2005
DOI: 10.2166/wst.2005.0557
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Application of the IWA Anaerobic Digestion Model (ADM1) for simulating full-scale anaerobic sewage sludge digestion

Abstract: A steady-state implementation of the IWA Anaerobic Digestion Model No. 1 (ADM1) has been applied to the anaerobic digesters in two wastewater treatment plants. The two plants have a wastewater treatment capacity of 76,000 and 820,000 m3/day, respectively, with approximately 12 and 205 dry metric tons sludge fed to digesters per day. The main purpose of this study is to compare the ADM1 model results with full-scale anaerobic digestion performance. For both plants, the prediction of the steady-state ADM1 implem… Show more

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Cited by 40 publications
(16 citation statements)
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“…Usually it is a challenge to estimate the percentage of these parameters since most of the time sludge COD is not reported (Parker 2005). However, the IWA group does not provide clear information on how the fraction of carbohydrates, proteins and lipids can be divided for MS (Shang et al 2005). Sludge composition based on COD, may contain 35% inert, 20% proteins, 20% carbohydrates, and 25% lipids.…”
Section: Model Descriptionmentioning
confidence: 99%
“…Usually it is a challenge to estimate the percentage of these parameters since most of the time sludge COD is not reported (Parker 2005). However, the IWA group does not provide clear information on how the fraction of carbohydrates, proteins and lipids can be divided for MS (Shang et al 2005). Sludge composition based on COD, may contain 35% inert, 20% proteins, 20% carbohydrates, and 25% lipids.…”
Section: Model Descriptionmentioning
confidence: 99%
“…At any rate, the differential equations of the model are non-linear and it is complicated to optimize all the model's coefficient to predict well the process of the anaerobic digestion. Several studies have reported disagreement between the model and the observed data for continuous and semi continuous stirred reactors ( (Fezzani and Cheikh 2008;Parker 2005;Razaviarani and Buchanan 2015;Shang et al 2005).…”
Section: Resultsmentioning
confidence: 99%
“…These inconsistencies between simulations and experimental results were due to the identification difficulties and validity of all the most sensitive ADM1 parameters for different OLRs which were the major drawbacks for ADM1 applications. In fact, ADM1 differential equations were non linear equations and it was complicated to optimise all the sensitive parameters by adjusting ADM1 outputs with all main experimental results simultaneously without making some discrepancy by any parameters identification method as mentioned by previous researchers that have implemented the ADM1 with other wastes such as: Parker Wayne [11], who found several discrepancies between simulations and measurements; Shang et al [12] who found good agreement between ADM1 output and measured data but with a 10% over prediction of gas flow. Furthermore, some parameters such as gas transfer coefficient may correlate with reactor configuration [10] and other parameters such as hydrolysis constants may correlate with feed concentrations and HRTs but this dependency was not taken into account by the ADM1.…”
Section: Discussionmentioning
confidence: 99%
“…Besides, it can be used either as a common basis for further development or as a common platform for dynamic simulation for a variety of anaerobic processes. Afterwards, many implementations of this powerful tool have been tested and proved their success in simulating the anaerobic digestion of several organic wastes such as: industrial wastewaters [9]; sludge from wastewater treatment plants [10,11]; sewage sludge [12]; black water from vacuum toilet [13]; olive mill solid wastes [14]. However, the ADM1 has never been applied by any researcher to simulate the anaerobic digestion of OMW either alone nor mixed with other solid wastes and mainly OMSW.…”
Section: Introductionmentioning
confidence: 99%