Versie 3 word 2009

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Evolutionary adaptation in the Spanish Anchitheriinae
in relation to environmental and climatic changes.
Masterthesis Biogeology
Stella Heijnens 3021394
Supervisors;
Dr. W. Wessels
Prof. Dr. J.W.F. Reumer
1
Index
-
General introduction
3
-
Thesis introduction
4
Main questions, outline and problems
Chapter 1 - Background and Setting
7
-
European Miocene Climate
7
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European Miocene Environment
8
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Anchitherium – MN3-MN9
9
o
o
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Taxonomy
Species included
Hipparion – MN9
o
o
10
Taxonomy
Species included
-
Systematic Paleontology Anchitherium
12
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Distribution
16
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Geological setting
16
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Biochronology
19
Chapter 2 – Literature Research and Methods
-
Evolution and adaptation
o
o
o
22
22
Body and tooth size
Micro and Mesowear
Isotope analysis
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Hypsodonty
25
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Climate and environment
26
o
o
Palaeoclimate and proxies
Palaeoenvironment and proxies
Chapter 3 - Practical research
31
Chapter 4 – Discussion
55
Chapter 5 – Conclusion
59
-
References
62
2
Introduction
The Anchitheriinae are an extinct subfamily of Equidae that first appeared in North America
near the base of the Miocene. The Anchitheriinae clade migrated via Asia to Europe and has
its first occurrences in Europe during the middle Orleanian, MN 3. The entire genus became
extinct in the Vallesian, MN 9. Thus the genus existed in Europe approximately from 20 until
10 Ma ago (Kaiser 2009, Forsten 1991) (for MN zonation see de Bruijn 1992).
Anchitheriinae have generally been considered to be browsing horses that occupied forested
habitats because of their low crowned, lophodont teeth (Forsten 1991, Janis 1995). One of
the classic examples of faunal turnover in the fossil record is the Late Miocene transition
from faunas dominated by Anchitheriinae with low crowned molar teeth to faunas with
Hipparion horses characterized by high-crowned teeth (Eronen et al. 2009, Strömberg 2005).
This spread of Hipparion horses is often associated with the expansion of open habitats and
also the increase of C4 grasses.
Both in the New and the Old World fossil material of horses consists mainly of isolated teeth
(Forsten 1991). It is generally accepted that Anchitheriine horses did not display an
evolutionary increase in tooth crown height prior to their extinction (Eronen et al. 2009).
“Lineages that remained as browsers in the Mid Miocene did not later transform into
grazers, the general evolutionary pattern in the late Miocene is for browsing lineages to be
replaced by ones adapted to more fibrous diets rather than the browsers themselves
undergoing evolutionary change” (Janis 1994). Recent research on Anchitherium teeth as
well as body size and isotopic composition of their dentition has shown however that
adaptations to the overall changing environments in Europe as well as to a changing local
climate and vegetation may have occurred in the Anchitheriine genus after all (Forsten 1991,
Eronen et al. 2009, Kaiser 2009).
Increased crown height has traditionally been used as an indicator for a change in diet
towards more abrasive foods, often towards eating (C4) grass (Retallack 1983, Janis 1995,
Fortelius et al. 2002). Therefore it has also been used as an indicator for environmental
change, shifts towards a more open vegetation and as an aridity proxy (Janis 1995, Fortelius
et al. 2002). An increase in abrasiveness of the food may not necessarily be due to phytoliths
in grass, it may also be caused by increased fibrousness, extraneous dust or a decrease in
nutritive value that requires the animal to increase its food uptake (Fortelius et al. 2002,
Strömberg 2005). There is also discussion about whether hypsodonty is a direct evolutionary
adaption or whether it might be due to phylogenetic effects, or ‘exaptation’ (Gould and Vbra
1981). Exaptation is a term coined by Gould and Vbra for traits shaped by selection to
perform a different function than they are presently serving, or that result from other
processes than natural selection. Therefore using it as a proxy for environment or climate
may be questionable.
3
Thesis introduction, Anchitherium
Anchitherium (meaning near-beast) is a small three toed horse that originates from the
genus Miohippus in North America during the Early Miocene. As Anchitherium moved
through Asia into Europe (MN 3) it underwent a phase of major diversification, among
others giving rise to the much larger genus Sinohippus. Anchitherium is part of the first of
four equid migrations from North America to the Old world. The second migration wave
brought the genus Hipparion to the Old world and after a short period of co-occurrence the
genus Anchitherium went extinct during the Late Miocene (MN 9) (Salesa et al. 2004).
Anchitherium is generally thought to be a browsing type of horse living in forested
environments because of its three toes and low crowned, lophodont teeth (Forsten 1991,
Janis 1995). Classically the extinction of the genus Anchitherium has been seen as a failure to
adapt to the more open and more arid vegetation of the Late Miocene. The Hipparion horse
with its high-crowned teeth is generally seen as the genus outcompeting the low-crowned
Anchitherium in a changing environment where Hipparion has the evolutionary advantage
(Eronen et al. 2009, Strömberg 2005).
Recently however Eronen et al. (2009) and Kaiser (2009) presented research showing that
Anchitherium may yet have adapted to the dryer conditions of the early Miocene. Eronen et
al. (2009) propose that Anchitheriines in Spain show ‘incipient hypsodonty’ and argue that
this is evidence that they did respond to the increasing aridity of Europe that started in the
Iberian region. They compare Spanish specimens with specimens found in Germany and
show by means of cluster analysis of fossil Anchitheriinae and modern day ungulate tooth
morphology that Spanish specimens cluster with ungulates that eat foliage and grass and the
German specimens cluster with modern day ungulates that eat mostly foliage. They
conclude that the Spanish species were slightly more adapted to drier conditions than the
German species and that Anchitherium may not be the purely browsing horse that it was
always thought to be. A problem concerning Eronen who links Anchitherium’s ‘incipient
hypsodonty’ to a diet of more abrasive food and an adaptation to drier conditions is brought
up by Kaiser (2009). According to Kaiser 2009 ‘there is a growing consensus that many
species of Neogene equids showing increased crown height were in fact mixed feeders and
even browsers’ (Hayek et al. 1991, Quade et al. 1994, MacFadden et al. 1999, Kaiser et al.
2000, Kaiser 2003). This doesn’t rule out the possibility Eronen suggests, that Anchitherium
may have become a mixed feeder while adapting to dryer conditions. But it does indicate
that hypsodonty is not necessarily a good indicator of adaptation to eating dryer, more grass
like vegetation.
However, Kaiser (2009) also concludes that Anchitherium might yet have adapted to a mixed
feeding strategy. He bases his results on a different proxy, the mesowear patterns in the
fossil teeth of Anchitherium. This proxy was developed by Fortelius and Solounias in 2000.
He concludes that these horses may have had a more abrasive diet than previously thought.
Kaiser concludes that members of the ‘Cormohipparion clade’ or Hipparion horses, that
arrived in Europe from North America, introduced competition for Anchitherium in its
feeding niche. He proposes that this was the case because Anchitherium had already
4
developed a mixed feeding strategy and Hipparion was also eating grass. Unfortunately
Kaiser (2009) does not explain the reason why Anchitherium had turned this strategy,
whereas Eronen et al. (2009) point to climatic and environmental change especially in Spain.
An interesting point raised by Kaiser and Solounias (2003) is that Hipparion upon entering
Europe changed its feeding strategy back to a more intermediate diet and even browsing
forms established in Central Europe. This then would be in support of a hypothesis that
Anchitherium may have changed to mixed feeding as an answer to competition in its dietary
niche.
Salesa et al. (2010) comment on Eronen et al. (2009) with two very valid points of critique.
First of all they point out that Eronen et al. (2009) do not take into account the actual
diversity of the Iberian representatives of Anchitherium. Therefore a comparison between
the specimens from Germany, which are very homogeneous because they come from a
single locality, and specimens from Spain, which represent a wide spatial range, is not
possible. This taxonomic comment of Salesa et al. (2010) on Eronen’s work is very important
and not only for Eronen’s research but for this thesis as well. The second point of critique is
that Eronen et al. (2009) not only use Spanish fossils from a wide spatial range but from a
wide temporal range as well. The German specimens in contrast are all from the same time
period. The Spanish fossils are from many different fossil sites and all represent different
time periods. According to Salesa et al. (2010) the comparison between Spain and Germany
as a whole is invalid based on these errors. Eronen et al. (2010) subsequently reply pleading
for the usefulness of looking at adaptations on the genus level.
Main questions and complicating factors
The interesting point brought up by Eronen et al. (2009) and also by Kaiser (2009) remains
and gives rise to more questions that form the main motivation for writing this thesis;
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Did Anchitherium adapt to eating grass (mixed feeding) or did Anchitherium fail to
adapt to the changing environmental conditions of the Early Late Miocene?
-
Shortly after the Hipparion-date, did Anchitherium go extinct because it didn’t adapt
or didn’t adapt quick enough to a changing environment or was it due to competition
of the Hipparion horse in its feeding (Kaiser 2009) and or living niche?
-
Did the environment change so drastically during the early Late to Late Miocene that
Anchitherium was likely to be forced into evolutionary adaptation or face extinction?
Apart from the supposed evolutionary changes that occurred within Anchitherium there are
many complicating factors that make this a very non-straight forward problem. Most of
these factors will be discussed in following separate chapters, they will be shortly introduced
here;
Incipient hypsodonty, as Eronen proposes the Spanish Anchitheriinae had developed, may
not necessarily be an evolutionary adaptation specifically for eating grass or even for
excessive tooth wear. A discussion about the development of hypsodonty is still ongoing.
5
And even if hypsodonty is an adaptation for excessive wear, it may be caused by other things
apart from eating grass such as; grid content, extrageneous dust or increased food uptake
due to switching to a less nutritious food source (Strömberg 2005, Eronen et al. 2009).
Simply looking at the level of hypsodonty will therefore not be enough to shed light on the
main questions of this thesis.
Furthermore Anchitherium went extinct shortly after the ‘Hipparion-date’ (Kaiser 2009,
Forsten 1991). This may indicate that the reason Anchitherium went extinct was due to
competition of Hipparion. Classically Anchitherium is seen as a browsing horse and Hipparion
as one of the first hypsodont grazing/mixed feeding horses. So within the feeding niche
these two genera should not present a threat to one another. If they did however invade
each other’s feeding niche, there are technically three possible hypotheses;
-
Hipparion changed its feeding strategy to mixed feeding or browsing (Kaiser and
Solounias 2003) thus invading Anchitherium’s browsing niche.
-
Anchitherium changed its feeding strategy towards more mixed feeding and
therefore partly entered the in-migrating Hipparion’s grazing niche.
-
The last possible hypothesis is that both horses changed their feeding strategies
towards mixed feeding and thus occupied the same feeding niche.
The evidence for a shift towards more mixed feeding by Anchitherium that is presented by
Kaiser (2009) and Eronen et al. (2009) suggests that this shift happened before the
Hipparion-date. And Kaiser and Solounias (2003) suggest that Hipparion also changed its
feeding strategy from grazing to a more mixed feeding to even browsing strategy upon
entering Europe. This would make sense because changing to a feeding niche that is already
occupied by another species is not a logical evolutionary step. So whichever adaptation took
place, by Anchitherium, by Hipparion or by both, it most likely happened before Hipparion
entered Anchitheriine territory. Competition in a spatial sense is also a form of competition
as it is generally uncommon for two equine genera or even two equine species to inhabit the
same habitat. We see this in fossil as well as in modern living assemblages (Janis, 2008). This
however may also be closely linked to equine species often sharing the same food source.
Also if Anchitherium were a pure browsing horse it would live in the forest and the grazing
Hipparion would inhabit the plains, which were present at the time. So basically the spatial
competition for the most part comes down to the competition for the feeding niches.
The role of climate and environment in this discussion is also not at all straightforward.
According to Eronen et al. (2009) the evolutionary change in Anchitherium is brought on by
climatic and environmental change. The Miocene aridification that supposedly started on
the Iberian Peninsula may have forced Anchitherium to start drawing upon other food
sources besides leaves. But was the Spanish climate really overall dryer? Many researchers
agree that the Miocene climate became dryer and cooler but many also point to the large
regional differences on the European continent and also especially on the Iberian Peninsula.
Another ongoing discussion deals with the spread of the grasslands. Did environmental
6
conditions really change so drastically from woodland to open savannah that Anchitherium
had to adapt in order to survive?
General practical problems
During the course of the literature research part of this thesis some problems had to be
solved or evaded. The various technical problems faced during the practical part will be
discussed separately in part 3 of the thesis. A main and ever returning challenge of the
literature part of this thesis is the diversity of languages in which the research about the
genus Anchitherium is presented. For this thesis it was chosen to ignore all articles published
in languages like Russian or Chinese. A couple of articles written in Spanish (Sánchez et al.
1998, Hernández Fernández et al. 2003) and in French (Alberdi et al. 2004) were used.
Another problem was the fact that some authors presented incomplete and in some cases
even incorrect information. Taxonomic references were incomplete or missing and materials
and methods were often unclear. Terminology and nomenclature was also used in different
ways by different authors and in different languages. Sometimes figures were even printed
upside down switching lingual and labial side. In this thesis it has been attempted to add as
much information about data, terminology, taxonomy and methodology as possible.
Chapter 1 - Background and setting
This part of the thesis will consist of a general introduction to Miocene climate and
environment. What are the major geological events influencing Miocene climate? In part 2
climate and environment will be discussed to much greater detail using many different
researches and proxies. Part 1 will form the background for the rest of the thesis. The
background of the genera Anchitherium and Hipparion will also be presented. Their
taxonomy and which species of the genera are included in the research. The distribution of
the different genera and species, the geological setting of the fossil finds and finally the
general biochronology will be discussed in this chapter. The geological setting of the fossil
finds that were used in the practical research will be discussed in part 3.
European Miocene climate
The Neogene climate system represents the transition from the greenhouse climate of the
Paleogene to the icehouse climate of the Quarternary. Within the Neogene the Miocene is
considered the most critical interval in the build-up of ice masses on land (Bruch et al. 2007).
Severe climatic and environmental changes occurred especially during the late Miocene, the
uplift of the Tibetan Plateau was an important geological cause for these changes, it
influenced for example the East Asian monsoon. Another global factor that may have driven
a major climatic change is the closure of the Panama Ishtmus. This event took place between
13 and 2.6 Ma and resulted in a decrease in the mixing of Atlantic and Pacific waters which
gave rise to the development of the modern Atlantic thermohaline circulation (Domingo et
al. 2008). During the early Miocene, an overall trend of increasing temperature is observed
by Mosbrugger et al. (2005), the curve however shows short term variations, These which
will be discussed further in Part two: climatic reconstructions and proxies. A short term
7
cooling is observed at the base of the Aquitanian (MN1 - MN2), in the later Burdigalian (MN3
- MN4) temperatures increase again and the succeeded into a warm time span that persisted
through the earlier part of the Serravallian (MN7/8). This warm period is often referred to as
the ‘Miocene Climatic Optimum’ (Costeur et al. 2008). The Miocene Climatic Optimum is
then followed by a sudden deterioration of the climate as a consequence of the
reestablishment of the Antarctic ice cap (Domingo et al. 2009). The Late Miocene, is
characterized by the aridification of the interiors or the continents (Bruch et al. 2007).
During the Late Miocene a cooling phase starts between 13 and 14 Ma (Mosbrugger et al.
2007). This cooling phase is often attributed to a drop in CO2 levels, Mosbrugger however
states that CO2 levels were not the driving force of the cooling phases. Between 15 and 13
Ma isotope curves show a gradual trend to heavier attributed to the cooling of deep ocean
water, growing ice sheets on Antarctica and the beginning of Arctic glaciations (Mosbrugger
et al. 2007).
Figure 1.1 - Continental temperature curves (CMM) for Central Europe during the last 45 My in comparison with
the global marine oxygen isotope record of (Zachos et al. ) adapted to the International Commission on
Stratigraphy 2004 time scale (Mosbrugger et al. 2007)
The European Miocene Environment
A consequence of the aridification of the continents’ interior during the Late Miocene was
the expansion of open landscapes. This spread of open landscapes also co-occurred with the
spread of the C4-grasses, however no causal relationship has yet been proven (Molnar
2005). The expansion of the C4 plants was originally attributed to a drop in atmospheric CO 2
concentrations. However Pagani et al. (1999) argue that the CO2 concentrations showed an
increase from a minimum value at 14 Ma (180 ppmv) up to values between 320 and 250
ppmv at the end of the Miocene (9 Ma). A drop in atmospheric CO2 levels as a cause for the
C3-C4 shift has according to Strömberg (2011) fallen out of favor because during the
Miocene CO2 levels remained stable and low. Both these researches are not in
8
correspondence with the popular belief that it was due to a drop in CO2 levels that the C4
plants expanded.
Northern and central Europe stayed fairly forested throughout the Cenozoic. Grasses gained
importance in Southern Europe and Asia Minor starting in the Miocene (Strömberg 2011). In
Spain palynofloras point to open, arid steppe and woodland environment during the Early
and Middle Miocene (Juménex-Moreno et al. 2007). For the Late Miocene Eronen et al.
(2008) also maintain that there is a dry steppe like environment present especially in Spain.
Van Dam et al. (2006) and Böhme et al. (2008) show in their researches that the Miocene
climate had at least one or two extremely wet periods, the washhouse climates (Böhme et
al. 2008). From 13 Ma both records that Böhme has reconstructed for Southwestern and
Central Europe show a similar trend, evolving from a long dry period (13-11) Ma into a
‘washhouse climate’ (10.2-9.8 Ma). Strömberg (2007) describes habitats that seem to
become more uniformly open towards the late Miocene (Strömberg 2007). According to
Strömberg (2007) the Miocene environment can be described as a habitat with a mosaic of
grass-dominated and more forest dominated habitats. Later Strömberg (2011) presents
evidence, mainly based on pollen, that supports a dry environment for Europe and especially
the eastern Mediterranean. This is in contradiction of the ‘washhouse climate’ for this period
as suggested by Böhme et al. (2008). For the environmental patterns, as for the climatic
patterns, it is noted by different authors that there were great regional differences
(Domingo et al. 2009). During the Miocene punctual more regional patterns of faunal
differentiations between eastern and western Spain are observed (Costeur 2008). This may
explain the large differences between the many researches.
Anchitherium
taxonomy
Within the order of Perissodactyla Owen, 1848 the Genus Anchitherium Meyer, 1844
belongs to the family of the Equidae Gray, 1821 and the subfamily Anchitheriine Leidy, 1869.
The first Anchitherium fossil, found in 1825, was named ‘Paleotherium aurelianense’ by
George Cuvier (Sanchez 1998). In this paper the following species of the Genus Anchitherium
are defined;
Anchitherium
|-- A. clarencei Simpson, 1932
|--+-- A. aurelianense Cuvier, 1812
| |-- A. parequinum Sánchez et al., 1998
| `--+-- A. corcolense Inigo, 1996
| `-- A. castellanum Sánchez et al., 1998
`--+-- A. hippoides (author unknown)
`--+-- A. matritense Sánchez et al., 1998
`--+-- A. alberdiae Sánchez et al., 1998
`--+-- A. cursor Sáncheze et al., 1998
`-- A. procerum Sánchez et al., 1998
And the Genus:
- Sinohippus sampelayoi (Salesa et al., 2004)
9
Species included
All species names printed in bold letters are species that are used in articles occurring in the
literature part of this study. The most common species of Anchitherium appears to be A.
aurelianense as described by Cuvier, 1812. Anchitherium gobiense Abusch, 1983 and
Anchitherium nannoxerum Abusch, 1983 are included in the species Anchitherium
aurelianense.
The new species Anchitherium corcolense Inigo, 1996 also includes the species Anchitherium
ezquerrae ezquerrae Abusch, 1983. The species A. ezquerrae ezquerrae is also identified in
the material present at the Utrecht University archives.
Salesa et al. (2004) proposed that Anchitherium sampeloy should in fact be grouped with the
genus Sinohippus and thus be named Sinohippus sampeloy (Villalta and Crusafont, 1945).
Due to discussion about whether Sinohippus is to be viewed as a separate species from
Anchitherium (Salesa 2004 and Villalta et al. 1945) and possible occurrence in the region of
interest the species Sinohippus sampeloy (Salesa, 2004) was also included. Also ezquerrae
sampelayoi Abusch-Siewert, 1983 is included into Sinohippus sampeloy (Salesa et al., 2004).
Hipparion
taxonomy
Within the Genus Hipparion (Hippotherium) much discussion has been going on about
nomenclature and taxonomic inclusions and exclusions within the genus. Hipparion was
named by Christol, 1832 and was assigned to Equidae by Kaup, 1833 and later to the tribus
Hipparionini Quinn, 1955 by MacFadden (1998). Within this tribus also the genera
Eurygnathohippus, Hippotherium, Nannihippus, Neohipparion and Pseudohipparion are
currently included. Hippotherium was named by Kaup, 1832 and was later synonomized with
Hipparion and Cormohipparion by MacFadden (1998) and Pesquero et al. (2006).
The taxonomic discussion about the genus Hippotherium seems to be endless. Its
diversification throughout Europe was very large. I will refer to the genus Hippotherium as a
whole in this thesis and in the text will name the genus Hipparion. This is because the
inclusion into Hippotherium is fairly recent and most authors still use the name Hipparion to
indicate this genus.
The species that are discussed in the papers used for this research (thus the species that
occur in Europe mostly) are printed in bold in the following phylogenetic tree. In this paper
the following species of the Genus Hipparion are defined:
10
Hipparion -genus-group
|
|?- Hipparion trampasense Edwards, 1982
|--o Merychippus sensu stricto
| |-- M. insignis
| |-- M. calamarius
| `-- M. californicus
|--o “Hipparion” group 3 [North American basal "Hipparion"]
| |-- H. shirleyi
| `--+-- H. tehonensis
| `-- H. forcei
`--o Cormohipparion Skinner & MacFadden, 1977
[Neohipparion, Notiocradohipparion]
|-- Cormohipparion goorisi MacFadden & Skinner, 1981 [Neohipparion]
|-- (Notiocradohipparion) Hubert, 1988
| |-- Cormohipparion (N.) plicatile (MacFadden, 1984) Hubert, 1988
| |-- Cormohipparion (N.) ingenuum (MacFadden, 1984) Hubert, 1988
| `-- Cormohipparion (N.) emsliei (Hubert, 1987a) Hubert, 1988
`--+?- Cormohipparion quinni Woodburne, 1994b [incl. C. sphenodus
Woodburne et al., 1981]
|-- Cormohipparion occidentale -species-group
| `-- Cormohipparion occidentale (Leidy, 1856) [Neohipparion
occidentale] Leidy, 1856, C. goorsi, C. quinni]
`--+?- Cormohipparion theobaldi (Lydekker, 1877a)
|?- Cormohipparion nagriensis (Hussain, 1971)
`--o Hippotherium Kaup, 1833 [Old World “Hipparion”]
|-- “Hippotherium” koenigswaldi Sondaar, 1961
|-- “Hippotherium” sebastopolianum
|-- Hippotherium primigenium (von Meyer, 1829)
|-- Hippotherium depereti Sondaar, 1974
|?- Hippotherium albertense (Hopwood, 1926)
|?- Hippotherium baardi (Boné & Singer, 1965)
|?- Hippotherium namaquense (Haughton, 1932)
|?-+-- H. weihoense
| `--+?- H. dermatorhinum
| `--+-- H. coelophyes
|
`-- H. hippidiodus
|--+--+-- “Hippotherium” catalaunicum (Pirlot, 1956)
| `?- “Hippotherium” aff. “H.” catalaunicum
`--+--+?- Hippotherium brachypus Hensel, 1862
| `-- Hippotherium giganteum Gromova, 1952
`--o Hipparion de Christol, 1832
|?- “Hipparion” melendezi Alberdi, 1974a
|?- H. laromae Pesquero, Alberdi & Alcalá, 2006
|-- H. prostylum Gervais, 1849
`--+-- H. gettyi Bernor, 1985
`--+?- H. concudense Pirlot, 1956
|?- H. huangheense
|-- H. campbelli Bernor, 1985
`-- H. dietrichi Wehrli, 1941
11
Anchitherium – Systematic Paleontology
Order PERISSODACTYLA Owen, 1848
Family Equidae Gray, 1821
Genus Anchitherium Meyer, 1844
Anchitherium aurelianense, Cuvier 1812
Type locality; Montabuzard (France) Early Miocene (MN4)
Locations; Dans les Sables de l’Orlénais; Chitenay; Neuville-aux-Bois and Chilleurs-aux-Bois
(MN 3); Baigneaux, Chevilly et Maigrewille (MN 4b); Faluns de Pontelevoy et faluns d’Anjou
(MN 5); La Romieu (MN 4b); Castelnau d’Arbieu (MN 5) in France; Buñol (MN 4) in Spain and
Atzelsdorf (MN 9) in Austria.
Diagnoses; (Abusch 1983) A. aurelianense is small and brachydont. The length of the upper
cheek teeth P2-M3 varies between 105 and 119 mm. The length of the lower cheek teeth
P2-M3 varies between 102 and 113 mm. In most of the M3 molars a crochet is present and is
usually absent in the other upper cheek teeth (it is more abundant in Sansan).
(extra) (Descprition of Daxner-Höck’s material from Atzelsdorf) The M3 is trapezoidal, the
mesial width extends almost on third beyond the distal width. The lophodont paracone and
metacone are integrated in the ectoloph. The bunodont lingual cones protocone and
hypocone are continuous with the S-shaped protoloph and metaloph. Protoloph and
metaloph contact the ectoloph. Protoconule and crochet are present. Parastyle and
mesostyle are prominent. The tooth has a semi-continuous cingulum. The labial cingulum is
weak, it extends from the parastyle towards the mesostyle. The pronounced distal and
lingual cingula are continuous, the mesial cingulum extends in lingual direction towards the
base of the protocone. Two pronounced conules are situated on the mesial and lingual
cingulum.
Anchitherium corcolense Inigo, 1996
Type locality; Córcoles (Guadalajara, Spain), Early Aragonian (MN4)
Locations; Only found at the type locality
Diagnoses; This species of Anchitherium has small postcranial bones and large teeth. The
mean length of the upper cheek teeth P2-M3 is 125,89 mm and of the lower cheek teeth P2M3 129.3 mm. The maximal length of Mc3 varies between 163.2 and 180 mm and the
maximal length of Mt3 between 160,3 mm and 181,5 mm. The upper jaw P1 tooth does not
have a hypocone. The crochet is extremely infrequent on the upper cheek teeth (about 0,5
%) whose internal cingulum is very small and generally absent on molars. Proximal epiphyses
of lateral metatarsals very broad related to their depth. The facets between internal
metapodials and magnum or big cuneiform are small, but generally well defined.
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Anchitherium castellanum Sánchez et al., 1998
Type locality; La Retama (Cuenca del Tajo, Spain) (MN 5)
Locations; Only found at the type locality
Diagnoses; The male canines are larger than the incisors. There is no crochet in the upper
cheek teeth. There is a crochet present in 20% of all upper jaw M2 molars. In 20% of the
upper jaw M3 molars there are styles and a valle central* present. There is no lingual
cingulum present on the upper jaw M1 and M2 and a lingual cingulum is present on 30% of
the upper jaw M3 molars. While in the premolars the lingual cingulum is almost always
present, sometimes in 100% of all the samples studied. The lingual cingulum never appears
on the lower jaw dentition. There is a high frequency of styles and the preflexid of the lower
jaw dentition except for P2 where it is virtually absent. A style and a preflexid is present in all
available lower jaw M3 samples.
Differential Diagnoses; A. castellanum is different from A. corcolense by the greater length of
the upper jaw M1 buccolingual; the absence of a lingual cingulum in the lower jaw dentition;
the presence of a crochette and the absence of a short crochette*.
A. castellanum differs from A. aurelianense in that their teeth are significantly larger.
Towards the back the teeth become larger. And also they have a larger body size.
*It is unclear how to translate ‘valle central’. ‘Valle distal’ means ‘Preflexid’ and ‘Valle
Mesial’ means ‘Postflexid’ and these are names of lower jaw tooth forms. I have not found a
translation for the apparent upper jaw tooth form ‘valle central’. Perhaps this is a new term
coined by Sánchez et al. (1998).
*’pliegue postfoseta corto’ translates as ‘short crochette’, this term probably is also coined
by Sánchez et al. (1998). It is however unclear from the article what form he means by this
‘short crochette’. For A. matritense Sánchez also uses the term ‘long crochette’.
Anchitherium matritense Sánchez et al., 1998
Type locality; Estacíon Imperial (Madrid, Spain) (MN 5)
Locations; Puente de Valecas; Puente de Toledo; Estación Imperial; La Fuentecilla and La
Cistérniga.
Diagnoses; They have an overall large dentition. The male canines are about the same size as
the incisors. A (short) crochette is present in all upper jaw teeth except the M2. The (long)
crochette is only present in P2. A ‘normal’ crochette is present in the upper jaw P3, M1 and
M3. The presence of a style and a preflexid in the lower jaw M3 is very low (8,33 %).
Differential Diagnoses; The difference between A. matritense and A. corcolense and A.
castellanum is the fact that the upper cheek teeth have a generally more square and more
rectangular form. Also the lower relative size of the male canines is a difference.
13
Anchitherium cursor Sánchez et al., 1998
Type locality; Alhambra-Túneles (Madrid, Spain) (MN 6)
Locations; Alhambra-Túneles and Arroyo del Olivar
Diagnoses; This species has the largest dentition of all Anchitheriine species. The canines are
similar in size to the incisors. The crochette is absent in the upper jaw dentition. The (short)
crochette varies between 16-50% in the lower jaw dentition and the (long) crochette is
present only in the M1.
Anchitherium procerum Sánchez et al., 1998
Type locality; Paracuellos V (Madrid, Spain) (MN 6)
Locations; Only present at the type locality
Diagnoses; This species is big in body and dentition. The male canines are similar in size to
the incisors. In the upper jaw P2 the style and central valley are absent. The buccal cingulum,
the Metalophid and Hipolophid are absent in the lower jaw M3. There is no (long) crochette
present in the upper jaw dentition, with the exception of P2 and M3. A (normal) crochette is
present in the upper jaw M1. There is no style or preflexid in the lower jaw P4, M1 and M3.
Differential diagnoses; A. procerum differs from A. cursor in its general size and the presence
of a crochette.
Anchitherium alberdiae Sánchez et al., 1998
Type locality; Paseo de las Acacias (Madrid, Spain) (MN 5)
Locations; Paseo de las Acacias, Peñuelas and la Hidroeléctrica (Madrid)
Diagnoses; This species is medium sized but has a large dentition. Its male canines are similar
in size to its incisors. The size of the canines would be comparable to those of a dog. The
authors note that none of the complete jaws contains a P1, they conclude that there may
have been an advanced reduction of the P1 in this species. Styles appear in the preflexid of
the M3 with high frequency (71,42 %).
Differential diagnoses; The P1 in this species is significantly smaller than the contemporary
species like A. matritense.
14
Anchitherium parequinum Sánchez et al., 1998
Type locality; El Terrero (Villafeliche, Spain)
Locations; El Terrero, Valdemoros and Ambos en Villafeliche
Diagnoses; This is a very small and slender species (no comments on the dentition)
Differential Diagnoses; this is smallest of all species by comparison.
Sinohippus sampelayoi (Salesa et al., 2004)
Type locality; Nombrevilla-1 (Calatayud-Daroca Basin, Zaragoza, Spain)
Locations; Only in type locality
Diagnoses; (Villalta and Crusafont 1945: 78, Diagnoses of Anchitherium sampelayoi)
“terminal derived Anchitherium of large size, with marked tendency to hypsodonty, basal
cingulum almost obsolete, mainly in the juvenile teeth; more evident homeodonty than in
the primitive forms, milk teeth highly reduced, special shape of d2”; additionally: upper
premolars with marked buccal cingulum and absence of lingual cingulum, hypostyle without
connection with the metalophe, and absence of crochet.
Remark; The lower premolars of the Nombrevilla-1 species are very similar to the
proportions of the remains from Sinohippus from another location. This relative reduction if
not present in Hypohippus and Megahippus. This reduction of the premolars is sufficient to
distinguish between the North American and the Eurasian giant Anchitheriinae (Salesa et al.
2004).
15
Distribution
Anchitherium first enters Europe during the Late Early Miocene. The first Anchitherium
fossils have been found in Chitenay; Neuville and Chitelleurs (France) (Abusch and Siewert
1983) and in Merkur (Czech Republic) and Wintershof-West (Germany) (Bruijn et al. 1992).
The first occurrence of Anchitherium in Spain is at the geological site of Agreda (Soria, Spain
MN 3) (Sanchéz 1998). Anchitherium is part of the second of four (equid) migration waves
from North America via Asia that took place during the Early Miocene (Salesa et al. 2004).
The third migration wave that took place during the Early Middle Vallesian includes the
North American tridactyl equid Hipparion (Salesa et al. 2004). This second migration into
Europe is marked as the ‘Hipparion date’ and coincided roughly with the decline and
extinction of the genus Anchitherium. Both genera show co-occurences at several different
sites in Europe so we know that both genera co-excisted in Europe for at least a while. Cooccurrence of Anchitherium and Hipparion is observed at a few localities of basal Vallesian
(MN 9) age from Atzeldorf; Mogersdorf; Mariathal and Radlebrunn (Austria) Geisenberg
(Germany) (Höck 2009) also in Nombrevilla-1 (Spain) (Villalta and Crusafont 1945); Doué-laFontaine and Soblay (France); Holzmannsdorfberg (Austria), Ucak (Turkey). Between its
initial arrival in Europe and its extinction roughly 10 million years later the Genus
Anchitherium was widespread throughout Europe and Asia. From the literature research it
can tentatively be concluded that one of the most common species in southern Europe,
France and the area of interest Spain appears to be Anchitherium aurelianense. A.
aurelianense has been described from more than 50 sites in Spain alone (Inigo 1997). By
authors Abusch, (1983) and Inigo (1993) this species is only recognized at the site of Buñol
(Valencia, Spain). These two authors classified the anchitheriines from many other sites of
the internal basins of the Iberian Peninsula as Anchitherium ezqeurrae (Meyer 1844), and
not as A. aurelianense. A. ezquerrae ezquerrae has by Inigo (1996) been reassigned to A.
corcolense.
Geological setting
Anchitherium
Anchitherium first appeared in North America in the Early Miocene and entered Europe via
Asia. This migration route also becomes apparent in the distribution of geological sites with
Anchitherium finds worldwide (figure 2.1). Anchitherium entered Europe during the middle
Orleanian, MN 3 and becomes extinct during the Vallesian, MN 9 (Kaiser 2009, Forsten
1991). Zone MN 3 is characterized by the establishment of land connections in south-eastern
Europe. The co-called ‘Gomphotherium landbridge’ (Rögl 1999) links the Eurasian and
African continents (Costeur and Legendre 2008). And several taxa immigrated into Europe.
Anchitherium however, unlike Hipparion much later, did not use these landbridges to
migrate into Africa. The oldest geological finds are located in North America but will not be
discussed here since the focus lies on European and especially Spanish localities.
16
Figure 2.1 – Worldwide distribution of the genus Anchitherium (Fortelius et al. 2009)
The first occurrence of Anchitherium in Europe is during the late Ramblian (Early Miocene).
The first Anchitherium fossils have been found in Chitenay; Neuville and Chitelleurs (France)
(Abusch and Siewert 1983) and in Merkur (Czech Republic) and Wintershof-West (Germany)
(Bruijn et al. 1992). The first occurrence of Anchitherium in Spain is at the geological site of
Agreda (Soria, Spain) (Sanchéz 1998).
Following are the different localities with Anchitherium finds that provided the data for the
articles that were used for the literature research. The localities used in the practical part of
this thesis will be discussed separately in another chapter (Practical work). Per locality it will
be discussed in what articles the locality is named, if possible how old it is and which species
of Anchitherium was found there.
Córcoles- (Guadalajara, Spain)
According to Inigo (1997) a new Anchitherium species was present at the Spanish site of
Córcoles, Anchitherium corcolense. This new species shows a primitive anatomy with respect
to A. aurelianense and A. ezquerrae. The species is related to a dry forest environment. The
site dates from the early Aragonian (the Spanish name for the Orleanian period, figure 2.3).
The local periods have not all been dated to the same time period.
Atzelsdorf- (Paleo-Danube delta in Austria)
Höck (2009) describes the Anchitheriine fossils found at Atzelsdorf as A. aurelianense. This
ancient delta is of Vallesian age and is therefore also one of the localities in which a cooccurrence with Hipparion can be observed (in zone C of the early Pannonian). The
Pannonian is a local name for the Vallesian period.
17
Nombrevilla 1- (Spain)
(Salesa 2004) propose that the species Anchitherium sampelayoi, found at the site
Nombrevilla 1, identified by (Sanchéz et al. 1998) should be included within the genus
Sinohippus and therefore be named Sinohippus sampelayoi.
Samosaguas- (Madrid basin, Spain)
The geological site for Anchitherium cursus is the site of Samosaguas in the Madrid basin
(Spain) (Domingo et al. 2009).
Sandelzhausen- (Germany)
At the geological site of Sandelzhausen in Germany the Anchitherium species found there
has been identified by many authors as A. aurelianense (Eronen et al. 2009) (Kaiser 2009)
Other localities of samples used by Eronen et al. (2009) in their research are Puente de
Vallacas (Spain) with Anchitherium aurelianense and Anchitherium sp. Alhambra (Spain) with
Anchitherium sp. and La Retama (Spain) with Anchitherium castellanum. It is interesting to
note that A. aurelianense as well as an unidentified species of the genus Anchitherium have
been noted to be present at the site at Puente de Vallacas in Spain. Janis (2008) states that
like in the present day it is also unlikely for fossil assemblages to contain more than one
species of horse. This might indicate that the unidentified species may also be A.
aurelianense. Or it may be an indication that a cooccurence of different species of horse in a
fossil assemblage isn’t so rare after all.
Hipparion
The mammalian ‘Hipparion Fauna’ was established in the early Vallesian and existed for
more than 7 million years up to the middle of the Pliocene. The dominant species of this
fauna was Hipparion that migrated from North America (Vislobokova 2006). The Hipparion
fauna populated the East Alpine Region alongside Middle Miocene forms that survived well
in wet situations (Vislobokova 2006). The earliest Hipparion horse fossils, Hippotherium
primigenium (previously Hipparion primigenium) were found in the Vienna Basin at the sites
Hovorany and Gaiselberg (Bernor et al. 1988, Rögl and Daxner-Höck, 1996). There is a
general consensus that this species appeared in this territory not earlier than 11.5 Ma
(Bernor et al. 1988, Vislobokova, 2006). A rather rapid dispersal of Hipparion and the
formation of the Hipparion fauna were promoted by geographical conditions that existed at
the boundary of the Middle and Late Miocene and during the late Miocene (Vislobokova
2006).
As becomes apparent from the world map (figure 2.2) showing geological finds generated by
the Palaeobiological database the Hipparion horses were much more wide spread than the
Anchitheriinae. From this map it becomes clear that the Hipparion migrated along the same
route as Anchitherium via Asia into Europe. Hipparion also made it into the Southern part of
Africa and South East-Asia which Anchitherium never did.
18
Figure 2.2 – Worldwide distribution of the genus Hipparion (Fortelius et al. 2009)
Biochronology
For continental fossil finds during the Miocene and Pliocene of Europe the MN-zonation
(Mammalian Neogene- zonation) is often applied. Because continental fossils are difficult to
date and also hard to relate to marine records, MN-zonations can be used to give an
indication of the time a certain species lived in an area. These zonations are defined through
reference faunas and are often bordered by migrations into or out of a certain area or
extinctions of certain species. There are sixteen consecutive MN zones spanning the
Miocene and Pliocene (MN 1 through MN 17; MN 7 and MN 8 have been joined into MN
7/8) MN 1 being the oldest and MN 17 the youngest fauna zonation (Bruijn de et al. 1992).
Due to redefinition of the boundary between the Neogene and Quarternary periods, MN 17
is now in fact considered a Quarternary biozone.
The MN zonations of interest to this research are the zonations MN 3 to MN 9 which roughly
correspond to 20-10 Ma ago (figure 2.3) MN 3 is (partly) defined by the introduction of
Anchitherium and MN 9 is (partly) defined by the introduction of Hipparion.
19
Iberian Biozonation
The biozonations vary per different country. Apart from the MN Zonation the Iberian
biozonation is also very relevant for this study. I have added a figure (figure 2.3) by (Hordijk,
2010) showing the MN zonation relative to the Spanish version, the Iberian biozonation.
Added are two different age calibrations by (Daams et al. 1999 and van Dam et al. 2006).
Figure 2.3 The Iberian biozonation (Hordijk 2010)
20
Central Paratethys biozonation
Figure 2.4 shows the Central Paratethys and the Eastern Paratethys biozonation. Of interest
to this research is mainly the Central Paratethys biozonation because it is the local zonation
for the Austrian faunas including Hipparion and Anchitherium. Most important in the Central
Paratethys biozonation is that the continental period ‘Vallesian’ is called the ‘Pannonian’. It
is named after the Austrian Pannonian basin where it is defined. The articles about the
German localities use the MN biozonation.
Figure 2.4 – The Central Paratethys biozonation (Vislobokova 2006)
21
Chapter 2 – Literature Research and Methods
Evolution and adaption of Anchitherium
If Anchitherium changed its diet morphological adaptations were needed. These adaptations
would probably have consisted of specialization of the molars and maybe of the digestive
system. This latter part of the animal does not fossilize very well, the teeth however are
often the body parts of large mammals that have the highest fossilization potential (Forsten
1991). There are many different methods to deduce a fossil species living environment and
diet. Micro and mesowear patterns on fossil teeth are one possible approach (Kaiser 2009,
Fortelius and Solounais 2000). Another method is to extract carbon isotope data from tooth
enamel (MacFadden 1994) or bones. Forsten (1991) bases her conclusions about
Anchitherium’s diet on its general body size compared to the size of its teeth. In this chapter
the methods used to deduce what the diet of Anchitherium was will be summarized. And
also the research dealing with Anchitherium’s possible evolutionary adaptations to a
changing world will be discussed.
Changes in body and tooth size
Forsten (1991) states that Anchitheriums never became hypsodont, or showed signs of
‘incipient hypsodonty’ in contrast to the later research of Eronen et al. (2009). Anchitherium
remained morphologically conservative and according to Forsten (1991) this may have been
the reason for its demise. The only morphological response that the Miocene Anchitherium
showed was a slight increase in occlusal surface, caused by an increase in tooth size. Inigo
(1996) describes Anchitherium corcolense found at Corcoles in layers from the lower
Aragonian (Orleanian) (MN3 – MN4). He describes this species as macrodont and defends
that this species was already separated from the most primitive microdont Anchitherium.
Forsten (1991) states that large teeth are derived in Anchitherium. She considers the species
A. aurelianense from Buñol as primeval and states that dental size increases abruptly in the
Spanish Anchitheres from the middle Orleanian (in Iberian biozonation: Aragonian) with A.
ezquerrae. Inigo later argues that the species A. corcolense from the lower Orleanian is older
than the specimens from Buñol and is macrodont. Thus according to Inigo (2001) these
Anchitheres were already separated from the most primitive forms earlier than Forsten
suggests. And macrodont Anchitherium species may have already been present on the
Iberian Peninsula from the early Orleanian, early Miocene (MN3).
Forsten (1991) concludes that the dental morphology and body size of the Middle and Late
Miocene Anchitherium suggest that it was a browser and perhaps a mixed feeder. If this is
the dental morphology that Inigo (2001) also refers to as macrodont teeth this may be an
indication that there are already signs of Anchitherium’s mixed feeding in the early Miocene
(MN3) when it first set foot on the European continent.
22
Micro- and Mesowear pattern analysis
Kaiser (2009) bases his conclusion that Anchitherium was a ‘dirty browser’, on the mesowear
patterns on fossil teeth. This method was initially developed by Fortelius and Solounias in
2000 and has proven a powerful tool for reconstruction palaeodietary adaptations. Unlike
the microwear method that may suffer from the ‘last supper syndrome’ (Solounias 1994) the
mesowear patterns reflect long term diet and is therefore much more reliable. Kaiser states
that the mesowear pattern found on Miocene Anchitherium teeth from in Sandelzhausen
(Germany) indicates a diet of mixed feeding. However, he acknowledges that grit
incorporated into a browsers food may have the same mesowear signature as a mixed
feeder (Williams and Kay 2001). For this reason Kaiser has aptly named his article
‘Anchitherium, a dirty browser’, hinting towards the possibility that Anchitherium browsed
for leaves in places with a high dirt content, such as near a river. Also Kaiser concludes that
Anchitherium was in fact probably an opportunistic mixed feeder instead of a pure browser.
Tooth enamel and bone Isotope analysis
Meso- and microwear analysis on the teeth of fossil species has provided clues about the
Anchitheriine diet (Eronen et al. 2009, Kaiser 2009. DeMiguel et al. 2011). Apart from mesoand microwear analysis and general crown height, isotope analyses of bones and tooth
enamel can also provide valuable clues about fossil species and their diet (Domingo et al.
2009, MacFadden et al. 1994).
Carbon-isotopes
The carbon isotopic composition of bones and tooth enamel of herbivore mammals records
the isotopic composition of the plants they ate and can therefore be used to distinguish
between the different types of palaeodiets. There are 3 different photosynthetic pathways,
C3, C4 and CAM (Crassulacean Acid Metabolism). The CAM Pathway is mainly used in
succulents and therefore not relevant for looking at the Anchitheriine palaeodiet. The C3
photosynthetic pathway is much older than the C4 pathway and includes about 85% of all
terrestrial plants including trees, most shrubs and high latitude or high elevation grasses.
About 10% of the terrestrial plant biomass today use the C4 pathway, these include mainly
tropical and temperate grasses that are adapted to climates with higher seasonality and with
relative greater aridity than C3 plants (Domingo et al. 2009, MacFadden et al. 1994). When
trying to determine whether the Anchitheriine diet contained grasses it is interesting to look
at the isotopic composition of its teeth and bones. C3 plants discriminate more against the
heavy isotope 13C during photosynthetic fixation of CO2 compared to C4 plants. This results
in different carbon isotopic compositions of the different plants. A relation has been
proposed between the enrichment in 13C of tooth enamel and diet by Domingo et al. (2009).
Lower values would be more indicative of more browsing behavior whereas higher values
indicate a diet of drought resistant plants of grasses. If the isotopic signal indicates that the
animal consumed C4 plants it is possible that it ate grass, because the C4 pathway is only
present in grasses. It may also mean that its habitat was relatively dry. However if there is no
isotopic signal indicating the consumption of C4 grasses this does not mean that
Anchitherium did not eat grass because C3 grasses were very abundant.
23
Domingo et al. (2009 B) find higher d13 C for the Anchitherium species A. cursor and also in
the extant ruminant species used for their research. They tentatively conclude that these
high values may be an indication that these species had a diet selection towards plant
species with a higher evaporation rate. They do not say that this means that they ate C4
grass, but they plot further away from the pure plant eating, thus browsing species. For the
ruminants the higher isotopic value may also be a result of their digestive tract, ruminants
produce high quantities of methane during their digestion as a result of foregut
fermentation (Domingo et al. 2009 B). For Anchitherium however this higher value may yet
be indicative of a diet of plants with a higher evaporation rate, and not a diet of juicy leaves
of a pure browsing animal. Domingo et al. (2009 B) do not directly conclude that
Anchitherium’s diet contained C4 grasses. In another article based on isotopic research on
Hipparion dental enamel from the Terual-Alfambra region Domingo et al. (2009. A) do
speculate about Hipparion’s diet. The isotopic research on Hipparion dental enamel has
yielded d13C values typical of a diet based on C3 plants (Domingo et al. 2009 A). It is
unfortunate that the Teruel-Alfambra paleontological sites span an age range between
approximately 10.9 and 2.7 Ma because the low values are found in dental enamel of
Hipparion horses older than MN14. It is during MN14 that Domingo et al. (2009 A) note a
significant increase in the isotopic d13C value that may be indicative of a slight increase of the
consumption of C4 plants. So it would appear as if Kaiser (2009) may be correct in stating
that Hipparion changed its feeding habits upon entering Europe from grazing to mixed
feeding or even browsing . Because from this isotopic data it appears as if Hipparion turned
(back?) to the grazing C4 niche much later.
Oxygen isotopes
By analyzing d18O values from herbivore tooth enamel it is possible to differentiate between
obligate drinkers (often grazers) and non obligate drinkers (browsers). Because grazers get
most of their water from drinking whereas browsers obtain their water via the diet of plants
that they eat. Domingo et al. (2009) do not interpret their oxygen isotope data in this way.
The values to plot their measurements against are absent so the Anchitherium tooth oxygen
isotopic data in the form of a water intake proxy cannot be interpreted as such.
Ba/Ca ratio
According to Domingo et al. (2009 B) the, enriched Ba/Ca ratio shows that Anchitherium cf.
cursor had a more mixed feeding strategy.
24
Hypsodonty
Apart from the question whether or not Anchitherium has adopted evolutionary changes for
eating grass by becoming more hypsodont (Eronen et al. 2009) and why, another important
question is; ‘Is hypsodonty really an adaptation for eating grass or more abrasive foods?’
Hypsodonty has evolved many times during the history of vertebrates and in many different
lineages. The evolutionary advantage of hypsodonty is obvious, since tooth wear is a
proximate cause for senescense (Eronen et al. 2009). Hypsodonty has also evolved along
many rodent lineages in order to cope with the hard nuts and seeds these animals eat and
do cut through tough roots while digging holes. Hypsodonty has evolved numerous times
within mammals in general (Janis 1994). Hypsodonty is not the only adaptation to eating
abrasive foods. Along with hypsodont teeth other changes in tooth morphology that
increased chewing effectiveness also occurred. Examples of this are increased tooth surface
(Forsten 1991) and increased complexity of enamel folding and development of cementum
(Evander 2004, Strömberg 2006). However according to Strömberg (2006) these dental
properties often seem decoupled in horses. The general accepted theory for grazing animals
is that they have developed hypsodont teeth in order to cope with the abrasive phytoliths
(silica particles that make grass an extremely abrasive food to eat) that are incorporated into
the structure of grass (Strömberg 2005). The general idea in horses and ruminants is that
hypsodonty indicates a diet based mainly on grass and therefore that the spread of
hypsodont ungulates must have coincided with the spread of the grasslands (Retallack
1983). However this idea is topic of debate. According to Janis (1994) hypsodonty is unlikely
to be a specialization for grazing. She notes this in the ungulate family. ‘Grazing is a fairly
recent specialization among ungulates although extensive grasslands appeared around 25
Ma - and along with them hypsodont ungulates – real specialized grazers did not appear
until around 10 Ma and most of these grazers are of Plio-Pleistocene age’ (Janis
1994).Fortelius et al. (2002) base their climatic reconstruction of Eurasia on the level of
hypsodonty. They state that in general a higher hypsodonty rate corresponds to an
environmental parameter that they call ‘generalized water stress’. They link hypsodonty
more to a dryer environment than an increase in grassland and open vegetation. Also
according to Strömberg (2011) the evolution of herbivores adapted to grasslands did not
necessarily coincide with the spread of open-habitat grasses. Modern faunal studies indicate
that hypsodonty correlates more closely with habitat openness, feeding height, and levels of
aridity than with proportion of grass consumed (Eronen et al. 2010).
Abrasiveness of the food of grazing animals is also not necessarily caused by the phytolith
particles in the grass. It may be due to:
-
An increase in grid uptake, caused by grazing near river beds.
Extrageneous dust covering the grass, often desert sand.
An overall increase in food uptake by the animal because it became bigger or the
food source became less nutritious (Strömberg 2005, Eronen et al. 2009).
25
Another reason why the evolutionary adaptation of hypsodont teeth is not necessarily a
consequence of the spread of grassland is the adaptive lag that is observed by (Strömberg
2001). The North American grasslands already developed during the Oligocene (Retallack
2001) and this was 5 million years before the development of hypsodonty in ungulates on
the North American continent (Strömberg 2001). According to Janis (1994) it is highly
unlikely that an adaptive trait develops after the need, because in this case hypsodonty is
essential to the grazing animal. The strange situation that now appears can be solved by a
principle that was coined by Gould and Vrba (1982) as ‘exaptation’. A trait may develop
shaped by selection to serve a different function than they are presently serving. Thus
hypsodonty may have developed earlier, or as in this case later serving a different purpose
but also seemed to increase fitness for grass eating animals. That is the reason why we
connect hypsodonty to eating grass, this may however not be its evolutionary origin at all.
The hypsodonty discussion learns us that we should not base our conclusions about the diet
of, for example, fossil horses on the level of hypsodonty of their teeth, and that the incipient
hypsodonty of Anchitherium may not have been a specific adaptation for eating grass. A
brachydont animal is extremely unlikely to be anything but a browser, but a hypsodont
species may have a variety of diets (Janis 1994). Also the paleoenvironmental reconstruction
of the spread of the grasslands can not necessarily be deduced from the spread of more
hypsodont species for an increase in grass consumption is probably not the, or not the only
cause for the evolutionary adaptation of hypsodonty. The most viable hypothesis according
to Strömberg (2001) is that hypsodonty is to be connected to feeding in an open habitat on
grass and or dust and grid contaminated food.
Climate and environment
In chapter 1 an overall climatic and environmental sketch was drawn of the Early to EarlyLate Miocene. Researchers agree that there are large local differences in environmental
conditions as well as climatic effects such as rainfall. This is called ‘local endemism’ and is
especially strong in south eastern Europe (Mosbrugger et al. 2005, Costeur and Legendre
2008). Also conditions have differed greatly throughout course of the Miocene. In chapter 2
climatic and environmental reconstructions and the proxies used will be discussed in order
to bring some detail to the overall sketch of the supposed dry ending of the Miocene which
brought about the expansion of open landscapes and disputably the spread of the C4 grasses
(Molnar 2005). When looking at the Miocene in greater detail it becomes apparent that the
dry periods were most likely set apart by wet periods and even a period at the end of the
Miocene that Böhme et al. (2008) refers to as the Late Miocene ‘washhouse climate’ (see
page 9).
There are many different ways to reconstruct palaeoclimate and environment: micro- and
macrofossil fauna, pollen and fossil flora, dental enamel isotopes, dental wear and level of
hypsodonty (Fortelius et al. 2002). All of these different methods lead to, sometimes very
different, results and conclusions about past climate and environment.
26
Climate reconstructions and proxies
An important point on which Eronen et al. (2009) base their assumptions of the adaptation
of Spanish Anchitherium is the fact that Spain was the first region to experience aridity
during the Early Miocene of Europe, and that the region where the ‘contemporary’ German
specimens are found remained humid during that time. In order to prove or disprove this
part of Eronen’s hypothesis it is important to study the climatic conditions in Europe, and
especially Spain during the Early Late Miocene. Overall the Late Miocene is seen as a period
that is characterized by the aridification of the interiors of the continents (Bruch et al. 2007).
Many researchers agree however that there may have been large regional differences
(Mosbrugger et al. 2005, Costeur and Legendre 2008).
Fossil fauna
Eronen and Bruch support an overall aridification of the continents however van Dam et al.
(2006) and Böhme et al. (2008) show in their researches that the Miocene climate had at
least one or two extremely wet periods, the washhouse climates (Böhme et al. 2008).
Böhme bases her estimates of precipitation on the ‘ecophysiological structure of
herpetological assemblages’ (amphibians and reptiles). Both records reconstructed for
Southwestern and Central Europe show a similar trend, evolving from a long dry period (1311) Ma (MN 7-8) into a ‘washhouse climate’ (10.2-9.8 Ma) (MN 9). They base their
conclusions on two records taken from two locations spatially far apart. One from the
Calatayud-Daroca basin in Spain (from two different continental sequences) and one from
several locations in the Paratethys region. Their proxies show that precipitation was several
times higher than present. From 9.7 Ma onward their records show that the climate became
dryer again and record a second washhouse climate between 9.0-8.5 Ma.
The first supposed wet climate in South Europe is of special interest for this research
because it roughly coincides (10.2 -9.8 Ma) with the extinction of Anchitherium and for
which at least one of this thesis’ hypotheses states that this may have been caused by
climatic change. It contradicts Eronen’s claim that Spain was dry during this period of the
Miocene. Böhme is not the first researcher arguing an increase in precipitation rates during
the Early Late and Late Miocene. Earlier van Dam (2006), who bases his research mainly on
rodent faunas from Spain, argues that after the relatively dry conditions of the Middle
Miocene (16-13 Ma), an increase in the precipitation rate took place between 13 and 11 Ma
(MN 7-8), reaching a maximum at about 11-10 Ma (MN 9).
Dental isotope composition
The isotopic composition of the dental enamel of fossil species can be a proxy for many
different things. Earlier in this chapter the use of Carbon isotopes to reconstruct diet has
been discussed. The water that the animals drink is often meteoric water from rivers and
lakes. Thus the isotopic composition of the water can be used (when analyzing only one
genus) as a proxy for palaeotemperatures and the evolution of past climates. The d18O values
measured in the dental enamel of Hipparion horses from Spain by (Domingo et al. 2009)
show an increase in d13C values during the period after the Miocene Climatic Optimum
27
indicating an increase in aridity (MN 7). Their data also shows a gradual increase in d13C CO2
values starting MN9 to MN16. This may be related to an increase in the mean annual
temperature of approximately 2,1 degrees Celsius.
Dental wear
Domingo et al. (2009)’s findings are contradicted by the data from DeMiguell et al. (2011).
They base their data on the dental wear of Spanish ruminants. He uses a combined approach
of dental microwear and mesowear, and uses the reconstructed diets as environmental and
climatic proxies. Their data show a transition from dry conditions in the Late Early (MN 4)
and Middle Aragonian (MN 5) that persisted into the Late Aragonian (MN 6, MN 7/8) to
more humid conditions during MN 7/8. However there are some problems however with the
microwear method, this method suffers from the so called ‘last supper syndrome’ (Solounias
1994).
Level of hypsodonty
Fortelius et al. (2002) in their climate research formulate a new quasi-quantitative proxy.
They link the level of hypsodonty to a environmental condition that they term ‘generalized
water stress’. According to Fortelius (2002) the Early Miocene shows a pattern of faunas
dominated by brachydont species except for two areas of early increase in crown height;
central Asia and the Iberian Peninsula. They conclude that the Early Miocene remained
green with only the slightest evidence of incipient aridity. They also note that the intervals
that show the incipient hypsodonty are all from the later part of the Early Miocene. The
Middle Miocene shows slightly more evidence of increasing aridity. The Earlier Late Miocene
however shows a major strengthening of the hypsodonty in the present day Mediterranean
region and in east-central Asia. If Fortelius’ climatic reconstructions are correct this would
imply that dry conditions in Spain occurred later than the Early Late Miocene. This partly
undermines Eronen’s (2009) claim that the Spanish Anchitherium responded to the
conditions on the Iberian Peninsula as the climate changed during the Early Miocene. This
new proxy is controversial because it has two major problems. First of all the link between
hypsodonty and climatic change is not as well established as Fortelius (2002) presents it.
There is still much discussion about hypsodonty and diet (Strömberg 2009). Linking diet to
environment and even climate is a dangerous step because other species that have already
evolved a high level of hypsodonty may move into an area making it appear drier. Fortelius
acknowledges this problem. Another important remark on Fortelius’ research is the fact that
the results, when including horses in the hypsodonty index faunas, change enormously. He
notes this in his paper and states that he does not have an explanation for the large
deviations in data when horse hypsodonty levels are included.
Pollen and flora
The marine realm is generally understood quite well, but the continental climate patterns
are not (Bruch et al. 2007). Earlier Mosbrugger et al. (2005) conclude that the European
continental climate correlates well with the oxygen isotope record from the marine
environment. Mosbrugger et al. (2005), who base their research on extensive floral data,
28
conclude, apart from some minor variations, that the Mean Annual Precipitation (MAP)
levels were commonly on a high level (of more than 1000 mm/y) throughout the Central
European Cenozoic. During the Late Miocene and earliest Pliocene he finds that MAP
remained constant at a level of ca. 1250 mm/y to then significantly drop only during the
Zanclean (MN 13, MN 14). However for Europe and the eastern Mediterranean region
Strömberg (2011) presents evidence, based on pollen data, that supports a dry environment.
Environmental reconstructions and proxies
As a consequence of the aridification of the interiors of the continents there was a supposed
expansion of open landscapes (Bruch et al. 2007). There is much discussion as to if this
‘overall continental aridification’ can be applied to all areas. Many researchers agree that
large regional differences should be taken into account, especially when looking at the
evolution and adaptation of large vertebrate species (Salesa et al. 2010). The aridification of
Europe during the Late Miocene supposedly started on the Iberian Peninsula (Eronen 2009)
and it brought about the spread of open landscapes which came with the invasion of the C4
type grasses. The adaptation that Anchitherium supposedly underwent was one for eating
more abrasive foods, and C4 grasses would qualify as more abrasive foods because of the
phytolith (silica) content. The timing of the spread of C4 grasses is therefore very important
for this thesis. There is much discussion about the exact timing of the spread of C4 grasses.
The Late Miocene is often seen as the period that witnessed the extreme radiation of this
grass type. For Anchitherium to so radically change its feeding habits that it required
evolutionary adaptation it is important to research the timing of the C4 type grasses
becoming the dominant vegetation in open landscapes.
Pollen, Flora
Many researchers argue that C4 grasses became the dominant open landscape vegetation at
the end of the Miocene (Janis 1994 and Domingo et al. 2008). Janis writes in her textbook
that around 8 Ma there was a shift in grass type from C3 to C4 type grasses. Grasses gained
importance in Southern Europe and Asia Minor starting in the Miocene. In Spain palynofloras
point to open, arid steppe and woodland environment during the Early and Middle Miocene
(Juménes-Moreno et al. 2007). This would support Eronen (2009) in his claim that in Spain
the arid steppe and woodland environment evolved earlier than in the rest of Europe.
However, Eronen times this event of aridification much later than Juménes-Moreno et al.
(2007). Strömberg (2011) states that Northern and central Europe stayed fairly forested
throughout the Cenozoic.
Isotopic composition
Several studies in paleosoil carbonates (Quade et al. 1992 and Morgan et al. 1994) place the
dominance of the C4 grasses during the Late Miocene and Early Pliocene (between 7- 5 Ma).
Even later than the Late Miocene in the studies of Janis (1994) and Domingo et al. (2009 B).
The isotope data extracted from paleosoils show a sudden change in d13C between 7 and 5
Ma. It needs to be noted that the two investigations that she uses to support this claim are
from researches done in Pakistan and Kenya. Macfadden (1994) finds that the isotopic value
29
of the grazing species that lived during the Late Miocene he researched indicates a C3
dominated diet. The fact that these animals are grazing species indicates, according to
Macfadden, that the dominating grass vegetation was still C3 and not C4 grass. This
conclusion is consistent with the isotopic shift, supposedly indicative of the shift from C3 to
C4 grass domination, that Quade et al. (1992) and Morgan et al. (1994) find between 7- 5 Ma
(Miocene Pliocene boundary). Domingo et al. (2009 A) note in their research on Hipparion
dental enamel that there is a significant increase in the isotopic d13C value around MN14MN15 (5-4 Ma) thus in the Pliocene. This increase may signify an increase in the
consumption of C4 plants. And may be indicative of an even later spread of the C4 grasses in
Europe than was previously thought (data from the Teruel-Alfambra region).
CO2
The overall consensus is that the predominance of C3 versus C4 plants depends on
temperature and CO2 partial pressure (Ehleringer and Pearcy 1983, Ehleringer and Monson
1993). Ecosystems dominated by C4 plants are those with high temperatures and aridity.
These are also the ecosystems that show low CO2 partial pressure values because C4 plants
can concentrate the CO2 in their leaf cells before carrying out photosynthesis (Domingo et al.
2009). Thus initially the spread of the C4 plants at the end of the Miocene was attributed to
a drop in CO2 concentrations during the Late Miocene. However Pagani et al. (1999) argued
that the CO2 concentrations showed an increase from a minimum value at 14 Ma (180 ppmv)
up to values between 320 and 250 ppmv in the later Miocene (9 Ma). A possible conclusion
from this can be that if the expansion of the C4 grasses was triggered by the lower CO2
values it should have occurred at the beginning of the Miocene. The presumed drop in CO2
levels at the end of the Miocene has often been seen as a cause for the spread of the C4
grasses, but if this drop never occurred this handheld is also lost.
Fauna
The macrodont species Anchitherium corcolense is, according to Inigo (1996), better adapted
to a drier environment. This species lived during the Aragonian (MN3 and MN4) in Spain.
Inigo associates this species with the environment ‘open woodland’ or ‘woodland savannah’.
Also found at Corcoles, is the rhinoceros Hispanotherium matritense, a grazer. However
Inigo does discuss that Anchitherium is more abundant in the layer that is associated with
less dry environmental conditions. Höck (2009) recognizes the fact that Anchitherium
aurelianense found in MN 3 layers from Austria is a typical brachydont species, which may
be indicative of a woodland environment. The faunal evidence by Inigo and Höck could point
out that Spain was already a drier area of Europe when Anchitherium first arrived during MN
3.
30
Chapter 3 - Practical research
Introduction
The practical part of this thesis will mainly consist of morphological research on
Anchitherium fossils from localities in Spain (figure 3.1) Like most fossil horse material from
the New as well as from the Old World (Forsten 1991) the material consists mainly of
isolated teeth. Measurements on different species as done by: Inigo (1997), Sanchez (1999),
Hernández Fernández et al. (2003), Alberdi et al. (2004), Salesa et al. (2004), Daxner-Höck
and Bernor (2009) will be repeated and compared to the data from the literature. The
specimens used in the research are from the Utrecht University paleontological collection.
Some specimen have been determined on species level and all specimens, bone and teeth,
belong to the genus Anchitherium Meyer, 1844. I will discuss the specimens per locality. The
morphology will be examined and the size of the teeth will be measured in order to
determine (wherever possible) the specimen on species level.
The original idea of this practical research was that micro- and mesowear analysis would be
attempted. It turned out however that Utrecht University did not posses research facility
needed for this kind of research and also that the sample sizes were too small for decent
statistical analysis. Isotopic research was not performed because of the small amount of
material and the fact that the fossils needed to be destroyed partly or entirely for this type
of analysis.
Figure 3.1 Localities
31
Methods
The measurements on the molars have been performed using a precise measuring device.
Measurements have been done multiple times in order to minimize room for error and have
been noted in mm (and 0,1 mm). Of the molars the anterior width, posterior width and
length have been measured on the widest part of the tooth. Length has also been measured
on the longest part. (figure 3.2)
Technical practical problems
Measuring problems
None of the authors included the measuring method of the molars in their article. Therefore
a problem that was faced was the fact that for species determination all authors used one
single value for width as well as for length of the teeth. During the first attempt, the mean
value of the posterior and anterior width of the samples was calculated and plotted in the
different graphs. Later it turned out that it was standard practice, unless indicated
otherwise, to always measure the widest part of the tooth. All graphs have been corrected
for this different approach.
Nomenclature
Another problem that was encountered was that of the nomenclature. The upper cheek
teeth of horses are among the largest and most complex of mammalian teeth. To make
matters worse, terms introduced by one author have not always enjoyed acceptance by
others. As a result, some lower molar structures have been given as many as five different
names (Evander 2004). Also the nomenclature developed for horse teeth does not entirely
correspond to the nomenclature of fossil mammals in general. And for Anchitheriine teeth in
particular some structures that are described for other fossil horse teeth are not present.
Unfortunately, no literature was found describing what the standard Anchitheriine molar
structure looks like. But by comparing the structures of the different species of Anchitherium
to the nomenclature of fossil horses in general (Evander 2004) it has been possible to
deduce at least some of the structures that are missing in, not described for or not used to
32
describe Anchitherium teeth. The following differences in tooth morphology definition are
those noted between the nomenclature as proposed by Evander (2004) and the
Anchitherium tooth nomenclature as used in Sánchez et al. (1998) and Alberdi et al. (2004);
-
-
-
-
-
-
-
The minor cusp located posterolabially to the hypocone and anterior to the
posterior cingulum was named hypostyle by by Osborn (1918) and Stirton (1941),
Sánchez et al. (1998) and Alberdi et al. (2004) also use this term. It has been
renamed ‘hypoconule’ by Evander (2004).
Likewise, the paraconule (Evander 2004) is still named protoconule (Osborn 1918,
Stirton 1941) in the Anchitherium tooth morphology used by Sánchez et al. (1998)
and Alberdi et al. (2004).
In (figure 3.3) is translated the ‘valle mesial’ and ‘valle distal’ (Spanish) directly to the
terminology of Evander’s (2004) ‘post’ and ‘pre-flexid’. Evander states that one of
the former names of the ‘Hypoflexid’ (see next comment) was ‘median valley’
(Quinn 1955). It can only be assumed that the English names for ‘valle mesial’ and
‘valle distal’ would subsequently be ‘mesial valley’ and ‘distal valley’. It cannot be
determined for sure whether these are also names proposed by Quinn (1955). But
when Evander (2004) discusses the previous names of both forms he does not name
mesial and distal ‘valley’ as one of them. The Spanish and French terms have
therefore been translated directly to Evander’s terminology.
It appears as if the hypoflexid (Evander 2004) is, at least by Sánchez et al. (1998) and
Alberdi et al. (2004), not used to describe Anchitherium tooth morphology. Which is
rather strange since the post and pre- flexid are used for the ‘valleys’ on the lingual
side of the lower cheek tooth.
The ‘anterostyle’ is most likely referred to by Evander (2004) as ‘Anterior Accessory
Rib’ but this is not certain and therefore it has been named anterostyle in (figure
3.3)
The terms ‘paraconid’ and ‘metalophid’ appear to be missing in Evander (2004). No
synonyms or clues that these are old names have been found.
The paraconid is in fact not present in the equine species. However it is named in
the literature about Anchitherium. It is possible that this is a leftover from the
original paraconid or that it is a new small form of the tooth. In this case it is falsely
named paraconid.
Inigo (1997) presents a new term ’internal cingulum’, this is the cingulum on the
lingual side of the tooth.
33
Nomenclature 2, language
Many articles dealing with species specific tooth morphology in Anchiteriine horses have
been published in French or Spanish. For this purpose a nomenclature overview of the
terminology in Spanish; French and English has been added (figure 3.3)
34
Materials
Following is an overview of the research material present from 11 different sites with
Anchitheriine remains in Spain (figure 3.4). It will be discussed whether there is secondary
literature about the site revealing what species of Anchitherium is present. All reference
fauna’s for these different sites has been attempted to gather for this research. Also the
Paleobiological database and the NOW database (Fortelius 2003) was consulted for
occurrences of Anchitherium or other Perrisodactyl genera. This secondary information was
connected to the measurements in order to determine what species is present at which site.
For every site there is a detailed description of the different specimens. A species
determination will also be attempted using the different characteristics in horse tooth
morphology and comparing them to the characteristics as described in the different
Anchitherium species descriptions (Appendix A)
Munebrega 1
Samples
55-1017 (P2 sin) and 55-1016 (P2 dex) (damaged) – Hypocone and hypostyle are clearly
present and well developed and connected to the posteriolingual side of the hypocone in
case of heavy wear. The hypostyle is lower than the hypocone and is triangular in shape. The
metalophe connects the hypocone to the ectolophe between the paracone and the
metacone. A crochet is not present. A basal cingulum is present from the anterior side at the
base of the anterostyle along the lingual side of the tooth to the posterior side ending at the
posterior side of the metacone. It is weak on the lingual side of the protocone and also on
the lingual side of the hypocone.
55-1015 (P2 sin) (strongly damaged on anterostyle) - The description is the same as the P2 sin
discussed above.
55-105 (P3 sin) (Hypocone and metacone absent) - The basal cingulum starts at the
anterostyle and runs along the anterolingual base of the protocone. It is absent on the
lingual side. A crochet is absent.
55-1017 (P3 sin) - The basal cingulum starts at the base of the anterostyle and runs along the
anterolingual base of the protocone and is absent on the lingual side. It then runs from the
posterior side of the hypocne to the metacone. The hypostyle is triangular and is separate
from the posterior cingulum. There is no crochet present.
55-1016 (P3 dex) – The basal cingulum runs from the anterostyle to the anterolingual base of
the protocone, it is absent on the entire lingual side and then runs from the posterior side of
the hypocone to the metacone. The metalophe does not have a crochet and the hypostyle is
strongly connected to the posterior basal cingulum.
35
55-1019 (P3-P4 sin) – Both have a very small style in the preflexid and a very clear basal
cingulum.
55-101 (M2 dex) – small style in the postflexid and a clear basal cingulum.
55-1006 (P4 dex) on the base of both the flexid’s the cingulum is incomplete or it has a
cingulum like style.
Literature and data
In the latest NOW database (Fortelius 2003) Anchitherium is not recorded for Munebrega 1.
The only perissodactyla present in the datebase from this site is the Rhinocerotidae
Hispanotherium matritense.
Species- The species Anchitherium castellanum can be ruled out because in this species a
basal cingulum is absent in the lower dentition. Anchitherium matritense can also be ruled
out on the bases of the crochet that should be present in all upper jaw dentition except the
M2. There is a style present in the preflexid of the lower jaw P4, this also rules out
Anchitherium procerum. And this dentition does not resemble the dentition of the species
identified as Sinohippus sampelayoi.
Armantes 1
Samples
41-564 (3* P or M lower jaw sin) – A basal cingulum is only present on the lingual side. All
three molars have a style in the flexid. The style is less pronounced in the presumable M2
molar.
41-503 (M2 dex) – The same description as above applies. The style is less pronounced.
41-505 (P1-P2 dex) – The basal cingulum is present on the lingual side of both teeth. The style
is very pronounced in P2.
41-500 (M1 dex) – A basal cingulum is present on the lingual side and on the labial side there
is a very weak basal cingulum and a style is present (the style almost seems to be part of the
cingulum).
41-501, 41-502, 41-504 (M3 dex, M3 sin, M2 dex). In all teeth the paraconid is very
pronounced and all have a basal cingulum on the lingual side. The cingulum is absent on the
labial side. A style is also present in all teeth.
36
Literature and data
In the latest NOW database (Fortelius 2003) Anchitherium is not recorded for Armantes 1.
The only perissodactyla present in the datebase from this site are the Rhinocerotidae
Alicornops simorrensis and Hispanotherium matritense.
Species- The species Anchitherium castellanum can be ruled out because in A. castellanum a
basal cingulum is absent in the lower dentition. A style is present in this species’ lower jaw
P2, this is also the reason for which Anchitherium castellanum can be ruled out. Anchitherium
castellanum has a high frequency of styles in the lower dentition however it is virtually
absent in the P2, and this dentition does not resemble the dentition of the species identified
as Sinohippus sampelayoi.
Arroyo del Val 4
Samples
AR4-471 (P2 dex) – A weak cingulum is present on the labial side of the tooth no style is
present.
AR4-106, AR4-107 (M3 sin, M3 dex) – A basal cingulum is present only on the lingual sied of
the tooth. A style is not present and the paraconid is entirely separate.
AR4- 105 (P3 dex) – A very pronounced cingulum is present on the lingual side there is no
style.
AR4-102 (M2 dex) – There is a cingulum on the lingual side and no style.
AR-104 (P4 dex, M1 dex) - There is a cingulum on the lingual side of the tooth and there is not
style in either of the flexids.
Literature and data
In the latest NOW database (Fortelius 2003) Anchitherium is not recorded for Arroyo del val.
The only perissodactyla present in the database from this site is the Rhinocerotidae
Alicornops simorrensis.
According to the handwritten cards provided with the Universities fossil material the species
of Anchitherium is A. ezquerrae ezquerrae.
Species: A cingulum is present in the lower jaw dentition, this rules out Anchitherium
castellanum as a possibility. A style is present in the lower jaw P2, this also rules out
Anchitherium castellanum. The fact that the style is absent corresponds with the diagnoses
of Anchitherium procerum. And this dentition does not resemble the dentition of the species
identified as Sinohippus sampelayoi.
37
Arroyo del Val 6
(AR6 25) upper jaw molar (Anchitherium ezquerrae ezquerrae)
Literature and data
In the latest NOW database (Fortelius 2003) Anchitherium is not recorded for Arroyo del val.
The only perissodactyla present in the datebase from this site is the Rhinocerotidae
Alicornops simorrensis.
Manchones 1
Samples
Noted: These samples are very different from the reference teeth used from the species
Anchitherium aurelianense.
MA1- 121 (P4 sin) – There is no cingulum present of either side of the tooth. The hypocone is
connected to the metalophe. The hypostyle is not entirely triangular and is connected to the
hypocone. No crochet is present.
MA(2)-52 (P3sin) - There is no cingulum present of either side of the tooth. The hypocone is
connected to the metalophe. The hypostyle is not entirely triangular and is connected to the
hypocone. No crochet is present.
MA1-118 (M1 sin) – There is a cingulum present starting at the paraconide and ending at the
Metaconide. The style is present, though very slightly.
Furthermore a strange M3 molar is present in the material. It has a slightly wrought form
towards the posterior of the tooth and it has no cingulum and no style.
Literature and data
In the latest NOW database (Fortelius 2003) Anchitherium is not recorded for Manchones 1.
The only perissodactyla present in the database from this site is the Rhinocerotidae
Alicornops simorrensis.
Species: A cingulum is present in the lower jaw dentition, this rules out Anchitherium
castellanum as a possibility. A slight style is present in the lower jaw M1 which rules out
Anchitherium procerum. this dentition does not resemble the dentition of the species
identified as Sinohippus sampelayoi.
38
Buñol
Samples
BU-2 (P1-M3 sin) (lower jaw complete sinistral side) These teeth all have a basal cingulm that
runs all around the tooth, except for P1. The paraconide in the M3 molar is not separate as
has been observed in other specimens.
(Upper jaw (pre-)molar- not specified). A cingulum is present on the lingual side. The
hypocone is connected to the metalophe. The hypostyle is triangular and separate from the
hypocone.
Literature and data
According to the notes enclosed with the universities specimen the Anchitherium material
found at Buñol is not further specified than the genus level (Anchitherium sp.). Van der
Made (1996) generalizes the Anchitherium fossils found at the Buñol site as Anchitherium sp.
According to Fortelius (NOW Database July 2003) however some Anchitherium specimen
found at the Buñol site belong to the species Anchitherium aurelianense (Fortelius 2003).
The primary reference for this fauna (Crusafont and Santonja 1957) also identifies the
Anchitheriine species at the Buñol site as A. aurelianense. In their revision of the genus
Anchitherium (Sanchez et al. 1998) also identify the fossils found at Buñol as Anchitherium
aurelianense aurelianense as does (Forsten 1991).
Other perissodactyl species found at Buñol belong to the family Rhinocerotidae;
Lartetotherium sensaniense; Prosentorhinus Sp. and Diaceratherium aurelianense. Another
perrisodactyl is the Phyllotillon narsicus of the family Chalicotheriidae (Fortelius, NOW 2003).
I am inclined to conclude that the Anchitherium specimen from Buñol all belong to the
species A. aurelianense because unlike for example the Rhinocerotidae, modern as well as
fossil Equidae often show an appearance of only one species per locality (Janis 2008)
Exceptions are for example the coexistence of Hipparion and Anchitherium species at some
localities (Höck 2009, Salesa 2004) however this coexistence may have been the cause for
Anchitherium to decline and disappear completely.
Species: A cingulum is present in the lower jaw dentition, this rules out Anchitherium
castellanum as a possibility. this dentition does not resemble the dentition of the species
identified as Sinohippus sampelayoi.
Nombrevilla
Samples
(P3, P4 dex) – No cingulum is present. The hypocone is connected to the metalophe and the
hypostyle is separate and triangular. No crochet is present.
(P4, M1, M2 dex) – A cingulum is present on the lingual side and a style is also present.
39
Literature and data
According to the universities’ handwritten guideline cards provided with the material the
species present in the Nombrevilla fossil finds is Anchitherium sampelayoi. Salesa (2004)
provides evidence for his claim that fossils so far identified as Anchitherium sampelayoi
should in fact be included in the Asian genus Sinohippus and thus named S. sampelayoi. The
primary reference for this fauna is Freudenthal (1966), in this article the equine species
found at Nombrevilla is identified as Anchitherium sampelayoi but in the ‘paleobiology
database’ this species is also synonym to Sinohippus sampelayoi. This reflects the changing
insight on the grouping of this species within a certain genus over time.
A problem however arises with the NOW data set, published in 2003 by (Fortelius 2003).
According to this data set the two genera of Equidae found at the Nombrevilla site are;
Hipparion koeningswaldi and Anchitherium aurelianense. A co-occurence of both these
genera has been described for multiple sites and has been generally accepted (Höck 2009,
Salesa 2004). However in past fossil assemblages as in modern faunas generally no more
than one species of Equidae is found at the same locality, so the co-existence of three
different genera (Anchitherium, Hipparion and Sinohippus) would be quite unlikely. A cooccurrence is not impossible but literature presents no further evidence for a co-occurrence
of both these species in Nombrevilla.
Other perissodactyl species occurring at this site are Diaceratherium aurelianense;
Alicornops simorrensis and Lartetotherium sansaniense, all belonging to the Rhinocerotidae
family. And Ancylotherium pentilicum of the Chalicotheriidae family (Fortelius 2003).
Torralba 1
samples
18-200 (M3) – There is a cingulum on the lingual side and a style is clearly present. The
paraconid is separate from the rest of the molar.
18-202 (P2 sin) – The cingulum appears to be present on both sides of the premolar. The
hypostyle is triangular and separate. The hypocone and metalophe are connected and no
crochet is present.
Torralba 3
samples
Noted: This is an abnormally large molar.
40
TOR3-5 (P3) - There is a cingulum present on the labial side of the tooth. The hypocone and
metalophe are connected . The hypostyle is sort of triangular but had another shape in the
middle (circle) and is separate from the hypocone. There is no crochet.
Val de Moros 3A
Samples
VAL3a-500 (P? dex) – A weak cingulum is present on the lingual side. The hypostyle is not
entirely triangular and it is separate. No crochet is present and the hypocone is connected to
the metalophe.
41
Material – fossil material and casts
Two or three photos per location of the most representative samples (figure 3.4)
42
43
44
Scatter-Plots- Species determination
For the determination of the species of Anchitherium from the different Spanish localities
scatterplots based on tooth measurements will be used. For the determination of the
samples on species level the measurements as presented by Inigo (1997), Salesa et al. (2004)
and Sanchez et al. (1999) will be used. The findings will be discussed in relation to the
information gathered about the species at the sites prior to the measurements (NOW
database, Paleobiological database and the reference fauna articles of the different sites).
Problems and inconsistencies will also be discussed.
Salesa et al. 2004-
45
Munebrega
Manchones
Nombrevilla
Torralba
Buñol
40
35
30
25
20
15
25
35
Figure 3.5- Salesa (2004) measurements vs. research measurements
45
The plot on the right (figure 3.5) is from Salesa et al. (2004) and it shows the relationship
between length and width of P3-P4 within the different species of Anchitherium. The plot
includes American as well as European species, the American species generally being larger.
Anchitherium sampelayoi plots high, close to the American species. Salesa et al. use this in
their argument that A. sampelayoi ought to be classified under de genus Sinohippus because
all the European Anchitherium species plot much lower in this figure.
The data from the practical research has been plotted into a similar graph (figure 3.5) in
order to identify the different species at the different localities. One problem that directly
arises is the fact that Salesa et al. (2004) fails to mention whether for their measurements of
P3 and P4 they have used upper or lower jaw molars. It was assumed that they had used the
upper jaw molars, and after plotting both figures it became clear that the figure by Salesa et
al. (2004) is indeed based on upper jaw molar measurements.
The two samples from Nombrevilla are of the newly defined species Sinohippus sampelayoi
(Salesa et al., 2004) and might thus form a good calibration for the graph. One value, as
measured on my samples plots as S. sampelayoi in Salesa’s figure, the other plots a little too
low. Overall Sinohippus sampelayoi appears to be a good match and thus reference point.
However, an important thing needs to be noted here; the samples in the universities
collection are with a high degree of certainty a cast of the originals that were used by Salesa
et al. (2004). The measurements from the practical research and theirs have thus been
performed on exactly the same specimens, fossil and cast. Therefore the offset is only
explainable by difference in measuring method. I may conclude from this that my method of
measuring differs from that of at least Salesa et al. (2004). However the values do plot
roughly in the same area so it was concidered the measurements of S. sampelayoi valid.
The samples from Munebrega all plot very low, in the area of Salesa’s graph that is only
occupied by A. aurelianense. For Munebrega no literature or occurrences was found in the
different databases suggesting which species of Anchitherium was present there. It can thus
tentatively be concluded (from the very few datapoints ) that the species most likely present
at Munebrega is Anchitherium aurelianense. Noted here needs to be that the few specimens
that were measured for Munebrega were almost all broken and incomplete. In some cases it
was compensated for missing parts by estimating how much of the particular tooth was
missing. This was never more that 3 to 4 millimeters.
The samples from Buñol also plot in the same area, but lower than Munebrega. For many
samples from Buñol it was not specified whether the tooth was a molar or premolar and
which one it was. Most of them were eventually classified within the ‘Unidentified Upper
jaw molars’ (Appendix B). The values have however been plotted in this graph. The reason
why the measurements may plot too low is that the teeth were not P3 and P4 But maybe P2
or M molars. Information from the reference fauna literature and databases shows that the
species at Buñol is most likely to be Anchitherium aurelianense as well. The measurements
are somewhat consistent with that even if they are slightly too low.
The only sample from Torralba plots so far from any of Salesa’s measurements it will not be
identified as Anchitherium aurelianense. There was only one other specimen from Torralba
46
but it was concluded that this tooth was so different from the other that it might not even
be an Anchitherium molar. Only one measurement remained and it showed such a deviation
I ruled it not acceptable as a semi-valid species determination. The only observation that can
be validly made is that it plotted by far nearest to A. aurelianense.
For Manchones however it’s more complicated. The samples plot generally in the area of A.
castellanum, A. matritense and A. alberdiae (and maybe also A. cursor). The fossils have
however been determined earlier as belonging to the species A. ezquerrae ezquerrae. This
species however has in 1997 by (Inigo 1997) been incorporated into the species
Anchitherium corcolense, but only the ones that have been found at Corcoles. It becomes
problematic because in Salesa’s figure the species A. corcolense is absent. In the next part
Inigo’s figures that do include A. corcolense will be plotted. Here a new hypothesis for the
species found at the Manchones site will be presented.
Inigo 1997In his presentation of the new species Anchitherium corcolense, Inigo presents a figure in
which he plots the values for all different teeth with measurements of A. ezquerrae and A.
aurelianense (figure 3.7). He aims to show that A. corcolense is a different species from the
A. aurelianense and A. ezquerrae found at different localities. The research data was plotted
in a similar fashion (figure 3.6) for comparative purposes. The alternative notation for upper
and lower jaw as used by Inigo was maintained only in figure 3.6 for better comparison to
figure 3.7.
Figure 3.6 – research measurements
47
Figure 3.7 – Inigo (1997) measurements
The P1 samples of Buñol plot in the general area of A. aurelianense, as was expected. The P3P4 samples of Buñol plot apparently too low. This has the same cause as the anomaly of
these samples within the figures of Salesa. Namely that these molars have not been
identified (see appendix B samples are listed under ‘unknown’). Thus the molars from Buñol
are probably not P3 or P4 but rather P2 or M1 or M2. The lower jaw M1 data point from Buñol
plots nicely within the range of A. aurelianense. The (single) P4 sample however plots
inexplicably far outside the area designated for A. aurelianense. I have no explanation for
this except that this sample from Buñol perhaps wasn’t a P4 lower jaw molar.
48
The Torralba sample, again, plots so off-chart than I deem it not acceptable as any kind of
species determination.
The Munebrega P3-P4 samples plot a little outside but still fairly close to the range identified
for the species A. aurelianense. This is also consistent with the findings from Salesa’s figure.
The P1 sample however plots within the range of A. corcolense which is very strange. I have
no explanation for this except that the sample was identified wrongly as a P1 molar. For the
lower jaw the Munebrega samples also plot fairly well within the ranges designated for A.
aurelianense. Only for the lower jaw M1 it appears as if the samples were too long. Which is
possible since identifying the M1 from for example P4 has proven difficult, as confirmed by
different authors and by myself.
The upper jaw P3-P4 samples for Nombrevilla (L28; W38) and (L30,5; W34) and also the lower
jaw M1 sample (L29,5; W21.75) plot outside of the range of the graphs. Which is again
consistent with Salesa’s conclusion that these teeth are substantially bigger than the average
European Anchitheriinae.
Newcomers in this graph are Armantes 1 and Aroyo del Val. From these sites the lower jaw
teeth were more abundant in the set I received. Saying something about Aroyo del Val is
difficult. The Utrecht University specimens are identified as A. ezquerrae ezquerrae but the
lower jaw data plots too low for the ezquerrae samples. In the case of the lower jaw M1 it
even appears as if the data point plots more within the area of A. corcolense. It could be
hypothesized that the species found at Aroyo del Val may also be in fact A. corcolense. But
this will not be done based only on one measurement. This hypothesis will be proposed for
the samples from Manchones (next paragraph).
The (single) lower jaw M1 Armantes sample plots on the edge of the area designated by Inigo
(1997) as A. aurelianense. Again this is too little information to base an actual species
determination on. Also because there is no additional information for this site that can
confirm that this species is present here. If this additional information were present this
single data point may have served as support or confirmation. On its own it is in my opinion
rather useless.
These plots, based on Inigo (1997), may also shed some light on the problem that arose with
Salesa’s figure and the samples from Manchones-1. In the P3-P4 figure, the same proxy that
was used by Salesa, the Manchones samples plot well within the range of A. corcolense.
They are in the overlapping zone of A. corcolense and A. ezquerrae. According to Inigo only
the samples originally classified as A. ezquerrae ezquerrae that where found at the site of
Corcoles were to be taken into the new species A. corcolense Inigo, 1997. The fossils from
Manchones-1 have been identified as belonging to the species A. ezquerrae ezquerrae by the
Utrecht University (date and person unknown). If identified correctly this figure might be a
clue that the species found at Manchones-1 might in fact also be A. corcolense, and this then
would imply that A. corcolense is not only found at the site of Corcoles. For the lower jaw it
is less apparent. In the M1 graph the samples from Manchones plot slightly outside the range
of A. corcolense but neither do they plot within the range or any of the other species. So for
the M1 figure I would still classify them as possibly A. corcolense. The only possible exception
49
is the plot P4 where it appears as if the (singly) sample from Manchones plots within the
range of A. aurelianense. But it plots very near the overlapping zone between A.
aurelianense and A. corcolense. And also in the plot P4 the zones of overlap between A.
ezquerrae ezquerrae and A. aurelianense with A. corcolense are very close together. This
then still leaves intact my theory that possibly A. ezquerrae ezquerrae from Manchones is in
fact also A. corcolense.
The location of the site Corcoles was plotted in figure (figure 3.8) Both sites are roughly 200
km apart. Thus a co-occurrence of the same species may not be very strange.
Figure 3.8 – the location of Corcoles relative to the other locations.
50
Sanchez et al. 1998
Figure 3.9 Sanchéz et al (1998) measurements
51
Sanchéz et al. has named typelocalitiess for his identified new species of Anchitherium. The
mean values of the different molars and premolars were plotted and the same was done for
the practical research’s measurements. The aim was to be able to match up these
measurements with Sanchéz’s and find out whether some of ‘his’ species could be identified
in one of ‘the research’ locations.
First of all, all of Sanchéz’s species, except for Anchitherium aurelianense that is clearly
smaller, group very close together. This already makes a species determination difficult.
The only clear match is that of Buñol. This is no surprise since Sanchéz’s data also comes
from Buñol. The rest of the data is unfortunately useless. In my opinion Sanchéz’s data is the
least reliable. Because he presents no less than 5 new species of Anchitherium that are very
much alike. At least their measurements all plot very close together. The fact that the only
‘known’ other species Anchitherum aurelianense is the only one to plot away from the
others makes this even more clear. These measurements have been omitted from the final
species determination.
Species determination - practical summary
In this summary of my practical work it will be attempted to determine what species is most
likely found at what location. This will be discussed per location separately and will be
supported by different measurements and data.
Munebrega 1
Based on the morphological research Anchitherium castellanum, Anchitherium matritense,
Anchitherium procerum and Sinohippus sampelayoi can be ruled out for Munebrega 1. The
NOW database does not have any data on this location. In size comparison to Salesa’s data
the samples from Munebrega plot in the area of the graph that is only occupied by the
species Anchitherium aurelianense. Also in the data by Inigo the Munebrega samples plot
fairly close to the range identified for the species Anchitherium aurelianense for the upper as
well as the lower jaw dentition. Judging from these two different data comparisons it would
seem as if this species can tentatively be identified as Anchitherium aurelianense. However
in the final set of datapoints, from Sanchéz, the Buñol samples (already positively identified
as Anchitherium aurelianense) are the only samples plotting near Sanchez’s Buñol samples
(in Sanchéz identified as A. aurelianense). The Munebrega samples appear to be much
larger. This is strange since in the data by the two other authors both locations appeared to
fall well within the range of Anchitherium aurelianense. I have no explanation why in
sanchez’s data Buñol does appear to be correct and Munebrega does not. Other than that
his data is less reliable than the others (something I am inclined to believe since he
miraculously created 5 new species of Anchitherium) and that Buñol is correct by chance
where the rest of the data is flawed.
The species at the site Munebrega 1, Anchitherium aurelianense
52
Armantes 1
Based on the morphological research Anchitherium castellanum and Sinohippus sampelayoi
can be ruled out. The NOW database does not have any data on this location. No samples
comparable to Salesa’s data was available for this location. The one datapoint that is
comparable to Inigo’s data plots in the range of Anchitherium aurelianense. However this is
not enough information to perform a decent species determination.
No species determined for this location.
Arroyo del val 4
Based on the morphological research Anchitherium castellanum, Anchitherium procerum and
Sinohippus sampelayoi can be ruled out. Sánchez et al. (1998) also state that the material
from Arroyo del Val could not be assigned to any of the proposed new species and remains
Anchitherium sp. The NOW database does not have any data on this location. No samples
comparable to Salesa’s data was available for this location. A weak argument may be made
for the determination of the species at the location Arroyo del val of Anchitherium
corcolense. This would be based on the data presented by Inigo et al. However I will not
hypothesize the species Anchitherium corcolense based on only one sample.
No species determined for this location.
Manchones 1
Based on the morphological research Anchitherium castellanum, Anchitherium procerum and
Sinohippus sampelayoi can be ruled out. The NOW database does not have any data on this
location. The samples have been earlier identified as A. ezquerrae ezquerrae. This species
has by Inigo been incorporated into Anchitherium corcolense nov sp. From Salesa’s data it is
hard to say anything because the species Anchitherium corcolense is not present in the data.
In Inigo’s data however the data plots in the overlapping zone between A. ezquerrae
ezquerrae and Anchitherium corcolense. I find it confusing that Inigo incorporates the
(former) species A. ezquerrae ezquerrae as described by Abusch (1983) in his new species.
Because if this sample is Anchitherium corcolense this would imply that this species is not
only found at the type location but also at the site Manchones 1. Both locations are also only
a rough 200 km apart this also makes this hypothesis more likely.
The species found at Manchonces 1 may be Anchitherium corcolense.
Buñol
Based on the morphological research Anchitherium castellanum and Sinohippus sampelayoi
can be ruled out. Van der Made (1996) does not further specify the species found at Buñol.
In the NOW database by Fortelius (2003) however some specimen are described as
Anchitherium aurelianense. Also the primary reference for this fauna Crusafont and Santonja
53
(1957) identifies the species found at Buñol as Anchitheriun aurelianense as do Sanchez et al.
(1998) and Forsten (1991). Within the data of Salesa, Inigo and Sanchéz the specimens from
Buñol are the only ones always significantly within the range identified as Anchitherium
aurelianense.
The species at the site Buñol Anchitherium aurelianense.
Nombrevilla
For the samples from Nombrevilla I can be very brief. The samples in possession of Utrecht
University are copies of the exact same specimens that were used as the holotype for the
new species Sinohippus sampelajoy.
The species found at Nombrevilla is Sinohippus sampelajoy.
Torralba 1 and 3
No species determined for this location.
Val de Moros 3 A
Sánchez et al. (1998) name the species found at the Val de Moros site Anchitherium
parequinum. However I could not compare my measurements from Val de Moros to
Sánchez’s. Therefore I have not enough information to soundly base a species
determination.
No species determined for this location.
54
Chapter 5 - Discussion
Diversity of species within the Genus Anchitherium
The hypotheses to be tested originates from an article by Eronen et al. 2009. They challenge
the generally accepted theory that Anchitherium did not adapt to environmental and
climatic changes and thus became extinct. They conclude that the Spanish Anchitheriine
horses did show signs of ‘incipient hypsodonty’ and thus adaptation to a drier environment.
They compare the Spanish species with German Anchitherium species and concludes that
these specimens do not show this incipient hypsodonty. They are challenged by Salesa et al.
(2010) who point out that Eronen and his group do not take into account the actual diversity
of the Iberian representatives of Anchitherium. The German specimens are from a
homogeneous selection because they came from a single location. The Spanish specimens
were collected over a wide spatial and temporal range. This comment is well grounded and
also a point of critique I wish to express in the discussion of this thesis. Aside from the fact
whether or not the Spanish Anchitheriine horses did show signs of incipient hypsodonty this
research is invalid because the comparison cannot be made on the basis of only one German
locality and species. For a better comparison more localities and more species from
Germany should be included.
A problem of almost all studies used in this thesis that their conclusions about
Anchitherium’s adaptation are based on several different species. From the practical
research it can be concluded that the diversity of traits and morphological features within
the genus Anchitherium is very high. An unfortunate effect of this is that all researches,
especially those based on morphological features of a few species can never represent the
entire genus of Anchitherium. Morphological changes may have occurred in one species
alone. Eronen et al. (2010) defend their methods by stating that looking at the genus level
can be a valuable way of gaining information. I disagree with this because when all the
species are so morphologically different the genus level will not reflect the overall changes
very well. Especially if some remained very conservative whereas other species underwent
major change. A discussion point may also be raised about this diversity in species within the
genus Anchitherium.
The validity of the new species by Sánchez et al. 1998
In their 1998 article Sánchez et al. identify no less than 6 new species within the genus
Anchitherium. These species are A. cursor (MN 6 Alhambra-Tüneles, Madrid), A. castellanum
(MN 4 La Retama, Cuenca), A. matritense (MN 5 La Fuentecilla, Madrid), A. alberdiae (MN 5
all sites from Madrid), A.procerum (MN 6 Paracuellos, Madrid) and A. parequinum (MN 5 El
Terrero and Valdemoros, Zaragoza). The validity of these 6 new is discussed here for several
reasons: first of all, all locations except that of the new species A. parequinum, are near
Madrid. So basically all species were found geographically close to one another. The
different species are however distinctly separated in a temporal range however and span
multiple different MN zonations. A second, stronger, argument for the invalidity of (most of)
these species is the data that Sánchez et al. present. From the figures on page 47 is becomes
55
clear that the tooth measurements, usually a valuable tool for telling species apart, are
useless. All of Sánchez’s measurements on the ‘new’ species dentition plot extremely close
to each other. The species are not separable from the other species in none of the plots
generated. The only distinct species that can be identified from the figures generated from
Sánchez’s data is the species A. aurelianense that clearly has a smaller dentition, which is
also recognized by Sánchez et al who base their differential diagnoses mainly on
morphological differences in the teeth and bone structure. The differences in especially
tooth morphology I judge so minimal that it is not necessarily due to variation between
species but possibly variety within one species. The size of the male canines is often named
in the differential diagnoses of the new species presented by Sánchez et al. (1998). However
this feature can easily be a ‘racial’ difference rather than a morphological difference on the
species level. If we look at how different the members of the species Equus ferus caballus
Linnaeus, 1758 are it can be concluded that large differences are possible within one equine
species. Mainly based on the minimal differences in dental size I would say that most of
these 6 new species probably belong to one existing or new species. The only species that
might be a genuinely separate species is Anchitherium parequinum. One reason to believe
this is the fact that it is the only geographically detached species and the fact that Sánchez et
al. (1998) also argue that it is found at Val de Moros. Unfortunately this is the only species
for which Sánchez et al. (1998) do not provide dental measurements! If it were a separate
species it would be expected to plot away from the other datapoints as Anchitherium
aurelianense clearly does. This however remains untestable.
These new species as defined by Sánchez et al. (1998) are used by Eronen (2009) in his
research on incipient hypsodonty in Spanish and German Anchitherine horses. Eventually
Eronen generalizes the Spanish species to genus level and thus it is irrelevant whether these
are all separate species or not. Salesa et al. (2009) in his comment on Eronen (2009)
acknowledges all of these different Spanish species of Anchitherium. He emphasizes that
there are many Spanish species of Anchitherium. If both these scientists acknowledge the
validity of all of these species then maybe discarding them on the basis of what was
discussed previously may not be the best option. More research is needed and good
comparable measurements should be provided for these 6 new species.
Spatial and temporal environmental variations in Spain
Another major part of this thesis is the role played by climatic and environmental change. An
important point on which Eronen et al. (2009) base their assumptions of the adaptation of
Spanish Anchitherium is the fact that Spain was the first region to experience aridity during
the Early Miocene of Europe. However, from the literature research conducted for this thesis
it would almost appear as if various climates and environmental conditions were present at
the same time in the same region. Many researchers agree that the overall Miocene climate
became cooler and dryer. Böhme et al. (2008) argue 2 ‘washhouse climates’ during the
Miocene age took place. The first of these two took place within the timespan of 10.2-9.8
Ma. And Böhme isn’t the only researcher arguing a wet period during MN 9 in Spain. Van
Dam (2006) also comes to a similar conclusion. Fortelius et al. (2002) conclude that the
Miocene was green with only the slightest hint of increasing aridity, the value of his proxy
56
however is arguable. Other researchers however do support an overall aridification of the
interior of the continents and the Iberian Peninsula, like Bruch et al. (2007). The solution is
to be found in a phenomenon that Mosbrugger et al. (2005) call ‘local endemism’. Even
though for the overall climatic conditions it may be said that they became dryer, in Spain this
local endemism was so large that small island environments persevered. This is why many
researches appear to contradict each other. The studies were performed in different places
and the large regional climatic and environmental differences during the Miocene cause the
results of these studies to vary immensely. It is apparently well known that these local
differences exist and many authors do note that this is a known factor. Still they base a
climatic reconstruction of a large region upon one or two different sites, or many different
sites that are located very near each other.
One of the goals of this thesis was to map the local climates in Spain during the early late
Miocene. It appeared impossible however to link the different species that showed different
evolutionary traits to different areas with a certain climate and environment. For the simple
reason that both types of studies were not detailed enough. The studies of Anchitherium’s
evolutionary adaptations were mainly conducted on genus instead of species level. And the
climatic researches about South Western Europe and Spain in general only speak of large
local differences.
Hypsodonty, the spread of the C4 grasses and Anchitherium’s adaptation
Hypsodonty
Fortelius et al. (2002) use level of hypsodonty as a proxy for an environmental condition the
call ‘generalized water stress’. There is still an ongoing discussion about whether or not
hypsodonty is an adaptation to dry food or abrasive food like grass. By calling the condition
‘generalized water stress’, they evade linking hypsodonty to grassland. Apart from this there
is also always the possibility of an inmoving already hypsodont species making the area
appear much drier. Another point of discussion is why the environmental reconstruction
Fortelius presents changes so severely when adding horses to the hypsodont species? His
theory works out well when comparing his data to existing climatic records. However
hypsodonty in horses seems to disturb the proxy. This is an interesting point of discussion
that Fortelius does not elaborate much on. If hypsodonty is a good proxy for aridity, then
why don’t horses respond in the same manner as ruminants?
Eronen et al. (2009) claim incipient hypsodonty for the Spanish specimens of Anchitherium.
Forsten (1991) however states that Anchitherium never became hypsodont. The definition of
hypsodont is clearly also a point of discussion. Eronen et al (2009) challenges Forsten’s
definition of hypsodont in his article. He states that an increasing steepness of cusp slopes is
a prerequisite for truly hypsodont molars. That is why he calls it incipient hypsodont and it is
probably why Forsten does not refer to these species as hypsodont. I would also like to
question Eronen’s definition of hypsodonty. He does defend that morphological research has
shown that increase in cusp slope is one of the first steps towards hypsodonty. But there has
been very little actual research in this direction. Is increased cusp slope really a precursor of
actual hypsodonty? I find Eronen’s ‘evidence’ not very compelling and suggest that more
57
research needs to be done to find out if increased cusp slope is really an early stage in the
development of hypsodonty in horses.
Forsten (1991) conciders the species A. aurelianense from Buñol a primeval species and
observes an abrupt increase in dental size in the Spanish Anchitheres from the middle
Orleanian. Inigo 2001 argues that the species A. corcolense was already separated from the
most primitive forms and possessed larger dentition. A. corcolense is slightly older than the
specimens from Buñol. Forsten links this increased tooth size to a mixed feeding diet. This
may indicate that members of the genus Anchitherium were already showing signs of mixed
feeding in the Early Miocene (MN 3)
Spread of the C4 grasses
There is still much discussion about the exact timing of the spread of the C4 grasses.
According to Eronen et al. (2009) the spread of the C4 grasses started with the aridification
of the continents during the late Miocene. They contradict themselves here because they
also state that the aridification of the continents starts at the beginning of the Miocene. But
apparently the environmental consequences were most severe near the early late Miocene.
Several other studies place the spread of the C4 grasses later. Janis (1994) places it at around
8 Ma And paleosoil studies by Quade et al. (1992) and Morgan et al. (1994) place the spread
of the C4 grasses even later, at the Miocene Pliocene boundary between 7-5 Ma And also
Macfadden (1994) concludes from his isotopic values of grazing species that lived during the
late Miocene that they ate predominantly C3 grasses so that this was most likely still the
dominant type of grass.
The hypsodonty discussion is still ongoing, the same goes for the discussion about the
spread of the C4 grasses. What is relevant for this thesis is the link to Anchitherium’s
extinction. A possible scenario is that Anchitherium witnessed the upcoming of the C4
grasslands that spread at the expense of Anchitherium’s main food source woodland and
that hypsodonty was a trait needed to access this new food source. Linking the spread of the
C4 grasses to Anchitheriums demise is in this case hard to do. And also linking Anchitherium’s
downfall to aridity is risky. Because even though most researchers agree that there was an
overall increasing aridity of the interiors of the continents that started on the Iberian
Peninsula there is also evidence that there were several wetter periods, one within the
range of Anchitheriums extinction period.
58
Chapter 6 - Conclusion
The central theme of this thesis is the faunal turnover in the fossil record of the Late
Miocene from faunas dominated by Anchitheriine horses with low crowned molar teeth to
faunas with Hipparionine horses characterized by high crowned teeth. The general belief is
that the spread of the Hipparionine horses as well as the demise of the Anchitheriine horses
is associated with the expansion of open habitats and the spread of the C4 type grasses. The
Anchitheriine horses and their demise are the central subject of this thesis. And because the
environmental change, aridification and increasing openness of the landscape, supposedly
started on the Iberian Peninsula especially the Spanish Anchitheriine horses from the Middle
to late Miocene are examined both in literature and in practical research.
In recent research by Eronen et al. (2009) and Kaiser (2009) evidence is presented that
Anchitherium may yet have adapted to the changing environmental conditions of the early
late Miocene after all. Eronen et al. compare the tooth morphology of Spanish species of
Anchitherium to German species and concludes that the Spanish specimens show signs of
incipient hypsodonty and the German specimens do not. This incipient hypsodonty may be
indicative of a change in feeding strategy from browsing to mixed feeding. Kaiser however
applying the micro and meso-wear proxy on a species of Anchitherium found in Germany,
also find his results indicative of a change in feeding strategy from browsing to mixed
feeding.
The main questions of this thesis were established as follows;
-
Did Anchitherium adapt to eating grass (mixed feeding) or did Anchitherium fail to
adapt to the new environmental conditions?
-
And, shortly after the Hipparion-date, did Anchitherium go extinct because it didn’t
adapt or didn’t adapt quick enough to a changing environment or was it due to
competition of the Hipparion horse in its feeding (Kaiser 2009) and or living niche?
-
Did the environment change so drastically during the early late to late Miocene that
Anchitherium was likely to be forced into evolutionary adaptation or face extinction?
It was attempted to answer these questions by presenting an literature overview of the
researches on these different topics and interlinking them. Unfortunately the practical part
of this thesis did not consist of repeating some of the original researches into micro and
mesowear of the Anchitherium molars an putting these results into the perspective of these
studies as was originally planned.
There is no direct answer to the first question. It is however more likely that it was not only
the adaptation to eating grass that was important to Anchitherium’s survival. The entire
climate changed continuously and the spread of the C4 grasslands cannot even be placed at
the exact time of Anchitherium’s extinction. Most researchers place it much later during the
Miocene-Pliocene transition. It is very likely that when the climate changed and the
59
environment became more arid that Anchitherium had to change food sources. The
evidence also supports this. It is also very likely that Hipparion introduced competition in
Anchitherium’s feeding niche. However this may not be only because Anchitherium partly
entered Hipparion’s grazing niche, or Hipparion partly entered Anchitherium’s. There is
evidence that Hipparion upon entering Europe changed his feeding strategy from grazing to
mixed feeding and even browsing. The most likely option for competition is thus that both
genera moved towards the same feeding habit of mixed feeding. This adaptation in both
genera probably took place before Hipparion migrated into Europe. Changing feeding
strategy to a niche that is already occupied by a similar animal does not make sense. A likely
explanation for Anchitherium’s demise may be that it was slowly adapting to the changing
environment by changing its feeding strategy and just could not handle the pressure of an in
migrating similar animal. It is also uncommon for more than one genus of horse to live in the
same region the reason for this is probably competition for food resources. This also answers
the final question. It does not appear as if the climate changed so drastically that
Anchitherium was driven towards extinction. The climate changed constantly and lots of
regional differences occurred. But the drastic overturn from woodland to mainly (C4)
grassland and savannah that is always pictured as the downfall of the little browsing horse is
not supported by most of the literature. Some species of Anchitherium may have adapted
more than others showing more signs of hypsodonty or other morphological adaptations.
That is one of the main conclusions of this thesis. Researching changes on a genus level
seems rather pointless when the differences in species are so extensive. This is an ever
returning problem in paleontology. Especially with the larger vertebrates, more species are
included in researches to reach sufficient sample sizes for statistical certainty or isotope
processing.
60
Short point summary of this thesis
-
There is a large diversity of (sometimes) contemporary species within the genus
Anchitherium therefore looking at adaptations on a genus level seems not very
useful.
-
The validity of the 6 new species within the genus Anchitherium created by Sánchez
et al. (1998) is questionable. His claims are based on minimal difference in dental
size and also in tooth morphology between the new species (that are almost all from
the Madrid basin). For the best morphological distingishable possible new species A.
parequinum no measurements are provided by the authors for comparison.
-
The large spatial and temporal variations (local endemism) in the Spanish Miocene
climate and environment make it hard to link them to Anchitherium’s demise alone.
-
The hypsodonty index as proposed by Fortelius et al. (2002) may be a valuable new
proxy for climatic and environmental reconstruction. However the many problems
with this proxy that Fortelius brushes away a little too easy do need a lot more
research. Is increased cusp slope really an early stage in the development of
hypsodonty? And why does the inclusion of hypsodont horse data make the proxy
less compatible with climatic reconstructions from the marine records?
-
The extreme radiation of the C4 grasses most likely took place during the MiocenePliocene boundary (MN 13) and not during the early-late Miocene (MN 9).
-
The development of hypsodonty is probably not an adaptation to eating grass alone.
It is probably an evolutionary trait acquired in many different ways in many different
lineages that also appeared to provide an advantage for eating the phytolith rich C3
and C4 grasses.
-
The reason for Anchitherium’s demise is probably not its failure to adapt to a grazing
feeding strategy alone. I was probably both climatic and environmental change
combined with an inmigrating very similar animal (Hipparion) occupying more or less
the same feeding niche (mixed feeding) that was also better suited for eating grass
and drier foliage because it had hypsodont teeth that Anchitherium did not have.
Most researchers agree that the climate became drier during the course of the
Miocene.
61
References
ABUSCH-SIEWERT, S. 1983. Gebiβmorphologische Untersuchungen an eurasiatischen
Anchitherien (Equidae, mammalia) unter besonderer Berüksichtigung der Fundstelle
Sandelzhausen. In Courier Forschungsinstitut Senckenberg, 62, 1-361 (not seen)*
ALBERDI, M. T. GINSBURG, L. RODRÍGUEZ, J. 2004. Anchitherium aurelianense (mammalian,
Equidae) (Cuvier, 1825) dans l’Orléanien (Miocéne) de France. In GEODIVERSITAS
26(1), 115- 155
BERNOR, R. L., KOVAR-EDER, J., LIPSCOMB, D. 1988. Systematic, Stratigraphic, and
Paleoenvironmental Contexts of First-Appearing Hipparion in the Vienna Basin,
Austria. In Journal of Vertebrate Paleontology. Vol 8 (4), 427-452
BRUIJN, DE H. DAAMS, R. DAXNER-HÖCK, G. FAHLBUSCH, V. GINSBURG, L. MEIN, P.
MORALES, J. 1992. Report of the RCMNS working Group on fossil mammals,
Reisenburg 1990. In Newsletters on Stratigraphy 26(2/3), 65-118
COSTEUR, L., LEGENDRE, S. 2008. Spatial and temporal variation in European Neogene large
mammals diversity. In Palaeogeography, Palaeoclimathology, Palaeoecology 261,
127-144
CRUSAFONT PAIRO, M. TRUYOLS SANTONJA, J. 1957. Descubrimiento del primer yacimiento
de mamiferos Miocenicos de la Cuenca Valenciana. Notas y Comunicaciones del
Instituto Geologico y Minero de Espana 48, 3-22 (not seen)
DAAMS, R., VAN DER MEULEN, A. J., ALVAREZ SIERRA, M. A., PELÁEZ-CAMPOMANES, P.,
KRIJGSMAN, W. 1999. Araonian stratigraphy reconsidered, and a re-evaluation of
the middle Miocene mammal biochronology in Europe. In: Earth and Planetary
Science Letters, 165, 287-294.
DAXNER-HÖCK, G. BERNOR, R. L. 2009. The early Vallesian vertebrates of Atzelsdorf (Late
Miocene, Austria) 8. Anchitherium, Suidae and Castoridae (Mammalia). Annalen der
Naturhistorischen Museum, Wien 111 A, 557-584
DEMIGUEL, D. AZANZA, B. MORALES, J. (2011) Paleoenvironments and paleoclimate of the
Middle Miocene of central Spain: A reconstruction from dental wear of ruminants. In
Palaeogeography, Palaeoclimatology, Palaeoecology 302 (34), pp452-463
DOMINGO L., GRIMES S. T., DOMINGO S. M., ALBERDI M. T. 2009 A. Paleoenvironmental
conditions in the Spanish Miocene-Pliocene boundary: isotopic analyses of Hipparion
dental enamel. In Naturwissenschaften 96, 503-511
62
DOMINGO, D. CUAVAS-GONZÁLEZ, J. GRIMES, S. T. HERNÁNDEZ FERNÁNDEZ, M. LÓPEZMARTÍNEZ, N. 2009 B. Multiproxy reconstruction of the palaeoclimate and
palaeoenvironment of the Middle Miocene Somosaguas site (Madrid, Spain) using
herbivore dental enamel. In Palaeogeography, Palaeoclimatology, Palaeoecology
272, 53-68
EHLERINGER J. R., MONSON, R. K. 1993. Evolutionary and ecological aspects of
photosynthetic pathway variation. In Annual Review of Ecological systems 24, 411439 (not seen)
EHLERINGER J. R., PEARCY, R. W., 1983. Variation in quantum yield for CO2 uptake among C3
and C4 plants. In Plant physiology 73, 555-559 (not seen)
ERONEN, J. T. EVANS, A. R. FORTELIUS, M. JERNVALL, J. 2009. The Impact of Regional Climate
on the Evolution of Mammals: A Case Study using Fossil Horses. In The Society for
the study of Evolution 64, 2398-408
ERONEN JT, PUOLAMAKI K, LIU L, LINTULAAKSO K, DAMUTH J. 2010. Precipitation and large
herbivorous mammals I: estimates from present-day communities. In Evolutionary.
Ecological. Res. 12, 217–33
EVANDER, R. L. 2004. (Chapter 16): A Revised Dental Nomenclature for Fossil Horses. In
Bulletin of the American Museum of Natural History, Number 285, 209-218
FORSTEN, A. 1991. Size trends in Holarctic Anchitherines (Mammalia, Equidae). In Journal of
Paleontology 65(1), 147-159
FORTELIUS, M. SOLOUNAIS, N. 2000. Functional characterization of ungulate molars using
the Abrasion-Attrition wear gradient: a new method for reconstructing paleodiets. In
American museum novitiates 3301, 1-36. (not seen)
FORTELIUS, M. (coordinator) (database July 2003). Neogene of the Old World Database of
Fossil Mammals (NOW). University of Helsinki. http://www.helsinki.fi/science/now/.
(April 2011)
FREUDENTHAL, M. 1966. On the mammalian fauna of the Hipparion-Beds in the CalatayudTeruel basin (Prov. Zaragoza, Spain) Part I. Proceedings of the Koninklijke
Nederlandse Akademie van Wetenschappen. Series B: Palaeontology, Geology,
Physics, Chemistry, Anthropology 67(5), 296-317 (not seen)
GOULD, S. J. VRBA, E. S. 1981. Exaptation – a missing term in the science of form. In
Paleobiology 8, 4-15
GRAY, J. E. 1821 – On the natural arrangement of vertebrose animals. London Med Reposit.
Rev. 15, 296-310 (not seen)*
63
HAYEK, L. A.C., BERNOR, R.L, SOLOUNIAS, N., STEIGERWALD P. 1991. Preliminary studies of
Hipparione horse diet as measured by tooth microwear. In: Bjorn Kurten. A
Memorial Volume. Annales Zoologici Fennici. 28(3-4), 187-200 (not seen)
HERNÁNDEZ FERNÁNDEZ, M. SALESA, M. J. SÁNCHEZ, I. M. MORALES, J. 2003. Paleoecology
of the genus Anchitherium von Meyer, 1834 (Equidae, Perrisodactyla, Mammalia) in
Spain: evidence from macromammal faunas (original title; Paleoecología del género
Anchitherium vonr Meyer, 1834 (Equidae, Perrisodactyla, Mammalia) en España:
evidencias a partir de las faunas de macromamíferos). In Coloquis de Paleontologica,
Vol. Ext. 1, 253-280
HORDIJK, K. 2010. Perseverance of Pikas in the Miocene. In: Geologica Ultraiectina,
Mededelingen
van
de
Faculteit
Geowetenschappen
departement
Aardwetenschappen Universiteit Utrecht No. 333 (Phd thesis)
INIGO, C. 1993. Estudio de los Perisodáctilos del yacinmiento Mioceno de Córcoles
(Guadalajara). Thesis Doctoral Facultad de Ciencias Biológicas de Universidad
Complutense Madrid; 559 p. Unpublished (source: Inigo 1997)
INIGO, C. 1997. Anchitherium Corcolense Nov. Sp., a new Anchitherine (Equidae,
mammalian) from the early Aragonian site of Córcoles (Guadalajare, Spain). In
GEOBIOS, 30, 6: 849-869
JANIS, C. 1995. An Evolutionary History of Browsing and Grazing Ungulates. (chapter) In The
Ecology of Browsing and Grazing Ecological Studies 195 (Gordon, I. J. Prins, H.H.T.)
21-45 © Springer 2008 (and published) In Developments in Palaeontology and
Stratigraphy Volume 14, 1995, Pages 147-189
JIMÉNEZ-MORENO, G., FAUQUETTE, S., SUE, J. P., AZIZ, H. A. 2007. Early Miocene repetitive
vegetation and climatic changes in the lacustrine deposists of the Rubielos de Mora
Basin (Teruel, NE Spain). In Palaeogeography, Palaeoclimatology, Palaeoeocology.
250, 101-13 (not seen)
KAISER, T. M., SOLOUNIAS, N., FORTELIUS, M., BERNOR, R. L., SCHRENK, F. 2000. Extending
the tooth mesowear method to extinct and extant equids. In: Geodiversitas 25(2),
321-345
KAISER, T. M., SOLOUNIAS, N. 2003. Extending the tooth mesowear method to extinct and
extant equids. In Geodiversitas 25(2), 321-345
KAISER, T. M. 2009. Anchitherium aurelianense (Equidae, Mammalia): a brachydont “dirty
browser” in the community of herbivorous large mammals from Sandelzhausen
(Miocene, Germany). In Paläontologische Zeitschrift 83, 131-140
64
LEIDY, J. 1869. The extinct mammalian fauna of Dakota and Nebraska: Including an account
of some allied forms from other localities, together with a synopsis of the
mammalian remains of North America. Published for the Academy by J.B. Lippincott,
Philadelphia*
LINNAEUS, C. 1758. Systema naturae per regna tria naturae: secundum classes ordines,
genera, species, cum charateribus, differentiis, synonymis, locis. In Holmiae
(Laurentii Salvii). P. 73*
MACFADDEN, B. J. CERLING, T. E. 1994. Fossil horses, carbon isotopes and global change. In
Elsevier Science, TREE vol. 9, no 12pp 481-485
MACFADDEN, B. J., CERLING, T. E. 1996. Mammalian herbivore communities, ancient feeding
evology, and carbon isotopes: a 10 Myr sequence from the Neogene of Florida. In:
Journal of Vertabrate Palaeontology 16(1), 103-115. (not seen)
MADE, VAN DER J. BELINCHÓN, M. MONTOYA, P. 1996. Suoidea (mammalia) from the Lower
Miocence Locality of Buñol, Valencia, Spain. GEOBIOS, 31, 1:99-112
MEYER VON, H. 1844. Die fossilen Knochen aus dem Tertiär-Gebilde des Cerro de Sand Isidro
bei Madrid. In Neues Jahrbuch für Mineralogie, Geognosie, Geologie und
Petrefaktenkunde 289-310 (not seen)*
MOLNAR, P., 2005. Mio-Pliocene Growth of the Tibetan Plateu and Evolution of the East
Asian climate. In Palaeontologia Electronica 8 (1), 1-23.
MORGAN, M. E., KINGSTON J. D., MARINO B. D. 1994. Carbon isotopic evidence for the
emergence of C4 plants in the Neogene from Pakistan and Kenya. In Nature 367,
162-165
MOSBRUGGER, V., UTESCHER, T., DILCHER, D. L. 2005. Cenozoic continental climatic
evolution of Central Europe. In Proceedings of the North American Science Society
Vol 102 No. 42
OSBORN, H. F. 1918. Equidae of the Oligocene, Miocene, and Pliocene of North American,
inconographic type revision. In Memoirs of the American Museum of Natural History,
ser. 2, 1-217 (not seen).
PAGANI, M., ARTUR M. A., FREEMAN, K. H. 1999. Late Miocene atmospheric CO2
concentrations and the expansion of the C4 grass. In Science 285, 876-878
QUADE J. CERLING T. E., BARRY, J. C., MORGAN, M. E., PILBEAM D.R., CHIVAS A. R., LEETHORP J. A., VAN DER MERWE N. J. 1992. A 16-Ma record of paleodiet using carbon
and oxygen isotopes in fossil teeth from Pakistan. In Chemical Geology 94, 183-192
(not seen)
65
QUADE, J., SOLOUNIAS, N. 1994. Stable isotopic evidence from paleosol carbonates and
fossil teethe in Greece for forest or woodlands over the past 11 Ma In:
Palaeooceanography, palaeoclimathology, Paleaeoecology. 108, 41-53 (not seen)
RETALLACK, G. J. 1983. Late Eocene and Oligocene paleosols from Badlands national Park,
South Dakota. In Geological Society of America Special Papers 193, 1-82
RETALLACK, G. J. 2001. Cenozoic expansion of grassland and climate cooling. In Journal of
Geology 109, 407-426
RÖGL, F. 1999 Mediterranean and Paratethys Palaeogeography during the Oligocene and
Miocene. In: AGUSTI, J., ROOK, L., ANDREWS, P. Hominoid evolution and climatic
change in Europe. The evolution of neogene terrestrial ecosystem in Europe, vol. 1
Cambridge Universiy Press, pp. 8-22 (not seen)
RÖGL, F., DAXNER-HÖCK, G. 1996. Late Miocene Parathetys Correlations. In The Evolution of
Western Eurasian Neogene Mammal Faunas, Wiley, New York pp. 47-55
M. J. SALESA, I.M. SANCHÉZ, J. MORALES. 2004. Presence of the Asian horse Sinohippus in
the Miocene of Europe. Acta Palaeontologica Polonica 49(2), 189-196*
SÁNCHEZ, I. M. SALESA, M. J. MORALES, J. 1998. Revision sistematica del genero
Anchitherium Meyer 1834 (Equidae; perissodactyla) en España. In Estudios geol, 54,
39-63
STIRTON, R. A. 1941. Development of characters in horse teeth and the dental
nomenclature. In Journal of Mammalogy 22, 434-446 (not seen)
STRÖMBERG, C. A. E. 2005. Evolution of hypsodonty in equids: testing a hypothesis of
adaptation. In Paleobiology, 32(2), pp. 236-258
TÜTKEN, T., VENNEMANN, T., 2009. Stable isotope ecology of Miocene large mammals from
Sandelzhausen. Southern Germany. In Fossil lagerstätte Sandelzhausen, fauna.
Paläontologische Zeitschrift 83(1) (not seen)
VAN DAM, J. A. 2006. Geographic and temporal patterns in the late Neogene (12-3 Ma)
aridification of Europe: the use of small mammals as paleoprecipitation proxies. In
Palaeogeograpy Palaeoclimatology Palaeoecology 238, 190-218
VILLALTA, J. F. CRUSAFONT-PIARO, M. 1945. Un Anchitherium en el Pontiense espanol.
Anchitherium sampelayoi, nova sp. In Notas y Communicationes del Instituto
Geológico y Minero de Espana, 14, 51-82 (not seen)*
66
VISLOBOKOVA, I., A. 2006. Associations of Ruminants in Miocene Ecosystems of Eastern
Alpine Region. In Paleontological journal vol. 40, No 4, pp. 438-447
WILLIAMS, L.H., OWEN-SMITH, N. 2000. The vegetation of the South African Lombard
Reserve and its utilization by certain antelope. In Zoologica Africana 1, 55-71 (not
seen)
QUINN, J. H. 1955. Miocene Equidae from the Texas Gulf Coastal Plain. In University of Texas
Publication Bureau of Economic Geology 5516, 1-102 (not seen)
ZACHOS, J., PAGANI, M., SLOAN, L., THOMAS, E., BILLUPS, K. 2001. Cenozoic Global Deep-Sea
Stable Isotope Data. In Science 292, 686-693
*Taxonomic reference
67
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