Reese_considerations on the Potential Use of Cliffs

Embed Size (px)

Citation preview

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    1/12

    ORIGINAL PAPER

    Considerations on the potential use of cliffs and caves

    by the extinct endemic late pleistocene hippopotami

    and elephants of Cyprus

    Eleftherios Hadjisterkotis &David S. Reese

    Received: 22 January 2007 /Revised: 15 June 2007 /Accepted: 20 June 2007 / Published online: 27 July 2007# Springer-Verlag 2007

    Abstract Most of the fossil mammal sites on Cyprus, as

    well as on other Mediterranean islands, consist of largequantities of bones found in caves. Of 32 sites with

    Phanourios minutus and 21 with Elephas cypriotes on

    Cyprus, 19 were located in caves, two in rock-shelters, and

    11 at open-air sites. Fifteen of them were littoral, four

    coastal, and 13 inland. The purpose of this paper is to

    examine possible reasons why Phanourios and Elephas

    remains accumulated mainly in littoral and coastal caves.

    Based on an analysis of the behavior exhibited by living

    hippopotami and elephants, we assume that the extinct large

    mammals of Cyprus entered these caves in search of fresh

    water and to protect themselves from the heat in the cool

    and moist cave environment. A further reason may have

    been that these mammals entered the caves seeking mineral

    licks to rectify possible mineral deficiencies, to bind

    secondary plant compounds such as tannins, or to counter-

    act acidosis. By entering caves, or even passing along

    narrow paths through cliffs, they were at risk of becoming

    trapped in natural traps, such as caves with their openings

    facing upwards, sinkholes, and mire traps. There is no

    evidence that Phanourios and Elephas remains were

    accumulated by natural predators because on the island

    there were no predators large enough to carry such large

    mammals. The only exception are the remains in the

    Akrotiri Aetokremnos rock shelter on the Akrotiri peninsu-

    la, where there is evidence that the 218,459Phanouriosand330 Elephas remains were accumulated by the first human

    settlers of Cyprus, about 10,000 years BP.

    Keywords Fossils . Cyprus . Pygmy Hippopotami .

    Pygmy elephants .Phanourios minutus .Elephas cypriotes

    Introduction

    The first evidence for the presence of humans on the island

    of Cyprus comes from a rock shelter or small cave at

    Akrotiri-Aetokremnos, where man-made artifacts were

    found together with a large number of skeletal remains of

    the extinct endemic pygmy hippopotamus (Phanourios

    minutus) and pygmy elephant (Elephas cypriotes), as well

    as many bird bones, reptile bones, edible marine mollusc

    shells, lithics, shell and stone ornaments, etc. The site,

    located on a steep sea cliff, dates to about 10,000 years ago

    (Hadjisterkotis et al.2000; Simmons1991a,b,1996,1999,

    2002; Simmons and Wigand1994).

    The main argument that some researchers have given for

    rejecting the association ofPhanouriosbones and the other

    remains with humans at Aetokremnos is that most of the

    fossil mammal sites on Cyprus, as well as on other

    Mediterranean islands, consist of large quantities of bones

    found in caves. Of 32 sites on Cyprus with Phanourios, of

    which 21 also had Elephas, 19 were located in caves, two

    probably in rock shelters, and 11 at open-air sites. Fifteen of

    them were littoral, four coastal, and 13 inland (Reese 1995,

    unpublished analyses). This was also observed at sites on

    Crete (Lax 1996), Malta (Hunt and Schembri 1999), and

    Sicily (Bonfiglio and Burgio 1992; Bonfiglio and Insacco

    1992; Bonfiglio and Piperno 1996). Unlike at Aetokrem-

    Eur J Wildl Res (2008) 54:122133

    DOI 10.1007/s10344-007-0121-3

    DO00121; No of Pages

    Communicated by W. Lutz

    E. Hadjisterkotis (*)

    Ministry of the Interior,

    1453 Nicosia, Cyprus

    e-mail: [email protected]

    D. S. Reese

    Peabody Museum, Yale University,

    P.O. Box 208118, New Haven, CT 06520-8118, USA

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    2/12

    nos, there is no evidence on these other islands that the

    extinct endemic animals were associated with humans.

    Reese (2001) provided a detailed study of the Aetok-

    remnos fauna from the features and lowest stratum which,

    in our opinion, leaves no doubt that the bones were

    contemporary with the man-made artifacts. Hadjisterkotis

    et al. (2000), in a paleoecological and paleoethological

    analysis of the site and its remains, noted that perhaps anumber of species found in the rock-shelter entered for

    nesting or hibernation or were brought there by the extinct

    endemic genet (Genetta plesictoides). However, they noted

    that the only way that the 218,459Phanouriosremains, 330

    Elephasremains, 3,200 bird bones, and 73,000 marine shell

    fragments could have gotten into the cave was if they were

    brought in by humans. Most of the bones are broken and

    many are burned.

    Although numerous studies have now been published

    that support the association between humans and Phanour-

    ios at Aetokremnos (Simmons1991a,b,1996,1999,2001,

    2002; Simmons and Reese 1993; Simmons and Wigand1994; Reese 1989, 1996, 2001; R eese et al. 1999;

    Hadjisterkotis et al. 2000), a few researchers are still not

    convinced of this association (noted in Reese 2001;

    Ammerman and Noller 2005). Although Aetokremnos is

    the only fossil site on the island with evidence on what

    caused the accumulation of the above skeletal remains,

    what brought the extinct endemic pygmy hippopotamus

    and a pygmy elephant in the other 19 caves remains

    unknown.

    The purpose of the present paper is to examine the

    possible reasons why Phanourios and Elephas remains

    accumulated mainly in littoral and coastal caves. The main

    hypothesis, which we examine here, is that these animals

    entered caves, or used paths going through cliffs, for

    several reasons and by doing so encountered a number of

    natural traps. Consequently, this study also discusses

    possible reasons why these animals would be attracted to

    cliff caves and rocky beaches.

    Materials and methods

    Our analysis relies on the known behaviors of living

    hippopotami and elephants, as well as on information from

    archaeological and paleontological studies on related

    pro boscidean s. The geological history of Cypr us is

    reviewed to understand the formation of the littoral and

    coastal caves of the island and some of the ecological

    peculiarities relevant to its extinct large mammals. To

    examine the hypothesis that animals had entered the caves

    in search of water and for the cool environment, we review

    the physiological needs of hippos and elephants as far as

    water is concerned and the set of behaviors observed for

    modern pachyderms to seek or struggle to get water, or to

    protect their bodies from heat under drought conditions.

    To investigate whether the extinct animals were attracted

    to caves or to the coast in search of mineral licks or other

    sources of minerals, the known mineral needs of living

    elephants and the actions taken by them to satisfy such

    needs are reviewed. To see if there were any mineral or

    nutrient deficiencies in the vegetation of Cyprus thatwould force the extinct elephants and hippopotamus to

    seek mineral licks or saline water, we investigate case

    studies on the largest living wild herbivore on the island,

    the Cyprus mouflon (Ovis gmelini ophion), and report

    findings on domestic animals as well.

    In the summer and fall of 1988, and in the winter, spring, and

    summer of 1989, 85 samples of mouflon forage species were

    collected and analyzed for nutrient content (Hadjisterkotis

    1993). Selection for analyses was based on plants found in

    the rumen and on visual observations of mouflon while

    feeding in the wild (Hadjisterkotis 1993, 1996b). Plant

    material collected mimicked plant parts selected by mou-flon. At least 100 g (fresh weight) of plant material was

    harvested from a minimum of 25 individuals of each

    species, with the exception of Mediterranean medlar

    (Crataegus azarolus) fruit, which had a very bad crop year.

    In this case, fruit was collected from only three trees.

    Samples were kept for about 2 days at ambient temperature

    until received at the Chemical Laboratory at the Ministry of

    Agriculture in Nicosia. Dry matter was determined by

    heating samples of a constant weight in a convection oven

    at 60C for 24 h. Dried material was then ground to a

    powder with a laboratory mill for further analytical

    procedures. Zinc, copper, iron, molybdenum, manganese,

    (ppm, mg/kg of dietary dry matter), and calcium (Ca

    percentage of dry matter) were determined with a Perkin

    Elmer atomic absorption spectrophotometer, after a 1-g

    sample was wet digested with a mixture of 10 ml of

    Nitric-perchloric acid. In the case of Ca, lanthanum oxide

    (La2O310%) was added to the sample. Sodium, potassium,

    and phosphorus (percentage of diet dry matter) were

    determined by using a Corning-EEI flame photometer.

    Nitrogen content was determined with the Kjeldahl method.

    Crude protein content was estimated by multiplying the

    nitrogen content by 6.25 (percentage of diet dry matter,

    Horwitz 1960). Sulfur (percentage of dry matter) was

    determined by using the dry ashingbarium sulfate method.

    Due to technical difficulties, the microelements iodine, cobalt,

    selenium, and fluorine were not examined. To determine if

    there were any macromineral or micromineral deficiencies or

    intolerable levels in the samples analyzed, the results were

    compared with the values presented by the National Research

    Council (1985, Tables 6 and 7).

    To clarify whether the accumulated bone remains were

    brought into the caves by predators, we review other known

    Eur J Wildl Res (2008) 54:122133 123

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    3/12

    cases where proboscidean remains were carried in by humans

    or other predators, and we list all the known predators found

    on Cyprus from prehistoric times until today.

    Results and discussion

    The origin of Cyprus and its littoral caves, and the arrivalof large mammals

    Cyprus begun forming between 92 and 85 million years

    ago (time scale of Harland et al. 1982) with the formation

    of the Troodos Massif, a fragment of uplifted oceanic crust

    (Gass 1980; Mukasa and Ludden 1987; McCallum and

    Robertson 1990; Robertson 1990). By the Late Miocene,

    the Troodos Massif was a low-lying island, and the Kyrenia

    Range, which had been deeply submerged, began to rise. A

    severe compression and drastic uplift occurred in Cyprus in

    the Pleistocene. The Troodos Massif, Kyrenia lineament,

    and Mesaoria basin were uplifted together, forming a singlestructural unit (McCallum and Robertson1990). That uplift

    raised Mt. Olympus to its present elevation of 1,951 m. In

    addition to the regional tectonic uplift, sea level fluctuations

    occurred throughout the Quaternary. These have contribut-

    ed to the generation of the river terraces and raised beaches

    of Cyprus and the formation of littoral caves from the

    action of the waves on the rocks in combination with

    underground flowing fresh water.

    Since Cyprus is an oceanic island that was never

    connected to the mainland, the only way large mammals

    could arrive was by swimming (Hadjisterkotis and Masala

    1995; Hadjisterkotis et al. 2000). When the first hippopot-

    ami and elephants arrived from the mainland they most

    likely had to face a completely different environment from

    that which they were used to. The only rivers present on the

    island today are torrential ones running during the winter

    after strong rains. During the Late Pleistocene, it is

    probable that hippos and elephants of the nearby mainland

    inhabited the estuaries of the large rivers such as the Nile,

    the Pyramos (modern Ceyhan river), or the Orontes, which

    flow into the Mediterranean both to the north and to the

    east of Cyprus. Hippopotamus amphibius first appear

    during the Middle and Upper Pleistocene in coastal sites

    in the southern Levant, such as Evron, Holon, Tabun,

    Sefunim, and Kebara caves (Tchernov 1981, 1984; Faure

    1986), and inhabited the Nile from at least the Pleistocene

    (Reese 1985; Horwitz and Tchernov 1990) until the last

    animal was shot in the Nile delta in the last century (Nowak

    and Paradiso 1983). It also existed in Lebanese coastal

    sites, such as Sidon, Naame, and Ras el-Kelb, and along the

    river systems such as at Latamne (Faure 1986) since the

    same period. The Orontes and Sinn rivers supported

    hippopotamus populations up to the early Iron Age.

    However, once hippos and elephants arrived on Cyprus,

    in the hot summers, they were faced with a new, much drier

    situation. This is evident from the adaptations that

    Phanouriosunderwent. These hippos lost the characteristic

    wide foot pad of the living large African hippopotamus

    (H. amphibius) and developed a more-or-less pig-like foot

    adapted to walking. The lowering of their eyes and nostrils

    also indicates that they were adapted to a more terrestriallife than the common hippo (Houtekamer and Sondaar

    1979; Spaan1996). These adaptations are an indication that

    Phanourios probably spent less time in the water than its

    ancestorH. amphibius.

    The use of caves for water and for the cool environment

    According to Haynes (1995), an adult elephant requires

    great quantities of moisture/water each day to digest food

    and regulate its body temperature. During dry seasons,

    elephants will travel to water every day when possible,

    although data from radiotelemetric studies show femalegroups regularly remaining without water for 48 h, even

    when only 5 km from a water source. Male bands were

    noted going 3 to 4 days without water, although never more

    than 20 km from pans during that time. When there is no

    water near feeding areas, elephants may travel long

    distances to water every 2 to 3 days. If visits to water are

    daily, elephants spend a relatively short time drinking,

    spraying, and wallowing (less than an hour in daytime).

    When visits are more widely spaced, the time spent at water

    may be much longer. However, a recent report by Douglas-

    Hamilton (2003) describes the elephants of the Gourma

    region of the Malian Sahel. These animals eke out a living

    at the northern extreme of the African elephants distribu-

    tion, showing remarkable adaptations to their desert

    environment and making long journeys. Based on data

    from three radio-collared elephants, it was found that a

    females home range exceeded 9,000 square miles. All

    three followed the rains, eating and drinking their way from

    water hole to water hole.

    According to Haynes (1995), during the dry season,

    elephants visit seeps to dig shallow wells 1 to 3 m deep to

    the water level and wait for water to ooze into the opening.

    This behavior was observed by early explorers such as

    Chapman in 1862 (Tabler 1971), Davison (1930, 1930

    1935), and others, and was seen mainly during the dry

    season when pans dried up or were muddied by heavy use

    (Davison 1930, 19301935). In very dry years, the water

    oozes so slowly into the wells that elephants sometimes

    stand at them waiting for hours to satisfy their thirst.

    In the 1980s, according to aerial surveys, 1,0002,000

    elephants were normally present near the seeps in Hwange

    National Park in Zimbabwe during the dry seasons (Haynes

    1995), and competition for access to the seeping water in

    124 Eur J Wildl Res (2008) 54:122133

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    4/12

    wells became intense as the dry season progressed. In spite

    of a succession of drought years, hundreds of elephants

    continued to spend the dry season in the area of the seeps

    each year.

    Wells were often redug, cleaned out, and enlarged by

    elephants, especially after traffic to the seeps and their use

    as water sources increased dramatically in the middle of the

    dry season (Haynes 1995). As the ground around wells istrampled bare, the sediments dry out, and wells often

    collapse. If a carcass or skeleton lay within the depression

    created by digging or trampling around a well opening, or

    within the well itself, elephants would kick it or move it

    with their trunks to get it out of the way. Elephants dug

    through buried carcasses as well, after young animals had

    died within wells and caused the holes to slump or collapse.

    Weakened animals occasionally become mired in the

    mud and muck of water-hole bottoms or banks (Murie

    1934; Matthiesson and Porter1974; Shipman1975; Sinclair

    1977) and such may have been the fate of Late Pleistocene

    mammals (Haynes1995). Many of their bones would havebecome incorporated into the mud and sediments and might

    become preserved, in contrast to the situation of bones left

    lying on the ground surface during times of drought.

    Hippopotami without water and mud baths, in a hot

    environment, are known to become dehydrated and to have

    difficulty surviving. According to Estes (1992), because

    hippopotami have a unique skin (thin epidermis, no sweat

    glands) which loses water at several times the rate of other

    mammals, a hippo out of water in hot weather risks rapid

    dehydration and overheating. In hippos, there are no sweat

    glands either within the dermis or at the base of the few

    hairs of the skin, where glands are almost always found in

    most other mammals. There are, however, large subdermal

    glands, made up of more than one type of cell, scattered

    regularly over the body (Wright 1987). They are sparsely

    distributed at a density in the common hippo of one per

    square centimeter, but they make up for that by being

    unusually large for a skin gland, with a weight of about 1 g

    and a duct clearly visible to the naked eye. Hence, the

    volume of secretion is quite high. These glands produce a

    viscous fluid varying from colorless to pink and dark

    brown. The color of the secretion gives a pinkish tinge to

    the whole body.

    Evaporation from the hippos skin was found to be very

    high compared with that of other mammals and varied from

    68 g m2 h1 when the skin was dry to 2,280 g m2 h1

    when the skin was wet with secretion (Wright1987). The

    latter value approaches the figures obtained by placing the

    hygrometric capsule over filter paper soaked in a KCL

    solution, suggesting that there is no control over water loss

    from the skin. If a hippo is actually unable to control the

    rate of water loss from its body, its ability to deal with heat

    stress will be limited. It may be for this reason that the

    hippo has evolved a semiaquatic life-style. The same is also

    true of the air temperature at night, and this may be a

    contributing reason for the hippos spending the night out of

    water for feeding, often traveling quite long distances to

    reach grazing areas (Eltringham 1999).

    Olivier (1975) measured water loss from the skin of

    living West African pygmy hippos (Choeropsis liberiensis).

    The results revealed a much lower water loss comparedwith the larger common hippo. However, the temperature

    was some 10C higher during the measurements of the

    common hippo, and, as the water vapor pressure doubles

    with each ten-degree rise, the water loss would also double.

    If the values forChoeropsis are doubled, they come within

    the range of the values for Hippopotamus, which seems

    more reasonable and suggests that the physiology of the

    skin as well as its anatomy is almost identical in the two

    species.

    The problems faced by hippos and elephants when they

    lack water were demonstrated by Joubert and Joubert

    (1988) in the film The Stolen River, and were also describedby Walker (1991) in the bookSavuti: the Vanishing River.

    The Linyanti River brings water in to the Savuti Channel in

    Botswana. Savuti was once a vast lake, then dried up for

    about 80 years. The river began to flow again in 1957, but

    in 1982, the channel stopped flowing for 7 years. Accord-

    ing to Walker (1991),

    maddened with thirst, the poor beasts continued to

    flock to the well-remembered place, to find, not relief,

    but foul mud; the stench from the rotting carcasses of

    earlier arrivals; and death in its ugliest form...The

    weaker individuals were immediately trapped, andtrampled down to rise no more, while the stronger

    ones floundered desperately round and round, butting

    one another in their agonies.

    In the last water pool left, 100 hippos were trapped in the

    mud (Joubert and Joubert1988). Most of them were killed

    by the blazing sun. The surviving hippos left the mud to

    seek the shade of trees. Some hippos lasted for several

    seasons, surviving on the moisture of the early morning and

    sheltering through the day, but by being away from the

    protection of the aquatic environment, they died from

    starvation or by being killed by lions and hyenas. The

    elephants of the Savuti were able to dig into the ground at

    the bottom of the empty canal, finding some water. The

    limited supply of water forced the elephants to stop their

    young from drinking, condemning them to death in order to

    survive themselves.

    Moss (1988) observed separation of cows with youngest

    calves during a drought in Amboseli National Park in

    Kenya. Old cows that are nursing may die during drought,

    leaving their calves to die, mainly from predation. Haynes

    (1995) reported seeing lactating cows without calves in tow,

    Eur J Wildl Res (2008) 54:122133 125

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    5/12

    resulting from the calves death or abandonment by the

    mother.

    Similarly,Phanouriosfaced a dry and hot environment in

    Cyprus and had to find ways to adapt. They had to search for

    shady places that would offer the appropriate moisture for

    their skin and drinking water. The best place for such

    protection would be the littoral caves and the Mediterranean

    Sea. Hippos are known to use the sea quite well; they havebeen known to swim from the East African mainland to the

    island of Zanzibar, more than 35 km away. In addition, in the

    Late Pleistocene/Early Holocene they reached the island of

    Madagascar by overcoming the 450-km-wide Mozambique

    Channel (Held 1989). Before Europeans introduced fire-

    arms to southern Africa in the 1830s, hippos were reported

    to swim in the sea as much as in rivers (Smith 1849).

    It is likely that Phanourios made use of the sea for

    cooling. However, even if they had the opportunity to use

    the sea, they still needed water for drinking. So they had to

    leave the sea to search for fresh drinking water and food.

    This brought them in touch with the coastal and littoralcliffs and caves, and they probably soon discovered and

    made use of the cool and moist environment of the caves.

    Inside the caves, evaporation is reduced and any spring

    water coming through the walls of the caves could create

    water pools with drinking water. Many of these caves were

    created from underground water dissolving the soft lime-

    stone. However, entering such locations, they had to face

    the possible natural traps left in the rocks by the action of

    the sea waves or the underground water. The heat-stressed

    hippos could enter the pools not knowing that getting out

    was an impossible task. Elephants, when faced with a

    steep-sided pool (contrary to the hippos) are reluctant to

    enter. They lower their trunk and lift one of their hind legs

    up, standing on only three legs in an attempt to lower their

    body to reach the water. This might explain why so few

    elephants were trapped in these caves.

    Mineral utilization

    A possible additional reason for entering caves may have been

    the search for minerals. Animals occasionally eat small rocks

    or soil impregnated with natural salts to rectify possible

    mineral deficiencies, something known as geophagy and

    pica behavior (Schaller 1977). Areas where ungulates

    actively ingest soil have commonly been referred to as salt

    licks (Ayotte et al. 2006). This name implies that licks serve

    a universal role of supplementing diets with sodium.

    Various reports exist showing that wild ungulates search

    for salt (Stockstad 1950; Dalke et al. 1965; Geist 1971;

    Schaller 1977; Weeks 1978; Watts 1979; Robbins 1993;

    Hadjisterkotis 1997; Fraser and Reardon 1980; Holl et al.

    1980; Ayotte et al.2006). Many studies have reported high

    concentrations of sodium in lick material (Hebert and

    Cowan 1971; Weeks and Kirkpatrick 1976; Reisenhoover

    and Peterson 1986; Tracy and McNaughton 1995). How-

    ever, many of the field observations of food preferences and

    mineral lick use are difficult to interpret, as it is usually

    unclear which element is being sought. Hadjisterkotis

    (1993, 1997), from December 1985 until December 1988,

    provided Cyprus mouflon with mineral blocks and table salt

    in six stations spread inside Pafos Forest in Cyprus. Wildmouflon never licked any of the mineral blocks or the salt,

    although there was evidence that they often bedded next to

    them. It is likely that sometimes elements other than

    sodium are sought in mineral licks (Chamberlin et al.

    1977; Coates et al. 1990; Heard and Williams 1990;

    Dormaar and Walker1996; Hadjisterkotis1997).

    Knight et al. (1988) studied ungulates that visited lick

    sites in the Kalahari and found (1) that browsers more often

    than grazers visited licks, (2) that animals living in highly

    seasonal (wet/dry) habitats countered springtime acidosis

    by ingesting mineral soils during the time of abrupt dietary

    shifts from dry forage to green sprouts, (3) that animalscorrected for the toxic compounds in plants, such as

    tannins, by eating clay particles, and (4) that a high sodium

    intake among herbivores in dry habitats was a regular

    strategy that enabled them to survive dehydration by

    protecting cell membranes from damage during osmosis.

    In other parts of the world, deficiencies in macro- and trace

    elements might be a result of digestive disorders associated

    with spring forage change (Watts 1979; Ayotte et al. 2006).

    The presence of many species of ungulates at mineral licks

    in the spring [moose (Alces alces), Tankersley and Gasaway

    1983; Ayotte et al.2006; elk (Cervus elaphus), Ayotte2004,

    Ayotte et al. 2006; Williams 1962; Dalls sheep (Ovis dalli

    dalli), Heimer1973, 1988; Tankersley 1984; bighorn sheep

    (Ovis canadensis mexicana), Watts 1979; mountain goats

    (Oreamnos americanus), Singer 1978; Ayotte et al. 2006;

    and Stones sheep (Ovis dalli stonei), Ayotte et al. 2006]

    coincides with the increased physiological demand of

    lactation, growth, or weight regain, which can be aggravated

    by electrolyte loss related to the stress of abrupt changes in

    forage chemistry (Ayotte et al. 2006). One source of

    physiological stress is the change from highly fibrous winter

    diets to flourishing spring plant growth resulting from a

    decrease in fiber and an increase in fermentable carbohy-

    drates and proteins that alter rumen pH and weaken proper

    microbial function. Ruminants exposed to sudden decrease

    in dietary fiber produce less saliva, which is high in

    bicarbonates (Kreulen1985). With less saliva, the buffering

    capacity of the rumen is reduced (Church1975), which can

    lead to a decrease in pH below the best possible conditions

    for rumen microbes, and weight gain (Klaus and Schmid

    1998; Kreulen1985).

    Physiological stress can also occur when high levels

    reduce the absorption and retention of other elements

    126 Eur J Wildl Res (2008) 54:122133

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    6/12

    (Klaus and Schmid 1998; Kreulen 1985). Early-season

    vegetation contains concentrations of potassium that elevate

    the osmotic pressure of the digestive tract, interfere with

    fecal water absorption, and lead to potentially unsafe

    electrolyte loss (Weeks and Kirkpatrick 1976; Kreulen

    1985; Klaus and Schmid1998).

    According to Ayotte et al. (2006), supplemental sources

    of carbonates during the transition to spring forage canimprove the buffering capacity of the rumen when saliva

    secretion is compromised (Kreulen 1985). During spring

    forage change, clay minerals can be associated with the

    adsorption of potassium and short chain fatty acids to

    cation exchange sites, adjusting and maintaining proper

    osmotic balance and pH of the rumen, enhancing its

    buffering capacity (Klaus and Schmid 1998; Kreulen

    1985; Cairns-Smith and Hartman 1986). Some kinds of

    absorptive clays are also able to bind secondary plant

    compounds such as tannins (Johns and Duquette 1991) and

    improve digestibility and feed conversion in domestic

    animals (Smith1992).The search for salt and mineral licks to rectify possible

    deficiencies has also been observed in living elephants.

    However, almost no information is available on the

    minimum levels of different nutritional substances required

    for maintenance and production in wild elephants (Haynes

    1995). There is good evidence that elephants benefit from

    seeking out mineral soils to ingest, even at the expense of

    optimized food intake. Moss (1988) has suggested that

    African elephants living outside Amboseli National Park

    traveled into the park to eat the salt found there.

    Buss (1990) observed five elephants in Tanzania

    (Ngorongoro Crater region) at a long, high trench that had

    evidently been grubbed and gouged out over a long period

    of time. Soil was gouged out with the tusks and transferred

    by the trunk to the mouth. Some of the previously used

    excavations that were too deep and inconvenient for easy

    access had been deserted by the elephants. Chemical

    analysis of the soil indicated relatively high manganese

    content. Buss therefore suggested that elephants migrated to

    the Ngorongoro Crater primarily for the manganese- and

    cobalt-laden soil. Manganese is an essential element for

    mammals, with Mn deficiency causing ataxia, abnormal

    brain function, abnormal development of the skeleton, still

    births, poor viability, etc. (Buss1990).

    A recent study of three different South African elephant

    populations suggests that reproduction rates may be

    significantly depressed if the major food plants provide an

    inadequate intake of phosphorus or if calcium intake is

    excessive as compared with phosphorus (Koen et al. 1988).

    A calciumphosphorus imbalance in association with

    phosphorus deficiency may be a population-limiting factor

    that can lead to longer interbirth intervals, delayed maturity,

    and increasing age at first conception (Haynes 1995).

    Elephants also need sodium in relatively large amounts

    (Weir 1972), as well as iodine, cobalt, and selenium

    (Milewski 2000; Milewski and Diamond 2000). According

    to Hold et al. (2002), most studies on lick chemistry show

    that lick soils consumed by African elephants have higher

    Na+ concentrations than the surroundings soils (Ruggiero

    and Fay1994; Stark1986; Weir1969), and it was assumed

    that licks are generally used to supplement an inadequatedietary Na+ intake (Reisenhoover and Peterson 1986;

    Weeks and Kirkpatric1976; Weir1972).

    A need for extra sodium in the diet is met by visiting

    mineral licks, where elephants excavate pits and even caves

    with their trunks, seeking alternative foods, or by drinking

    saline water (Weir 1972; Sukumar 2003, Fig. 5.7). The

    Kalahari-sand region of Hwange National Park, Zimbabwe,

    is particularly poor in soil nutrients including Na+

    (Weir

    1969; Hold et al. 2002). Plants in this habitat are,

    therefore, presumably low in Na+ (McDowell 1985).

    Elephants create and maintain depressions in patches of

    Na+-rich soil in this area (Weir 1969), and positivecorrelation has been found between the number of

    elephants visiting pans (clay-rich depressions that hold

    rainwater during the dry season) and the Na+ content of

    water in pans located in the Kalahari-sand region of

    Hwange (Weir 1972). Hold et al. (2002) studied the use

    of mineral licks by African elephants during the dry season

    in a Kalahari-sand habitat in Hwange to investigate the role

    of geophagy as a mechanism for supplementing low Na+

    levels in browse and natural water supplies. According to

    their findings, elephants in Hwange may have difficulty in

    meeting their maintenance requirements of Na+ from forage

    alone, but are probably able to obtain sufficient Na+ from

    licks and some Na+-rich water sources to satisfy their

    requirements of this mineral. In Kalahari-sand areas, licks

    may be the primary source of Na+ supplementation in areas

    without Na+-rich borehole water. At supplemented pans

    with elevated water-Na+ concentrations, geophagy may not

    be necessary as a means of Na+ intake. Hold et al. (2002)

    concluded that Na+ appears to play an important role in

    attracting elephants to licks and, thus, in affecting move-

    ment and habitat-use patterns by this species.

    There is evidence that not only modern elephants travel

    long distances in search of minerals, but that mammoths

    and mastodons did as well (Holman et al. 1988). These

    authors suggested that proboscideans migrated from rela-

    tively saltless areas in Ohio, Indiana, and Illinois to eat

    sodium-rich earth in Michigan salt licks.

    Holman et al. suggested that proboscideans are found in

    such abundance at Michigan salt licks because they traveled

    north into the periglacial forests seeking minerals that were

    not available elsewhere. Other geologically similar areas

    rich in salts also contain large accumulations of probosci-

    dean bones, such as Big Bone Lick in Kentucky, USA.

    Eur J Wildl Res (2008) 54:122133 127

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    7/12

    Based on the above evidence, the question arises

    whether there are any mineral deficiencies on the island

    of Cyprus which would have forced Phanourios and

    E. cypriotes to search for salt licks, saline water and

    minerals in cliffs and caves.

    Since there are no wild elephants or hippos on Cyprus

    today, the only way to investigate any mineral shortages in

    soil or vegetation is by examining possible deficiencies ofthe living large mammals on the island. The only large wild

    herbivore living on the island today is the Cyprus mouflon,

    which inhabits Pafos forest (Hadjisterkotis1993,1996a,b,

    1997, 1998, 1999, 2001, Hadjisterkotis and Bider 1997;

    Hadjisterkotis and Van Haaften 1997; Hadjisterkotis and

    Vakanas1997; Toumazos and Hadjisterkotis 1997; Serreri

    et al.2000).

    Fifteen elements have been demonstrated to be essential

    for domestic sheep (National Research Council 1985).

    Seven are major mineral constituents: sodium, chlorine,

    calcium, phosphorus, magnesium, potassium, and sulfur.

    The other eight are trace elements: iodine, iron, molybde-num, copper, cobalt, manganese, zinc, and selenium.

    Hadjisterkotis (1993) examined the major forage species

    selected by O. g. ophion for most of the above elements.

    The study examined two different regions of the forest.

    The first region was the center of the forest, which is an

    undisturbed Mediterranean pine (Pinus brutia) and golden

    oak (Quercus alnifolia) forest. The second region was an

    area of mixed forest and agriculture, with many open

    abandoned fields. The study concluded that O. g. ophion

    during the late summer/early fall could have phosphorus,

    protein, and sodium deficiencies (Hadjisterkotis 1993).

    Although O. g. ophion are not expected to be subject to

    dietary calcium deficiency, in some other parts of the

    island, there is evidence that there might be such a

    deficiency. In Mesaoria, cattle used to lick the plaster from

    the walls, perhaps to rectify calcium deficiencies. The

    sandy soils in certain villages of Mesaoria are deficient in

    calcium.

    During rumen analysis of O. g. ophion found dead in

    their natural habitat, it was observed that a number of

    individuals had eaten small stones of gabbro (Hadjisterkotis

    1997). This type of stone has a higher phosphorus and

    potassium content than diabase, and it breaks up much

    more easily than the usual diabase. Therefore, based on the

    above evidence, it was concluded that O. g. ophion ate

    rocks and soil possibly to correct mineral deficiencies.

    Mouflon might be deficient in sodium, particularly at the

    edge of the forest during late summer and early fall

    (Hadjisterkotis 1993, 1997). In Cyprus it was observed by

    EH that domestic sheep foraging near the coast at Neta

    village on the Karpas peninsula (under Turkish military

    occupation since 1974) often visited rocky beaches to eat

    salt from seawater pools. The water in these pools, naturally

    collected during the winter storms, had evaporated, leaving

    a layer of salt. According to Varnava, former Officer of the

    Game and Fauna Service of the Ministry of the Interior,

    sheep, goats, and donkeys licked salt from the rocky

    beaches of Kormakitis in southwestern Kyrenia district

    (personal communication to EH, 2002).

    There is thus sufficient evidence that at least during

    some seasons of the year the vegetation on Cyprus isdeficient in certain minerals and nutrients, particularly

    phosphorus and sodium. Therefore, it is possible that the

    extinct Cypriot mammals could have searched for these

    minerals, as do wild and domestic herbivores today.

    A further question to be discussed is whether hippos and

    elephants enter caves to search for minerals. Redmond

    (1982) reported that elephants go deep within a cave on

    Mount Elgon in western Kenya to eat salt-laden rock. It is

    possible that, in areas where trace metal concentration in

    the topsoil are low due to leaching, and where these metals

    are only available deep in the ground, they might be more

    accessible through caves. However, by entering caves, orgoing through steep rocks on rocky beaches, these animals

    are at risk of getting caught in natural traps.

    Occasionally, mammoths entered caves to escape bad

    weather, give birth, or search for water or salt. A striking

    indication of this is the presence of quantities of mammoth

    dung in dry caves in the American southwest (Mead et al.

    1986).

    Natural traps

    Natural traps can be caves with their openings facing

    upwards, sinkholes, tar pits, bog traps, mire traps, etc. Such

    traps of modern elephants, but also of mammoth and

    mastodon remains, are well known. According to Haynes

    (1995), the main natural causes of mortality among modern

    African elephants are accidental capture in natural traps

    such as mud holes, drowning, or falling from steep slopes.

    Most Late Pleistocene mastodon finds in North America

    involve single skeletons or small numbers of individuals. A

    few mass occurrences are known from artesian springs

    (Saunders1977,1984). In South America, a mastodont has

    been found in at least one mass site (Simpson and De Paula

    Couto1957).

    At Condover in Shropshire, England, four or five wooly

    mammoths (Elephas primigenius), dating between 12,700

    and 12,300 years BP, were found in a kettle hole in 1986

    (Lister 1993; Lister and Bahn 1994). This is a feature

    formed as a result of the melting of a large buried block of

    ice left by a retreating glacier and the collapse of the

    overlying sediments. The Condover kettle hole was 10 m

    deep at its center, but at the end of the Pleistocene its sides

    were not very steep. It is therefore most likely that the

    mammoths entered it in search of food or drink and became

    128 Eur J Wildl Res (2008) 54:122133

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    8/12

    mired in mud at the bottom. The Condover site probably

    represents occasional deaths over several centuries.

    Another spectacular accumulation discovered in 1914 in

    downtown Los Angeles, CA, is the famous tarpits of

    Rancho La Brea. From these tarpits, over 100 tons of fossils

    were excavated, 1.5 million vertebrates, 2.5 million

    invertebrates, often in densely concentrated masses. The

    animals included 17 proboscideans [both mastodons andColumbian mammoths (Mammuthus columbi)]. Most of the

    remains date between 40,000 and 10,000 years ago.

    The most spectacular accumulation of large mammalian

    fossils is perhaps the accumulation ofM. columbi remains

    at a former sinkhole at Hot Springs, SD, USA (Agenbroad

    and Mead 1994; Lister and Bahn 1994). About 50

    individual mammoths were discovered up to 1994. It was

    estimated that about 100 met their deaths in the sinkhole.

    These mammoths died about 26,000 years ago, the trap

    being open for 300 to 700 years before it finally filled up

    with sediment. The individual mammoths are spread

    throughout the sediment, indicating that they did not enterat the same time. Most of the animals were young males,

    caught at their most adventurous age. Sinkholes in which

    hippos and elephants got trapped were also found in the

    Mediterranean region, particularly on Malta.

    We assume that a pygmy elephant or a pygmy hippo

    could quite easily get trapped in a natural trap. Carrington

    (1962) describes how they used to trap elephants in Africa

    with pitfalls, which he describes as the simplest and most

    effective of all elephant hunting methods widely used in

    Africa until recent times.

    The supposed behavior of elephants when one of their

    number falls into a pitfall was recorded by Pliny nearly two

    thousand yeas ago. In his Natural History (book VIII,

    chapter 8), he writes: In Africa they take them in pit-falls;

    but as soon as an elephant gets into one, the others

    immediately collect boughs of trees and pile up heaps of

    earth, so as to form a mound, and then endeavor with all

    their might to drag it out.

    Is not certain how accurate the above description of

    elephant behavior by Pliny actually is, but elephants are

    known to assist other elephants of their group to free

    themselves, particularly when they are trapped in muddy

    pools. The pitfall is probably the oldest of all forms of

    animal trap, and extinct proboscideans must have fallen

    victim to it (Lister and Bahn1994, pp 122123).

    Bunimovitz and Barkai (1996) suggested that the lowest

    bone deposit at Aetokremnos is natural, not of anthropo-

    genic origin. Hadjisterkotis et al. (2000) noted that the

    piling of such a large number of hippos in such a small spot

    in such steep cliffs usually takes place in the case of water

    holes or sink holes with steep sides. Turner and Weaver

    (1981, Fig. 7.3, p 108) describe one such death trapwater

    hole in the Chocolate Mountains, CA, where the remains of

    34 trapped bighorn sheep were found in a steep-sided

    natural water tank in 1969. Bighorn were in peak

    abundance in the Trap Cave deposits during the cold

    phases of the Pleistocene. Two peaks, one at about

    18,000 years ago and another 14,000 years ago, coincided,

    respectively, with the glacial maximum and the severe

    Older Dryas cold phase (Geist1999).

    However, there is no geomorphic evidence for such atrap at Aetokremnos. The floor of the rock shelter did not

    have any evidence of sedimentation and there are no

    features on the cliffs or plateau above Aetokremnos to

    account for a repeated natural jump site (Mandel and

    Simmons 1997). The presence of one frog and an aquatic

    snake could indicate the presence of water that attracted the

    birds and mammals for drinking. However, the floor of the

    rock shelter did not have any evidence of sedimentation or

    other debris indicating the presence of a pond or running

    water or a sink hole (Mandel and Simmons 1997, Mandel

    1999).

    Natural predators

    Besides the possibility of a large mammal entering a cave

    or a natural trap and dying there, complete animals

    carcasses or parts of them can be brought into a cave by a

    predator. According to Lister and Bahn (1994), mammoth

    remains found in caves frequently were carried in by

    humans or other predators. For example, juvenile mammoth

    remains were accumulated in Friesenhahn Cave in Texas,

    USA, by the extinct Scimitar cat (Homotherium), and in

    Kents Cavern in southwestern England, by the Spotted

    hyena (Crocuta crocuta). At Kents Cavern, a former hyena

    den, thousands of hyena fossils have been excavated,

    mingled with bones of juvenile woolly mammoths, many

    of which bear the tooth marks of these scavengers. Neither

    big cats nor hyenas could have hunted adult mammoths, but

    they may have killed young animals.

    Since on Cyprus there is no evidence of large predators

    capable of killing pygmy hippos or elephants, the accumu-

    lation of their bones cannot be attributed to predators or

    scavengers. The only predator on Cyprus, besides man, at

    the time of Aetokremnos was the extinct endemic genet

    G. plesictoides(Steensma and Reese1999). Genets feed on

    invertebrates, particularly insects and small rodents. Rep-

    tiles, amphibians, birds, and other small mammals are also

    taken, as well as wild fruits.

    Based on the above reasoning, we therefore reject the

    hypothesis that predators or natural traps were responsible

    for the collection of hippos and elephants at Aetokremnos.

    Conversely, we accept the conclusion of Hadjisterkotis et

    al. (2000), Reese (1989, 1995, 1996, 2001; Reese et al.

    1999), and Simmons (1991a, b, 1996, 1999, 2001, 2002)

    that the bone accumulations are of anthropogenic origin and

    Eur J Wildl Res (2008) 54:122133 129

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    9/12

    that the people of the Akrotiri peninsula were responsible

    for the extinction of the two endemic mammal species in

    that area.

    However, it is possible that natural traps were the reason

    for trapping these animals in caves elsewhere on the island,

    attracted by the cave microclimate with possible availability

    of water, or even concentrations of minerals. Shortage of

    water under drought conditions conceivably drove them toseek water/moisture in caves or in hollow places in the

    sides of cliffs and to look for protection from the blazing

    sun during the long dry summers. Packed in these places to

    avoid the burning Mediterranean sun and seeking the

    moisture oozing from the cave walls, most possibly

    suffered the torments of death from dehydration when

    water sources gave out, or from thirst and hunger when

    caught in natural traps.

    The numerous sites on the island yielding large numbers of

    trapped or otherwise killed mammals, together with the

    consequences of the indiscriminate hunting of hippos and

    elephants at Aetokremnos and the subsequent extinction ofthese species on Cyprus, record the final events of extinction.

    They provide a complex but readable record of a process

    whose outcome is clearly known. These deposits may not

    record the death of the very last animal, but they are

    evidence of major mortality processes that affected both

    pygmy mammals on Cyprus.

    References

    Agenbroad LD, Mead JL (eds) (1994) The Hot Springs mammoth site:a decade of field and laboratory research in paleontology,

    geology and paleoecology. Mammoth Site of Hot Springs, South

    Dakota, Hot Springs

    Ammerman A, Noller J (2005) New light on Aetokremnos. World

    Archaeol 37(4):533543

    Ayotte JB (2004) Ecological importance of licks to four ungulate

    species in north-central British Columbia. M.S. thesis, University

    of Northern British Columbia

    Ayotte JB, Parker KL, Joselto MA, Gilingham MP (2006) Chemical

    compostion of lick soils: functions of soil ingestion by four

    ungulates. J Mammal 87(5):878888

    Bonfiglio L, Burgio L (1992) Significato paleoambientale e cronolo-

    gico delle mammalofaune pleistoceniche della sicilia in relazione

    allEvoluzione paleogeographica. Quaternario 5(2):223234

    Bonfiglio L, Insacco C (1992) Palaeoenvironmental, Paleontologicand stratigraphic significance of vertebrate remains in Pleistocene

    limnic amd alluvial deposits from southeastern Sicily. Palaeogeogr

    Palaeoclimatol Palaeoecol 95:195208

    Bonfiglio L, Piperno M (1996) Early faunal and human populations. In:

    Leighton R (ed) Early societies in Sicily: new developments in

    archaeological research. Accordia specialist studies on Italy 5.

    Accordia Research Centre, University of London, London, pp 2129

    Bunimovitz S, Barkai R (1996) Ancient bones and modern myths:

    ninth millennium BC Hippopotamus hunters at Akrotiri Aetok-

    remnos, Cyprus? J Mediterr Archaeol 9(1):8589

    Buss IO (1990) Elephant life: fifteen years of high population density.

    Iowa State University Press, Ames, pp 1191

    Cairns-Smith AG, Hartman H (1986) Clay mineral and the origin of

    life. Cambridge University Press, Cambridge

    Carrington R (1962) Elephants: a short account of their natural

    history, evolution, and influence on mankind. Penguin Books

    in association with Chatto and Windus, Harmondsworth,

    Middlesex

    Chamberlin LC, Timmerman HR, Snider B, Dieken F, Loescher B,

    Fraser D (1977) Physical and chemical characteristics of some

    natural licks used by big game animals in northern Ontario. Proc

    North Am Moose Conf Workshop 13:200214Church DC (1975) Digestive physiology and nutrition of ruminants.

    O&B Books, Corvallis

    Coates KP, Schemnitz SD, Peters JT (1990) Use of rodent middens as

    mineral licks by bighorn sheep. Proc Bienn Symp North Wild

    Sheep Goat Counc 7:206209

    Dalke PD, Beeman RD, Kindel FJ, Robel RJ, Williams TR (1965)

    Seasonal movements of elk in the Selway River drainage, Idaho.

    J Wildl Manage 29:333338

    Davison E (1930) Report on Wankie Game Reserve to the end of the

    year ending 31 March 1930. Manuscript letter to chief forest

    officer, Rhodesian Agriculture Department, Salisbury, on file,

    Awange National Park Main Camp

    Davison E (19301935) Monthly progress reports, Wankie Game

    Reserve (19301935). Manuscript on file, Hwange National Park

    Dormaar JF, Walker BD (1996) Elemental content of animal licks

    along the eastern slopes of the Rocky Mountains in southern

    Alberta, Canada. Can J Soil Sci 76:509512

    Douglas-Hamilton I (2003) Migrationspachyderms hit the road,

    desert elephants need sustenance, will travel. Natl Geogr 203(2)

    Eltringham SK (1999) The hippos, natural history and conservation.

    Academic Press, London, pp 1184

    Estes RD (1992) The behaviour of African mammals: including

    hoofed mammals, carnivores, primates. University of California

    Press, London, pp 1611

    Faure M (1986) Les Hippopotamida (Mammalia, Artiodactyla) du

    Gisement Plistocne Ancien dOubeidiyeh. In:Tchernov E (ed)

    Les Mammiferes du Plistocne Infrieur de la Vale du Jordan

    Oubeidiyeh. Mmoires et Travaux du Centre de Recherche

    Francais de Jrusalem No. 5. Association Palorient, Paris,

    pp 107142

    Fraser D, Reardon E (1980) Attraction of wild ungulates to mineral-

    rich springs in central Canada. Holarct Ecol 3:3640

    Gass IA (1980) The Troodos massif: Its role in the unravelling of the

    amphibolites problem and its significance in the understanding of

    constructive plate margin processes. In: Panayiotou A (ed)

    Ophiolites. Proceedings of the International Ophiolite Symposium,

    Cyprus, 1979. Geological Survey Department, Nicosia, pp 2335

    Geist V (1971) Mountain sheep: a study in behavior and evolution.

    University of Chicago Press, Chicago, pp 1383

    Geist V (1999) Adaptive strategies in American mountain sheep:

    Effects of climate, latitude and altitude, ice age evolution, and

    neonatal security. In: Valdez R, Krausman PR (eds) Mountain

    sheep of North America. University of Arizona Press, Tucson, pp

    192

    208Hadjisterkotis E (1993) The Cyprus mouflon Ovis gmelini ophion,

    management conservation and evolution. Ph.D. thesis, Depart-

    ment of Renewable Resources, McGill University

    Hadjisterkotis E (1996a) Herkunft, Taxonomie und neuere

    Entwicklung des Zyprischen Mufflons (Ovis gmelini ophion)

    (Origin, taxonomy and recent developments in the Cyprian wild

    sheep [Ovis gmelini ophion]). Z Jagdwiss 42:104110

    Hadjisterkotis E (1996b) Ernhrungsgewohnheiten des Zyprischen

    Mufflons Ovis gmelini ophion (food habits of the Cyprus

    mouflon Ovis gmelini ophion). Z Jagdwiss 42:256263

    Hadjisterkotis E (1997) Mineral consumption by Cyprus mouflon. In:

    Hadjisterkotis E (ed) Proceedings of the Second International

    130 Eur J Wildl Res (2008) 54:122133

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    10/12

    Symposium on Mediterranean Mouflon. Game Fund, Nicosia,

    pp 5154

    Hadjisterkotis E (1998) Wildlife research in Cyprus. Gibier Faune

    Sauvage. Game Wildl 15(Hors serie 3):11871194

    Hadjisterkotis E (1999) Gefahren fr das Zyprische Mufflon

    aufgrund des Vorkommens als einzelne Restpopulation in einem

    einzigen Verbreitungsgebiet (Dangers facing the Cyprus mou-

    flon from being one population in one reserve). Z Jagdwiss

    45:2734

    Hadjisterkotis E (2001) The Cyprus mouflon, a threatened species in abiodiversity hotspot area. In: Nahlik A, Walter U (eds)

    Proceedings of the International Mouflon Symposium, Sopron,

    pp 7181

    Hadjisterkotis E, Bider JR (1997) Cyprus. In: Shackleton DM (ed)

    Wild sheep and goats and their relatives, status survey and

    conservation action plan for Caprinae. Information Press, Oxford,

    pp 8992

    Hadjisterkotis E, Masala B (1995) Vertebrate extinction in Mediterranean

    islets: an example from Cyprus. Biogeographia 18:691699

    Hadjisterkotis E, Vakanas C (1997) Agricultural damages caused by

    mouflonOvis gmelini ophion in Cyprus. In: Hadjisterkotis E (ed)

    Proceedings of the Second International Symposium on Medi-

    terranean Mouflon. Game Fund, Nicosia, pp 111117

    Hadjisterkotis E, Van Haaften JL (1997) Die Niederwildjagd im Wald

    von Paphos und ihre Auswirkungen auf das gefhrdete zyprische

    MufflonOvis gmelini ophion(small game hunting in the forest of

    Paphos and its effects on the endangered Cyprian mouflon Ovis

    gmelini ophion). Z Jagdwiss 43:279282

    Hadjisterkotis E, Masala B, Reese D (2000) The origin and extinction

    of the large Pleistocene Mammals of Cyprus. Biogeographia

    21:593606

    Harland WB, Cox AV, Llewellyn PG, Pickton CAG, Smith AG,

    Walters R (1982) A geological time scale. Cambridge University

    Press, Cambridge

    Haynes G (1995) Mammoths, mastodonts & elephants: biology,

    behavior, and the fossil record. Cambridge University Press,

    Cambridge, pp 1423

    Heard DC, Williams TM (1990) Ice and mineral licks used by caribou

    in winter. Rangifer Spec Issue 3:203206

    Hebert D, Cowan IM (1971) Natural salt licks as part of the ecology

    of the mountain goat. Can J Zool 49:605610

    Heimer WE (1973) Dall sheep movements and mineral lick use.

    Project W-17-2. W-17-3, W-17-4, W-17-5. Report to the Alaska

    Department of Fish and Game, Fairbanks

    Heimer WE (1988) A magnesium-driven hypothesis of Dall sheep

    mineral lick use: preliminary tests and management relevance.

    Proc Bienn Symp North Wild Sheep Goat Counc 6:269278

    Held SO (1989) Colonization cycles on Cyprus 1: the biogeographic

    and paleontological foundations of early prehistoric settlement.

    Report of the Department of Antiquities, Cyprus, pp 728

    Hold RH, Dudley JP, McDowell LR (2002) Geography in the

    African elephant in relation to availability of dietary sodium. J

    Mammal 83(3):652664

    Holl SA, Bleich VC, Rios B (1980) San Gabriel bighorn sheep. US

    For Serv San Bernardino Natl For Annu Rep

    Holman JA, Abraczinskas LM, WestJohn DB (1988) Pleistocene

    proboscideans and Michigan salt deposits. Natl Geogr Res 4

    (1):45

    Horwitz W (ed) (1960) Official methods of analysis of the association

    of official agricultural chemists, 9th ed. Association of Official

    Agricultural Chemists, Washington DC, pp 1832

    Horwitz LK, Tchernov E (1990) Cultural and environmental implica-

    tions of hippopotamus bone remains in archaeological context in

    the levant. Bull Am Sch Orient Res 280:6776

    Houtekamer JL, Sondaar PY (1979) Osteology of the fore limb of the

    Pleistocene dwarf hippopotamus from Cyprus with special

    reference to phylogeny and function. Proc K Ned Akad Wet B

    82(4):411448

    Hunt CO, Schembri PJ (1999) Quaternary environments and bioge-

    ography of the Maltese Islands. In: Facets of Maltese prehistory.

    Prehistoric society of Malta, Valetta, pp 4175

    Johns T, Duquette M (1991) Detoxification and mineral supplemen-

    tation as functions of geophagy. Am J Clin Nutr 53:448456

    Joubert D, Joubert B (producers) (1988) The stolen river (video film).

    Wildlife films, Botswans and Partridge Productions Ltd., for The

    National Geographic Society, Washington DCKlaus G, Schmid B (1998) Geophagy at natural licks and mammal

    ecology: a review. Mammalia 62:481497

    Knight MH, Knight-Elof AK, Bornman JJ (1988) The importance of

    borehole water and lick sites to Kalahari ungulates. J Arid

    Environ 15:269281

    Koen JH, Hall-Martin AJ, Easmus T (1988) Macro nutrients in plants

    available to Knysna, Addo, and Kruger National Park elephants.

    S Afr J Wildl Res 18(2):6971

    Kreulen DA (1985) Lick use by large herbivores: a review of benefits

    and banes of soil consumption. Mamm Rev 15:107123

    Lax E (1996) A gazetteer of Cretan paleontological localities. In:

    Reese DS (ed) Pleistocene and holocene fauna of Crete and its

    first settlers. Prehistory Press, Madison, pp 132

    Lister AM (1993) The Condover mammoth site: excavation and

    research 19861993. Cranium 10:6167

    Lister A, Bahn P (1994) Mammoths. MacMillan, New York, pp 1168

    Mandel RD (1999) Stratigraphy and sedimentology. In: Simmons AH

    (ed) Faunal extinctions in an island society. Kluwer, London,

    pp 4969

    Mandel RD, Simmons AH (1997) Geoarchaeology of the Akrotiri

    Aetokremnos Rockshelter, Southern Cyprus. Geoarchaeology 12

    (6):567605

    Matthiesson P, Porter E (1974) The tree where man was born: the

    African experience. Avon, New York

    McCallum JE, Robertson AHF (1990) Pulsed uplift of the Troodos

    Massifevidence from the Plio-Pleistocene Mesaoria basin. In:

    Malpas J, Moores EM, Panayiotou A, Xenophontos C (eds)

    Ophiolites, oceanic crustall analogues. Proceedings of the

    symposium Troodos 1987. Geological Survey Department,

    Nicosia, pp 217229

    McDowell LR (1985) Contribution of tropical forages and soil

    towards meeting mineral requirements of grazing ruminatnts.

    In: McDowell LR (ed) Nutrition of grazing ruminants in warm

    climates. Academic Press, London, pp 165188

    Mead JL, Agenbroad LD, Davis OK, Martin PS (1986) Dung of

    Mammuthus in the arid southwest, North America. Quat Res

    25:121127

    Milewski AV (2000) Iodine as a possible controlling nutrient for

    elephant populations. Pachyderm 28:7890

    Milewski AV, Diamond RE (2000) Why are very large herbivores

    absent from Australia? A new theory of micronutrients. J

    Biogeogr 27:957979

    Moss C (1988) Elephant memories: thirteen years in the life of an

    elephant family. New Southwest J Anthropol 6(2):139142

    Mukasa SB, Ludden JN (1987) Uranium-lead ages of plagiogranites

    from the Troodos ophiolite, Cyprus, and their tectonic signifi-

    cance. Geology 15(9):825828

    Murie A (1934) The moose of Isle Royale. University of Michigan

    Museum of Zoology miscellaneous publications No. 25, Ann

    Arbor

    Nowak RM, Paradiso JL (1983) Walkers mammals of the world, vol

    2, 4th edn. John Hopkins, Baltimore

    National Research Council (1985) Nutrient requirements of sheep, 6th

    edn. National Academy Press, Washington DC, pp 199

    Olivier RCD (1975) Aspects of skin physiology I the pygmy

    hippopotamus Choeropsis liberensis. J Zool 176:211213

    Eur J Wildl Res (2008) 54:122133 131

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    11/12

    Redmond I (1982) Saltmining elephants of Mount Elgon. Swara 5

    (4):2831

    Reese DS (1985) Hippopotamus and elephant teeth from Kition. In:

    Karageorghis V (ed) Excavations at Kition V. The pre-Phoenician

    levels II. Department of Antiquities, Nicosia, pp 391408

    Reese DS (1989) Tracking the extinct pygmy hippopotamus of

    Cyprus. Field Mus Nat Hist Bull 60(2):2229

    Reese DS (1995) The Pleistocene vertebrate sites and fauna of Cyprus.

    Geological Survey Department Bulletin No. 9, Nicosia, pp 230

    Reese DS (1996) Cypriot hippo hunters no myth. J Mediterr Archaeol9(1):107112

    Reese DS (2001) Some comments on the Akrotiri-Aetokremnosfauna.

    In: Swiny S (ed) The earliest prehistory of Cyprus: from

    colonization to exploitation. American Schools of Oriental

    Research, Boston, pp 1936

    Reese DS et al (1999) The faunal assemblage. In: Simmons AH,

    Faunal (eds) Extinction in an island society. Kluwer, London, pp

    153191

    Reisenhoover KL, Peterson RO (1986) Mineral licks as a sodium

    source for Isle Royale moose. Oecologia 71:121126

    Robbins CT (1993) Wildlife feeding and nutrition. Academic Press,

    New York, pp 352

    Robertson AHF (1990) Tectonic evolution of Cyprus. In: Malpas J,

    Moores EM, Panayiotou A, Xenophontos C (eds) Ophiolites,

    oceanic crustal analogues. Proceedings of the symposium Troodos

    1987. Geology Survey Department, Nicosia, pp 235250

    Ruggiero RD, Fay JM (1994) Utilization of termitarium soils by

    elephants and its ecological implications. Afr J Ecol 32:222232

    Saunders JJ (1977) Late Pleistocene vertebrates of the western Ozark

    Highland, Missouri. Illinois State Museum Reports of Inves-

    tigations, No. 33

    Saunders JJ (1984) Late Pleistocene Mastodonts of North America.

    Paper presented at the Society for American Archeology Annual

    Meeting, Portland, 1214 April 1984

    Schaller G (1977) Mountain monarchs: wild sheep and goats of the

    Himalaya. University of Chicago Press, Chicago, pp 425

    Serreri E, Hadjisterkotis E, Naitana S, Rando A, Ferranti P, Corda M,

    Manca L, Masala B (2000) The organization of the -globin

    gene cluster and the nucleotide sequence of the -globin gene of

    Cyprus Mouflon (Ovis gmelini ophion). In: Di Prisco G, Giardina

    B, Weber RE (eds) Hemoglobin function in vertebrates:

    molecular adaptation in extreme and temperate environments.

    Springer, Berlin Heidelberg New York, pp 109120

    Shipman P (1975) Implications of drought for vertebrate fossils

    assemblage. Nature 257:667668

    Simmons AH (1991a) Humans, island colonization and Pleistocene

    extinctions in the Mediterranean: the view from Akrotiri

    Aetokremnos, Cyprus. Antiquity 65(249):857869

    Simmons AH (1991b) One flew over the hippos nest: extinct

    Pleistocene fauna, early man, and conservative archaeology on

    Cyprus. In: Clark GA (ed) Perspectives on the past: theoretical

    biases in Mediterranean huntergatherer research. University of

    Pennsylvania Press, Philadelphia, pp 282304

    Simmons AH (1996) Whose myth? Archaeological data, interpreta-

    tions and implications for the human association with extinct

    Pleistocene fauna at Akrotiri Aetokremnos, Cyprus. J Mediterr

    Archaeol 9(1):97105

    Simmons AH (1999) Faunal extinction in an island society: pygmy

    hippopotamus hunters of Cyprus. Kluwer, London, pp 381

    Simmons AH (2001) The first humans and last pygmy hippopotami of

    Cyprus. In: Swiny S (ed) The earliest prehistory of Cyprus: from

    colonization to exploitation. American Schools of Oriental

    Research, Boston, pp 118

    S im mons A H ( 2002) The r ol e of i sl ands i n pus hi ng t he

    Pleistocene extinction envelope: the strange case of the

    Cypriot pygmy hippos. In: Waldren WH, Ensenyat JA (eds)

    World islands in prehistory: international insular investiga-

    tions. V Deia international conference of prehistory. British

    archaeological reports international series 1095. Archaeopress,

    Oxford, pp 406414

    Simmons AH, Reese DS (1993) Hippo hunters of Akrotiri. Archae-

    ology 46(5):4043

    Simmons AH, Wigand PE (1994) Assessing the radiocarbon determi-

    nations from AkrotiriAetokremnos, Cyprus. In: Bar-Yosef O, Kra

    RS (eds) Late quarternary chronology and paleoclimates of the

    Eastern Mediterranean. American School of Prehistoric Research,Cambridge, pp 247264

    Simpson GG, De Paula Couto C (1957) The mastodonts of Brazil. Am

    Mus Nat Hist Bull 112:125190

    Sinclair ARE (1977) The African buffalo: a study of resource

    limitation of populations. University of Chicago Press, Chicago

    Singer FJ (1978) Glacier national park, Montana. J Wildl Manage

    42:591597

    Smith A (1849) Under the description of Hippopotamus amphibius.

    In: Illustrations of the zoology of South Africa Mammals. Smith,

    Elder & Co., London

    Smith SG (1992) Toxification and detoxification of plant compounds

    by ruminants: an overview. J Range Manag 45:2530

    Spaan A (1996) Hippopotamus cretzburgi: the case of the Cretan

    hippopotamus. In: Reese DS (ed) Pleistocene and holocene fauna

    of Crete and its first settlers. Prehistory Press, Madison, pp 99110

    Stark MA (1986) Analysis of five natural soil licks. Benoue National

    Park; Cameroon, West Africa. Afr J Ecol 24:181187

    Steensma K, Reese DS (1999) Genet. In: Simmons AH (ed) Faunal

    extinctions in an island society. Kluwer, London, pp 167169, 165

    Stockstad DS (1950) The chemical characterization of natural licks

    used by big game animals in western Montana. M.S. thesis,

    Montana State University

    Sukumar R (2003) The living elephants: evolution ecology, behavior,

    and conservation. Oxford University Press, Oxford, pp 478

    Tabler EC (ed) (1971) [James Chapmans] travels in the interior of

    South Africa 18491863: hunting and traiding journeys from

    Natal to Walvis bay and visits to lake Ngami and Victoria falls,

    part 2. Balkema, Cape Town

    Tankersley N (1984) Mineral lick use by Dall sheep in the Watana

    Creek Hills, Alaska. Proc Bienn Symp North Wild Sheep Goat

    Counc 4:211230

    Tankersley N, Gasaway WC (1983) Mineral lick use by moose in

    Alaska. Can J Zool 61:22422249

    Tchernov E (1981) The impact of the postglacial on the Fauna of

    South-West Asia. In: Frey W, Uerpmann H-P (eds) Contributions

    to the environmental history of South-West Asia. Wiesbaden,

    Reichert, pp 197216

    Tchernov E (1984) The fauna of Sefunim Cave, Mt. Carmel. In:

    Ronen A (ed) Sefunim prehistoric sites, Mount Carmel, Israel.

    British archaeological reports international series 230, Oxford,

    pp 401419

    Toumazos P, Hadjisterkotis E (1997) Diseases of the Cyprus mouflon

    as determined by standard gross and histopathological methods.

    In: Hadjisterkotis E (ed) Proceedings of the second international

    symposium on Mediterranean Mouflon. Game Fund, Nicosia,

    pp 150161

    Tracy BF, McNaughton J (1995) Elemental analysis of mineral lick

    soils from the Serengeti National Park, the Konza Prairie and

    Yellowstone National Park. Ecography 18:9194

    Turner JC, Weaver RA (1981)Water. In:Monson G, Summer L (eds) The

    desert bighorn. University of Arizona Press, Tucson, pp 100112

    Walker C (1991) Savuti: the vanishing river. Southern Book,

    Johannesburg, p 129

    Watts TJ (1979) Detrimental movement patterns I a remnant

    population of bighorn sheep (Ovis canadensis mexicana). M.S.

    thesis, New Mexico State University, Las Cruces

    132 Eur J Wildl Res (2008) 54:122133

  • 7/25/2019 Reese_considerations on the Potential Use of Cliffs

    12/12

    Weeks HP Jr (1978) Characteristics of mineral licks and behavior of visiting

    white-tailed deer in southern Indiana. Am Midl Nat 100:384395

    Weeks HP Jr, Kirkpatric CM (1976) Adaptation of white-tailed deer to

    naturally occurring Na+ deficiencies. Wildl Manage 40:610625

    Weir JS (1969) Chemical properties and occurrence on Kalahari sand

    of salt licks created by elephants. J Zool (London) 158:293310

    Weir JS (1972) Spatial distribution of elephants in an African national

    park in relation to environmental sodium. Oikos 23:113

    Williams TR (1962) The significance of salt and natural licks in elk

    management. M.S. thesis, University of Idaho

    Wright PG (1987) Thermoregulation in the hippopotamus on land. S

    Afr J Zool 22:237242

    Eur J Wildl Res (2008) 54:122133 133