4.1. The Satellite Images Forming the Basis of this Review: The Airbus© Mission
At the time of writing, the most recent satellite mission covering the Aqqa/Tāmdult area available on Google Earth dates from 23 May 2023. It belongs to the company Airbus
©. It is this coverage of the area that has prompted the revision of our 2011 article [
3], owing to the excellent quality of the fossil traces of developments in the Tāmdult plain. These new data modify and, above all, supplement the observations and interpretations made on the area in 1999. Such optimal conditions result not only from the high definition of the imagery but also from the combination of climatic conditions prevailing in the preceding period and those of 2023 in particular.
The report by the Moroccan Meteorological Agency gives a clear account of the country’s rainfall and temperature conditions. The year 2023 was the hottest since the beginning of the 20
th century, with temperatures averaging 1.77 °C above the 1981-2010 baseline. It was also the driest for at least 80 years, showing a 48% rainfall deficit and marking the fifth consecutive year of drought in Morocco. Over the 2019-2023 period, the country as a whole recorded an ‘extreme rainfall deficit’ of around 35%, including a severe shortfall in precipitation (29.22% below normal), exacerbated by an exceptional rise in temperatures. As for the region we are concerned with, the province of Tata, conditions were even harsher, with a temperature increase of between 2.5 °C and 3 °C relative to the normal reference period, and annual rainfall between 50% and 80% below the same reference values. This led to between 30-40% greater evapotranspiration and a 30-50% water deficit [
30] (pp. 12-13; pp. 26-28, Figure 26-27). However, these climatic conditions, clearly linked to global warming, had positive consequences for the images taken in May 2023. The extreme dryness and increased evapotranspiration accentuated the shadows created by moisture preserved at the bottom of the former irrigation channels, which rises to the surface by capillary action. In addition, the remains themselves generate shadows that are often visible – whether they rise above bare ground or, when buried by sand, produce minor topographical anomalies that reveal archaeological structures differently from agricultural structures. A further advantage of this aerial coverage for archaeological interpretation is that it already highlights the major agricultural transformations underway. Future satellite missions will reveal a landscape profoundly altered by new agricultural practices: in short, a terrain very different from the one we surveyed in 1999 during our fieldwork.
We extended our observations across a trapezoidal area of around 200 km
2, running parallel to the Jebel Bani and the isoclinal ridges of Izerzatene, bounded to the north-east by the
fūm and the still-productive oasis of Aqqa, and to the south-west by a line located two kilometres downstream from the site identified as the abandoned medieval town of Tāmdult. It should be noted that the term
fūm (in its original sense of ‘mouth’) is deeply ingrained in the toponymy of the Anti-Atlas because it refers to a geomorphological feature conducive to the exploitation of the aquifer. Specifically, it denotes the point where a wadi valley, deeply incised in the mountains, opens onto the plain; here, the configuration of the underlying geological strata creates a threshold that forces the aquifer to rise, producing resurgences [
31].
We then created a WebGIS interface on an IR Huma-Num* server. This phase of the work was carried out mainly by Laurent Costa (CNRS – UMR 7041 Archaeology and Sciences of Antiquity, ArScAn) and should form the subject of a dedicated publication at a later date. Into this interface we integrated the Airbus© image stream visible on Google Earth, dated 23 May 2023, together with the now historical IGN map, at a scale of 1/100,000 (Sheet NH-29-X-2, Akka – 1969), and the thematic maps derived from interpretations based on field observations and on the enlargement of a vertical aerial photograph from the 1952 IGN mission, which we had already used in 1999. Finally, we undertook a reinterpretation of the numerous fossil traces of archaeological remains, including buildings, irrigation canals, plots of land, and even the outlines and boundaries of cultivation plots).
4.2. Accomplishments of 1999-2011 and New Results
The principal outcome of the 1999 fieldwork was the physical identification of a vanished ancient oasis – a ‘first’ in this field of Moroccan archaeology. An irrigated area,
or ḥawz, linked to the foundation of the town, extended alongside it (
Figure 2,
Figure 3 and
Figure 4). The hydraulic network that sustained it drew its source from the outlet
(fūm) of Aqqa, carrying water across the plain to a point 2.3 km north-east of the town (
Figure 2 and
Figure 4-A), beyond which began the irrigation of land organised into a field system extending a further 3 km south. The slope affecting the initial section was 0.53% (a drop of 81 m over a distance of 15.1 km), while the average gradient between the source and the downstream limit of the cultivated zone was 0.51% (91 m over 17.9 km). The total area under cultivation covered approximately 300 ha.
We were thus able to document the flood irrigation of cultivation plots and also to demonstrate the presence of an intercalated settlement within the field system, revealed by surface material: ceramic sherds (whose typology and morphology correspond to those of the assemblage recovered from our excavations in the urban zone), small hand millstones (for grinding grain or other domestic products), as well as large-diameter millstones indicating the existence of horizontal watermills installed along the irrigation canals (
sāqiya-s) or on short branches derived from them. No associated regulating basin, however, was detected on the satellite images (
Figure 7).
The origin of the water that irrigated the Tāmdult plain is suggested by the direction of the large canals visible in the images: the water intake was probably located between the ancient centres of the Aqqa oasis and the outlet of
the fūm. The canals observed in the field were constructed in earth, raised about one metre above the surrounding ground (
Figure 5 and
Figure 6). They flowed parallel to the Jebel Bani, at the foot of the erosional glacis overlooking the Tāmdult plain (
Figure 3). Observation of this part of the network showed a system heavily fragmented by erosion. It was possible to identify at least four main canals, but no more than six. The routes ran parallel and were intended to supply water to the various sectors corresponding to the basic agricultural units defined by each of them.
Figure 5.
“Dead head” canal upstream of the Tāmdult plain cut by modern works or river avenues. © RGV - Project Genèse de la ville islamique.
Figure 5.
“Dead head” canal upstream of the Tāmdult plain cut by modern works or river avenues. © RGV - Project Genèse de la ville islamique.
Figure 6.
“Dead head” canals upstream from the Tāmdult plain. Jebel Bani mountain range in the background. © RGV - Project Genèse de la ville islamique.
Figure 6.
“Dead head” canals upstream from the Tāmdult plain. Jebel Bani mountain range in the background. © RGV - Project Genèse de la ville islamique.
Figure 7.
Hydraulic millstone on a canal diversion in the plain of Tāmdult. © RGV - Project Genèse de la ville islamique.
Figure 7.
Hydraulic millstone on a canal diversion in the plain of Tāmdult. © RGV - Project Genèse de la ville islamique.
It should be emphasised that, although probably discontinuous at the level of each individual plot, the flow of the sāqiya-s was sufficiently constant to allow the proliferation of freshwater gastropods (observed in abundance along the canal routes), which could not have survived even brief periods of drought.
The abandonment of the irrigation system, after several centuries of operation, entailed the partial destruction of the layout of each technical unit of water distribution. Once the intake had lost its functionality, water circulation became limited to occasional torrential flows across the plain, caused by violent meteorological events and resulting in severe erosion of the canals. Evidence for this is seen particularly in their terminal sections, where several have been transformed into gullies or runoff channels. What can now be observed, both on the ground and through remote sensing, is thus a ‘hybrid’ system of surface water flow, both anthropogenic and natural. This explains the confusion of the cartographer who produced the IGN 1:100,000 map, the only official one available in 1999: the hydrographic network shown there indiscriminately mixes ancient sāqiya-s with natural or man-made ravines. Aerial imagery presents the same difficulty: it is often tricky to identify a canal, which is generally rather straight, that cuts across the ‘meandering’ dark traces formed by residual soil moisture.
Today, the Airbus
© 2023 imagery allows us to confirm these observations in part. The multiplication of canals creates a palimpsest, not only (as we had previously thought) as a result of the degradation and hybridisation of surface water flow after the abandonment of agricultural activity, but also possibly due to dynamics inherent to the network during its operational phase. It is possible that the earthen
sāqiya-s had already suffered damage while the oasis was still active, and that partial or alternate reconstructions were responsible for the multiplication of traces visible on the Airbus
© 2023 mission imagery. It should be remembered that in 1999 we had identified the dead heads (the sections of the conduits between the intake and the first point of water use) of between four and six main canals, extending from the
fūm downstream for up to 15 km. In certain places, the parallel alignments of two canals were separated by a very small distance – barely 4 to 5 metres (
Figure 6).
The open-air flow of water combined with the high temperatures of the region led to the formation of dense calcareous concretions at least 30 cm thick, coating the inner walls of the canals and in some places reducing their functional cross-section to a width of about 60 cm at the end of the hydraulic system’s active life.
Today, despite the quality of the 2023 satellite imagery, we cannot yet assess with any certainty the exact number of canals upstream of the cultivated fields. Even though the traces appear to multiply, the indicators interpretable as water conduits cluster around four major ‘flows’. Here, we apply to our analysis the conceptual framework proposed by S. Robert [
32] (pp. 95-101, Figure 3-18, 3-19) for the study of road networks. That author suggests interpreting such systems by distinguishing three analytical levels: the
flow, the route, and
the construction. The first, the flow, represents the relationship established between two poles involving movement or transport. In our case, this is the transport of water between the intake and the irrigated plots. The second, the route, is the optimum path determined by topographic conditions, allowing for measured flow and efficient distribution; it results from empirical calculations made by the builders. Finally, the construction refers to the mode of viability, the main or secondary route, that is to say, in our case, the hierarchical level of the canal within the system: primary, secondary, or tertiary. In the upstream section of the network, the impression is one of multiple routes organised around four major flows carrying water from the intake at the level of the
fūm of Aqqa. This multiplicity could also be interpreted as alternative configurations of a still-functioning system, later supplemented and altered spontaneously after its abandonment by torrential and destructive watercourses generated by climatic events. In addition, certain ‘inconsistencies’ in the fossil traces (
Figure 3) may suggest the existence of other flows originating from short ravines on the Jebel Bani, oriented differently from that of the oasis’s hydraulic network. The hydrological and geomorphological characteristics of these short valleys indicate that such flows could only have been episodic and violent, yet no traces of possible diversion dams intended to incorporate this water into the system, (as are known, for example, in the Algerian Mzab [
33]
(pp. 169-175), could be identified on the ground or in satellite imagery.
However, the principal new insight provided by the 2023 Airbus
© image concerns the area where the canals cease to be mere ‘dead heads’ (initial segments whose sole function was the conveyance of water) and where the first cultivated fields appear. In 1999, lacking higher-quality imagery and with no readable remains visible on the ground, we had interpreted the original labour investment required to construct four or six separate flows, instead of a single channel – an apparently disproportionate undertaking – as the solution adopted by the founding communities of Tāmdult in order to preserve their autonomy in the management of water and land. Logically, this plurality of flows ought to have continued downstream, with the parallel circulation of the different channels feeding the strips of land [
3] (
Figure 3, canals 1-4). Yet the photo-interpretation of the 2023 image appears to suggest a certain convergence towards a zone located 15 km from
the fūm and 2.3 km north-east of the outer perimeter of the ruined settlement identified as the medieval town (
Figure 4-A). Here, the four to six major flows lie less than 40 m apart. It is from this small area, where the various routes unfortunately become blurred on the satellite image, that a clear branching dispersion occurs, spreading out from each
sāqiya. However, this convergence cannot be interpreted as a merger of the flows into a single canal. Indeed, remote sensing cannot determine the chronological sequence of the network’s development, nor confirm or refute the contemporaneity of the large, almost rectilinear canals. The junction of the dead heads would have required the construction of a substantial hydraulic infrastructure, a large accumulation and redistribution basin. It is therefore difficult not to question the value of such a costly arrangement: the multiplication of canals upstream would have entailed a significant additional expense in the construction and maintenance – a total of 60 km (15 km for each of the four canals) or even 90 km (if six) – only to bring the waters back together halfway downstream. One possible explanation for this apparent incongruity is the need for multiple intakes along the wadi to maximise the exploitation of available water resources, which does not exclude the distribution of land and water by lineage within a single (tribal) population group, since it appears that the major
sāqiya-s remain autonomous beyond the convergence zone.
In 1999, drawing on the few remains clearly visible in the aerial photograph, we were able to define the field morphology generated by the hydraulic system. It consisted of a series of ‘bands with a regular orientation (NG-38.8°E) whose intermediate boundaries – the major
sāqiya-s – run longitudinally across the plain for 3 km, while their secondary canals intersect the bands transversely’. The six bands thus identified can be related to the maximum number of four to six major flows proposed above. They extend with a constant orientation (though with very slight variations between the upstream and downstream sections) over 2.9 km, between the point of confluence of the dead heads and the end of the irrigation network. These bands display signs of metrical regularity, although it remains difficult to quantify: the central band has a module of approximately 75 m in width between the axes of the
sāqiya-s
, while elsewhere values close to 84 m are observed. The only exception to this general orientation of the system is a very distinct canal, visible for a distance of 1.5 km on the 2023 imagery, which in 1999 had been interpreted as a palaeo-channel. This canal runs towards the northernmost part of the town of Tāmdult and passes close to a 2,400 m² building (
Figure 3 and
Figure 4-D).
Within the areas delineated by the canals themselves (1999 study area,
Figure 4), it is possible to reconstruct the irrigation system using dividers that distributed water from the higher-order canals to the secondary and then tertiary ones, and so on down to the level of the individual plot (
Figure 8 and
Figure 9). These figures show the long duration of use of these structures, with several phases of operation and the presence of layers of aquatic gastropods (
Figure 9). They also illustrate the layout of cultivation plots within each parcel, a typical organisation of oasis systems, as was still practised in the Aqqa oasis at the time of our field surveys and the brief ethnographic study we conducted there (
Figure 12). This irrigation technique is particularly suited to low-gradient soils, with slopes between 0.2% and at most 3%, allowing the flooding of the area bounded by small earthen ridges or bunds, shaped with a hoe, about 20 to 30 cm above the water level. The method is mainly used for growing cereals, alfalfa, and vegetables [
34] (pp. 2-3) [
35] (pp. 29-32). These crops form the lower stratum of the three that constitute oasis agriculture: 1: date palms; 2: fruit trees; and 3: cereals, market-garden species, and fodder plants [
36] (p. 312).
In 1999, through excavation within the fossil field system, we were able to document several of these micro-agricultural structures, a level smaller than the parcels themselves, by conducting a detailed ground analysis of a 225 m
² test window (
Figure 10,
Figure 11 and
Figure 13). The excellent conditions at the time the Airbus
© satellite images were taken, combined with their high resolution, now make it possible to extend this analysis to the scale of the entire
ḥawz (
Figure 14). The cultivation plots are grouped within ‘cultivation quarters’ (equivalent to urban blocks), defined by secondary
sāqiya-s. These quarters may contain several parcels, but it is not always easy to discern any subdivisions beyond those of the plots themselves. The plots are roughly rectangular, bounded in turn by small earthen ridges, and their longer side generally runs parallel to the path of the water. Their size varies, no doubt adapted to the type of crop grown, the season, and the preferences of each farmer, ranging from 12 to 60 m
2 (around 250 to 1,000 square feet), with an average of 23 m
2 (around 580 square feet) (close to the 21 m
2 (around 570 square feet) of the only complete example excavated in our observation window in 1999 (
Figure 13).
Figure 10.
Secondary channel partially excavated in the 1999 study field area. Jebel Bani mountain range in the background. © RGV - Project Genèse de la ville islamique.
Figure 10.
Secondary channel partially excavated in the 1999 study field area. Jebel Bani mountain range in the background. © RGV - Project Genèse de la ville islamique.
Figure 11.
Secondary channel excavated and border irrigation system in the study field area (1999). © RGV - Project Genèse de la ville islamique.
Figure 11.
Secondary channel excavated and border irrigation system in the study field area (1999). © RGV - Project Genèse de la ville islamique.
Figure 12.
Border irrigation system observed in 1999 in the Aqqa oasis. © RGV-EOX - Project Genèse de la ville islamique.
Figure 12.
Border irrigation system observed in 1999 in the Aqqa oasis. © RGV-EOX - Project Genèse de la ville islamique.
Figure 13.
Partial plan of border irrigation stripped in the study field area (1999). © RGV - Project Genèse de la ville islamique.
Figure 13.
Partial plan of border irrigation stripped in the study field area (1999). © RGV - Project Genèse de la ville islamique.
Figure 14.
Border irrigation in the Tāmdult plain visible in the 2023
©Airbus mission (see
Figure 4-B and
Figure 11).
Figure 14.
Border irrigation in the Tāmdult plain visible in the 2023
©Airbus mission (see
Figure 4-B and
Figure 11).
This oasis landscape included buildings occupying the interstitial spaces between canals and cultivated fields. The aerial photographs used in 1999 already showed a large number of these structures, often located on ground slightly higher than the fields, but they appear much more clearly and in greater numbers on the Airbus© 2023 imagery. Following surface surveys, we interpreted these structures as habitation sites (attested by the presence of potsherds and hand-mills), whose main activities were both agricultural (proximity to sāqiya-s and cultivation plots) and craft-based (evidence of metallurgy, such as slag stains). Although the mapping of these structures can – and must – still be refined, remote sensing does not allow for a more detailed characterisation of the buildings. However, it is worth noting that some of these mounds are identified by local inhabitants as burǧ-s (‘towers’).
Among the buried archaeological structures that we were able to identify, particular attention should be drawn to those on the periphery of the ancient town. At its north-eastern extremity, alignments and complex buildings can be discerned, linked by what appear to be long passages between two parallel walls. Their extramural location, their overall dimensions (between 7 and 10 ha), and the presence within this area of a square building measuring some 2,800 m
2, suggest that this was a
funduq-type complex
, a conclusion consistent with Tāmdult’s role as a commercial hub situated at the crossroads of caravan routes (
Figure 3 and
Figure 4-E).
An obvious question arises: how much land, and how much water, are we talking about? In light of the preceding discussion, we deemed it relevant to estimate (at least approximately) the volume of water required to meet the needs of the palm groves of Tāmdult and Aqqa, and, hypothetically, those of the two oases if they had operated simultaneously. Fully aware of the uncertainties inherent in this type of calculation, we nevertheless consider it useful for assessing, on the one hand, the effort undertaken by the builders of the Tāmdult oasis to conduct water from the
fūm to the plain; and, on the other, for defining the operational limits of the two oases functioning separately or jointly with the flow currently available at the
fūm of Aqqa. It should be remembered that no archaeological evidence has yet demonstrated the contemporaneity of the present-day oasis of Aqqa and the now-abandoned one of Tāmdult. The parameters for this calculation derive from Kh. Amrani’s estimates of water requirements, following other authors [
37] (pp. 93-95) [
38] (pp. 209-210), summarised here in a table (
Table 1). To this end, we also used the flow and abstraction figures for the basin and the
fūm of Aqqa provided by the Draa Oued Noun Water Basin Agency. These are 600 L/s for the total flow and 200 L/s for water abstraction [
39]
. Nevertheless, these figures must be interpreted with caution. The reference standard used by Kh. Amrani is 20,000 m³/ha/year for a density of 100 palm trees per hectare, though the author also notes other reference values that vary primarily with palm-tree density. G. Toutain [
40], moreover, highlights an apparent paradox: that a higher density of palms actually reduces total water requirements by providing more shade for crops in the lower strata and consequently reducing evapotranspiration. If we assume a withdrawal of 200 L/s at the
fūm of Aqqa, and irrigable areas of 600 ha for the Aqqa territory and 300 ha for that of medieval Tāmdult, we immediately observe that, in most hypothetical estimates, the required volume exceeds that allowed by the current discharge. Even though the Aqqa oasis remains functional today, this is only possible through the overexploitation of the aquifer. Numerous studies on Saharan and pre-Saharan oases show that such overexploitation is now widespread, while traditional irrigation causes losses estimated at 30% through evapotranspiration or percolation [
41] (p. 6). The most important point revealed by these data is that it is very difficult to imagine both oases functioning simultaneously, unless one were to adopt much more optimistic assumptions regarding their water requirements.
If we assume that both oases functioned simultaneously, two scenarios are possible. The first is that this occurred for a limited period, under hydrological conditions similar to those of today, but only until overexploitation of the aquifer rendered it unsustainable. The second would imply more favourable hydrological conditions at the time of the foundation of one or both systems, followed later by climatic deterioration that eventually forced the abandonment of one of the territories, at a date yet to be determined.