The Phytodepuration of Wastewater for Tourism Facilities in Rural Areas: The Atlas Kasbah Ecolodge—A Pilot Site in the Argan Biosphere Reserve ()
1. Introduction
The evolution of wastewater purification systems has grown rapidly because of the recent increasingly stringent environmental regulations. Small communities could not use the conventional sewage systems, so since 1997, alternative treatments have been developed with the macrophytes bed filter treatments of domestic wastewater. Several studies including Boutin and Molle were recently published stressing the relevance of this process. In Morocco, it remains little known but there is a huge demand for this type of sewage treatment as it represents a reliable, easy-to-use technology. It not only enables an efficient sewage sludge management but it is also well accepted by the locals because of its landscape integration.
At the Atlas Kasbah, we have opted for the separation of waters. The pre-treatment applied to grey water is used for the elimination of suspended solids and it optimizes the quality of released water. The entire system is based on gravity. The tightness is ensured by compaction and also by thin layers of non-expansive iolite-dominated clay. In addition to regular materials, a natural layer of Titanium oxide sand and another one of anthracite coal are being tested. This combination represents a unique process in this pilot project, thus constituting a new contribution to improving it.
Finally, this article is structured around the following content: first a presentation of the issue, then a view of the geographical and managerial context, a description of the used method, the analysis and discussion of the results and finally conclusion.
2. The Operating Environment of the Souss Water Resources
The Souss basin which houses most of the Argan biosphere is located in the south-west of Morocco, in a semiarid area. There is a major tourism development mainly because of the seaside, the argan tree (Argania spinosa) and its products and the desert with its cultures. The number of hotels has grown in the last decades. Consequently, the groundwater consumption has increased to a great extent. Water resources are scarce and even more so as there are a lot of agricultural facilities and irrigation systems. But only a reasonable and fair use of water can ensure long-term survival of the agricultural and tourism activities in the Souss region.
During recent years, an evolution in water consumption has lead to:
-An alarming drop in groundwater: more than 6.5 feet/year sometimes with a decrease in the water catchment. The study called “Drinking Water Supply for Agadir Region” has identified, since 2010, a 5% decrease of the groundwater resources each year;
-Salted water wedges in coastal aquifers resulting in an increase in conductivity;
-A scarce rain and an increase in drought in southern Morocco because of climate change.
3. Location of the Project (Figure 1(a), Figure 1(b))
The Atlas Kasbah Ecolodge is located in the southern part of Tighanimine village, 5 kilometers from the city of Agadir. The guesthouse has 11 rooms and is based on sustainability. It is perfectly integrated into the landscape with its traditional architecture. This accommodation facility is built on a hill on over 7.7 miles2 of land with an estimated built up area of 25%. The remaining land is used for the organic garden and plants and for livestock (poultry, sheep...).
The Ecolodge is located in an area that is also part of the tourism region Ida Outanane (PATI) launched by the Moroccan Ministry of Tourism in 2005 to promote rural tourism in the hinterland of Agadir. From a historical perspective, it is an ancient place of caravan trade. There are several remains of these periods such as the transSaharan Trade Tower of control and the ancient Saadian Tombs (XVI century). As for archaeology, some excavations have shown that there was a human presence already in the Neolithic period (about 10,000 years BP). Relations field for the use of water in this Ecolodge (Figure 2) are summarized.
In addition, proactive measures are implemented using the following criteria: water, energy, waste, perm culture, purchasing policy, the landscape integration and the external and internal awareness. In detail [1] , the measures implemented within the framework of the approach on the management of water resources are listed as Figure 3.
The analysis on the initial quality of water (Table 1) used was made at the National Office of Drinking Water (ONEP). It shows that according to Moroccan standards this is a neutral water of acceptable hardness and salinity.
4. Materials and Method: The Unconventional Vertical Flow Filter
Major purification mechanisms rely on the combination of multiple processes in aerobic condition, successively occurring on two floors of serial processing. Vertical flow filters are powered in surface. Effluent percolates vertically through the substrate. Physical retention of suspended solids is carried out on the surface of filters. Bio-
(a)
(b)
Figure 1. (a) Location of the pilot project; (b) A panoramic view of the Atlas Kasbah.
Figure 2. Characteristics and use of water in the project.
logical degradation of dissolved solids is carried out by aerobic bacterial biomass fixed on the unsaturated media. The system has the following advantages:
-Neither regular renewal filter layer nor biological sludge evacuation;
-Physical retention of suspended solids in surface filters;
-Simple technique with gravity flow;
-The area occupied is small and integrated into the overall landscape;
-Substantial savings in irrigation water especially for trees (argan, olive, orange, carob and almond);
-Preservation of soil quality and protection against contamination of the groundwater.
5. Design and Implementation of the System of the Kasbah (Figure 4)
The station was monitored over a period of 3 years (2012/2013/2014) with a comprehensive analysis during

Figure 4. Diagram of the process for recycling wastewater in the Kasbah.

Table 1. Physico-chemical analysis of water from the Kasbah (ONEP, 2012)
spring and performed on 2 samples taken spontaneously. The size of the two stories was respectively of 26 feet × 6.5 feet × 4 feet for wastewater and 19.6 feet × 6.5 feet × 4 feet for gray water. This choice was motivated by the accommodation occupancy rate which is irregular and varies between 11 and 18 guests per day for an average of 10 EH. The basins lie at an altitude of 190 m with a drop of 4 m.
The station thus treats raw wastewater from a sanitary system rarely affected by pests and water running completely by gravity so without any energy supply. Upstream of the system, the water undergoes anaerobic pretreatment settling in two septic tanks with 2 compartments. According to Figure 4, the materials used in filters are made of non-carbonate aggregates to avoid the phenomena of dissolution/precipitation that could participate in obstructing porosity. A layer of natural titaniferous sand is associated with the filter as this brings very interesting levels (98% phosphate, 98% COD, 99% BOD5) obtained in preliminary experiments [2] .
The system consists of two vertical flow filters with cattails (Typha, Photo D) and bamboos (Phyllostachys, Photo E). Blackwater (from the restaurant and showers) and gray water (from the toilets) are treated separately throughout the process (Table 2) and eventually come out in small waterfalls in basins on a distance of 144 feet (Photo C). After this process and, in spite of the variations of hydraulic loads (0.03 feet to 1.6 feet/d), the waters of the last clear and odorless basin reflect the great potential of the purifying device given the levels of discarding and objectives of reuse in agriculture (Figure 5).
6. Performance of the Station
The effluents are not connected to any source of metals and, the manager does not allow upstream chemicals. Tiny particles suspension settle on the surface of filters at an average height of 0.6 inches/year × 52 feet2 × 0.25

Table 2. Evolution of bio-physico-chemical parameters.
= 0.40 pounds to evacuate during three years. This mud is important to stop the infiltration rate and thus reduce the allowed CH [3] .
Over the three years (Figure 6), the stability of the system is noticed and the performance in terms of DCO, BOD5, MIS remain largely acceptable given the best rates recorded in literature (DCO < 90 mg/l and MIS < 40 mg/l) [4] . Given the sensitivity of the nitrification in the presence of oxygen and its competition with the carbonaceous material degradation, the stirring and oxygenation stage should be implemented during the process with the use of successive waterfalls so as to filter the output. In basins designated for that purpose, the waters are also exposed to UV rays with a view to improving their particular disinfection against E. coli and fecal coliforms (Table 3). The ratio between the measured values of upstream basin and downstream is close to 1.5. This system also shows encouraging results and may constitute a contribution to current trends that the filters planted chain knows [5] .

Figure 6. Comparison of the main purification indicators of the system.

Table 3. Effects of waterfalls on the treatment efficiency.
7. Conclusion
This pilot test has tested the efficiency of planted filters in order to use them in tourism facilities in rural Morocco. Overall, this system adapts well to local physical and socio-economic backgrounds and provides excellent purifying efficiency in spite of the variation of hydraulic loads due to the varied occupancy rate. The titaniferous sand bed seems to reinforce reduction treatments while waterfalls with UV rays represent a tertiary stage in the treatment which ensures a good final quality of the released water on all levels.