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Pollution of water sources by produced landfill leachate [18] 

Pollution of water sources by produced landfill leachate [18] 

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Conference Paper
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Abstract: Presently, estimated disposed municipal solid waste at Erbil landfill site (ELS) exceeded 700 tons/day. ELS is considered as Level 2 (sanitary landfill with daily cover) and anaerobic landfill. Based on the age of ELS, it is in the methane formation phase. Produced leachate from ELS regards as mature leachate. The values of parameters suc...

Contexts in source publication

Context 1
... raw leachate is disposed to the natural environment without treatment, it could become a main source of water pollution because it can percolate through soils and sub- soils, causing high contamination of the receiving water ( Figure 5). The treatment of potentially hazardous constituents of leachate prior to discharge is a legal requirement to avoid contamination of water sources to prevent both acute and chronic toxicity [15][16][17][18]. ...
Context 2
... raw leachate is disposed to the natural environment without treatment, it could become a main source of water pollution because it can percolate through soils and sub- soils, causing high contamination of the receiving water ( Figure 5). The treatment of potentially hazardous constituents of leachate prior to discharge is a legal requirement to avoid contamination of water sources to prevent both acute and chronic toxicity [15][16][17][18]. Due to lack of the suitable design for ELS, the produced raw landfill leachate can not be collected and monitored. Thus, it mixes with the natural environment. Of course, mixing untreated landfill leachtae from ELS with the natural environment causes threaten to the natural environment (particularly water sources). C. Potential Treatment Techniques for Produced Leachate from ELS To reduce the negative effect of discharged raw leachate on the natural environment, several methods of water and wastewater treatment have been used. The processes for the treatment of landfill leachate could be classified as physical, chemical, and biological [1,19]. Generally, the methods are applied as an integrated system because it is not easy to obtain the satisfied treatment efficiency by using only one technique. Normal treatment techniques commonly need multistage process treatment. To set up adequate treatment process for removal of pollutants from leachates, various physicochemical and biological techniques and/or their different combinations could be ...

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... Schematic diagram of a landfill(Aziz 2013). ...
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... As the landfill wastes reach the third phase, that is, the final anaerobic phase in which methanogenic bacteria typically come last, the pH starts to increase as acids are consumed and converted mainly into methane and carbon dioxide. In this phase, the biodegradability of the organic matter plumps resulting in old leachate containing more refractory and xenobiotic organic matter such as humic-like substances and pesticides and inorganic compounds such as ammonia than the young leachate [8]. ...
... Technical landfills has been discovered to be the utmost economic MSW disposal method when equated with other systems of disposal, such as thermal and composting [1][2][3]. But the produced landfill leachate and gas emissions are common shortcomings of the MSW [4][5]. Without scientific solution, disposed landfill leachate and emitted gas from Erbil Landfill Site (ELS) cause pollution of the environment. ...
... The current work presented the ELS problems, especially mixed MSW without separation and emitted gas, and attainment of income and energy from MSW at ELS. The data were obtained from literature and Presidency of Erbil Municipality [2][3][4][5][6][8][9]. To see the risks directly and to get extra information, site visit were carried out to ELS in June and November 2017. ...
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... To reduce the negative effect of discharged fresh leachate on the natural environment, several methods of water and wastewater treatment have been used. The processes for the treatment of landfill leachate could be classified as physical, chemical, and biological (Renou et al. 2008;Abbas et al. 2009;Aziz et al., 2011aAziz et al., , 2011cAziz, 2013 andAziz et al., 2014). Generally, the methods are applied as an integrated system because it is not easy to obtain the satisfied treatment efficiency by using only one technique. ...
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... Generally, biological treatment methods are effective for young or freshly (<5 years) produced leachate, but are ineffective for leachate from older landfills (>10 years old). In contrast, physical-chemical techniques which are not favoured for young leachate treatment are advised for older leachate treatment (Aziz, 2013 andAziz et al., 2014).Additionally, recently published works revealed that combination of physical-chemical and biological methods (such as adsorption and aerobic processes) is efficient in removal of hazardous contaminants from mature landfill leachate (Ghafari et al., 2009;Aziz et al., 2011a;2011b;Aziz, 2013andMojiri et al., 2014a. Raw and treated landfill leachate by using adsorbent augmented SBR process are illustrated in Figure 10. Figure 11 shows the technologies to treat landfill leachate. ...
Chapter
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... The generation of highly contaminated leachate that can seep into the ground and contaminate the ground water, surface water, and soil is principally a main negative aspect associated to municipal sanitary landfill disposal method (Bashir et al., 2012. Additionally, leachate is liquid contain large amounts of organic compounds measured as chemical oxygen demand (COD), biochemical oxygen demand (BOD 5 ), ammoniacal nitrogen (NH 3 -N), halogenated hydrocarbons suspended solid, significant concentration of heavy metals, and inorganic salts (Aziz, 2013; Bashir et al., 2012; Aziz et al., 2010; Uygur and Kargi, 2004). If not treated and disposed safely, landfill leachate could be a major source of water contamination because it could percolate through soil and subsoil, causing high pollution to receiving waters. ...
... The phases of leachate are transition (0 -5 years), acid-formation (5 - 10 years), methane fermentation (15 -20 years), and final maturation (greater than 20 years). The age of the landfill is one of the most important factors that affect leachate characteristics (Kostova, 2006; Aziz, 2013) The levels of some leachate characteristics such ...
... SBR augmented powdered activated carbon (PAC- SBR) showed higher removal efficiencies of NH 3 -N, COD, colour, and TDS when compared with normal SBR. Furthermore, PAC-SBR improved sludge volume index (SVI) (Aziz et al. 2011; 2013) ...
Data
Production of raw leachate from landfills regards as shortcoming for the sanitary landfills. Unprocessed landfill leachate requires treatment prior disposal to the natural environment. In this work, leachate channeling, biological, and physical-chemical treatment processes for treatment of formed landfill leachate were presented in details. Definite treatment processes were resulted in high removal of pollutants such as ammonia (NH 3 -N), chemical oxygen demand (COD), biochemical oxygen demand (BOD 5), phenols, color etc. Practically, age of produced leachate have influence on the treatment systems. Efficient treatment methods were explained for fresh, medium, and stabilized landfill leachates.
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... The phases of leachate are transition (0 -5 years), acid-formation (5 - 10 years), methane fermentation (15 -20 years), and final maturation (greater than 20 years). The age of the landfill is one of the most important factors that affect leachate characteristics (Kostova, 2006; Aziz, 2013) The levels of some leachate characteristics such ...
... SBR augmented powdered activated carbon (PAC- SBR) showed higher removal efficiencies of NH 3 -N, COD, colour, and TDS when compared with normal SBR. Furthermore, PAC-SBR improved sludge volume index (SVI) (Aziz et al. 2011; 2013) ...
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