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Australia: The Land Where Time Began |
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Aboriginal Stone Walled Intertidal Fishtraps –
Morphology, Function and Chronology Around the coastline of Australia there are
stone-walled intertidal fish traps that are among the largest structures
that were built by Australian Aboriginal people. Globally, fishtraps are
considered to be important elements of the production of food,
domestication, territoriality, and ceremonial landscapes, but there is
highly variable viewable level of detail in their documentation and
there is scarce scholarly knowledge of these structures. There is a lack
of detail and reproducibility of recording, which hinders the
comparative analysis of their morphology, function and chronology. Kreij
et al. used a
high-resolution, close-range aerial vehicle (UAV) [aka drone]
photogrammetry and a suite of spatial information analytical techniques
in this study to investigate the stone-walled fish traps of the Kaiadilt
Aboriginal people, Sweers Island, southern Gulf of Carpentaria,
Australia. Modelling of tidal inundation was undertaken to assess:
1)
Working range of fish traps,
2)
Individual and simultaneous function of fishtraps,
3)
Seasonal fluctuation, and
4)
Chronology that was based on the history of sea level. There are 13 fishtraps that were identified in
the study area, which ranged from 38 m long to 287 m long. It was shown
by inundation modelling that all fishtraps operate most efficiently at
sea level of the present mean sea level (PMSL), which indicates that
they were built in the last 3,500 years. An opportunity to improve
approaches to the recording of large-scale stone features and
standardise documentation of stone-walled intertidal fish trap sites is
provided by quantitative recording techniques, analytical procedures and
terminology that were developed in this study. In the Australian archaeological record
stone-walled intertidal fishtraps are among the largest structures that
have been documented. Fishtraps, which were constructed with rock and/or
organic matter, are argued to be designed primarily to trap or control
the movements of marine resources across tidal cycles in coastal or
riverine contexts (Campbell, 1982; Dortch et
al., 2006; Jeffery, 2013;
Rowland & Ulm, 2011). Stone-walled intertidal fishtraps are defined for
the purposes of this study as structures that can control the movements
of marine animals. As structures testifying to local subsistence,
the organisation of labour, occupation, and social strategies, fishtraps
have been cited as features of early domestication (Codding & Bird,
2015; Smith, 2014; Zeder, 2015), anthropogenic niche construction
(Lepofsky & Caldwell, 2013; Lourandos, 1980; Smith, 2014, Zeder, 2015),
and mid- to Late-Holocene economic social intensification (Lourandos,
1980, 1983; McNiven et al.,
2012, 2015). A variety of approaches to the recording of sites have been
led to by physical and conceptual challenges of characterising fishtraps
in spite of interest in fields such as archaeology, evolutionary
biology, and human behavioural ecology. Resulting from this researchers
often adopt vague definitions of fishtraps and terminology (Bannerman &
Jones, 1999; Jeffery, 2013; Ross, 2009; Rowland & Ulm, 2011, and
fundamental questions concerning the construction and function of
fishtraps remain to be addressed(Caldwell et
al., 2012; Elder et
al., 2014; Moss et
al., 1998). Access is often restricted and is dependant of
movements of tides; as a result of the location of fishtraps in
intertidal and riverine settings, and in some parts of the world the
work of field workers can be made hazardous by the presence of marine
predators. Tides also control the times of visibility and recording
time, and are restricted further by wind which causes swell and sediment
that obscures structures. As well as such environmental factors, there
are impacts of recreational vessels, which cause intertidal stone
features to be eroded partially or completely, which underlies the
urgency of recording the fishtrap structures that remain (Elder et
al., 2014; Memmott et
al., 2008; Roberts et
al., 2016; Rowland & Ulm,
2011; Rowland et al., 2014).
In spite of the urgency of documentation, and a global interest in
fishtrap construction (Greene et
al, 2015; Jeffry, 2013), most recordings consist of basic sketch
maps of limited detail, with a few quantitative data or photographic
records (see Coutts et al.,
1978; Greene et al., 2015;
Koivisto et al., 2018;
Langouët and Daire, 2009; McNiven et
al., 2012; O’Sullivan, 2004).
There has been a proliferation of terms that describe attributes of
fishtraps as a result of varied approaches to the recording of sites,
which leads to challenges for the management of sites, comparisons
between sites, and the ability for fishtraps to be considered in
meaningful debates. The focus of this study was intertidal stone-walled
fishtraps, and proposes a standard high-resolution recording scheme for
intertidal stone features on a large scale, to improve knowledge of the
construction, function and age of fishtraps.
Discussion It was demonstrated by the GIS-generate sea level
scenarios that the stone-walled structures of Ngathald and Kabar Bays
would not have had effective ranges earlier than about 3,500 BP, which,
according to Kreij et al.,
correlates with the earliest dates of occupation of Sweers Island and
Bentinck Island, which date to about 3,500 BP (Memmott et
al., 2016). There was a
continuous signal of occupation from about 2,000 cal. BP in the
archipelago, and ethnographic records that outline the need for fishtrap
maintenance that is on-going for optimal function (e.g. Tindale, 1960),
it can be concluded that the fishtraps were constructed within the last
2,000 years. With the current placement and a consistent height of
fishtraps below 1 m, the traps of Ngathald Bay and Kabar Bay would have
functioned with tides of 0.5 m ± PMSL. With a fishtrap range that was
relatively narrow, sea level shifts of ±0.5 would have an impact that
was significant on the functioning of the trap. It will become possible
to further refine construction chronologies as regional and local sea
level curves become available. It was acknowledged that the height of a
trap may be decreased over time; however it cannot be demonstrated that
such erosion has occurred without monitoring of morphology in the long
term, this study was based analysis on current properties of the
structure. Based on fishtrap construction findings, and
interaction with past and current tidal regimes, high resolution
documentation of fishtrap metrics (length, height and width) were
recommended by Kreij et al.,
particularly elevation in relation to a national height datum.
Photogrammetric UAV recording proved particularly useful for documenting
features in the intertidal zone, while the method and majority of the
analytical procedure can be applied to other archaeological site types.
Earlier documentation of fishtraps has varied in detail, and there is
limited cross-site comparison due to ambiguous descriptions.
Quantitative analysis of geometric properties was enabled by GIS
assessment of the physical features of fishtraps, and formed a basis for
robust comparative studies. The risk of misidentification is minimised
and the potential for comparison of sites and modelling is maximised, by
describing the structures through geometric variables. It is recommended
to move towards a standardised objective industry practice, involving
simple, though inclusive terms, such as fishtraps, which represent
structures, either natural or constructed, that enclosed bodies of
water, described by metric properties. Geomorphological studies of the
environmental impacts on local ecosystems within the structures will
assist in gaining an understanding of local resource management, and
impacts on the wider intertidal zone of potential erosion and
sedimentation. Site-specific cultural heritage management plans for
stone-walled features in intertidal environments of low energy can be
contributed to by such recent and historical information, of structural
function and impact on the intertidal environments. Indictors of
concepts, such as domestication, cultural niche constructions, and
potential aquaculture paradigms, will be furthered by evidence of local
marine resource technologies, as well as their impacts.
Conclusion In this study 13 Kaiadilt fishtraps were
identified by the use of a dataset that was highly accurate that had
been obtained by high-resolution UAV photogrammetric mapping of Ngathald
Bay and Kabar Bay, Sweers Island, where it was determined that the local
topography was determined to be the dominant consideration of the
placement and construction of fishtraps. Operation of fishtraps
throughout the year was effectively enabled by the intertidal locations,
and the stone-walled fishtraps are placed for optimal use during PMSL.
In times of increased sea levels the structures can be effectively used
during low tide up to +1 m above PMSL, which indicates, in combination
with archaeological records, a date for construction at some point in
the last 2,000 years. In this study the basis for further refinement of
the chronology of construction is provided by the UAV documentation
technique and GIS analysis that is presented, when regional sea level
histories of higher-resolution are available for the Late Holocene.
Considering the working range of fishtraps at times of past sea levels
is the most recent, viable option to date stone-walled fishtraps that
are located in the intertidal zone of the present. Future impact of sea
level rise on fishtraps can also be modelled for applications of
cultural heritage management. Management plans for preservation of this
type of site can benefit further from aligning recording methods and
terminology to a standardised quantitative technique, and can contribute
to a broader cross-disciplinary understanding of stone-walled intertidal
fishtraps.
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| Author: M.H.Monroe Email: admin@austhrutime.com Sources & Further reading | ||||||||||||||