Veget Hist Archaeobot
DOI 10.1007/s00334-013-0394-2
ORIGINAL ARTICLE
Climate, human palaeoecology and the use of fuel in Wadi Sana,
Southern Yemen
Masoumeh Kimiaie • Joy McCorriston
Received: 30 July 2012 / Accepted: 5 February 2013
Ó Springer-Verlag Berlin Heidelberg 2013
Abstract This study integrates analysis of wood charcoal
assemblages with climate proxies, palaeoenvironmental
and archaeological data sets in hyper-arid Wadi Sana,
Yemen, to address the availability and use of wood fuels
by South Arabian hunter-herder groups from the Early
Holocene (8000–7700 cal. B.P.) to Middle Holocene
(6000–4800 cal. B.P.) periods. The Early Holocene environment, regulated by a stronger Southwest Asian monsoon, was moister than the present, providing a marshy
winter grazing area for cattle herders, whose construction
of hearths and food preparation strategies changed over
time. This study provides an insight into long term stability
of land cover and use as well as the dynamics of human
contributions to landscape change. We suggest that complex environmental and cultural processes affect species
availability, fuel choice and land use management. Despite
environmental and economic changes in Wadi Sana, our
dataset does not show changes in fuel choice from the
Early to Middle Holocene.
Keywords Holocene Palaeoecology Wadi Sana
Charcoal analysis Fuel choice Human impact
Communicated by G. Willcox.
M. Kimiaie (&) J. McCorriston
Department of Anthropology, The Ohio State University,
4034 Smith Laboratory, 174 W. 18th Ave., Columbus,
OH 43210, USA
e-mail: kimiaie.1@osu.edu
Introduction
During the Holocene period, the local environments of
South Arabia were regulated by a stronger Southwest Asian
monsoon than today and were generally moister than the
present (Davies 2006; Fleitmann et al. 2007; Parker and
Goudie 2008). While the climate history and regional
moisture balances of the Holocene are broadly understood
across Arabia (Lézine et al. 2010), local ecosystem histories and especially human-environment interactions are
poorly documented, and the dynamic of human contributions to landscape change is poorly understood. This study
explores a record of archaeological wood charcoals once
used as fuel to assess whether economic and landscape
management changes in the Early-Middle Holocene correspond to changes in fuel choices and ultimately in woody
vegetation cover.
Fuel use is a major source of charred macro-botanical
remains. Where populations lived in permanent settlements, such remains may accumulate in site middens as the
result of numerous hearth and cooking episodes (Miller
1984; McCorriston 1998), but in the Wadi Sana, no settlement occurred prior to about the 3rd century A.D.
(McCorriston et al. 2005; McCorriston 2006). Archaeological charcoal came from numerous, widely distributed
camp hearths, and each archaeological charcoal assemblage is the product of the last use episode of a hearth.
These hearths may be safely associated with mobile peoples and show a distinct shift in construction techniques
over time, possibly corresponding to changing cooking
practices. Furthermore, these assemblages may be dated,
either with radiometric dates on charcoal (14C) or in
stratigraphic context with other absolutely and relatively
dated features. The composition of fuels in hearths provides a sequence of cooking events that contribute overall
123
Veget Hist Archaeobot
to our understanding of human use of natural resources
throughout the Early Holocene wet period and across
important changes in human economy. Although our
sample size is small and might not be suitable for palaeovegetation reconstruction (Chabal 1997), it can be a good
indicator of human management of landscapes and economical patterns.
Palaeoclimate and human adaptations in Wadi Sana
Researchers in Africa have argued that Early Holocene cattle-centred mobility may have retarded people’s commitment
to agriculture and sedentism (e.g. Marshall and Hildebrand
2002; McIntosh 1994; Wengrow 2006; Haaland 1992), a
cultural framework also plausible for Southern Arabia, where
cattle herding preceded agriculture by at least 3,000 years
(McCorriston 2006; McCorriston et al. 2012). Field research
and analysis over a decade in the highland arid zone of
Southern Arabia (Hadramawt, Southern Yemen) by the
RASA Project (Roots of Agriculture in Southern Arabia) has
yielded integrated palaeoecological and archaeological data
that allows us assess early landscape management and
environmental impacts by humans and their animals.
The Wadi Sana which drains northward through the
Southern Arabian highlands, today flows only episodically
with discharge from summer rainfall (Fig. 1). The modern
channel is deeply incised through well-dated silt terraces
laid down during an Early Holocene phase of aggradation
when summer flooding created wetlands suitable for winter
pasture (Harrower et al. 2012). Well-documented, largeregion environmental proxies like pollen, stable isotopes
and dune formation (e.g. Lézine et al. 2010; Parker and
Goudie 2008), indicate that major climate change—the
weakening of the southwest monsoon—would have aridified the Middle-Late Holocene Wadi Sana environment.
Wadi Sana palaeoenvironmental responses to this climate
change have been inferred from geomorphologic sequences
(Harrower et al. 2012; McCorriston et al. 2012) and hyrax
middens (McCorriston et al. 2002) that suggest that the
uplands have had no soil (and therefore almost no cover)
for all of the Holocene. Sparse parkland with xerophytic
trees such as acacias and myrrh clung to the slopes, and
most vegetation, including grasses, rushes, and shrubs was
concentrated along channels and the seeps from springs.
GIS-calculations suggest that pasture could support up to
60 herders (about 7–8 households) dispersed along the
Wadi Sana marshlands during the period 8000–4800 B.P.
Regional surveying and excavations have provided an
Early-Middle Holocene cultural history (Crassard et al.
2006; McCorriston et al. 2002, 2005). The earliest Holocene
dates are from the seasonal, re-visited campsite of Manayzah, adjacent to a natural spring and pool. Broad exposures
123
Fig. 1 Map of the modern Arabian Peninsula. The oval on the far
right shows the location of Wadi Sana
revealed multiple contemporaneous hearths, pits, post-holes
and stone tools (Crassard 2008), and suggested a mixed
hunting-herding economy of ungulates, sheep, goats and the
earliest domesticated cattle recorded in Arabia (McCorriston
and Martin 2009; Martin et al. 2009). Several hearths
included in this study come from the sequence at Manayzah
dating back to 8000–7700 cal. B.P.
The seasonally visited site of Shi’bKheshiya, some
1,500 years later, is significant in Arabian prehistory for
the preservation of an adjacent ring of cattle skulls representing the ritual aftermath of a sacrifice, gathering and
feast, which united pastoral groups in supra-household
alliances across broad territories (McCorriston et al. 2012).
Although this site lacks much economic data, it is significant in its cultural and social constitution (McCorriston
et al. 2011), and is consistent with a wider pattern of cattlehuman symbolism across the Old World tropics (Wengrow
2006; Di Lernia 2006; Boivin 2004). Several of the surrounding hearths were sampled for wood charcoal.
Regional surveying has detected a wide array of stratified
hearths with preserved charcoal. People remained mobile in
small groups, even as they adopted new vegetation management. New practices included anthropogenic firing of local
vegetation (McCorriston et al. 2005) and subsequent smallscale water management channels and check-dams (Harrower
2008). Over time, there was a shift in the manner in which
people constructed hearths. In the Early Holocene hearths
were built into a steep pit lined with small slabs of limestone
(Fig. 2). Cooking relied on the even heat released from
cooking stones, smooth limestone cobbles brought from the
active Wadi channel. In modern Bedouin practice, a hot fire is
built atop the hearth then cinders and charcoal are stirred into
the cobbles to ensure a long-lasting heat. The top of such a
hearth can be blown free of ash and cinders to provide a
searing surface for grilling meat, while the oxygen-poor
interior may be used for cooking tubers or dough without fear
Veget Hist Archaeobot
Fig. 2 Illustrating three different Holocene hearth types in Wadi
Sana: Hearth type I (lower), hearth type II (middle), and hearth type
III (upper). The analyzed samples in this paper only come from hearth
types I and II (drawn by Jennifer Everhart)
of combustion. Such a hearth also produces hot stones used to
boil milk or liquids in perishable leather-lined baskets.
By the Middle Holocene, hearth construction practices
had changed; archaeologists find numerous hearths directly
or stratigraphically dated to 6800–4700 B.P. built as a shallow
scoop filled with cooking cobbles (Fig. 2). Some hearths
contain charred animal bone fragments, a few of which have
been definitively assigned to cattle (McCorriston et al. 2002).
Finally, people began constructing hearths on surfaces by
erecting a ring of small boulders to retain hot cooking stones
and charcoal. This style continues to be built and used today,
and surface examples contain charcoal that may be very
recent (Fig. 2). Although ethno-archaeological observations
show that modern Bedouin bury dough to cook (gritty) bread
in ashes, and also make charcoal in buried pits containing no
stone, there is no archaeological evidence for use of multiple
types at any one time in the past. Hearth types were
sequential, and apparently replaced earlier types throughout
the Holocene (Table 1).
Data and methods
The data generated for this paper consists of 20 charred
wood samples from hearth types I and II in Wadi Sana
excavated from 1998 to 2005. Archaeologists recovered
charcoal pieces greater than 5 mm length to reach a minimum sample size of 20-plus intact specimens. (It was
impractical to recover every [5 mm-sized piece). Where
charcoal crumbled, as is normal in hyper-arid conditions, a
few fragments were selected and an aluminium foil wrap
ensured that these could travel together to minimize multiple identifications on one plant (pre-excavation fragmentation could not be addressed in this study). These
samples were sorted by 109 magnification stereomicroscope. Within each sample (one per hearth) twenty pieces
of charred wood greater than 2 mm in size were chosen for
identification, where available. Flotation samples, which
were collected to look for seeds, also yielded some identifiable charcoal fragments. In total, 331 wood fragments
were identified. In small assemblages (less than 20 fragments within the sample) every attempt was made to
identify as many wood fragments as possible, regardless of
fragment size. While it would be desirable to examine
much larger assemblages, preservation, small deposits
(hearths) and field collection constraints (water for limitedsize flotation samples, fragility of charcoal that pulverizes in
sieving in arid environments) meant that samples were
small. The procedure for identifying charred wood involved
matching microscopic cellular patterns with modern reference material, charred and mounted on glass slides in three
fracture planes: tangential, radial and transverse. These
different sections were identified under a Leica compound
forensic microscope with 50–1,0009 magnification and a
dual stage with bridge prisms for simultaneous viewing of
archaeological and reference specimen. All wood taxa are
identified to the genus level. The key characteristics and
terminology used for identification of these taxa are drawn
from wood anatomy reference manuals and keys (Asouti and
Fuller 2008; Fahn et al. 1986; Jagiella and Kürschner 1987).
The modern reference collection is housed in McCorriston’s
Archaeobotany Laboratory at The Ohio State University.
To explore quantitative differences across sets of samples, we generated a Shannon Index of Diversity for each
sample. Next we performed a two-tailed Monte Carlo test
to assess the statistical significance of differences in taxa
representation in the two groups of hearths. A Monte Carlo
randomization resampling test can be used in conjunction
with any measure of population based on observed species
abundances and runs for up to 1,000 iterations, which
makes this test a robust procedure with a high degree of
confidence regardless of the size of the population (Zhu
2005). When the assumption of a normal distribution is not
satisfied or the sample size is too small, a Student T test is
not valid. In this case, a two-tailed test should be used to
test the hypothesis that both diversity means were generated from sampling the same population. A two-tailed test
allocates the 5 % chance of an error under the null
123
123
Table 1 Details of all samples presented in this paper including hearth type, context code, date, absolute counts of identified taxa, Shannon Diversity Index, and percentage of determined
fragments
Hearth type
Context
2
SU110-6-3
4800
22
2
SU37-3-C-012 BAG 5
6500
20
2
SU37-3-0-D-002 BAG 1&2
6500
2
SU 37-3-C-14 BAG 6
6500
2
SU 037-3-C-12
6500
20
2
WS 1 Hearth 001 FS1112
6610
6
2
SU154-1-2
6610
20
2
WS Hearth 8 FS1103
6610
19
18
2
WS Hearth 9 FS1104
6610
14
12
2
WS 1 Hearth 002 FS1111
6692*
20
2
WS Hearth VI FS1102
6700
19
19
2
2
SU80-4 Hearth 2-2
SU151-1-H3-1
6800
6861*
13
10
2
2
WS Hearth 14 FS1107
6933*
8
2
WS Hearth 16 FS1101
6968*
5
1
SU155-2 K9 Hearth1 FS1413
7742*
20
1
SU155-2-M11 QuadB-007 FS1399
7755
17
3
1
SU155-2-L11 QuadB-005 FS1404
7755
27
5
1
SU155-2 K9 Niv14 FS1416
7829
20
1
SU155-2-K9-18
8044
11
1
331
59
Total (n)
(%)
Date (ca.l B.P.)
Number of ident. fragm.
Acacia
Anogeissus
Cadaba
1
Ficus
13
Tamarix
Ziziphus
8
Shannon div. index
0.82
19
1
0.20
20
8
12
0.67
20
20
5
1.04
0
0.47
5
1.03
20
5
1
0
10
0.45
5
2
20
13
3
8
2
3
0.67
20
4
10
0.96
1
21
0.63
20
18.0
10
30
9.2
33
10.1
145
44.3
0.30
16
4.9
44
13.5
Veget Hist Archaeobot
All dates calibrated using online Calpal (indicated by *). Other dates have been interpolated from stratigraphy and stratified dates on other features that could be stratigraphically related to the
hearth
Veget Hist Archaeobot
Table 2 List of modern Wadi Sana vegetation (left) and analyzed
archaeobotanical taxa (right)
Modern woody taxa
Archaeobot. taxa
Acacia ramulosa W. Fitzg (Pedley)
Acacia sp.
Acacia odorata Desv.
Acacia sp.
Acacia mellifera (M. Vahl.) Benth.
Anogeissus bentii Baker.
Anogeissus sp.
Boswellia sacra Flueck.
Commiphora kataf Engl.
Cadaba heterotricha Stocks.
Cadaba sp.
Calotropis procera (Aiton) W.T. Aiton
Commiphora gileadensis (L.) C. Chr
Cyphostemma crinitum (Planch.) Desc.
Delonix elata Gamble.
Ficus salicifolia Vahl.
Ficus sp.
Indigofera s.l.
Lycium shawii Roem. & Schult.
Maerua crassifolia Forssk.
Moringa peregrina Fiori.
Tamarix L.
Tamarix sp.
Ziziphus leucodermis (Baker) O. Schwartz
Ziziphus sp.
hypothesis equally to both tails so each tail has the probability of 0.025, and the null hypothesis is rejected if the
test statistic is too extreme in either direction. In other
words, the two groups of hearths would be significantly
different if the p value was below the 2.5th percentile or
above the 97.5th percentile of the distribution.
Fig. 3 Distribution of taxa (percentages of species by count) in
hearth type I, 8000–7700 B.P. (top) and hearth type II, 6900–4700 B.P.
(bottom)
Results
A Monte Carlo test with 1,000 iteration runs testing the
null hypothesis that the means of Shannon Diversity Index
values of the two groups of hearths are drawn from the
same population resulted in a p value of 0.76. This suggests
no significant change in the composition of wood fuels
preserved as charcoals in hearths of type I and type II.
The composition of fuel in these hearths is dominated by a
few woody species still present in the region today (Tables 1,
2). Modern taxa distribution, including a single Ficus salicifolia tree in Wadi Sana, is known from the collections and
identifications by McCorriston and Ms. Catherine Heyne in
conjunction with widespread archaeological fieldwork. Inferences about regional palaeovegetation come from the Middle
Wadi Sana work on hyrax middens (Cole in McCorriston et al.
2002) and the palaeoenvironmental reconstructions from sediment sequences and modern analog plant communities (McCorriston et al. 2012; McCorriston and Martin 2009). Figure 3
shows the percentage of charred wood recorded by counts from
different hearths in Wadi Sana. The identified charred woods
include Acacia sp., Anogeissus sp., Cadaba sp., Ficus sp.,
Tamarix sp. and Ziziphus sp. All of these are the result of fuel
use during the dry season of Wadi Sana when there was human
aggregation in the marshy oxbows as the grassy flushes rimming the upland vernal pools were depleted (McCorriston et al.
2012). All of the species found in archaeological hearth
structures are present in modern day Wadi Sana (Table 2).
Acacia sp.
This wood has homogeneous uni- to multi-seriate rays,
procumbent cells, simple perforation plates, and storied
paratracheal parenchyma. Its foliage is used today as good
source of fodder, especially for confined goats and is well
known among herders as a livestock fatness enhancer and
milk enricher (Ghazanfar 1994; Miller and Morris 1988).
Acacia is an excellent fuel providing good charcoal (Miller
and Morris 1988), and preferentially collected in the recent
past for charcoal production destined for urban consumption.
123
Veget Hist Archaeobot
Anogeissus sp.
Diffuse-porous wood and heterogeneous rays with upright
and tile cells, radially arranged pores, and paratracheal
parenchyma characterize this wood (Asouti and Fuller
2008; Fahn et al. 1986). While the foliage is never browsed
by cattle, the wood provides an excellent fuel and yields
good charcoal (Arbonnier 2004). Modern residents of Wadi
Sana pollard the trees to provide fodder for camels and
goats, which also browse the trees in modern Dhufar.
Cadaba sp.
This wood has diffuse-porous vessels, heterogeneous rays
with procumbent and upright cells and paratracheal parenchyma (Fahn et al. 1986). Ethnographic and ethnobotanical
research show that Cadaba foliage is fed to herds when there
is no graze, and its firewood produces an unpleasant flavor.
The ash from Cadaba mixed with butter is used as a remedy
on livestock skin where hair has fallen out. It is also
important as treatment of parasitic skin infestation in goats
and camels in modern day Oman (Ghazanfar 1994; Miller
and Morris 1988). Since the shrub is a common woody plant
of the arid rain shadow of the Southern Arabian highlands
and Wadi Sana today in particular, its presence in ancient
hearths may reflect its common occurrence.
Ficus sp.
This taxon has diffuse-porous vessels with wide parenchyma
bands, and bi- or multi-seriate heterogeneous rays (Fahn et al.
1986). Ficus produces much smoke, so local people of the
Southern Arabian highlands find it a desirable quality wood
for fires lit for livestock—especially those inside cattle byres,
where such fires have a deterrent effect on pests and insects
(Ghazanfar 1994; Janzen 1986; Miller and Morris 1988). The
high percentage of Ficus in the samples suggests that early
inhabitants of Wadi Sana predominantly used a fuel wood that
was not a provider of browse. Ficus trees are present in modern
day Wadi Sana but with a different distribution than suggested
by the representation of Ficus wood in Early-Middle Holocene hearths across a 40 km region. For example, F. salicifolia
Vahl is still present today but very sparse and limited to a small
number of plants in the entire Wadi channel. There is a strong
possibility that the identified charred Ficus recovered from
Holocene samples is F. salicifolia, but other potential Ficus
species would include F. vasta or F. sycomorus L. which are
today limited to Dhufar in the Southern Arabian highlands.
Tamarix sp.
The most important characteristic of this taxon is diffuseporous vessels with simple perforation plates, vasicentric
123
parenchyma storied with vessels, and heterogeneous multiseriate rays (Fahn et al. 1986). The ash from Tamarix is
effective in treating animals and it was used widely in the
Arabian Peninsula (Ghazanfar 1994; Miller and Morris
1988). It is an extremely hard wood, resistant to termites, and
a desirable firewood with long, slow-burning properties.
Ziziphus sp.
This taxon is characterized by a diffuse-porous wood, simple
perforation plates, scanty to vasicentric parenchyma, radially-arranged pores, and mostly uniseriate narrow heterogeneous rays (Fahn et al. 1986). Ziziphus foliage is browsed by
herds especially during the dry season; moreover it bears an
edible fruit (Miller and Morris 1988) and its hard wood is a
popular fuel. Charred Ziziphus seeds are also occasionally
recovered from hearths in Wadi Sana (perhaps discarded
after eating or possibly introduced with branch wood) and are
one of the few edible archaeobotanical taxa found commonly
throughout Arabia.
Discussion
Wood fuel remains, as indirect evidence of ancient land use
and vegetation, help us understand not only ancient environmental conditions, but also the behavioral patterns that
impose a selective filter on the preservation of charred
remains. This study provides an insight into long term
stability of land cover and use as well as human interactions with the surrounding landscape. We suggest that
understanding the archaeological context of archaeobotanical materials helps to reconstruct pastoral land use, and
secondly we suggest an approach to understand the weight
of environmental and cultural variables in fuel and land use
management.
Wood charcoal data reported here are best understood
within the context of Wadi Sana palaeoenvironmental data
constructed from sediment sequences, hyrax middens, and
modern vegetation analogs across the Southern Arabian
highlands. These data provide insight into the availability
of fuels preferred by humans. In Wadi Sana aridification
has changed the density of cover, but not the woody taxa
represented. In wood charcoal data, this is reflected in
Ficus sp., which has high ubiquity across assemblages,
suggesting that this taxon was once readily obtainable and
not limited to the single plant growing as seen today.
There is also good evidence for landscape manipulation by
humans. From about 8000 cal. B.P. archaeologists have dated
regional brush fires that were human-set (McCorriston et al.
2002, 2005). While it is unknown whether these were set for
game drives or to increase grazing and browsing resources,
this strategy represents a modest labour investment by humans
Veget Hist Archaeobot
in landscape change. In the archaeological sequence, burning
precedes the onset of ritual sacrifices, linked to greater territorial defence of limited resources by mobile pastoralists
(McCorriston et al. 2012). Finally, there appear water management channels and check-dams that represent an intensification of labour input to resource production and landscape
manipulation (Harrower 2008).
Yet the data available from a sample of hearths suggest
that Early-Middle Holocene landscape manipulation thus
practiced from 8000 to 4700 cal. B.P. did not impact the
availability of preferred fuel to a point where people were
forced to shift their acquisition of it. From the identified
woods we see no change, despite change in construction
technique and possible changing use of hearths. Although
the growing population was using new practices such as
burning and territorial defence marked by communal sacrifices, the human population did not over time exceed the
capacity of Wadi Sana to provide the preferred fuels. In an
arid landscape occupied only by mobile herders, the
amount of wood used as fuel depends on the following
factors: the quality of the species as a fuel source, the
population of people using wood, and the demand of herds
for browsing. The low percentage of some taxa recovered
from the hearth structures may be interpreted as economic
choice of those species which do not provide good charcoal
but instead offer a very good quality browse.
Based on our wood analysis and statistical results we
argue that economic changes, especially the growing
population pressure documented in Wadi Sana through
archaeological and geomorphological data, did not entail
changes in fuel choice from the Early to Middle Holocene.
Not only did economic changes such as the emergence of
territorial defence of resources (McCorriston and Martin
2009; McCorriston et al. 2012) not alter fuel choice and
land use by Wadi Sana inhabitants, but the data suggest
that changes in lithic technologies (Crassard 2008), pastoral camps (McCorriston et al. 2002), or even hearth types
did not entail changes in plant resource availability and
fuel use strategies employed by Early-Middle Holocene
Wadi Sana pastoralists.
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