Z. Kapelan
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15 records found
1
The thesis aims to develop and validate a new 1D model, based on the widely used SWMM solver, capable of describing the air-water interaction during pipe-filling events in IWS systems. The specific objectives of this research are: i) to identify, understand and characterise the most relevant air pocket related phenomena during pipe-filling events in single pipes and looped networks; ii) to learn how to incorporate the air pressurisation in SWMM solver as well as iii) the different mechanisms associated with the air pocket creation; iv) to understand the model's uncertainties related to these phenomena; and v) to test the developed model in a real-life network.
To accomplish objective i) and to contribute to objectives ii) - iv), an extensive experimental data collection program is developed to understand the phenomena related to the air pocket creation during the pipe-filling event. Collected data include time series of pressure and flow rate and video recordings of entrapped air pockets, for different pipe configurations and aeration conditions. Three pipe configurations are tested: a straight horizontal pipe, a single pipe with a high point and a single-loop pipe network. Three aeration conditions end are tested: no air release, restricted and unrestricted air release.
Several novel numerical developments are gradually implemented to fulfil key objectives ii) - iv). The first is the modification introduced in the existing SWMM hydraulic solver to incorporate the air phase. A conventional air accumulator model is implemented and coupled with SWMM flow calculations. Experimental data collected during the rapid filling of a single horizontal pipe for the three referred aeration conditions are used for model calibration and validation (fulfilling objective ii). Results show that the improved SWMM, AirSWMM(v1.0), describes better the effect of air behaviour during pipe-filling events than the original SWMM when using the EXTRAN surcharge method.
The AirSWMM(v1.0) model is improved to locate and quantify entrapped air pockets created during the pipe-filling events in single undulating pipe systems. Measurements are collected and video recordings are carried out to assess air pocket volumes for the three referred air release conditions. The stochastic nature of air pocket creation results in a range of air volumes predicted for the same aeration conditions. The new version of the model developed, AirSWMM(v2.0), is capable of simulating the air pocket creation, transport and entrainment (air and water mixing process). The stochastic nature of air pocket formation can be numerically simulated by conducting multiple runs of the new solver with different air entrainment ratios. The obtained numerical results show that AirSWMM(v2.0) can accurately locate and approximately quantify the entrapped air pocket volumes. These developments contribute to objective iii).
The AirSWMM(v2.0) model is further tested and validated using experimental data from a single-loop network laboratory setup. Experimental data consisting of pressure-head at multiple locations and video recordings of air entrapment for two high point locations and different nodal elevations, under three aeration conditions, are used. Experimental tests show that air entrapment occurs not only at the high point but along the pipe network, creating air pockets with elongated shapes and larger volumes than for single pipe systems. AirSWWM(v2.0) model results for the looped pipe network demonstrate that this model can correctly locate large air pockets with a tendency to underestimate their volumes. These developments contribute to objective iv).
The AirSWWM(v2.0) model is also tested using a case study of a real-life network published in the literature to assess the accuracy of predicted locations and volumes of the air pockets created during a pipe-filling event. For this purpose, pressure-driven analysis is implemented to better simulate the nodal demands, leading to AirSWMM(v2.1), since this feature was not originally included in SWMM. Results show that pressure-heads predicted by AirSWMM(v2.1) compare well with field data when constant spatial discretisation is used, provided the Courant number is close to 0.15. The recommendations from international guidelines for the location of air release devices (from the American Water Works Association and Deltares) are compared to the predicted air pocket locations. The locations of the estimated air pockets agree with those from the international guidelines for air valve installation. However, these locations only represent part of the air valves needed, those that are necessary for releasing entrapped air during the pipe-filling events, not accounting for other air valves important for pipe failure or conservative design purposes. These developments contribute to objective v).
Further research on AirSWMM should focus on assessing the spatial discretisation that corresponds to the best compromise between accuracy and computational effort to describe the air pocket dynamics in real-life networks. Additional numerical analyses should assess if the developed methodologies can be incorporated into the Preissmann slot pressurisation scheme. More experimental tests are needed to better quantify the air entrainment in piped flows and to analyse the effect of two-phase flows on leakage rate. Further field tests, collecting high-frequency pressure head data, should be carried out during pipe-filling events to validate the developed models. ...
The thesis aims to develop and validate a new 1D model, based on the widely used SWMM solver, capable of describing the air-water interaction during pipe-filling events in IWS systems. The specific objectives of this research are: i) to identify, understand and characterise the most relevant air pocket related phenomena during pipe-filling events in single pipes and looped networks; ii) to learn how to incorporate the air pressurisation in SWMM solver as well as iii) the different mechanisms associated with the air pocket creation; iv) to understand the model's uncertainties related to these phenomena; and v) to test the developed model in a real-life network.
To accomplish objective i) and to contribute to objectives ii) - iv), an extensive experimental data collection program is developed to understand the phenomena related to the air pocket creation during the pipe-filling event. Collected data include time series of pressure and flow rate and video recordings of entrapped air pockets, for different pipe configurations and aeration conditions. Three pipe configurations are tested: a straight horizontal pipe, a single pipe with a high point and a single-loop pipe network. Three aeration conditions end are tested: no air release, restricted and unrestricted air release.
Several novel numerical developments are gradually implemented to fulfil key objectives ii) - iv). The first is the modification introduced in the existing SWMM hydraulic solver to incorporate the air phase. A conventional air accumulator model is implemented and coupled with SWMM flow calculations. Experimental data collected during the rapid filling of a single horizontal pipe for the three referred aeration conditions are used for model calibration and validation (fulfilling objective ii). Results show that the improved SWMM, AirSWMM(v1.0), describes better the effect of air behaviour during pipe-filling events than the original SWMM when using the EXTRAN surcharge method.
The AirSWMM(v1.0) model is improved to locate and quantify entrapped air pockets created during the pipe-filling events in single undulating pipe systems. Measurements are collected and video recordings are carried out to assess air pocket volumes for the three referred air release conditions. The stochastic nature of air pocket creation results in a range of air volumes predicted for the same aeration conditions. The new version of the model developed, AirSWMM(v2.0), is capable of simulating the air pocket creation, transport and entrainment (air and water mixing process). The stochastic nature of air pocket formation can be numerically simulated by conducting multiple runs of the new solver with different air entrainment ratios. The obtained numerical results show that AirSWMM(v2.0) can accurately locate and approximately quantify the entrapped air pocket volumes. These developments contribute to objective iii).
The AirSWMM(v2.0) model is further tested and validated using experimental data from a single-loop network laboratory setup. Experimental data consisting of pressure-head at multiple locations and video recordings of air entrapment for two high point locations and different nodal elevations, under three aeration conditions, are used. Experimental tests show that air entrapment occurs not only at the high point but along the pipe network, creating air pockets with elongated shapes and larger volumes than for single pipe systems. AirSWWM(v2.0) model results for the looped pipe network demonstrate that this model can correctly locate large air pockets with a tendency to underestimate their volumes. These developments contribute to objective iv).
The AirSWWM(v2.0) model is also tested using a case study of a real-life network published in the literature to assess the accuracy of predicted locations and volumes of the air pockets created during a pipe-filling event. For this purpose, pressure-driven analysis is implemented to better simulate the nodal demands, leading to AirSWMM(v2.1), since this feature was not originally included in SWMM. Results show that pressure-heads predicted by AirSWMM(v2.1) compare well with field data when constant spatial discretisation is used, provided the Courant number is close to 0.15. The recommendations from international guidelines for the location of air release devices (from the American Water Works Association and Deltares) are compared to the predicted air pocket locations. The locations of the estimated air pockets agree with those from the international guidelines for air valve installation. However, these locations only represent part of the air valves needed, those that are necessary for releasing entrapped air during the pipe-filling events, not accounting for other air valves important for pipe failure or conservative design purposes. These developments contribute to objective v).
Further research on AirSWMM should focus on assessing the spatial discretisation that corresponds to the best compromise between accuracy and computational effort to describe the air pocket dynamics in real-life networks. Additional numerical analyses should assess if the developed methodologies can be incorporated into the Preissmann slot pressurisation scheme. More experimental tests are needed to better quantify the air entrainment in piped flows and to analyse the effect of two-phase flows on leakage rate. Further field tests, collecting high-frequency pressure head data, should be carried out during pipe-filling events to validate the developed models.
During contamination events in the DWDN, water utilities need to act quickly, make informed decisions, assess the threat, and effectively mitigate the event. The central objective of the study of this thesis was to generate knowledge to help address the growing challenge of waterborne pathogen contamination in DWDNs and develop applications that can enhance decision-making and immediate actions in such emergencies. Tools and methodologies were developed and evaluated focusing on two main pillars. The first pillar involves understanding the event based on historical knowledge. Innovative approaches were developed and assessed for Artificial Intelligence-based information extraction and question-answering using scientific publications, enabling rapid access to up-to-date pathogen characteristics, historical information on contamination events, and control actions. The second pillar focuses on predicting and managing the specific contamination event in real-time. Advanced modeling tools were created to simulate contamination events in DWDNs, providing realistic representations of hydraulics and water quality dynamics, predicted health impacts, and support for real-time decision-making during emergencies.
Chapter 2 describes the development of an Artificial Intelligence (AI)-based model that extracts specific pathogen information from the scientific literature. By leveraging Natural Language Processing (NLP) and Deep Learning (DL) techniques, the study evaluated the feasibility and performance of an Information Extraction model to extract both qualitative and quantitative information from scientific publications about the waterborne pathogen Legionella. For the development of the model, a combination of supervised and rule-based techniques was adopted. The evaluation metrics showed a satisfactory performance for extraction of both qualitative and quantitative information with an overall F-score of 85% and 95% for the supervised and rule-based technique respectively. The model was also compared with a human extraction, returning similar results and indicating that the extracted information is of high quality. The results showed that the model can be used to rapidly extract critical information from text documents and be a useful tool for water utilities, enabling faster and more informed decision-making during the early stages of contamination.
Chapter 3 systematically assesses the performance of various open-source Large Language Models (LLM), including Llama 2, Mistral, and Gemma (and their variations) in a question-answering task related to pathogen contamination events of drinking water. The evaluation metrics included Precision, Recall, F1 score, Automated Accuracy, and Empty Score. The model with the highest performance on a set of 23 questions using 188 scientific publications was then manually evaluated by a human (Human Evaluation). The results showed that all models performed reasonably well with an average F1 score ranging from 81% to 87%. After considering all the evaluation metrics, the Llama 2 model was the most reliable model with an average Automated Accuracy of 86%. However, the hallucination effect of Llama 2 was evident. The Gemma model had a lower Automated Accuracy score but was less prone to hallucination. The Human Evaluation showed that the Llama 2 model delivered correct answers when the questions were clear and straightforward. However, when the question required further interpretation, the model often struggled. Overall, the study demonstrated that the use of LLMs in automated information extraction tasks show great potential for time-critical applications, such as processing large volumes of (historical) data in real-time thereby making it feasible to make historical information available in near rea-time in case of emergencies.
Building on the response to a pathogen contamination event in the DWDN, Chapter 4 presents the BeWaRE benchmark testbed, a comprehensive model. This testbed went beyond the state-of-the art and integrated all current relevant knowledge on pathogen transport and fate, bulk and wall chlorine decay, fast and slow chlorine reactions with TOC, TOC degradation, stochastic water demands, hydraulic uncertainty, and individual consumption patterns to calculate pathogen exposure and infection risk following the steps of Quantitative Microbial Risk Assessment (QMRA). A large wastewater contamination in different locations in a chlorinated and non-chlorinated network was simulated using three pathogens: Campylobacter, enterovirus, and Cryptosporidium. The results of this study showed that in non-chlorinated DWDNs, the modeled wastewater contamination event led to 11-46% infection risk in the total population, depending on the contamination location, but irrespective of the selected pathogen (due to the high pathogen concentration). On the other hand, in chlorinated DWDNs, the same scenarios resulted in lower infection risk for the pathogens that are susceptible to chlorine; 0.78-2.1 % for Campylobacter and 7.8-26.6 % for enterovirus. Moreover, the enterovirus infection risk was higher, despite the concentrations in the contamination source being lower, due to the lower susceptibility to chlorine than Campylobacter. While chlorination aids mitigation, large contaminations can still lead to infections due to chlorine resistance (for Cryptosporidium) and chlorine depletion at the contamination point. Finally, the varying levels of pathogen susceptibility to chlorine, the contamination location and duration, influenced the infection risk, while the response window to reduce the health impact was short; in these scenarios 5-10 hours post-contamination. The study provided a novel approach to assessing health risks, offering critical insights for water utilities to optimize their response during emergencies.
Chapter 5 further explores the added value of using modeling tools to support decision-making during emergencies in the DWDN. This was demonstrated through PathoINVEST, an analytical tool that utilizes the BeWaRE benchmark methodology, which was presented in the previous Chapter, to support water utilities in modeling contamination events in the DWDN. A case study was conducted with the aim of comparing a traditional approach (representing the status quo of current practices of water utilities) with a model-based approach (use of real-time modeling tools) during an emergency response to a contamination event in the DWDN. The model-based approach was shown to be more efficient than the traditional approach in identifying the source of contamination (1.3 versus 3.7 hours), requiring fewer samples (4 versus 11) and resulting in lower infection risk by the time the source was identified (12% versus 20%) in this case study. Moreover, the model-based approach was more effective in finding the best valves to close in the network (as mitigation measures) since it resulted in a 3%-point infection risk reduction. However, some actions taken in the traditional approach, such as the rapid closure of valves (cutting the network in half and thus limiting further spreading) before the contamination source was identified, were critical in mitigating the contamination. Another key finding was the importance of having an up-to-date overview of valve settings in the DWDN schematization to provide reliable results on source identification since any discrepancies between the actual network and the model can lead to inaccurate infection risk estimates when using modeling tools to support decision-making. Overall, this case study showed that integrating modeling tools in the current practices of water utilities provides a robust framework for improving water contamination management and decision-making processes, thus safeguarding public health during emergencies.
A concluding viewpoint is offered in Chapter 6, which considers whether the initial research questions from Chapter 1 were successfully answered. The implications of this research for water utilities are examined, providing information on how the proposed methodologies can be (and have been) used in real-world scenarios, facilitating a faster decision-making and contributing to effective mitigation of emergencies. Finally, the perspectives and future research are discussed, emphasizing the role of AI and the advancements in modeling tools. AI has shown significant potential in enhancing situational awareness and rapid information extraction during emergencies. Water utilities should explore the integration of AI into their standard operating procedures to further enhance emergency responses and routine management. Regarding the use of modeling tools during emergencies, future research should address key gaps, such as the complex dynamics when wastewater interacts with chlorine, the competition between chlorine-reducing agents, and the validity of hydraulic modeling assumptions such as perfect mixing. Accounting for cumulative health risks (multiple pathogens) and refining dose-response models to differentiate between infection and illness probabilities can provide insights for effectively managing risks to vulnerable populations. Moreover, the incorporation of metrics like Disability-Adjusted Life Years (DALYs) into modeling efforts could enable better communication of health impacts and evaluation of mitigation strategies. Finally, Digital Twins and real-time microbial sensors are identified as transformative technologies that can provide real-time insights into network dynamics. These advancements can shift water utility management from reactive approaches to proactive, data-driven strategies, significantly enhancing public health protection, operational efficiency, and resilience.
...
During contamination events in the DWDN, water utilities need to act quickly, make informed decisions, assess the threat, and effectively mitigate the event. The central objective of the study of this thesis was to generate knowledge to help address the growing challenge of waterborne pathogen contamination in DWDNs and develop applications that can enhance decision-making and immediate actions in such emergencies. Tools and methodologies were developed and evaluated focusing on two main pillars. The first pillar involves understanding the event based on historical knowledge. Innovative approaches were developed and assessed for Artificial Intelligence-based information extraction and question-answering using scientific publications, enabling rapid access to up-to-date pathogen characteristics, historical information on contamination events, and control actions. The second pillar focuses on predicting and managing the specific contamination event in real-time. Advanced modeling tools were created to simulate contamination events in DWDNs, providing realistic representations of hydraulics and water quality dynamics, predicted health impacts, and support for real-time decision-making during emergencies.
Chapter 2 describes the development of an Artificial Intelligence (AI)-based model that extracts specific pathogen information from the scientific literature. By leveraging Natural Language Processing (NLP) and Deep Learning (DL) techniques, the study evaluated the feasibility and performance of an Information Extraction model to extract both qualitative and quantitative information from scientific publications about the waterborne pathogen Legionella. For the development of the model, a combination of supervised and rule-based techniques was adopted. The evaluation metrics showed a satisfactory performance for extraction of both qualitative and quantitative information with an overall F-score of 85% and 95% for the supervised and rule-based technique respectively. The model was also compared with a human extraction, returning similar results and indicating that the extracted information is of high quality. The results showed that the model can be used to rapidly extract critical information from text documents and be a useful tool for water utilities, enabling faster and more informed decision-making during the early stages of contamination.
Chapter 3 systematically assesses the performance of various open-source Large Language Models (LLM), including Llama 2, Mistral, and Gemma (and their variations) in a question-answering task related to pathogen contamination events of drinking water. The evaluation metrics included Precision, Recall, F1 score, Automated Accuracy, and Empty Score. The model with the highest performance on a set of 23 questions using 188 scientific publications was then manually evaluated by a human (Human Evaluation). The results showed that all models performed reasonably well with an average F1 score ranging from 81% to 87%. After considering all the evaluation metrics, the Llama 2 model was the most reliable model with an average Automated Accuracy of 86%. However, the hallucination effect of Llama 2 was evident. The Gemma model had a lower Automated Accuracy score but was less prone to hallucination. The Human Evaluation showed that the Llama 2 model delivered correct answers when the questions were clear and straightforward. However, when the question required further interpretation, the model often struggled. Overall, the study demonstrated that the use of LLMs in automated information extraction tasks show great potential for time-critical applications, such as processing large volumes of (historical) data in real-time thereby making it feasible to make historical information available in near rea-time in case of emergencies.
Building on the response to a pathogen contamination event in the DWDN, Chapter 4 presents the BeWaRE benchmark testbed, a comprehensive model. This testbed went beyond the state-of-the art and integrated all current relevant knowledge on pathogen transport and fate, bulk and wall chlorine decay, fast and slow chlorine reactions with TOC, TOC degradation, stochastic water demands, hydraulic uncertainty, and individual consumption patterns to calculate pathogen exposure and infection risk following the steps of Quantitative Microbial Risk Assessment (QMRA). A large wastewater contamination in different locations in a chlorinated and non-chlorinated network was simulated using three pathogens: Campylobacter, enterovirus, and Cryptosporidium. The results of this study showed that in non-chlorinated DWDNs, the modeled wastewater contamination event led to 11-46% infection risk in the total population, depending on the contamination location, but irrespective of the selected pathogen (due to the high pathogen concentration). On the other hand, in chlorinated DWDNs, the same scenarios resulted in lower infection risk for the pathogens that are susceptible to chlorine; 0.78-2.1 % for Campylobacter and 7.8-26.6 % for enterovirus. Moreover, the enterovirus infection risk was higher, despite the concentrations in the contamination source being lower, due to the lower susceptibility to chlorine than Campylobacter. While chlorination aids mitigation, large contaminations can still lead to infections due to chlorine resistance (for Cryptosporidium) and chlorine depletion at the contamination point. Finally, the varying levels of pathogen susceptibility to chlorine, the contamination location and duration, influenced the infection risk, while the response window to reduce the health impact was short; in these scenarios 5-10 hours post-contamination. The study provided a novel approach to assessing health risks, offering critical insights for water utilities to optimize their response during emergencies.
Chapter 5 further explores the added value of using modeling tools to support decision-making during emergencies in the DWDN. This was demonstrated through PathoINVEST, an analytical tool that utilizes the BeWaRE benchmark methodology, which was presented in the previous Chapter, to support water utilities in modeling contamination events in the DWDN. A case study was conducted with the aim of comparing a traditional approach (representing the status quo of current practices of water utilities) with a model-based approach (use of real-time modeling tools) during an emergency response to a contamination event in the DWDN. The model-based approach was shown to be more efficient than the traditional approach in identifying the source of contamination (1.3 versus 3.7 hours), requiring fewer samples (4 versus 11) and resulting in lower infection risk by the time the source was identified (12% versus 20%) in this case study. Moreover, the model-based approach was more effective in finding the best valves to close in the network (as mitigation measures) since it resulted in a 3%-point infection risk reduction. However, some actions taken in the traditional approach, such as the rapid closure of valves (cutting the network in half and thus limiting further spreading) before the contamination source was identified, were critical in mitigating the contamination. Another key finding was the importance of having an up-to-date overview of valve settings in the DWDN schematization to provide reliable results on source identification since any discrepancies between the actual network and the model can lead to inaccurate infection risk estimates when using modeling tools to support decision-making. Overall, this case study showed that integrating modeling tools in the current practices of water utilities provides a robust framework for improving water contamination management and decision-making processes, thus safeguarding public health during emergencies.
A concluding viewpoint is offered in Chapter 6, which considers whether the initial research questions from Chapter 1 were successfully answered. The implications of this research for water utilities are examined, providing information on how the proposed methodologies can be (and have been) used in real-world scenarios, facilitating a faster decision-making and contributing to effective mitigation of emergencies. Finally, the perspectives and future research are discussed, emphasizing the role of AI and the advancements in modeling tools. AI has shown significant potential in enhancing situational awareness and rapid information extraction during emergencies. Water utilities should explore the integration of AI into their standard operating procedures to further enhance emergency responses and routine management. Regarding the use of modeling tools during emergencies, future research should address key gaps, such as the complex dynamics when wastewater interacts with chlorine, the competition between chlorine-reducing agents, and the validity of hydraulic modeling assumptions such as perfect mixing. Accounting for cumulative health risks (multiple pathogens) and refining dose-response models to differentiate between infection and illness probabilities can provide insights for effectively managing risks to vulnerable populations. Moreover, the incorporation of metrics like Disability-Adjusted Life Years (DALYs) into modeling efforts could enable better communication of health impacts and evaluation of mitigation strategies. Finally, Digital Twins and real-time microbial sensors are identified as transformative technologies that can provide real-time insights into network dynamics. These advancements can shift water utility management from reactive approaches to proactive, data-driven strategies, significantly enhancing public health protection, operational efficiency, and resilience.
This dissertation examines novel bio-composite materials derived from resources recovered from the water sector. These materials incorporate natural fibres derived from untreated wastewater (i.e., cellulose fibres) or surface water management (i.e., reed and grass fibres), as well as fillers such as calcite derived from drinking water softening processes or agricultural waste (i.e., coconut shells, olive powder, and food residue). Bio-based resins, such as polyester with a reduced styrene content or furan resin, containing furfuryl alcohol, serve as binders.
The presence of a wide range of pollutants has a significant impact on water resources as a result of human activities. It is therefore imperative that comprehensive testing is conducted to ensure that the utilisation of recovered resources does not result in any adverse effects on human health or the environment. It is crucial to emphasise that, because of their derivation from recycled raw materials, the utilisation of the novel bio-composite materials should not be assumed to be intrinsically risk-free. It is therefore imperative that a comprehensive risk assessment of the environmental and human health risks associated with the production and application of the new bio-composite materials is conducted.
The overall aim of this research project is to develop an approach for the evaluation of potential risks to human health and the environment that may result from the production and application of the new bio-composite materials. In line with this, four research questions have been formulated to conduct this study:
- What are the main risks and related hazards associated with the production of new resource recovery-based bio-composite materials and their applications and how are these interlinked?What existing methods can be potentially used (and with what modifications) and which new ones need to be developed to assess these risks?
- What is the best approach to define and quantify the human health risks involved in the production of bio-composite materials?
- What is the environmental risk associated with the use of the new bio-composite materials in the aquatic environment? More specifically, what is the risk in case of canal bank protection elements made from these new materials?
- What is the environmental risk associated with the use of new bio-composite materials based building façade elements and how does the weathering of these elements affect this risk?
Above research questions have been addressed and answered in Chapters 2 – 5 of this dissertation. Below, a summary of the work done in order to address the formulated research questions is provided.
A comprehensive literature review, detailed in Chapter 2, was conducted at the outset of this work to identify the principal hazards and associated risks involved in drinking water and wastewater treatment plants, water reuse, and water-based resources recovery. The literature study identified potential microbial and chemical contaminants of the raw materials used to produce the new water-based resource recovery bio-composite materials. These contaminants may pose a risk to human health and the environment. Nevertheless, it was found that no risk assessment methodologies have yet been used to assess the potential human health and environmental risks associated with the production and application of the new bio-composite materials.
The novel human health risk assessment framework, which is described in Chapter 3, employed a qualitative risk analysis as the initial step, followed by a quantitative risk analysis. The Hazard and Operability (HAZOP) method identified the principal hazards during the production, and the qualitative Event Tree Analysis (ETA) methodology created a corresponding risk map. The results of the qualitative risk assessment indicated that the main risks of new bio-composite materials are caused by chemical and microbial contamination, which can have a negative impact on human health and the environment. A quantitative human health risk assessment was conducted on four alternative new bio-composite materials, employing both Quantitative Chemical Risk Assessment (QCRA) and Quantitative Microbial Risk Assessment (QMRA) methodologies, with deterministic and stochastic approaches. The results of the chemical risk assessment indicated that the cancer risk from styrene and furfuryl alcohol exceeded the established safety threshold. Similarly, the microbial risk assessment identified significant concerns with E. coli in cellulose fibres, with the risk exceeding safety limit. The assessments were conducted under the most unfavourable circumstances, without the use of personal protective equipment (PPE) or safety protocols. Furthermore, the assumption of maximum exposure to contaminants was made due to the limited availability of input data, which resulted in an overestimation of the overall risk.
The presence of chemical contamination in raw materials used for the production of new bio-composite materials gave rise to concerns not only for human health but also for potential negative environmental impact. In order to assess the environmental risks involved, two applications of these new materials were considered in this study: (a) canal bank protection elements, which prevents soil from collapsing into the water and (b) façade building elements as decorations panels.
To assess the environmental risks of chemical release, from the bio-composite materials used as canal bank protection, laboratory column leaching tests were conducted. This preliminary step provided data for an approximate environmental risk assessment in real-world conditions. The environmental risk assessment framework, developed in accordance with European guidelines, as detailed in Chapter 4, showed that the concentration of chemicals leached into surface water was within safety threshold. However, styrene and furfuryl alcohol contained in the resins may still pose a concern to environmental risk. It is crucial to acknowledge that the interpretation of these results should be approached with caution, given the absence of on-site data and the numerous assumptions made, including instantaneous mixing of the leaching chemicals and the absence of Brownian motion. Furthermore, the background concentrations in freshwater and the fate and degradation of chemicals in surface water were not considered. Also, the leaching process was evaluated over time, with the observation of a plateau indicating a significant slowdown in the leaching process accompanied by a reduction in the driving force, thereby providing a better understanding of the leaching behaviour.
Bio-composite materials utilised as façade construction elements are more susceptible to adverse weather conditions than those used for canal bank protection. Chapter 5 presents an analysis of potential leaching from bio-composites on a real-world building of a pumping station in the Netherlands. Two bio-composite alternatives were tested, and two samples per material were used: one new sample (as the initial application) and one UV-treated sample (as the long-term application after weathering) per material, for a total of four samples. The samples were subjected to leaching tests simulating two rainfall events of a duration of one hour. The risk assessment demonstrated that no leached chemicals exceeded the safety threshold, with no detection of styrene or furfuryl alcohol in the leaching effluent samples. However, these findings should be interpreted with caution due to the limited input data and the assumptions made, including the lack of on-site data and the focus on a single rain event rather than analysing leaching over a longer time period. The weathering treatments affected the materials in different ways based on their resin composition. Material M3 (made of polyester resin) exhibited aesthetic changes, while Material M4 (made of furan resin) demonstrated increased roughness, reduced water resistance and fibre detachment. Microscopic examination revealed significant wrinkling in M4, indicating that environmental exposure significantly affects these materials.
Overall, it can be concluded (Chapter 6) that both microbial and chemical risks are inherent in the production and applications of new bio-composite materials considered in this thesis. These risks originate from the utilization of specific raw materials, including calcite from drinking water, cellulose derived from wastewater, reed and grass sourced from surface water management conducted by water boards, as well as the resins and additives employed in new materials. The framework developed in this research, which includes laboratory testing, modelling and risk assessment methods, has been validated as applicable to the case studies used in this work. Being generic in nature, the framework also shows potential for human health and environmental risk assessments associated with different future applications of new bio-composite materials. ...
This dissertation examines novel bio-composite materials derived from resources recovered from the water sector. These materials incorporate natural fibres derived from untreated wastewater (i.e., cellulose fibres) or surface water management (i.e., reed and grass fibres), as well as fillers such as calcite derived from drinking water softening processes or agricultural waste (i.e., coconut shells, olive powder, and food residue). Bio-based resins, such as polyester with a reduced styrene content or furan resin, containing furfuryl alcohol, serve as binders.
The presence of a wide range of pollutants has a significant impact on water resources as a result of human activities. It is therefore imperative that comprehensive testing is conducted to ensure that the utilisation of recovered resources does not result in any adverse effects on human health or the environment. It is crucial to emphasise that, because of their derivation from recycled raw materials, the utilisation of the novel bio-composite materials should not be assumed to be intrinsically risk-free. It is therefore imperative that a comprehensive risk assessment of the environmental and human health risks associated with the production and application of the new bio-composite materials is conducted.
The overall aim of this research project is to develop an approach for the evaluation of potential risks to human health and the environment that may result from the production and application of the new bio-composite materials. In line with this, four research questions have been formulated to conduct this study:
- What are the main risks and related hazards associated with the production of new resource recovery-based bio-composite materials and their applications and how are these interlinked?What existing methods can be potentially used (and with what modifications) and which new ones need to be developed to assess these risks?
- What is the best approach to define and quantify the human health risks involved in the production of bio-composite materials?
- What is the environmental risk associated with the use of the new bio-composite materials in the aquatic environment? More specifically, what is the risk in case of canal bank protection elements made from these new materials?
- What is the environmental risk associated with the use of new bio-composite materials based building façade elements and how does the weathering of these elements affect this risk?
Above research questions have been addressed and answered in Chapters 2 – 5 of this dissertation. Below, a summary of the work done in order to address the formulated research questions is provided.
A comprehensive literature review, detailed in Chapter 2, was conducted at the outset of this work to identify the principal hazards and associated risks involved in drinking water and wastewater treatment plants, water reuse, and water-based resources recovery. The literature study identified potential microbial and chemical contaminants of the raw materials used to produce the new water-based resource recovery bio-composite materials. These contaminants may pose a risk to human health and the environment. Nevertheless, it was found that no risk assessment methodologies have yet been used to assess the potential human health and environmental risks associated with the production and application of the new bio-composite materials.
The novel human health risk assessment framework, which is described in Chapter 3, employed a qualitative risk analysis as the initial step, followed by a quantitative risk analysis. The Hazard and Operability (HAZOP) method identified the principal hazards during the production, and the qualitative Event Tree Analysis (ETA) methodology created a corresponding risk map. The results of the qualitative risk assessment indicated that the main risks of new bio-composite materials are caused by chemical and microbial contamination, which can have a negative impact on human health and the environment. A quantitative human health risk assessment was conducted on four alternative new bio-composite materials, employing both Quantitative Chemical Risk Assessment (QCRA) and Quantitative Microbial Risk Assessment (QMRA) methodologies, with deterministic and stochastic approaches. The results of the chemical risk assessment indicated that the cancer risk from styrene and furfuryl alcohol exceeded the established safety threshold. Similarly, the microbial risk assessment identified significant concerns with E. coli in cellulose fibres, with the risk exceeding safety limit. The assessments were conducted under the most unfavourable circumstances, without the use of personal protective equipment (PPE) or safety protocols. Furthermore, the assumption of maximum exposure to contaminants was made due to the limited availability of input data, which resulted in an overestimation of the overall risk.
The presence of chemical contamination in raw materials used for the production of new bio-composite materials gave rise to concerns not only for human health but also for potential negative environmental impact. In order to assess the environmental risks involved, two applications of these new materials were considered in this study: (a) canal bank protection elements, which prevents soil from collapsing into the water and (b) façade building elements as decorations panels.
To assess the environmental risks of chemical release, from the bio-composite materials used as canal bank protection, laboratory column leaching tests were conducted. This preliminary step provided data for an approximate environmental risk assessment in real-world conditions. The environmental risk assessment framework, developed in accordance with European guidelines, as detailed in Chapter 4, showed that the concentration of chemicals leached into surface water was within safety threshold. However, styrene and furfuryl alcohol contained in the resins may still pose a concern to environmental risk. It is crucial to acknowledge that the interpretation of these results should be approached with caution, given the absence of on-site data and the numerous assumptions made, including instantaneous mixing of the leaching chemicals and the absence of Brownian motion. Furthermore, the background concentrations in freshwater and the fate and degradation of chemicals in surface water were not considered. Also, the leaching process was evaluated over time, with the observation of a plateau indicating a significant slowdown in the leaching process accompanied by a reduction in the driving force, thereby providing a better understanding of the leaching behaviour.
Bio-composite materials utilised as façade construction elements are more susceptible to adverse weather conditions than those used for canal bank protection. Chapter 5 presents an analysis of potential leaching from bio-composites on a real-world building of a pumping station in the Netherlands. Two bio-composite alternatives were tested, and two samples per material were used: one new sample (as the initial application) and one UV-treated sample (as the long-term application after weathering) per material, for a total of four samples. The samples were subjected to leaching tests simulating two rainfall events of a duration of one hour. The risk assessment demonstrated that no leached chemicals exceeded the safety threshold, with no detection of styrene or furfuryl alcohol in the leaching effluent samples. However, these findings should be interpreted with caution due to the limited input data and the assumptions made, including the lack of on-site data and the focus on a single rain event rather than analysing leaching over a longer time period. The weathering treatments affected the materials in different ways based on their resin composition. Material M3 (made of polyester resin) exhibited aesthetic changes, while Material M4 (made of furan resin) demonstrated increased roughness, reduced water resistance and fibre detachment. Microscopic examination revealed significant wrinkling in M4, indicating that environmental exposure significantly affects these materials.
Overall, it can be concluded (Chapter 6) that both microbial and chemical risks are inherent in the production and applications of new bio-composite materials considered in this thesis. These risks originate from the utilization of specific raw materials, including calcite from drinking water, cellulose derived from wastewater, reed and grass sourced from surface water management conducted by water boards, as well as the resins and additives employed in new materials. The framework developed in this research, which includes laboratory testing, modelling and risk assessment methods, has been validated as applicable to the case studies used in this work. Being generic in nature, the framework also shows potential for human health and environmental risk assessments associated with different future applications of new bio-composite materials.
To evaluate the performance of SUDS, assessment frameworks include Key Performance Indicators (KPIs). KPIs are measurable indicators demonstrating how effective SUDS are in achieving their objectives. This research highlights that there is no universal or even country based standard assessment framework for SUDS. Furthermore, there are few examples of the translation of the scientific assessment methods of SUDS to engineering practice available. The assessment of the full effect of SUDS therefore remains unclear to practitioners.
This research proposes a new framework (”extended framework”) to assess the performance of SUDS, building on the existing framework (”conventional framework”) which assesses cost and water quantity currently used in engineering practice. The extended framework adds KPIs assessing the remaining three objectives of SUDS design. Firstly, water quality is assessed with the KPIs Site Pollution Index (SPI) and Pollutant Removal Capacity (PRC). Amenity with the KPIs Thermal Comfort Score (TCS) and impervious area. Thirdly, biodiversity is assessed with the KPI Biotope Area Factor (BAF). Furthermore, it improves the assessment of water quantity by replacing the currently used KPI with Expected Annual Damages (EAD). With the choice of KPIs in the extended framework, it is ensured that their assessment methodologies are suitable to engineering practice. Furthermore, by including KPIs that assess the multi-objectiveness of SUDS, the co-benefits are included in the extended framework.
With the application of both frameworks on the municipality of Alkmaar, this research substantiates the positive influence of SUDS on urban areas. The case study shows improving performance for water quantity, water quality, amenity and biodiversity if the number of SUDS increases.
To assess the effect of the extended framework on the decision making process, the MCDA type Compromise Programming (CP) is applied to the results of both frameworks. With the identification of the best choice of design based on the performance results of either the conventional or extended framework, the outcome of the CP method showed that using the extended framework as opposed to the conventional framework sometimes led to different design choices.
It is demonstrated that the extended framework indeed improves the decision making process to improve the live-ability of the urban environment. Even though the extended framework is more time consuming and may result in more costly designs, using this framework to base decision making on is likely to result in better quality of life for humans with a reduced negative impact on the associated natural environment. This framework better equips decision-makers to face
emerging urban challenges. However, both frameworks are of use in engineering practice. The ultimate choice of using either one of the frameworks is dependent on the goal of the project, the client, and the amount of time and money available. ...
To evaluate the performance of SUDS, assessment frameworks include Key Performance Indicators (KPIs). KPIs are measurable indicators demonstrating how effective SUDS are in achieving their objectives. This research highlights that there is no universal or even country based standard assessment framework for SUDS. Furthermore, there are few examples of the translation of the scientific assessment methods of SUDS to engineering practice available. The assessment of the full effect of SUDS therefore remains unclear to practitioners.
This research proposes a new framework (”extended framework”) to assess the performance of SUDS, building on the existing framework (”conventional framework”) which assesses cost and water quantity currently used in engineering practice. The extended framework adds KPIs assessing the remaining three objectives of SUDS design. Firstly, water quality is assessed with the KPIs Site Pollution Index (SPI) and Pollutant Removal Capacity (PRC). Amenity with the KPIs Thermal Comfort Score (TCS) and impervious area. Thirdly, biodiversity is assessed with the KPI Biotope Area Factor (BAF). Furthermore, it improves the assessment of water quantity by replacing the currently used KPI with Expected Annual Damages (EAD). With the choice of KPIs in the extended framework, it is ensured that their assessment methodologies are suitable to engineering practice. Furthermore, by including KPIs that assess the multi-objectiveness of SUDS, the co-benefits are included in the extended framework.
With the application of both frameworks on the municipality of Alkmaar, this research substantiates the positive influence of SUDS on urban areas. The case study shows improving performance for water quantity, water quality, amenity and biodiversity if the number of SUDS increases.
To assess the effect of the extended framework on the decision making process, the MCDA type Compromise Programming (CP) is applied to the results of both frameworks. With the identification of the best choice of design based on the performance results of either the conventional or extended framework, the outcome of the CP method showed that using the extended framework as opposed to the conventional framework sometimes led to different design choices.
It is demonstrated that the extended framework indeed improves the decision making process to improve the live-ability of the urban environment. Even though the extended framework is more time consuming and may result in more costly designs, using this framework to base decision making on is likely to result in better quality of life for humans with a reduced negative impact on the associated natural environment. This framework better equips decision-makers to face
emerging urban challenges. However, both frameworks are of use in engineering practice. The ultimate choice of using either one of the frameworks is dependent on the goal of the project, the client, and the amount of time and money available.
Assessing the hydrologic performance of the Aquaflow in Rotterdam
A monitoring case study of the Agniesebuurt area of Rotterdam
Serious gaming to support the adoption of sustainable drainage solutions
A serious game to educate citizens about private household SuDS
This thesis provides relatively comprehensive and overall ideas to research drinking water temperature. The objective of this thesis consists of three parts: i) Determining impact factors on water temperature; ii) Simulating water temperature in the distribution system; iii) Choosing measures to control water temperature. Firstly, data measurement and analytical methods were applied to determine impact factors on water temperature, and the influence level of each impact factor had been identified. Subsequently, implementing these impact factors to calibrate the water temperature simulation model to verify the model’s feasibility. Finally, the performance on reducing water temperature of three measures, porous asphalt, pervious interlocking concrete pavement, and grass cover, were compared to determine the most effective measure from the standpoint of pipe cover. The results show as following: i) Four impact factors are summarized as surface cover material, district heating pipe, shade effect and groundwater level based on the collected data; ii) It is feasible to simulate the water temperature in the water distribution system. For the model of city Almere, around 88% of simulation values had a difference smaller than 1℃ compared with measurement data; iii) Grass cover has a better performance than the porous asphalt and pervious interlocking cement pavement. Additionally, this thesis discusses limitations during the measurement and simulation process and more relative interventions to reduce water temperature.
In summary, this thesis further summarizes the various impact factors that affect the drinking water temperature and the measure to control drinking water temperature has launched from the point of pipe cover compared with previous references. These results provide guiding advice on the engineering projects of constructing and renovating drinking water distribution systems considering water temperature. ...
This thesis provides relatively comprehensive and overall ideas to research drinking water temperature. The objective of this thesis consists of three parts: i) Determining impact factors on water temperature; ii) Simulating water temperature in the distribution system; iii) Choosing measures to control water temperature. Firstly, data measurement and analytical methods were applied to determine impact factors on water temperature, and the influence level of each impact factor had been identified. Subsequently, implementing these impact factors to calibrate the water temperature simulation model to verify the model’s feasibility. Finally, the performance on reducing water temperature of three measures, porous asphalt, pervious interlocking concrete pavement, and grass cover, were compared to determine the most effective measure from the standpoint of pipe cover. The results show as following: i) Four impact factors are summarized as surface cover material, district heating pipe, shade effect and groundwater level based on the collected data; ii) It is feasible to simulate the water temperature in the water distribution system. For the model of city Almere, around 88% of simulation values had a difference smaller than 1℃ compared with measurement data; iii) Grass cover has a better performance than the porous asphalt and pervious interlocking cement pavement. Additionally, this thesis discusses limitations during the measurement and simulation process and more relative interventions to reduce water temperature.
In summary, this thesis further summarizes the various impact factors that affect the drinking water temperature and the measure to control drinking water temperature has launched from the point of pipe cover compared with previous references. These results provide guiding advice on the engineering projects of constructing and renovating drinking water distribution systems considering water temperature.
Optimal Rehabilitation of Urban Drainage Systems
Application of single-objective optimisation for the implementation of Green-Blue-Grey Infrastructures in changing climate
Rehabilitation of UDS can be done in several ways, including implementing Green-Blue-Grey Infrastructures (G-B-G measures). The combination of G-B-G measures can increase the resiliency of the UDS to withstand higher intensity rainfall by reducing both the peak flow and enlarging the capacity of the UDS system. Therefore, this thesis aims to develop a method to find the optimal way to rehabilitate an existing UDS to reduce the risk of flooding under the climate change rainfall scenarios.
The method developed coupled a hydrodynamic model, Storm Water Management Model (SWMM), and Genetic Algorithm (GA) to find the optimal solution to rehabilitate UDS. The effect of climate change was incorporated by simulating the solutions using composite design storms that represent the increase in hourly and daily rainfall extremes for 2030, 2050, and 2085. The objective function of this optimisation problem becomes the minimisation of the total cost to implement the measures for the rehabilitation of UDS, under the constraint that no flooding can happen on the system when tested against the climate change rainfall scenarios. Therefore, the decision variables of this optimisation are the size and location for each implemented measure, while the penalty cost is associated with the cost of each m3 of flooding.
Based on the analysis of the case study, the most appropriate Green-Blue measures to be implemented is Rain Barrels, Infiltration Trenches, and Pervious Pavements. Meanwhile, for grey measures, it is best to consider pipe and pump replacements and increasing the CSOs’ weirs. The optimisation was done using the developed formal method and manual trial-and-error. The results of the formal optimisation have been confirmed to outperform the result from manual optimisation using the traditional trial-and-error method. The optimal solutions proved that a combination of both grey and G-B measures produced the lowest cost to reduce flooding. Although the solutions can be adapted over time from 2030 until 2085, the results show that adaptive solutions might not be needed when the solution for 2085 is better implemented from the year 2030. Overall, it can be projected that in the future, the combination of G-B-G measures can produce an economically optimal solution to be implemented in order to achieve zero floodings in the case study location. ...
Rehabilitation of UDS can be done in several ways, including implementing Green-Blue-Grey Infrastructures (G-B-G measures). The combination of G-B-G measures can increase the resiliency of the UDS to withstand higher intensity rainfall by reducing both the peak flow and enlarging the capacity of the UDS system. Therefore, this thesis aims to develop a method to find the optimal way to rehabilitate an existing UDS to reduce the risk of flooding under the climate change rainfall scenarios.
The method developed coupled a hydrodynamic model, Storm Water Management Model (SWMM), and Genetic Algorithm (GA) to find the optimal solution to rehabilitate UDS. The effect of climate change was incorporated by simulating the solutions using composite design storms that represent the increase in hourly and daily rainfall extremes for 2030, 2050, and 2085. The objective function of this optimisation problem becomes the minimisation of the total cost to implement the measures for the rehabilitation of UDS, under the constraint that no flooding can happen on the system when tested against the climate change rainfall scenarios. Therefore, the decision variables of this optimisation are the size and location for each implemented measure, while the penalty cost is associated with the cost of each m3 of flooding.
Based on the analysis of the case study, the most appropriate Green-Blue measures to be implemented is Rain Barrels, Infiltration Trenches, and Pervious Pavements. Meanwhile, for grey measures, it is best to consider pipe and pump replacements and increasing the CSOs’ weirs. The optimisation was done using the developed formal method and manual trial-and-error. The results of the formal optimisation have been confirmed to outperform the result from manual optimisation using the traditional trial-and-error method. The optimal solutions proved that a combination of both grey and G-B measures produced the lowest cost to reduce flooding. Although the solutions can be adapted over time from 2030 until 2085, the results show that adaptive solutions might not be needed when the solution for 2085 is better implemented from the year 2030. Overall, it can be projected that in the future, the combination of G-B-G measures can produce an economically optimal solution to be implemented in order to achieve zero floodings in the case study location.
Application of business intelligence as decision support systems in asset management of water connections
Case study in the Netherlands, in collaboration with water company “Evides”
Replacement optimisation for public infrastructure assets
Quantitative optimisation modelling taking typical public infrastructure related features into account