<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">JEP</journal-id><journal-title-group><journal-title>Journal of Environmental Protection</journal-title></journal-title-group><issn pub-type="epub">2152-2197</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/jep.2014.510084</article-id><article-id pub-id-type="publisher-id">JEP-48070</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>EARTH &amp; ENVIRONMENTAL SCIENCES</subject></subj-group></article-categories><title-group><article-title>The Phytodepuration of Wastewater for Tourism Facilities in Rural Areas: The Atlas Kasbah Ecolodge—A Pilot Site in the Argan Biosphere Reserve</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Hassan</surname><given-names>Aboutayeb</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Belkacem</surname><given-names>Kabbachi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Abdelkrim</surname><given-names>Ezaidi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Department of Earth Sciences, Ibn Zohr University, Agadir, Morocco</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>HassanAboutayeb@gmail.com(HA)</email>;<email>B.kabbachi@uiz.ac.ma(BK)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>24</day><month>07</month><year>2014</year></pub-date><volume>05</volume><issue>10</issue><fpage>819</fpage><lpage>825</lpage><history><date date-type="received"><day>2</day>	<month>May</month>	<year>2014</year></date><date date-type="rev-recd"><day>27</day>	<month>May</month>	<year>2014</year>	</date><date date-type="accepted"><day>15</day>	<month>June</month>	<year>2014</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
	In recent years, rural
tourism has developed a lot and especially in the Souss Massa Draa region, in
the South West of Morocco. The need to implement an eco-friendly sewage
treatment has grown accordingly to resolve the wastewater issue. In this
context, a pilot project of planted filters has been achieved in the Atlas
Kasbah Ecolodge. During 3 years, the water purification performance and its
compliance with the requirements of environmental management were assessed. The
objective was to find an eco-friendly and affordable alternative to
noncompliant ditches and sumps found in the rural areas of Morocco. The
monitoring of physicochemical parameters of treated wastewater has revealed a
perfect adaptation of the system to the needs of rural tourism facilities both
in terms of efficiency and in terms of integration into the natural
environment. Thus, such a technique could be spread in remote areas. 
</p></abstract><kwd-group><kwd>Sanitation</kwd><kwd> Biofilter Treatment</kwd><kwd> Environmental Management</kwd><kwd> Rural Tourism Facility</kwd><kwd> Morocco</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>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.</p><p>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-domi- nated 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.</p><p>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.</p></sec><sec id="s2"><title>2. The Operating Environment of the Souss Water Resources</title><p>The Souss basin which houses most of the Argan biosphere is located in the south-west of Morocco, in a semi- arid 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.</p><p>During recent years, an evolution in water consumption has lead to:</p><p>-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;</p><p>-Salted water wedges in coastal aquifers resulting in an increase in conductivity;</p><p>-A scarce rain and an increase in drought in southern Morocco because of climate change.</p></sec><sec id="s3"><title>3. Location of the Project (Figure 1(a), Figure 1(b))</title><p>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 miles<sup>2</sup> 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...).</p><p>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 trans- Saharan 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 (<xref ref-type="fig" rid="fig2">Figure 2</xref>) are summarized.</p><p>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 [<xref ref-type="bibr" rid="scirp.48070-ref1">1</xref>] , the measures implemented within the framework of the approach on the management of water resources are listed as <xref ref-type="fig" rid="fig3">Figure 3</xref>.</p><p>The analysis on the initial quality of water (<xref ref-type="table" rid="table1">Table 1</xref>) 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.</p></sec><sec id="s4"><title>4. Materials and Method: The Unconventional Vertical Flow Filter</title><p>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-</p><fig-group id="fig1"><caption><title>Figure 1</title><p> (a) Location of the pilot project; (b) A panoramic view of the Atlas Kasbah</p></caption><fig id ="fig1_1"><label>(a)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\e5f62ca8-79ea-4ebd-becc-074077a6b265.png"/></fig><fig id ="fig1_2"><label>(b)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\675997a7-a33e-4614-a1ef-bc3fab997030.png"/></fig></fig-group><table-wrap id="table1"  position="float"><object-id pub-id-type="pii">Table 1</object-id><label>Figure 1</label><caption><p>. (a) Location of the pilot project; (b) A panoramic view of the Atlas Kasbah</p></caption><table><thead><tr><th align="center" valign="middle" >• Geological terrain with rough brownish-yellow limestone-marl inclined to 6%; • Eroded soil with a small evolution, poor in organic matter and revitalized by runoff; • No drinking water supply; • 40 m deep well with a downstream pump; • Drip irrigation system on cultivated terraces (permacultures: fruits, vegetables and herbs); • Water consumption for the accommodation = 4 m<sup>3</sup>/day on average.</th></tr></thead><tbody></tbody></table></table-wrap><p><xref ref-type="fig" rid="fig2">Figure 2</xref>. Characteristics and use of water in the project.</p><p>logical degradation of dissolved solids is carried out by aerobic bacterial biomass fixed on the unsaturated media. The system has the following advantages:</p><p>-Neither regular renewal filter layer nor biological sludge evacuation;</p><p>-Physical retention of suspended solids in surface filters;</p><p>-Simple technique with gravity flow;</p><p>-The area occupied is small and integrated into the overall landscape;</p><p>-Substantial savings in irrigation water especially for trees (argan, olive, orange, carob and almond);</p><p>-Preservation of soil quality and protection against contamination of the groundwater.</p></sec><sec id="s5"><title>5. Design and Implementation of the System of the Kasbah (Figure 4)</title><p>The station was monitored over a period of 3 years (2012/2013/2014) with a comprehensive analysis during</p><fig id="fig2"><label>Figure 3</label><caption><p> Water control</p></caption><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\590da6e8-ca24-40ed-b1d1-39b6f7824107.png"/></fig><fig id="fig3"><label>Figure 4</label><caption><p> Diagram of the process for recycling wastewater in the Kasbah</p></caption><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\2e4fbd7e-226c-494d-a87f-350c91025c4b.png"/></fig><table-wrap id="table2"  position="float"><object-id pub-id-type="pii">Table 2</object-id><label>Table 1</label><caption><p>. Physico-chemical analysis of water from the Kasbah (ONEP, 2012)</p></caption><table><thead><tr><th align="center" valign="middle" >Characteristics</th><th align="center" valign="middle" >Concentration</th></tr></thead><tbody><tr><td align="center" valign="middle" >Temperature ˚F</td><td align="center" valign="middle" >67</td></tr><tr><td align="center" valign="middle" >PH</td><td align="center" valign="middle" >7.5</td></tr><tr><td align="center" valign="middle" >Turbidity NTU</td><td align="center" valign="middle" >46</td></tr><tr><td align="center" valign="middle" >Conductivity μs/cm</td><td align="center" valign="middle" >1720</td></tr><tr><td align="center" valign="middle" >Salinity mg/l</td><td align="center" valign="middle" >1280</td></tr><tr><td align="center" valign="middle" >Chloride (Cl<sup>−</sup>) mg/l</td><td align="center" valign="middle" >285</td></tr><tr><td align="center" valign="middle" >Complete alcalimetric titration m&#233;q/l</td><td align="center" valign="middle" >8.6</td></tr><tr><td align="center" valign="middle" >Total hardness TH m&#233;q/l</td><td align="center" valign="middle" >17.5</td></tr><tr><td align="center" valign="middle" >Calcium hardness mg/l</td><td align="center" valign="middle" >156</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >524</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >20.5</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >25.5</td></tr><tr><td align="center" valign="middle" >Dissolved oxygen mg/l</td><td align="center" valign="middle" >1.2</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >0</td></tr><tr><td align="center" valign="middle" >Ammonuim (NH<sup>4+</sup>) mg/l</td><td align="center" valign="middle" >0</td></tr><tr><td align="center" valign="middle" >Fluoride (F<sup>−</sup>) mg/l</td><td align="center" valign="middle" >0.55</td></tr></tbody></table></table-wrap><p>spring and performed on 2 samples taken spontaneously. The size of the two stories was respectively of 26 feet &#215; 6.5 feet &#215; 4 feet for wastewater and 19.6 feet &#215; 6.5 feet &#215; 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.</p><p>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 <xref ref-type="fig" rid="fig4">Figure 4</xref>, 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 [<xref ref-type="bibr" rid="scirp.48070-ref2">2</xref>] .</p><p>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 (<xref ref-type="table" rid="table2">Table 2</xref>) 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 (<xref ref-type="fig" rid="fig5">Figure 5</xref>).</p></sec><sec id="s6"><title>6. Performance of the Station</title><p>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 &#215; 52 feet<sup>2</sup> &#215; 0.25</p><fig-group id="fig4"> <caption><title>Figure 5</title><p> Picture of the switching station: (a) Biofilters; (b) Oxygenation and UV treatment; (c) &amp; (d) Macrophytes</p></caption><fig id ="fig4_1"><label>(a)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\71875c06-e51c-40a9-8097-949475ee566c.png"/></fig><fig id ="fig4_2"><label>(b)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\5cfca8c0-daae-4e61-b48d-b1c1c83d7fbc.png"/></fig><fig id ="fig4_3"><label>(c)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\fe4c899f-156b-4f46-9850-80e5c416f8c0.png"/></fig><fig id ="fig4_4"><label>(d)</label><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\527f4198-be62-4eca-af11-6affb663d75e.png"/></fig></fig-group><table-wrap id="table3"  position="float"><object-id pub-id-type="pii">Table 3</object-id><label>Table 2</label><caption><p>. Evolution of bio-physico-chemical parameters</p></caption><table><thead><tr><th align="center" valign="middle" >Analyzed Elements</th><th align="center" valign="middle" >Results April-12</th><th align="center" valign="middle" >Results June-13</th><th align="center" valign="middle" >Results March-14</th></tr></thead><tbody><tr><td align="center" valign="middle" >PH</td><td align="center" valign="middle" >7.85</td><td align="center" valign="middle" >8.2</td><td align="center" valign="middle" >7.22</td></tr><tr><td align="center" valign="middle" >T ˚C</td><td align="center" valign="middle" >70</td><td align="center" valign="middle" >70</td><td align="center" valign="middle" >62,6</td></tr><tr><td align="center" valign="middle" >Conductivity μs/cm</td><td align="center" valign="middle" >2600</td><td align="center" valign="middle" >-</td><td align="center" valign="middle" >2710</td></tr><tr><td align="center" valign="middle" >MIS mg/l</td><td align="center" valign="middle" >32</td><td align="center" valign="middle" >8</td><td align="center" valign="middle" >20</td></tr><tr><td align="center" valign="middle" >MVS mg/l</td><td align="center" valign="middle" >26</td><td align="center" valign="middle" >-</td><td align="center" valign="middle" >17</td></tr><tr><td align="center" valign="middle" >DBO5 mg/l</td><td align="center" valign="middle" >22</td><td align="center" valign="middle" >12</td><td align="center" valign="middle" >30</td></tr><tr><td align="center" valign="middle" >DCO mg/l</td><td align="center" valign="middle" >62</td><td align="center" valign="middle" >44</td><td align="center" valign="middle" >71</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >25</td><td align="center" valign="middle" >15</td><td align="center" valign="middle" >18.5</td></tr><tr><td align="center" valign="middle" >PT</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >13</td><td align="center" valign="middle" >-</td></tr><tr><td align="center" valign="middle" >DBO5/DCO</td><td align="center" valign="middle" >0.35</td><td align="center" valign="middle" >0.27</td><td align="center" valign="middle" >0.51</td></tr><tr><td align="center" valign="middle" >Fecal coliform/100ml</td><td align="center" valign="middle" >800</td><td align="center" valign="middle" >760</td><td align="center" valign="middle" >580</td></tr></tbody></table></table-wrap><p>= 0.40 pounds to evacuate during three years. This mud is important to stop the infiltration rate and thus reduce the allowed CH [<xref ref-type="bibr" rid="scirp.48070-ref3">3</xref>] .</p><p>Over the three years (<xref ref-type="fig" rid="fig6">Figure 6</xref>), 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 &lt; 90 mg/l and MIS &lt; 40 mg/l) [<xref ref-type="bibr" rid="scirp.48070-ref4">4</xref>] . 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 (<xref ref-type="table" rid="table3">Table 3</xref>). 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 [<xref ref-type="bibr" rid="scirp.48070-ref5">5</xref>] .</p><fig id="fig5"><label>Figure 6</label><caption><p> Comparison of the main purification indicators of the system</p></caption><graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="http://file.scirp.org/Html/htmlimages\4-6702345x\bfd4bdcd-8b32-4df3-8d95-6806fffc0d63.png"/></fig><table-wrap id="table4"  position="float"><object-id pub-id-type="pii">Table 4</object-id><label>Table 3</label><caption><p>. Effects of waterfalls on the treatment efficiency</p></caption><table><thead><tr><th align="center" valign="middle" >Analyzed elements</th><th align="center" valign="middle" >Results</th><th align="center" valign="middle" ></th></tr></thead><tbody><tr><td align="center" valign="middle" >Sample</td><td align="center" valign="middle" >Downstream basin</td><td align="center" valign="middle" >Upstream basin</td></tr><tr><td align="center" valign="middle" >Sampling</td><td align="center" valign="middle" >Ponctual</td><td align="center" valign="middle" >Ponctual</td></tr><tr><td align="center" valign="middle" >T˚F water/T˚F air</td><td align="center" valign="middle" >62.6/63.5</td><td align="center" valign="middle" >62.6/63.5</td></tr><tr><td align="center" valign="middle" >PH</td><td align="center" valign="middle" >7.22</td><td align="center" valign="middle" >7.35</td></tr><tr><td align="center" valign="middle" >Conductivity μs/cm</td><td align="center" valign="middle" >2710</td><td align="center" valign="middle" >2825</td></tr><tr><td align="center" valign="middle" >Dissolved oxygen mg/O<sub>2</sub>/l</td><td align="center" valign="middle" >0.4</td><td align="center" valign="middle" >0.2</td></tr><tr><td align="center" valign="middle" >DBO5 mg O<sub>2</sub>/l</td><td align="center" valign="middle" >30</td><td align="center" valign="middle" >60</td></tr><tr><td align="center" valign="middle" >DCO mg O<sub>2</sub>/l</td><td align="center" valign="middle" >71</td><td align="center" valign="middle" >98</td></tr><tr><td align="center" valign="middle" >DBO5/DCO</td><td align="center" valign="middle" >0.42</td><td align="center" valign="middle" >0.61</td></tr><tr><td align="center" valign="middle" >MIS mg/l</td><td align="center" valign="middle" >20</td><td align="center" valign="middle" >28</td></tr><tr><td align="center" valign="middle" >MVS mg/l</td><td align="center" valign="middle" >17</td><td align="center" valign="middle" >21</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" >18.5</td><td align="center" valign="middle" >32</td></tr><tr><td align="center" valign="middle" >Fecal coliform/100ml</td><td align="center" valign="middle" >580</td><td align="center" valign="middle" >730</td></tr></tbody></table></table-wrap></sec><sec id="s7"><title>7. Conclusion</title><p>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.</p></sec></body><back><ref-list><title>References</title><ref id="scirp.48070-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">ABOUTAYEB, H. (2011) SUSTAINABLE TOURISM IN THE BIOSPHERE RESERVE OF THE ARGAN IN MOROCCO. EDITIONS UNIVERSITAIRES EUROPEENNES, 156. (IN FRENCH)</mixed-citation></ref><ref id="scirp.48070-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">AGGA, K., ABAAAKI, R., KABBACHI, B., EZ-ZAHRY, M. AND EL ALEM, N. (2013) USING THE SOLID TITANIFEROUS SAND FILTER AS IN THE PROCESS OF INFILTRATION-PERCOLATION WASTEWATER. INTERNATIONAL CONFERENCE “WATER, WASTE &amp; ENVIRONMENT”, ABSTRACT BOOK, AGADIR, 48.</mixed-citation></ref><ref id="scirp.48070-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">MACROPHYTES AND WATER TREATMENT GROUP GMTE (2005) TREATMENT OF DOMESTIC WASTEWATER BY MACROPHYTES PLANTED FILTERS. SINGLE REPORT, RHONE ALPE MEDITERRANEAN AND CORSICA WATER AGENCY, 39. (IN FRENCH)</mixed-citation></ref><ref id="scirp.48070-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">MOLLE, P., LIENARD, A., BOUTIN, C., MERLIN, G. AND IWEMA, A. (2004) STATE OF THE ART AND PERFORMANCE OF FILTERS PLANTED REEDS IN FRANCE. ENGINEERING, NATURE &amp; TECHNIQUES, 23-32. (IN FRENCH)</mixed-citation></ref><ref id="scirp.48070-ref5"><label>5</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>MOLLE</surname><given-names> P. </given-names></name>,<etal>et al</etal>. (<year>2012</year>)<article-title>FILTERS REEDS PLANTED: RESEARCH DEVELOPMENTS AND CURRENT TRENDS</article-title><source> SCIENCES WATERS AND TERRITORY</source><volume> 9</volume>,<fpage> 24</fpage>-<lpage>31</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref></ref-list></back></article>