The Development of Anaerobic Digestion Technology and the Potential of Biogas in Moroccan Regions of Doukkala-Abda, Chaouia-Ourdigha & Tadla-Azilal

DOI : 10.17577/IJERTV3IS110063

Download Full-Text PDF Cite this Publication

Text Only Version

The Development of Anaerobic Digestion Technology and the Potential of Biogas in Moroccan Regions of Doukkala-Abda, Chaouia-Ourdigha & Tadla-Azilal

Fatima Zahra Beraich

Laboratory "Eco-Design, Energy, Environment & Innovation (3EI)"University Hassan 1, Faculty of Siences and Techniques Settat, Morocco

Mina Bakasse

Laboratory of Organic Chemistry, Bioorganic and Environment (LOCBE); Faculty of Sciences University Chouaib Doukkali El Jadida

El Jadida, Morocco

Moha Arouch

Laboratory "Eco-Design, Energy, Environment & Innovation (3EI)"University Hassan 1, Faculty of Siences and Techniques

Settat, Morocco

Abstract The lack of energy resources and wastes piles not exploited in Moroccan rural areas, represent major problems that prompt us to develop methods to take advantage of such wastes. The goal of our research is to implement an innovative leading-edge technology for the management and enhancement of rural waste with double stakes: 1- methanisation of organic waste which is a source of a clean and renewable energy. 2- The production of organic fertilizers. I other words, the first step of our work consists of evaluating the energy potential of existing biomass resources in the most famous agricultural regions in Morocco, namely DOUKKALA-ABDA, CHAOUIA- OURDIGHA and TADLA-AZILA, including the provinces of SAFI, EL JADIDA, EL YOUSSOUFIA, SETTAT, BERRCHIDE, KHOURIBGA, BEN SLIMANE, FKIH BEN

SALEH, TADLA & BENI MELLAL. The biomass potential from DOUKKALA-ABDA region is about 5, 6 million tons per year. This biomass potential can theoretically generate more than 0,14 Mtep of biogas energy per year. The biomass potential of CHAOUIA-OURDIGHA region is about 5,1 million tons per year. This biomass potential can theoretically generate 0,13 Mtep of biogas energy per year. The biomass potential of TADLA-AZILA region is about 5,8 million tons per year. This biomass potential can theoretically generate 0,19 Mtep of biogas energy per year. With a total of 0,46Mtep per year such potential can encourage business executives and investors to establish a biogas network in these regions and; consequently, contribute to the self-sufficiency of energy in Morocco

Keywords- biomass; biogas; energy potential; biogas; renewable energies; waste;

  1. INTRODUCTION

    In rural areas, the lack of energy resources becomes a central concern for each country. It is a crisis that involves a considerable human workforce [1]. More than 40% of the

    population lives in rural areas and whose primary needs keep increasing: cooking, water pumping and the home heating. The problematic and stakes related to energy in rural areas prompt public and private actors to a profound reflection on the vectors of change that can improve the living conditions of rural populations. Methanisation technology was introduced to Morocco in the early eighties by the intermediate of pilot digestor of research and development or demonstration projects. More than 350 digestors have been made to contribute to solving energy problems in rural areas. The volume produced by the digestors ranged between 10 and 180 m3. Approximately 45% of existing fermenters (digestors) do not work properly mainly due to technical problems: (1) poor construction, (2) lack of maintenance, (3)operators carelessness, (4) lack trained users (5) bad composition of the introduced mixture [2]. The methanisation is a technique of energy converting of biomass which is considered an important process in the concept of sustainable development. It allows the recovering of organic resources such as: organic waste, agricultural waste, sewage sludge, manure. In order to obtain the biogas (precisely methane) the gas has a high calorific ability that can be used for heating, generating electricity, cooking, or even turned into biofuel, replacing thus fossil energy sources [3] [4] . This current work suggests a the development of this technology for the treatment of and the recovering of rural waste. In the beginning, we carried out a meticulous evaluation of energy potentials of biomass resources existing in regions known for agricultural activities, namely the regions DOUKKALA- ABDA, CHAOUIA Ourdigha-and-TADLA AZILAL,

    counting provinces: SAFI, El Jadida, EL YOUSSOUFIA, SETTAT, BERRCHIDE, KHOURIBGA, BEN SLIMANE,

    fkih BEN SALEH, TADLA and Beni Mellal. In the second

    step of this work, we will proceed with the construction of biogas plants installation in order to develop its operating parameters and optimize its productivity. We chose the region of Khouribga as pilot project then the process will includes all Moroccan countryside [5].

  2. BIOMASS AND BIOMETHANISATION TECHNOLOGY

    1. Biomass

      Biomass is a set of organic substance coming from animals or plants; it is the biodegradable fraction of products, wastes and farming residues (animals and plants substances), of sylviculture and related industries, residues and vegetable waste of industry. We distinguish four main constituents: [6] biomass made up of wood and green waste, glucide/sugar biomass such as cereals, sugar beet, sugar cane, oil producing biomass, rich in lipid/fat like colza, sunflower [7], oil palm tree etc a fourth axis is that of the recovery of energy (in the form of biogas) in the domestic and industrial waste treatment process [8].

    2. Biomethanization

      Biomethanization or anaerobic digestion of organic substances is not a new concept. This phenomenon happens when micro organisms decompose the organic substance in anaerobic mode. That is to say, without oxygen and in specific conditions such as the temperature and the pH. These reactions occur naturally in the environment. The marshes and landfills which generate biogas are a good example. Biomethanization technologies tend only to reproduce these reactions under optimal conditions [9].

      The byproducts of anaerobic digestion are of course the biogas, as well as the digestat. The biogas consists of 50 to 75% of methane, 25 to 45% of carbon dioxide and of some minor gas (less than 2%), such as hydrogen sulphide [10] (H2S), hydrogen, water, oxygen, ammonic (NH3) and nitrogen. Typically the production of methane is at almost 60%. The biogas can be used to produce heat, electrical energy as it can be injected in a network of natural gas or even be liquefied. The biomethanezation also produces the digestat, a sewage sludge which possesses a solid and liquid phase [11] [12]. The solid phase can be exploited through manuring on agricultural land or it can be transformed into compost. Regarding the liquid phase, it can also be spread on fields as fertilizer or it can be dealt to reduce the charges in organic substance and conventionally be injected in the sewage networks. The digestat contains more or less the same quantity of fertilizers as the intrants, such as azote, phosphor and potassium [13].

      Figure 1. Representation of biomethanization benefits

    3. Design and construction of digester

      The volume of the digestor essentially depends on retention time (RT) and the quantity of the available substrate. [14]. This quantity must be composed of digested matter and water. The cow dung requires a substance / water mixture with a 1:1 ratio [15].

      The retention time (RT)) indicates the time spent by the waste material in the digestor. It is noticeably shorter than the total time required for the complete digestion of feed material [16].

      The digester volume (Vd) is calculated according to the formula:

      Vd (l) = Sd (l/days)* RT (days) (1) Vd= 0,95*Vc (2)

      Vc (l) = [Sd (l/days)* T (days)] / 0,95 (3)

      (Sd) is a daily fermentation slurry arisings,

      (Vc) is the volume of construction of the digestor,

      (Vd) represents 95% of construction volume (Vc), [17].

      On a farm in the region of Khouribga, following the approved model specifications by the national project biogas development such as described in a handbook, [18] we built a digestor with a capacity of 20 m3 dome (Figure I). Fitted with an irrigation system to ensure a smooth mixture and drain out of gas, and a system of temperature monitoring. Biogas is quantified with a pressure gauge [19]. Biogas product contains water steam which is removed via a pet cock installed at the lowest point of the pipe. The biogas is then purified by removing the H2S gas through a filter composed of iron oxide. The purified biogas supplies the gas engine that is used to start water pumps for agricultural use [20].

      Figure 2. Construction of digester by dome in the region of khouribga

  3. REGIONS

    A comprehensive study of the regions covered has proven importance in what follows; we identify each region with its riches,

      1. Doukkala-abda region

        DOUKKALA-ABDA Region covers an area of 13285 Km2, a 1, 9% of the total area of the kingdom. This region is delimited in the north by Settat province, and in the east by Kalaa Sraghna, in the south and south east by Marrakech city and in the south west by Essaouira province. It enjoys a important geostrategic location with a maritime façade of 350 Km on the Atlantic Ocean.

        The DOUKKALA ABDA region includes the province of Safi, youssoufia, Sidi Bennour and El Jadida with 2 046 000 inhabitants in which 56% are subject to El Jadida province against 44% for Safi province.

        The DOUKKALA-ABDA region enjoys significant economic potentials and likely to launch its economic and social development. These potentials are capable of a modern agriculture, in fact, the DOUKKALA ABDA region has 12,7% of cows, 8,9% of ovines and 1% of gouts, compared to the nation as a whole[21].

        Fishing occupies a pro-eminent position in the regional economy. In addition to that, naval construction activity set up in Safi has ranked this city first world capital in sardines.

      2. Tadla-azilal region

        Situated in the centre of Morocco, between two lands of phosphate and the Atlas in an area of 17125 km2, TADLA AZILAL region is limited by kalaa Sraghna province and al Hawez to the west, by Khouribga and Settat to the north, Errachidia and Khenifra to the east and Ourzazat to the south.

        TADLA-AZILAL region comprises currently 3 provinces: Beni Mellal, Fkih ben saleh and Azilal.

        The TADLA-AZILAL population reaches 1516200 inhabitants approximately 4, 6% of the country total population [22].

        Agriculture is the dominant activity in the region, it is one of the pillars of Moroccan economy, with agricultural area (SFA) which reaches 259600 ha, representing 80% of the whole land.

        Irrigated lands reach 126000 ha. in the region, 49% of (SFA). We notice that on the national level almost 74, 9% of the rural population was involved in this sector and thus taking part in the local market sufficiency by means of food products: cereals, sugar, meat, milk [23].

      3. Chaouia ourdigha region

    This region is situated between the Casablanca Marrakech poles, delimited in the east by the Atlantic Ocean.

    The region has a surface area of 16751 Km2, that is to say 2, 4% of the total area of the kingdom. This region is delimited by Rabat to the north, and Sale Zemmour Zair Province to the north west, Casablanca to the North east, TADLA AZILAL region to the west, Marrakech province to the South, and DOUKKALA ABDA region to the South east.

    CHAOUIA OURDIGHA region comprises nowadays four provinces: Settat, Berrechid, Benslimane and Khouribga. It is considered among the most well-known agricultural regions in Morocco, known for their cereal production and breeding. Farming represents the dominant activity in the region with a utilized agricultural area of 933009 ha, 63% of the land is situated in Settat province, 23% in Khouribga province and 14% in the province of BenSlimane [24].

  4. METHOD

    The aim of this work focuses on testing the energy potential of biomass resources existing in the most well- known agricultural regions in Morocco [25], namely DOUKKALA-ABDA, CHAOUIA-OURDIGHA and

    TADLA-AZILA. This study will serve as a basis in decision making on development of renewable energies in the country.

    The determination of energy potential in biogas is carried out in two stages:

    1. Determination of quantities of wastes and residues in the regions under study

      For this, we made reference to statistics collected by regional agricultural department from different establishments: the monograph of regions, the yearbook of statistics published by the high commission [26].

      The study takes into account animals excreta (bovine, ovine race, goat) which can be recoverable for metanization, cereal residue, leguminous plants, market gardening, agro- industrial residue, the organic fraction of household refuse [27] [28].

    2. Calculation of energy potential and potentail in biofertilizers

    The calculation is carried out by applying to the quantities of raw materials a specific biogas yield. So it is expressed in KWH of energy under the form of biogas per ton of fresh substance [29].

  5. RESULTS AND DISCUSSION

region

Agricultural Residues (MWh)

Manure (MWh)

Organic waste and Sewage sludge

(MWh)

Fish and Slaughterhous waste (MWh)

Doukkala- Abda

54462,3

1473541

53409,1

17586,1

Chaouia- Ourdigha

14224,05

1474281,6

63789,8

4425,8

Tadla – Azilal

29650,5

2151762,6

49208,8

2040,6

Total

98336,85

5099585,2

166407,7

24052,5

Many studies focus on the determination of the pollution potential of organic waste; however they may have great value, by recycling and using them as a feedstock.

Our goal in this work is the evaluation and establishment of appropriate to take into account in determining the energy potential of waste [30].

The following chart shows a summary of the quantities of waste.

Organic waste and Sewage sludge (MWh)

Fish and

Slaughterhous waste (MWh)

96.38%

TABLE I. THE QUANTITIES OF THE LISTED WASTE OF THE REGION

TABLE II. PRESENT THEORIC ENERGETIC POTENTIAL OF ORGANIC WASTE FOR METHANIZATION.

regions

Agricultural Residues (T/year)

Mobilized Manures (T/ year)

Sludge Sewage

Organic F Municipal

waste(T/ year)

Slaughter- hous

waste(T/ year)

Doukkala-

Abda

2425181

2988927

2671

220968

4098,5

Chaouia-

Ourdigha

1826844,3

2990429,1

2158

265980

12418,4

Tadla-

Azilal

1124231,4

4364630

1584

205344

5725,6

Total of

regions

5376256,7

10343986,1

6413

692292

22242,5

0.09%

2.20% 1.33%

Agricultural Residues (MWh)

Manure (MWh)

ACKNOWLEDGMENT

The authors thank the staff of the Regional offices for Agricultural of DOUKKALA-ABDA, CHAOUA OURDIGHA and TADLA-AZILA for all informations and

the staff of construction for their contribution in built of digestor and implementation of analysis.

REFERENCES

  1. Document M.Wauthlet, "Development of biogas technology in Morocco," Case Study, Moroccan-German Cooperative, GTZ GmbH, Special Energy Programme, p. 72-76, 1990

  2. Elena Comino, Maurizio Rosso, Vincenzo Riggio "Development of a pilot scale anaerobic digester for biogas generation from cow manure and whey mix" Bioresource Technology, Pages 5072-5078, Volume 100, Issue 21, November 2009, ISSN: 09608524

  3. Dr. Abdelali Dakkina "exprerience and potential biogas production in Morocco," published by ADEREE, Awareness and planning on biogas, 2012

  4. A. Saidi and B. Abada, "Anaerobic digestion: a solution for sustainable development", Journal of Renewable Energies CER'07 Oujda, 2007, pp. 31-35.

  5. Joost Lauwers, Lise calls, Ian P. Thompson, Jan Degrève, Jan F. Van Impe, Raf Dewil "Mathematical modeling of anaerobic digestion of biomass and waste: Power and limitations" Progress in Energy and Combustion Science, Vol.39, pp.383 402, August 2013.

  6. Elena Comino, Vincenzo A. Riggio, Maurizio Rosso "Biogas Production by anaerobic co-digestion of cattle slurry and cheese whey" Bioresource Technology, Vol. 114 , pp. 46-53,June 2012.

  7. Carlos García-Dieguez, Olivier Bernard, Enrique Roca "Anaerobic Digestion Reducing the Model No. 1 for icts applying to an industrial wastewater treatment plant treating Display winery wastewater effluent" Bioresource Technology, Vol. 132, pp. 244-253, March 2013.

  8. Wei Qiao, Kazuyuki Takayanagi, Mohammad Shofie, Qigui Niu Han Qing Yu, Yu-You Li "Thermophilic anaerobic digestion of coffee grounds with and without waste activated sludge as co-substrate using a submerged AnMBR System amendments and membrane performance "Bioresource Technology, Vol.150, pp. 249-258, December 2013.

  9. N. Laskri, O. Hamdaoui and N. Nedjah, "Treatment and recovery of waste by anaerobic digestion: biogas production", Journal of Renewable Energies CER'07 Oujda, 2007, pp. 23- 26.

  10. Ludwig Sasse, "Biogas Plants Development technologies "- GATE in: German. Agency for Technical Cooperation (GTZ), 1988.

  11. Carlos García-Dieguez, Olivier Bernard, Enrique Roca "Anaerobic Digestion Reducing the Model No. 1 for icts applying to an industrial wastewater treatment plant treating Display winery wastewater effluent" Bioresource Technology,

    Vol. 132, pp. 244-253, March 2013

  12. Andrew J. White, Donald W. Kirk, John W. Graydon "Analysis of small-scale biogas utilization systems on Ontario cattle farms" Renewable Energy, Vol. 36, pp. 1019-1025, March 2011.

  13. Martina Poeschl, Shane Ward, Philip Owende "Prospects for expanded utilization of biogas in Germany" Renewable and Sustainable Energy Reviews, Volume 14 , pp. 1782-1797, September 2010.

  14. CDER-GTZ (Centre for Development of Renewable Energy and Gesellschaft für technische Zusammenarbeit), construction of biogas plant handbook, 1990 .

  15. M. E Afilal, N. Belkhadir, H. Daoudi, O. Elasri "Methanic fermentation of different organic substrates" J. Mater Environ. Sci 4 (1), pp 11-16, 2013.

  16. Matias Vanotti, Ariel Szogi, Ma Pilar Bernal, José Martinez "Livestock waste treatment systems of the future: A challenge to environmental quality, food safety, and sustainability. OECD Workshop "Bioresource Technology, Vol. 100, pp. 5371-5373, November 2009.

  17. Patricia D. Millner "bioaerosols Associated with Animal Production operations" Bioresource Technology, Vol. 100, 2009, pp. 5379-5385.

  18. Konrad Koch, Manfred Lübken, Tito Gehring, Marc Wichern, Harald Horn "Biogas from grass silage – Measurements and modeling with ADM1" Bioresource Technology, Vol. 101, pp. 8158-8165, November 2010.

  19. Piotr Biernacki, Steinigeweg Sven Axel Borchert, Frank Uhlenhut, Axel Brehm "Application of Anaerobic Digestion Model No. 1 for Describing an existing biogas power plant" Biomass and Bioenergy, Vol. 59, pp. 441-447, December 2013.

  20. W. Martens, R. Böhm "Overview of the Ability of different treatment methods for liquid and solid manure to inactivate pathogens" Bioresource Technology, Vol. 100, pp. 5374-5378,

    November 2009

  21. Report, 'Monograph Doukkala-Abda Region, published by the Office of Planning, Kingdom of Morocco, 2010.

  22. Report, 'Monograph Region TADLA-AZILAL, published by the Office of Planning, Kingdom of Morocco, 2010.

  23. Report, 'Statistical Yearbook of the Tadla-AZILAL, published by the Office of Planning, Kingdom of Morocco, 2012.

  24. Report, 'Monograph Region Chaouia-Ourdigua, published by the Office of Planning, Kingdom of Morocco, 2010.

  25. V. Lemesle and J.L. Gouzé. Hybrid bounded error observers for uncertain bioreactor models Bioprocess Biosystem, 2005, pp. 311318.

  26. T. Jiang, S. Myngheer, D.J.W. De Pauw, H. Spanjers, I. Nopens, M.D. Kennedy, G. Amy, Vanrolleghem. Modelling the production and degradation of soluble microbial products (smp) in membrane bioreactors (mbr), water research, 2008, pp. 49554964.

  27. G. Lettinga and L.W.H. Hulshoff Pol. Uasb-process design for various types of wastewaters. Water Science and Technology, 24(8) :87107, 1991.

  28. Moletta R, « methanization », Editions Tec et Doc, Publication Lavoisier, 2008.

  29. S. Fiore, B. Ruffino, F. Marchese, D. Novarino and M.C. Zanetti: Preliminary Evaluation of the Potential Biogas Production of Food-Processing Industrial Wastes American Journal of Environmental Sciences 8 (3): 291-296, 2012

  30. Report, PRRS, 'Valuation of organic waste by anaerobic bio in the Oujda region (MOROCCO)', Version 1.1, No. 09-3103-TB, 2009.

Leave a Reply