetic bottleneck is consistent with the Mormotomyia during previous collecting expeditions undertaken throughout the 20 th century.
The remarkable diversity observed at both the nuclear and mitochondrial level, in concert with the evidence for a recent genetic and thus demographic bottleneck, suggests that this population may in fact exist within a meta-population framework. Indeed, if past collection expeditions failed to collect specimens due to temporal extinction events within the cave, this would be explain their patchy appearance over time. The large number of microsatellite DNA markers we developed will be extremeboth temporally, throughout seasons and across years and, potentially, among other populations if, indeed, they are found in nearby localities in Kenya and other East African countries.

Conservation status of Ukasi Hill
As noted above, the area of Ukasi and its surroundings is hot and dry and, at best, provides only marginal prospects for agriculture. Wright (1964) stated that the mean annual precipitation on the western boundary of the Ndenyini area (where Ukasi is ca 381 mm). Rainfall data for Sosoma, approximately 14.5 km southwest of Ukasi, was 330 mm between 1 January 1953 and 5 June 1954, and 445 mm between 19 April 1956 and 15 January 1957 (Wright 1964). At the time of Sharpe's discovery of M. hirsuta the area was sparsely inhabited, mostly by nomadic groups, although Ukasi itself had a small permanent human population prior to 1956 and, at that time, an impoundment already existed at the southern base of the hill (Wright 1964). Since then, as elsewhere, population has increased throughout the for charcoal. Animal tracks are evident on the hill and it is likely that goats browse on vegetation, probably up to the entrance of the cleft. The fact that M. hirsuta was found in large numbers outside of the cleft, suggests that, currently, the Ukasi population is relatively robust. Nonetheless, the site is the only documented home of one of the the type habitat. Both Courtney et al. (2009) andStuckenberg (2009) M. hirsuta. Accordingly, the site deserves special protection and the species should appear in the IUCN Red List of Threatened Species™.

Future research
The rediscovery of M. hirsuta opens up several promising avenues of research. This paper and that of Kirk-Spriggs et al. (2011) offer some insights into the biology and natural history of M. hirsuta. Additional research will test the reproducibility of the preliminary conclusions regarding male-biased sexual-size dimorphism and female allometry, and will determine the evolutionary advantages for maintaining these.
Knowledge of the precise site of M. hirsuta development and the seasonal appearance M. hirsuta pass the very hot, dry seasons? Is M. hirsuta phoretic either on bats or, less likely, resident birds? Which bat species are resident in the cleft and responsible for paper from skulls collected within the cleft?
Freshly-preserved material of this enigmatic species has now been made available to molecular geneticists/ does Mormotomyiidae belong in the Diptera tree of life, and secondly, is the Ukasi of the phylogenetic placement of the Mormotomyiidae will be addressed elsewhere (Wiegmann et al. in prep.). In this paper, data on genetic variation revealed a surprising covered populations of this, or other Mormotomyia species? The numerous hills and inselberge spread about the landscape of eastern Kenya, of which Ukasi Hill is but one representative, are the visible remnants of ancient Precambrian rocks of the basement system that underlie the entire country (Cole 1950). Over geological time these other ancient rocks may have experienced the conditions that lead to the fracturing of rock, producing clefts and cracks similar to that found at Ukasi. Such habitats may conceal other populations of M. hirsuta or its relatives. Clearly, the opportunities for research on Mormotomyia are considerable, and the preliminary results presented here offer only a glimpse of the possibilities.