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In the course of the faunistic inventory in Wadi Ramm Protected Area, a total of 34 species of reptiles representing nine families (Gekkonidae, Chamaeleonidae, Agamidae, Lacertidae, Scincidae, Varanidae, Leptotyphlopidae, Colubridae, and Viperidae) were recorded from different habitats in Wadi Ramm and its closest vicinity. Three species (Lacerta cf. kulzeri, Chamaeleo chamaeleon, and Ablepharus rueppellii) are considered to represent relicts from earlier, more humid periods. Habitat preferences for collected species are included.

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The present work provides a list of all amphibians and reptiles recorded from Iraq up to 2014. It includes 115 species (105 species of reptiles and 10 species of amphibians) dating back to 25 families (20 families of reptiles and 5 families of amphibians). Conservation status of each species was mentioned.

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Oxygen consumption levels and metabolic rate temperature curves of various lizard species from three different climatic regions were examined in relation to ambient temperature. The species used in this research were as follows: Anguis fragilis, Lacerta vivipara, Lacerta agilis (cool temperate species); Blanus cinereus, Podarcis hispanica, Podarcis lilfordi brauni, Podarcis lilfordi lilfordi, Podarcis muralis, Psammodromus algirus, Tarentola mauritanica (warm temperate species); Chalcides ocellatus, Acanthodactylus opheodurus, Acanthodactylus schmidti (desert species). A double chamber volumetric closed system was used to measure the resting oxygen consumption of the lizards. Acute oxygen consumption determinations were made, that is the lizards were not allowed to acclimate to the test temperatures. Interspecific differences in levels of resting oxygen consumption and in the characteristics of the metabolic rate temperature curves were examined in relation to methods of thermoregulation and in relation to the ecology of the respective species. Evidence for `temperature dependent shifts` and `low thermal dependence` was found in the metabolic rate temperature curves of some species. A diminishing Q10 at or below the voluntary body temperatures suggests some degree of metabolic homeostatsis and energy conservation.

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An extensive review on the taxonomic status, occurrence, geographical distribution, and the IUCN conservation status of 122 species/taxa (10 amphibians and 112 reptiles) belonging to 71 genera (8 genera of amphibians and 63 of reptiles) and to 25 families (5 families of amphibians and 20 families of reptiles) was made. As a part of Iraq’s unique biota, the knowledge of the herpetofauna of Iraq is poorly discovered and requires extensive field surveys, further research, and explorations in order to create full frame knowledge of its status and conservation.

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A total of 44 species of amphibians and reptiles are reported from Al Madinah Al Munawwarah Province, Saudi Arabia. They include two species of amphibian in two families (Bufonidae and Dicroglossidae) and 42 reptiles belonging to 16 families (Agamidae, Boidae, Chamaeleonidae, Colubridae, Elapidae, Gekkonidae, Lacertidae, Lamprophiidae, Leptotyphlopidae, Phyllodactylidae, Psammophiidae, Scincidae, Sphaerodactylidae, Varanidae, Typhlopidae, and Viperidae). Platyceps sinai, Psammophis sibilans, Rhynchocalamus melanocephalus, are recorded for the first time to the herpetofauna of Saudi Arabia. Range expansion for Euphlyctis ehrenbergii and Acanthocercus adramitanus to northern Saudi Arabia is reported. Our records expand the known distribution range of the Arabian Cobra, Naja arabica, further northwest

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Seventeen (17) and twenty-two (22) species of terrestrial reptiles were recorded from ‘Uruq Bani Ma’arid and Harat al Harrah protected areas, respectively. Eight sites in ‘Uruq Bani Ma’arid and eleven sites in Harat al Harrah were surveyed for the presence of reptiles. A comparison between the two protected areas’ reptile fauna is provided, with brief descriptions of their habitat preferences. Uromastyx aegyptia, categorised by the IUCN Red List as Vulnerable, occurs in both protected areas. Ptyodactylus puiseuxi is a new species record for the herpetofauna of Saudi Arabia. This study indicates the importance of protected areas within Saudi Arabia for the conservation of reptile biodiversity, the need for extension of the protected area network and additional biodiversity surveys in other regions. Studies on species richness, biology and population size for endangered species should be a priority for future studies.

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Tathleeth governorate in Aseer region of southwestern Saudi Arabia has been surveyed for 22 lizard species belonging to 6 families throughout three years started from 2015. A total of 412 specimens of these lizards were encountered and identified. Gekkonidae represented the major family inhabiting the region comprising more than 50% of the collected lizards. Agamidae was represented by 5 species comprising more than 23% of the recorded lizards. The other four families (Lacertidae, Scincidae, Chamaeleonidae and Varanidae) comprised approximately 20% of all the collected lizards. The current survey could be used as conservational clue for the herpetofauna of Tathleeth.

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We surveyed the historical Faid Hema, Ha’il region in Saudi Arabia and identified 22 species of reptiles (17 lizards and five snakes). We recorded for the first time nine reptiles (six lizards and three snakes) in the Faid Hema. Of these, one lizard, Mesalina adramitana, and two snakes, Cerastes gasperetti and Walterinessia aegyptia, were reported for the first time for the entire Ha`il region. We recorded 50% of all species for the entire study area at one site, which may be because it had three different habitat types near it (the Jannin mountain, soft soil, and firm, sandy soil). The next highest number of species we found was at an open site with firm, sandy soils and with gravel (containing 45.5% of the total species recorded), followed by a site that contained only sand (36.4% of the total). The lowest number of species was reported at an agricultural site, with only 13.6% of the total species found.

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In this study, we identified the diversity of the freshwater, marine and terrestrial herpetofauna of the State of Kuwait. It consists of a total of 45 extant species; 44 species of reptiles and a single species of amphibian according to recent updated taxonomic studies. All specimens of reptiles collected and held in American and European natural history museums are documented. Four species are added to the herpetofauna of Kuwait: Chalcides ocellatus, Hydrophis lapemo ides, Hydrophis viperina, and Trapelus agnetae.

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Some 500 Dhofar reptiles and amphibians are discussed and a minimum of 48 terrestrial species recognised for the area of which 5 were previously undescribed; these are a gecko, Hemidactylus lemurinus, and the lacertids Acanthodactylus felicis, A. opheodurus,A. masirae and Mesalina ayunensis; a new subspecies of gecko from north Oman, Bunopus spatalurus hajarensis is also reported. Various other species are reviewed; it appears that Bunopus abudhabi is a synonym of B. blanfordi, which is probably conspecific with B. tuberculatus, Hemidactylus parkeri is regarded as a subspecies of H. turcicus, the Arabian agamas of the Agama cyanogaster group are shown to include 2 species to which the names adramitana and yemenensis are applicable although their status relative to African populations in the group is not clear; A. jayakari is conspecific with A. flavimaculata, and A. neumanni with A. sinaita; Chamaeleo chamaeleon orientalis is similar to more northern populations of C. chamaeleon but C. c. arabicus is very well differentiated and may be a separate species, the use of genitalia in the classification of Acanthodactylus is emphasised and A. arabicus, A. blanfordi and A. schmidti are all given full species status; the recognition of Mesalina as a genus indepemdemt of Eremias is confirmed, it is suggestes that Atractaspis engeddensis may be conspecific with A. microlepidota and that Lytorhynchus gaddi is a synonym of L. diadema; the distinctive population of Echis carinatus in Dhofar appears to be closely related to those in south-west Arabia and adjoining Africa but animals from northern Oman and the rest of south-west Asia are very different. Additional specimens are reported of Bunopus s. spatalurus and Coluber thomasi, both previously known from only 2 individuals. Geographical variations of a number of species is discribed including 3 geckos that show very considerable differences within southern Dhofar: Hemidactylus homocolepis, H. yerburii and Tropiocolotes scorteccii. Observations on the ecology of many species are noted, especially for the aberrant gecko genus Pristurus, one species of which, P. carteri, behaves like a small, ground-dwelling diurnal agamid. Resource partition, at least amongst the lizards, appears to be largely based on parameters of time, food (especially prey size), hunting method and space. A number of forms occourring in both noreth Oman and Dhofar show differences in niche in the two areas apparently related to the presence of absence of a competitor. Several species are recorded from Dhofar for the first time including Bunopus spatalurus, Hemidactylus flaviviridis, H. turcicus parkeri, Pristurus minimus, Agama adramitana, Acanthodactylus boskianus,Mabuya tessellata, Leptotyphlops macrorhynchus and Lytorhynchus diadema. The herpetofauna of the area can be divided into a largely northern element of desert-adapted forms widespread in the Arabian peninsula and a more peripheral element in the south which shows considerably more affinity to south-west Arabia than to northern Oman. No reptile of amphibian endemics occur in the forested areas of Dhofar but 3 species present in the drymesic habitats on the north side of the mountains may be restricted to the region. Acanthodactylus opheodurus, Acanthodactylus felicis, Acanthodactylus masirae, Acanthodactylus boskianus, Acanthodactylus schmidti, Mesalina adramitana, Mesalina ayunensis.

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The ability to shed (autotomize) all or part of the tail, usually in response to predator attack, and often to subsequently regenerate it is widespread in lizards and amphisbaenians and also occurs in a few snakes and in the tuatara. Most species possess a sophisticated intravertebral autotomy mechanism which seems to be primitive in the Squamata. This appears to have been independently lost in members of many groups, but some agamids and snakes have regained the ability to shed their tails by a simpler intervertebral means and a -number of agamids have also redeveloped tail regeneration as well. Breakable tails are used to evade capture in two main ways: by enabling reptiles to break away from predators that have grasped them by the tail and by providing a distraction which deflects the attention of the attacker away from the vulnerable head and body. It is argued that loss of caudal autotomy has occurred when the costs of tail shedding outweigh its benefits. Likely costs include the expense of regrowing the tail and the loss of a variety of possible tail functions that may cause partial incapacitation, at least until the tail regenerates. Benefits of autotomy are liable to be low if predation is rare, if the animal is able to protect itself effectively in other ways, if it is too slow to evade further pursuit after the tail is shed, or if the tail is small or unpalatable and consequently not likely to distract a predator. Benefit variation may well be greater than cost variation and therefore more important in initiating the loss of autotomy mechanisms. Many taxa that do not shed the tail appear to conform to the above interpretation, but in some cases, such as the Platynota, Agamidae and Chamaeleonidae, lack of intravertebral autotomy may reflect the history of these groups rather than being a direct result of present ecological pressures. The distribution of intervertebral autotomy in the Agamidae suggests that it may have evolved only in rather special circumstances where tail fragility is advantageous even in the absence of the ability to regenerate. Restriction ot autotomy planes to the tail-base, so that the whole organ is lost, a condition found in a number of relatively slow-moving geckoes, is interpreted as a means of ensuring that enough of the tail is shed to distract a predator from further pursuit. The stimulus necessary to induce autotomy can vary rapidly in individual lizards and at least some of these changes probably maximize the effectiveness of the tail-shedding mechanism. Differences in the readiness with which all or part of the tail is shed exist between species and are likely to reflect the balance of costs and benefits in particular cases. Variations in incidence of broken tails between species and populations may be due to such differences in fragility but many other factors may play a part, including the age structure of samples, incidence of unsuccessful attacks by predators and ability to evade predators after autotomy. There is a clear tendency for climbing lizards, especially those living on rock surfaces, to have higher incidences of broken tails than ground-dwelling species, perhaps because the tail is usually less important in locomotion in the first group. Many lizards possess conspicuously coloured tails and tail movements that seem likely to help distract attention from the head and body. Conspicuous tail colouring is more frequent and often better developed in young animals, which tend to be more vulnerable than adults, and in active species from open habitats where crypsis may not always be very effective. Conspicuous tails usually have contrasting light and dark areas in nocturnal forms but are often a single bright colour in diurnal ones, probably reflecting the visual capacities of their respective predators. The predominance of blue tails in day-active species may be because this colour is striking close to but not very arresting at a distance, so it may not attract predators from far away while still drawing their attention at close quarters.

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Arabia, including the arid lowland regions of Jordan, Syria, Iraq and southwest Iran, has approximately 128 species of terrestrial reptiles and about 7 of amphibians. Endemicity is high, 55% of species being largely or entirely confined to the area. Abrupt faunal discontinuities are present between Arabia and neighbouring regions, namely the Horn of Africa, the Sahara desert and the relatively mesic areas to the north. However, there must have been substantial interchange with these areas in the past. Within Arabia, the main Zoogeographie division is between the arid regions occupying most of the peninsula and much smaller, often more mesic areas of endemicity in the south. The former are mainly occupied by Saharo-Sindian taxa and have rather more affinities with the Sahara than to arid regions east of Arabia. Southern areas of endemicity include: 1. The southwestern coast, with affinities to the Horn of Africa and the inland deserts of Arabia. 2. The southwest and southern highlands which share a number of forms with northeast African relationships but differ significantly, the former having more, often endemic species with African affinities and a number with relatives in the Mediterranean and other northern mesic regions. The drier southern mountains have their own endemics, some of which have representatives in the öiddat al-HaräsIs area to the east. 3. The north Oman mountains also possess distinctive species and populations, some of which are related to forms in the less arid parts of the Iranian area. Finally there are a number of mesic forms distributed around the periphery of Arabia, and populations at oasis sites in the arid region which are probably relicts of forms more widespread in Quaternary pluvial phases.

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Kurze Vorstellung der drei Eidechsenarten Acanthodactylus felicis, A. opheodurus und Mesalina ayunensis aus der omanischen Provinz Dhofar.

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The physical geography of Iraq is summarised. Using data from the relevant literature and current information from the Internet, a very provisional checklist of Iraqi amphibians and reptiles is presented. Ten amphibian species are reported for Iraq, and exactly 100 reptile species.

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In the present work, we use an exceptional database including 5,359 records of 101 species of Oman’s terrestrial reptiles together with spatial tools to infer the spatial patterns of species richness and endemicity, to infer the habitat preference of each species and to better define conservation priorities, with especial focus on the effectiveness of the protected areas in preserving this unique arid fauna. Our results indicate that the sampling effort is not only remarkable from a taxonomic point of view, with multiple observations for most species, but also for the spatial coverage achieved. The observations are distributed almost continuously across the two-dimensional climatic space of Oman defined by the mean annual tempera- ture and the total annual precipitation and across the Principal Component Analysis (PCA) of the multivariate climatic space and are well represented within 17 out of the 20 climatic clusters grouping 10% of the explained climatic variance defined by PC1 and PC2. Species richness is highest in the Hajar and Dhofar Mountains, two of the most biodiverse areas of the Arabian Peninsula, and endemic species richness is greatest in the Jebel Akhdar, the highest part of the Hajar Mountains. Oman’s 22 protected areas cover only 3.91% of the country, including within their limits 63.37% of terrestrial reptiles and 50% of all endemics. Our analy- ses show that large areas of the climatic space of Oman lie outside protected areas and that seven of the 20 climatic clusters are not protected at all. The results of the gap analysis indi- cate that most of the species are below the conservation target of 17% or even the less restrictive 12% of their total area within a protected area in order to be considered adequately protected. Therefore, an evaluation of the coverage of the current network of protected areas and the identification of priority protected areas for reptiles using reserve design algorithms are urgently needed. Our study also shows that more than half of the species are still pending of a definitive evaluation by the International Union for Conservation of Nature (IUCN).

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We have updated the list of the lizard species present in Qatar and produced the first distribution maps based on two field surveys in 2012 and 2013. We used the QND95/Qatar National Grid with a grid of 10 × 10 km squares for mapping. Our results show the occurrence of 21 lizard species in Qatar, from the 15 species indicated in the last biodiversity report conducted in 2004. The most abundant family found in Qatar is Gekkonidae with nine species (Bunopus tuberculatus, Cyrtopodion scabrum, Hemidactylus robustus, H. flaviviridis, H. persicus, Stenodactylus arabicus, S. slevini, S. doriae, Pseudoceramodactylus khobarensis), followed by Lacertidae with four species (Acanthodactylus schmidti, A. opheodurus, Mesalina brevirostris, M. adramitana), Agamidae with three species (Trapelus flavimaculatus, Uromastyx aegyptia, Phrynocephalus arabicus), Scincidae with two species (Scincus mitranus, Trachylepis septemtaeniata), and Varanidae (Varanus griseus), Sphaerodactylidae (Pristurus rupestris) and Trogonophiidae (Diplometopon zarudnyi) with one species each. The species richness fluctuated largely across Qatar between one and eleven species per grid square. We believe that the lizard fauna records in Qatar are still incomplete and that additional studies are required. However, our study here fills a gap concerning lizard biodiversity knowledge in the Gulf Region.

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Acanthodactylus opheodurus ARNOLD 1980 ist im Gebiet zwischen Al Ain und dem Jebel Hafit (Emirat Abu Dhabi, Vereinigte Arabische Emirate) lokal regelmäßig anzutreffen, In der heißen Jahreszeit ist die Art ausschließlich morgens (07.30 – 10.30) an der Oberfläche aktiv und erbeutet die Nahrung (vorwiegend Ameisen) sowohl aktiv jagend als auch als Lauerjäger. Zum Zweck der Trhermoregulation, Beutefang und Feindvermeidung wird am häufigsten das Requisitangebot buschförmiger Haloxylon salicornicum und Acacia tortilis genutzt.

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Zoogeographically, the Jordanian herpetofauna is heterogeneous, originating from four biogeographical regions (Oriental, Palearctic, Saharo-Sindian, and Afrotropical) and occupying four different ecozones. Ninetythree species and subspecies of amphibians and reptiles are recorded from Jordan, showing different distribution patterns. The Mediterranean ecozone harbours the highest number (35) of recorded species, followed by the Sudanian Tropical penetration zone (16), and the Badyiah ecozone (12), respectively. Jordan is not separated by natural boundaries from the surrounding countries, which prevents the operation of isolation mechanisms, and seems to result in the absence of endemism. There are, however, three areas of endemism within the Eastern Mediterranean region taken as one whole unit: the Badyiah shared by Syria, Iraq, Saudi Arabia and Jordan, the northern part of the Mediterranean ecozone shared by Lebanon, Israel, Syria and Jordan, and southwest Jordan, Israel and Sinai. Some Palearctic species such as Coluber schmidti and C. ravergieri are relicts of the postglacial period and continue to survive in refugal enclaves with delicate ecological patterns. The distribution of some species, such as Bufo viridis, Mauremys caspica rivulata, Natrix tessellata, Coluber ventromaculatus, C. jugularis asianus, Walterinnesia aegyptia, and Vipera palaestinae, has been greatly influenced by climatic as well as anthropogenic changes.

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The lizard fauna of Jordan is very diverse and forms 55.5% of the terrestrial herpetofauna of the country. Lizard species of Arabian origin form the highest percentage (43%) of the lizards, followed by Saharo-Sindian (35%), Palaearctic (20%) and only 2% with Afrotropical affinities. 69.1% of the lizard species inhabit two ecozones: Badia (Eastern Desert); and Wadi Araba and Wadi Rum. The Badia may form the focal point for the evolution of certain Acanthodactylus species. Jordan forms the southernmost limit of the distribution of some Palaearctic species (i.e. Lacerta media, L. laevis, Pseudopus apodus) and they inhabit the Mediterranean ecozone. The presence of diverse habitats in Jordan allowed certain allopatric congeneric species of the genus Ptyodactylus to live in isolation from one another. Southern Jordan and Wadi Rum are part of the Levantine land bridge and act as a “biogeographical filter”. Most of the species found in Wadi Rum are of Arabian affinities and their distribution does not extend towards the west.

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Zoogeographically, the Syrian herpetofauna is heterogeneous, originating from four biogeographical regions (Oriental, Palearctic, Saharo-Sindian and Afrotropical) and is characterized by the presence of five ecozones. 50% of the terrestrial herpetofaunal species are of palaearetic affinity while 32.3%, 14.6% and 3.1% are of Saharo-Sindian, Arabian and Afrotropical affinities, respectively. Five records of reptiles are new to the Syrian fauna: Emys orbicularis, Acanthodactylus opheodurus, Acanthodactylus schreiben syriacus, Pseudotrapelus sinaitus, Uromastyx aegyptia microlepis, and Lepto- typhlops macrorhynchus; Coluber rogersi is reported for the second time. An updated list of the herpetofauna of Syria is given.

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The terrestrial reptiles oft he UAE the lizards, snakes and a single species of amphisbaenian or worm lizard. There are no extant native crocodiles, tortoises or freshwater terrapins. Lizards, snakes and amphisbaenians are all classified under the reptilian order Squamata, in the suborders Sauria, Serpentes and Amphisbaenia respectively. Characterised by their dry, scaly skin, which protects them from drying out, and by their reliance on external heat sources to maintain their body temperatures, reptiles are well-suited to hot and arid areas. In Arabia, reptiles are a major component of the desert and mountain ecosystems and a total of at least 54 species of terrestrial reptile are found in the UAE. So far, a comprehensive handbook covering all of the UAE reptiles in detail is not available. The Handbook to Middle East Amphibians and Reptiles (Leviton et al. 1992) does not cover the species of the mountains or Northern Emirates and gives little information on natural history. Useful general sources of information are Wild about Reptiles (Jongbloed 2000) and Terrestrial Reptiles of Abu Dhabi (Baha El Din 1986).

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Mitochondrial DNA sequences consisting of 645 sites from the 12S rRNA and 16S rRNA genes were used to estimate the phylogeny of 15 of the 32 species of spiny-footed lizards Acanthodactylus. The resultant tree has similarities to that produced from a differentially weighted data set of 32 morphological characters but there are also significant differences. However, combined analysis of molecular and morphological data sets produces the same tree topology as DNA sequence alone. The molecular data confirm that there are distinct eastern and western clades within Acanthodactylus, but place A. boskianus in the former while the A. scutellatus group constitutes a third clade. Species for which only morphological information is available were integrated with the combined tree to give a provisional phylogeny for 31 species. This phylogeny indicates that the ancestor of existing Acanthodactylus probably originated in south-west Asia and that North Africa was invaded by more than one lineage of the genus. It also suggests that soft aeolian sand habitats may have been independently occupied more than once. Molecular data provide independent evidence that the differential weighting of morphological characters in past analyses was appropriate.

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The distribution of herpetofauna on the Arabian Peninsula is generally poorly known, particularly in Saudi Arabia. The King Abdulaziz Royal Nature Reserve (KARNR) in east-central Saudi Arabia is in an area predicted to have high reptile species richness, yet there is no baseline reptile checklist for the reserve. Knowing which species occur within a protected area is vital for ensuring that conservation strategies and long-term monitoring are effective. Here, we provide the first detailed list of reptile fauna occurring in the KARNR. This study recorded a total of 31 species from 1,551 observations, including 25 lizards and six snakes. A desktop study identified three additional species, bringing the total number of herpetofaunal species known in the KARNR to 34. Two of the species found in the reserve are of conservation concern: Uromastyx aegyptia (VU) and Tropiocolotes wolfgangboehmei (DD). Through species accumulation curves we were able to determine that the sampling methods implemented during the survey were adequate, and we predicted that the species richness of the reserve is likely as much as 38 species. Prior to this study, only 82 reptile records (30 species) were known from the study area, so we add a significant number of new records to the reserve and an additional four species that were previously unknown from the region.

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In this third paper on the herpetofauna of Oman, three families are treated: eleven Lacertidae, six Scincidae and one varanid. New records, notes on ecology and localities are combined with data from literature.

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Aim To map and assess the richness patterns of reptiles (and included groups: amphisbaenians, crocodiles, lizards, snakes and turtles) in Africa, quantify the overlap in species richness of reptiles (and included groups) with the other terrestrial vertebrate classes, investigate the environmental correlates underlying these patterns, and evaluate the role of range size on richness patterns. Location Africa. Methods We assembled a data set of distributions of all African reptile species. We tested the spatial congruence of reptile richness with that of amphibians, birds and mammals. We further tested the relative importance of temperature, precipitation, elevation range and net primary productivity for species richness over two spatial scales (ecoregions and 1° grids). We arranged reptile and vertebrate groups into range-size quartiles in order to evaluate the role of range size in producing richness patterns. Results Reptile, amphibian, bird and mammal richness are largely congruent (r = 0.79–0.86) and respond similarly to environmental variables (mainly productivity and precipitation). Ecoregion size accounts for more variation in the richness of reptiles than in that of other groups. Lizard distributions are distinct with several areas of high species richness where other vertebrate groups (including snakes) are species-poor, especially in arid ecoregions. Habitat heterogeneity is the best predictor of narrow-ranging species, but remains relatively important in explaining lizard richness even for species with large range sizes. Main conclusions Reptile richness varies with similar environmental variables as the other vertebrates in Africa, reflecting the disproportionate influence of snakes on reptile richness, a result of their large ranges. Richness gradients of narrow-ranged vertebrates differ from those of widespread taxa, which may demonstrate different centres of endemism for reptile subclades in Africa. Lizard richness varies mostly with habitat heterogeneity independent of range size, which suggests that the difference in response of lizards is due to their ecological characteristics. These results, over two spatial scales and multiple range-size quartiles, allow us to reliably interpret the influence of environmental variables on patterns of reptile richness and congruency.

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A review of a recently published analysis of the zoogeography of the Syrian herpetofauna is presented. Nine taxa are deleted from the faunal list, six subspecies and species respectively are added, in three the occurrences are questionable and in two the taxonomy and systematic^ are discussed; moreover, several additional `doubtful` Syrian reptiles are listed. Critical comments are made on the numerical analysis, the ecozones of the country and the zoogeographical affinities o f its herpetofaunal elements.

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As part of the conservation efforts in the northern Red Sea development areas, the nests of Osprey (Pandion haliaetus) have been moved, out of nesting season, to relocate them away from areas where they would be damaged or disturbed by development. During these operations, a significant association with these structures and lizard species has been identified. The implications are threefold. Primarily, the nests may provide an important refuge habitat for these species on the uninhabited islands in the Red Sea. Secondly, as Osprey nests are avoided during surveys to ensure the species is not disturbed, there is a potential under reporting of the populations of small reptile species on the islands. This in turn has implications for wider population assessments and their consideration in the environmental impact assessment process. Thirdly, the potentially high numbers of Stenodactylus doriae and Acanthodactylus sp (likely A. opheodurus) in close proximity or a potentially loose colony structure in the nests is at odds with the published and accepted behavioural norm of these usually territorial species. Records are from initial observations only and further more structured research is required. Further investigation into this association can only be recorded on an opportunistic approach, as Osprey nests (and particularly active nests) should only be disturbed where all other avoidance mitigation has been exhausted.

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Aim Body size is instrumental in influencing animal physiology, morphology, ecology and evolution, as well as extinction risk. I examine several hypotheses regarding the influence of body size on lizard evolution and extinction risk, assessing whether body size influences, or is influenced by, species richness, herbivory, island dwelling and extinction risk. Location World-wide. Methods I used literature data and measurements of museum and live specimens to estimate lizard body size distributions. Results I obtained body size data for 99% of the world`s lizard species. The body size–frequency distribution is highly modal and right skewed and similar distributions characterize most lizard families and lizard assemblages across biogeographical realms. There is a strong negative correlation between mean body size within families and species richness. Herbivorous lizards are larger than omnivorous and carnivorous ones, and aquatic lizards are larger than non-aquatic species. Diurnal activity is associated with small body size. Insular lizards tend towards both extremes of the size spectrum. Extinction risk increases with body size of species for which risk has been assessed. Main conclusions Small size seems to promote fast diversification of disparate body plans. The absence of mammalian predators allows insular lizards to attain larger body sizes by means of release from predation and allows them to evolve into the top predator niche. Island living also promotes a high frequency of herbivory, which is also associated with large size. Aquatic and nocturnal lizards probably evolve large size because of thermal constraints. The association between large size and high extinction risk, however, probably reflects a bias in the species in which risk has been studied.

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Aim Temperature influences most components of animal ecology and life history – but what kind of temperature? Physiologists usually examine the influence of body temperatures, while biogeographers and macroecologists tend to focus on environmental temperatures. We aim to examine the relationship between these two measures, to determine the factors that affect lizard body temperatures and to test the effect of both temperature measures on lizard life history. Location World-wide. Methods We used a large (861 species) global dataset of lizard body temperatures, and the mean annual temperatures across their geographic ranges to examine the relationships between body and mean annual temperatures.We then examined factors influencing body temperatures, and tested for the influence of both on ecological and life-history traits while accounting for the influence of shared ancestry. Results Body temperatures and mean annual temperatures are uncorrelated. However, accounting for activity time (nocturnal species have low body temperatures), use of space (fossorial and semi-aquatic species are ‘colder’), insularity (mainland species are ‘hotter’) and phylogeny, the two temperatures are positively correlated. High body temperatures are only associated with larger hatchlings and increased rates of biomass production. Annual temperatures are positively correlated with clutch frequency and annual longevity, and negatively correlated with clutch size, age at first reproduction and longevity. Main conclusions Lizards with low body temperatures do not seem to have ‘slower’ life-history attributes than species with high body temperatures. The longer seasons prevalent in warm regions, and physiological processes that operate while lizards are inactive (but warm enough), make environmental temperatures better predictors of lizard life-history variation than body temperatures. This surprisingly greater effect of environmental temperatures on lizard life histories hints that global warming may have a profound influence on lizard ecology and evolution.

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Faunal lists are important tools in ecology, biogeography, and conservation planning. Such lists can identify gaps in our knowledge of the distribution and taxonomy of regional faunas, and highlight issues needing further study. We present an up to date list of all land vertebrates occurring in Israel. We identify 786 species, of which 551 are birds, 130 are mammals, 97 are reptiles and eight are amphibians. Of these 369 species breed in Israel (including reintroductions), 199 (mostly birds) are regular visitors and 182 are accidental. Fourteen other species are invasive, and 22 species are extinct. We identify issues with the taxonomy and status of several species, and note recent developments in our understanding the Israeli land vertebrate fauna.

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Jordan has a very diversified morphology, which is reflected also in the diversity of its herpetofauna. A total 90 amphibian and reptilian species is known to inhabit Jordan. Of those three are amphibians, with the fourth species most probably already extinct, 47 are lizard species, 35 are snake species and five turtle species. The amphibians are represented by three different families, lizards and snakes both by seven families and turtles by four families. The distribution, ecology and systematics for most species are given.

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During a four week journey to Jordan in summer of 1994 the following five species of the lizard family Lacertidae were observed: Acanthodactylus boskianus asper, A. opheodurus, A. schmidti, Ophisops elegans ehrenbergii, and Lacerta cf. kulzeri.

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During a journey to Jordan in July/August 1994, 19 species of amphibians and reptiles were recorded. Some ecological observations were made in their habitats. The find of giant tadpoles of Rana ridibunda and the problematic, unclear systematic status of Ophisops elegans ehrenbergi in Jordan are emphasized

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Many animals display complex colour patterns that comprise several adjacent, often contrasting colour patches. Combining patches of complementary colours increases the overall conspicuousness of the complex pattern, enhancing signal detection. Therefore, selection for conspicuousness may act not only on the design of single colour patches, but also on their combination. Contrasting long- and short-wavelength colour patches are located on the ventral and lateral surfaces of many lacertid lizards. As the combination of long- and short-wavelength-based colours generates local chromatic contrast, we hypothesized that selection may favour the co-occurrence of lateral and ventral contrasting patches, resulting in complex colour patterns that maximize the overall conspicuousness of the signal. To test this hypothesis we performed a comparative phylogenetic study using a categorical colour classification based on spectral data and descriptive information on lacertid coloration collected from the literature. Our results demonstrate that conspicuous ventral (long wavelength-based) and lateral (short wavelength-based) colour patches co-occur throughout the lacertid phylogeny more often than expected by chance, especially in the subfamily Lacertini. These results suggest that selection promotes the evolution of the complex pattern rather than the acquisition of a single conspicuous colour patch, possibly due to the increased conspicuousness caused by the combination of colours with contrasting spectral properties.

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Acanthodactylus hardyi Haas, 1957 has traditionally been treated as a subspecies of the widely distributed A. scutellatus, but was recently elevated to specific rank. The occurrence of A. hardyi in Jordan was discovered very recently. Four specimens collected from Batn al Ghul and Al Hazim have the diagnostic features of A. hardyi and are therefore assigned to this taxon. This finding is considered as further proof of the validity of the taxon and of its recognition at the specific level. Ecological requirements and niche partitioning are discussed in the light of the co- occurrence of A. hardyi with A. schmidti and/or A. opheodurus.

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Die vorliegende Revision betrifft die Gattung Acanthodactylus (Damilie Lacertidae), die die Trocken- und Wüstengebiete des nördlichen Afrika und des südwestlichen Asiens bewohnt, mit Randpopulationen auf der Iberischen Halbinsel und auf Zypern. Mehr als 6000 Exemplare der Gattung, aus den bedeutendsten europäischen und amerikanischen Sammlungen, wurden untersucht. Zusätzlich wurden über 450 Röntgenaufnahmen für osteologische Untersuchungen ausgewertet. Die historische Übersicht behandelt in chronologischer Reihenfolge alle Arbeiten, die sich mit der Gattung Acanthodactylus beschäftigen, mit besonderer Berücksichtigung taxonomischer Studien. Ein beigegebener Bestimmungsschlüssel ermöglicht die Determination aller Arten der Gattung. Eine Reihe äußerer (Größe und Proportionen, Pholidose, Färbung und Zeichnung) und innerer (d.h. osteologischer) Merkmale wurde im Hinblick auf ihre Variabilität untersucht. Dann wurde ein Land ausgesucht, z.B. Ägypten, aus dem eine gute Materialbasis zur Verfügung stand. Für einen bestimmten Fundort in diesem Lande wurden sodann einige Kombinationen von Merkmalszuständen ermittelt, die sich aus dem Auftreten verschiedener Arten ergaben. Derselbe Vorgang wurde sodann auf den Rest Ägyptens übertragen, und die Merkmalskombinationen stellten sich als übereinstimmend heraus; sie erlaubten dadurch eine sichere Zuordnung von Tieren zu folgen Arten: A. boskianus, A. scutellatus und A. pardalis. Durch die Ausdehnung der Untersuchung nach Westen und Osten kamen weitere Taxa hinzu. Besonderer Aufmerksamkeit wurde diesen Merkmalskombinationen im Hinblick auf sympatrisches oder allopatrisches Auftreten der betroffenen Arten gezollt, mit dem Ergebnis, daß es in einigen Fällen möglich war, abzusichern, daß es sich um Populationen derselben Art handelt. Die Gattung Acanthodactylus wurde in mehrere Artengruppen gegliedert, die sich durch engere Beziehungen ihrer Arten untereinander auszeichnen. Die erste ist die micropholis-Gruppe mit der einzigen Art A. micropholis. Sie wird als die ursprünglichste der gesamten Gattung angesehen. Eine weitere Gruppe ist die boskianus-Gruppe, mit den Arten A. boskianus und A. schreiberi. Erstere wird ausführlich analysiert im Hinblick auf ihre außerordentlich große geographische Variabilität. Die yemenicus-Gruppe besiedelt die Arabische Halbinsel und besteht aus A. yemenicus sp.n., A. masirae, A. opheodurus und A. felicis. Eine weitere Gruppe ist die tristrami-Gruppe mit den Arten A. tristrami und A. robustus. Für erstere wird die Validität der Unterart orientalis verneint, die für iracensis dagegen bejaht. In die grandis-Gruppe wird hier nur A. grandis gestellt, während A. fraseri als dessen Synonym aufgefaßt wird. Die erythrurus-Gruppe enthält A. erythrurus, A. savignyi, A. blanci, A. boueti und A. guineensis. Letzterer rangierte bislang in der Gattung Eremias, gehört aber nach den hier vorgelegten Befunden in die erythrurus-Gruppe von Acanthodactylus. In der pardalis-Gruppe sind enthalten: A. pardalis, A. bedriagai, A. maculatus, A. spinicauda und A. busacki sp.n. aus Marokko. Die scutellatus-Gruppe besteht aus A. scutellatus, A. aureus, A. dumerili und A. longipes. Die letzte Gruppe ist die cantoris-Gruppe mit den Arten A. cantoris, A. arabicus, A. schmidti, A. blanfordi, A. gongrorhynchatus und A. haasi. Eine Bibliographie über die Gattung beschließt die Arbeit. Für jede Art werden Diagnosen, Verbreitungskarten, Synonymien, Beschreibungen und Materiallisten der untersuchten Tiere sowie auch Strichzeichnungen gegeben.

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Evaluating flagship species and their potential for biological preservation and ecotourism development is a key issue for many audiences within the conservation and social fields. Despite several methods available to identify flagships, their application is often constrained in remote, poorly studied regions. Developments are needed in statistical and spatially-explicit approaches to assess species` traits influencing flagship appealing, to identify flagship fleets, and to map the location of flagship hotspots. Here, we developed a new method to identify flagship species in regions with knowledge gaps, using a two-stage statistical approach (ordination and clus- tering algorithms) to assess variable`s contribution to appealing and to group species sharing similar char- acteristics into flagship fleets. We then mapped areas concentrating the highest richness of flagships. Unique morphologies and behaviours, conservation status, endemicity, body size and weight, and feeding habits were the traits contributing the most to the flagship appealing. Nine flagship fleets were identified, from which two were the most suitable for conservation marketing and ecotourism promotion campaigns in Sahara-Sahel: Fleet A comprising 36 large-bodied species (18 mammals, 18 reptiles) and Fleet B including 70 small-bodied species (10 birds, six mammals, 54 reptiles). A total of 19 and 16 hotspots were identified for large-bodied and small-bodied flagships, respectively. The methodology was suitable to identify flagship species for conservation marketing and for developing ecotourism operations in the Sahara-Sahel, to independently assess which species` traits are re- levant for flagship appealing, and to organise fleets for multispecies-based marketing campaigns. The framework is scalable and replicable worldwide.

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In this paper, the evolution and ecology of directional asymmetry (DA) during the developmental trajectory (DT) is compared with that of its product, morphological DA (MDA). DT and MDA are calculated for two bilateral morphological scale characters of lizards, the number of subdigital lamellae beneath the fourth toe in 10 agamid and 28 lacertid taxa, and the number of rows of ventral scales in 12 lacertid taxa. MDA, the subtraction between left and right sides (classical measure of DA), is functional in adult animals. Results confirm the hypodiesis that, in DT, the regression parameters a (constant) and b (regression slope) of counts on the right side with those on the left describe a developmental process. No phylogenetic or environmental effects were observed on a and b, but analyses considering both a and b together show non-random phyletic patterns. Independent analyses deduced the same ancestral DT in Agamidae and Lacertidae. In Lacertidae, distance between pairs of taxa in a + b (standardized values) correlates positively with die phylogenetic distance between taxa. Phyletic trends in MDA are indirect, and due to the link of MDA with a + b. The MDA of species is more dissimilar in sympatry than in allopatry. The phyletic trends suggest evolution of DT, while die association of MDA witii sympatry suggests that ecological pressures shape MDA in adult animals. Evolution of DT is independent from tiiat of its product, MDA–adaptive determinism defines the result of, but not the mechanistic process of, development. Deterministic environmental processes define MDA, and deterministic evolutionary processes define the interactive result of a and b, but not each separately. According to circumstances, different DTs produce similar or different MDA, and a particular DT can produce different MDAs.

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Aim: Deserts are generally perceived as areas of low diversity, and hence receive little attention from researchers and conservationists. Squamates are the dominant group of vertebrates in arid regions, and as such represent an ideal model to study biodiversity patterns in these areas. We examine spatial patterns of diversity, evolutionary history and endemism of terrestrial squamates of the Arabian Peninsula and test hypotheses on the role of topography and history of isolation so as to identify possible environmental drivers of diversification. Location: The Arabian Peninsula. Taxon: Squamate reptiles (Squamata; lizards and snakes). Methods: We generated distribution maps for all Arabian squamate species (including yet undescribed) and reconstructed their phylogenetic relationships using existing and newly produced genetic data for nearly all the species. We assessed patterns of the distribution of species richness, phylogenetic diversity and phylogenetic en demism across the peninsula to identify areas that could be considered evolutionary or endemicity hotspots for squamates. We evaluated community turnover across the peninsula and assessed the possible environmental drivers affecting the diversity of Arabian squamates in a regression framework. Results: The main hotspots of Arabian squamate diversity are mostly along the mountains that rim the peninsula while the most arid, central regions support a low diversity of species. The distribution of the phylogenetic diversity mirrors that of the species richness. Phylogenetic endemism is also highest in the mountains, especially when only endemic species are analysed. The deserts of northern Arabia are poor in terms of species richness and they show low connectivity to the peninsular communities. Topographic heterogeneity is the strongest predictor for Arabian squamates, followed by elevation. There is no correlation between richness and temperature. Main conclusions: The mountains of Arabia support rich and unique squamate communities that are dominated by local radiations of closely related and narrow-ranging species. In particular, the Asir Mountains of SW Arabia, Dhofar Province of Oman and the Hajar Mountains of northern Oman and UAE show unprecedented levels of squamate endemism and phylogenetic endemism. While many generalist species range across Arabia, a low number of species is shared between the peninsula and mainland Asia, indicating an effective isolation of the Arabian fauna. Squamate richness is highest in heterogeneous, topographically complex habitats.

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This paper provides an updated checklist of the United Arab Emirates (UAE) native and alien herpetofauna. The UAE, while largely a desert country with a hyper-arid climate, also has a range of more mesic habitats such as islands, mountains, and wadis. As such it has a diverse native herpetofauna of at least 72 species as follows: two amphibian species (Bufonidae), five marine turtle species (Cheloniidae [four] and Dermochelyidae [one]), 42 lizard species (Agamidae [six], Gekkonidae [19], Lacertidae [10], Scincidae [six], and Varanidae [one]), a single amphisbaenian, and 22 snake species (Leptotyphlopidae [one], Boidae [one], Colubridae [seven], Hydrophiidae [nine], and Viperidae [four]). Additionally, we recorded at least eight alien species, although only the Brahminy Blind Snake (Ramphotyplops braminus) appears to have become naturalized. We also list legislation and international conventions pertinent to the herpetofauna.

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Acanthodactylus lizards are among the most diverse and widespread diurnal reptiles in the arid regions spanning from North Africa across to western India. Acanthodactylus constitutes the most species-rich genus in the family Lacertidae, with over 40 recognized species inhabiting a wide variety of dry habitats. The genus has seldom undergone taxonomic revisions, and although there are a number of described species and species-groups, their boundaries as well as their interspecific relationships are largely unresolved. We constructed a multilocus phylogeny, combining data from two mitochondrial (12S, cytb) and three nuclear (MC1R, ACM4, c-mos) markers for 302 individuals belonging to 36 known species, providing the first large-scale time-calibrated molecular phylogeny of the genus. We evaluated phylogenetic relationships between and within species-groups, and assessed Acanthodactylus biogeography across its known range. Acanthodactylus cladogenesis is estimated to have originated in Africa due to vicariance and dispersal events from the Oligocene onwards. Radiation started with the separation into three clades: the Western and scutellatus clades largely distributed in North Africa, and the Eastern clade occurring mostly from Arabia to south-west Asia. Most Acanthodactylus species diverged during the Miocene, possibly as a result of regional geological instability and climatic changes. We support most of the current taxonomic classifications and phylogenetic relationships, and provide genetic validity for most species. We reveal a new distinct blanfordii species-group, suggest new phylogenetic positions (A. hardyi, A. masirae), and synonymize several species and subspecies (A. lineomaculatus, A. boskianus khattensis and A. b. nigeriensis) with their phylogenetically closely-related species. We recommend a thorough systematic revision of taxa exhibiting high levels of intraspecific variability as well as clear evidence of phylogenetic complexity such as A. guineensis, A. grandis, A. dumerilii, and A. senegalensis and the pardalis and erythrurus species-groups.

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Das Vorkommen von Acanthodactylus opheodurus ARNOLD, 1980 und von Coluber ventromaculatus GRAY, 1834 wird erstmals aus dem Emirat Abudhabi und damit auch aus den Vereinigten Arabnischen Emiraten gemeldet. A. opheodurus konnte am Fuße des Jebel Hafit, südlich von Al Ain, nachgewiesen werden. Das nächstgelegene bekannte Vorkommen befindet sich ungheähr 500 km westlich davon in Saudi Arabien. Weiters erwies sich eine Natter von der Insel Sir Bani Yas als C. ventromaculatus. Dieser Fund erweitert das bisher bekannte Verbreitungsgebiet dieser Schlange auf der Arabische Halbinsel um etwa 280 km in Richtung Südosten.

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hese notes on some Egyptian lacertid lizards contribute to faunal data for the planning of biodiversity conservation. Mesalina bahaeldini curatorumn. subsp. is described from Suez, characterized by coloration and larger (fewer) body scales. Range extensions are documented for Acanthodactylus aegyptius, Mesalina olivieri, and M. rubropunctata. The previously reported occurrence of A. opheodurusin Sinai is doubted. The fact that the M. b. curatorum types were collected in the 1820s demonstrates the importance of museum collections.

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The distribution of the Arabian desert lizard Acanthodactylus opheodurus Arnold, 1980 in the Levant is re-examined. West of Jordan it is almost limited to the ‘Arava Valley, absent from most of the Negev and from Sinai. This correction of an earlier report derives from re-identification of specimens, relying on the colour pattern difference from the syntopic sibling A. boskianus asper (Audouin, 1829). The vertebral dark stripe is simple in A. opheodurus but forked in A. boskianus. The vertebral stripe is forked but light-colored in two geographically adjacent related taxa, A. b. boskianus (Daudin, 1802) of northern Egypt and A. schreiberi syriacus Boettger, 1878 of coastal Israel.