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Numerical modeling of pipe leakage in variably saturated soil

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Pipe leakage related to defect urban sewer and stormwater pipe networks may lead to subsurface contamination, reduction of groundwater recharge or a significant decrease of the groundwater table. The quantification of pipe leakage is challenging, mostly due to the uncertain forming of a colmation layer in the defect vicinity and inaccessibility of both, pipe defects and the surrounding soil. Numerical models can be used to quantify leakage. At present times, only few physically-based pipe leakage models exist, all of which either neglect or simplify variably-saturated flow. In the present dissertation, a novel and unique three-dimensional physically-based pipe leakage model for variably saturated soil is presented. The model consists of the newly implemented coupling between the pipe flow simulator HYSTEM-EXTRAN and the unsaturated-saturated flow simulator OpenGeoSys. The coupling is based on updating of boundary conditions and source terms. The interprocess data transfer is realized using a shared-memory. The pipe leakage model is successfully validated and verified using a newly generated benchmark library for pipe leakage models. Benchmarks are based on two physical experiments described in literature and two newly derived analytical solutions. A novel method for upscaling pipe leakage is presented. The method enables to significantly reduce the local refinement of spatial discretization in the pipe vicinity, which leads to a substantial reduction of computational costs. The method is based on leakage functions. Two leakage functions representing both, sewer and stormwater pipe leakage are presented. Accuracy and time efficiency of the upscaling method is demonstrated by comparing results from a fully discretized model and an upscaled model. In the present dissertation, the pipe leakage model is applied to several case studies to investigate the pipe leakage process. Model setups represent (i) a single defect, (ii) a leaky sewer pipe of 30 m length, and (iii) a 53 km long defect stormwater pipe network in an urban catchment. Results of the single defect and leaky sewer pipe model (models i,ii) show that leaky pipes can hydraulically disconnect from groundwater. It is found that, for a given pipe water level, pipe water exfiltration converges as the groundwater table is lowered. Further, it is found that pipe water exfiltration increases as the intensity and duration of pipe flow events increase. The temporal distribution of pipe flow has a negligible effect on pipe water exfiltration. Results of the model representing a defect stormwater pipe network in an urban catchment (model iii) show the impact of pipe leakage on urban groundwater. It is shown that groundwater infiltration into a largely defect pipe network may be in the order of annual groundwater recharge. Further, it is shown that groundwater infiltration may reduce the groundwater table by several meters and that the groundwater table may be lowered to the elevation of the pipe network.
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... Integrated 1D-3D models were developed to simulate sewer exfiltration dynamics but are hard to validate due to the large number of data required for model parametrization (Rutsch et al., 2008;Peche et al., 2017;Tscheikner-Gratl et al., 2020). Karpf (2012) and Peche (2019) proposed simplified approaches for modeling sewer exfiltration, but the methods have been tested only to site-specific and pipe scales. Wolf et al. (2012) considered the temporal and spatial variation of sewer exfiltration to groundwater by conducting sampling for the period from 2002 to 2008 in the city of Rastatt. ...
... Lee et al. (2015) and Roehrdanz et al. (2017) developed a spatial model of sewer exfiltration, which allows predicting the occurrence of exfiltration in shallow groundwater and incorporates various wastewater indicators, but the outputs of the model are subjected to the groundwater shortterm observations in a small region of a city. Besides, the uncertainty of upscalling approaches in sewer exfiltration modelling remains significant issue due to a lack of understanding of core parameters and processes of sewer exfiltration (Wolf and Hötztl, 2007;Karpf, 2012;Peche, 2019). So far, the studies by Rutsch et al. (2005) and Rutsch et al. (2008) remain the only reviews that incorporate modelling aspects of sewer exfiltration (Table 1), though many changes have occurred since then. ...
... At large hydraulic gradients (between the pipe and the soil in the pipe vicinity) and soil moisture, increased sewer exfiltration leads to downwards propagation of a wetting front and sewer outflow may recharge groundwater. Sewer exfiltration is governed by the presence of a colmation layer forming in the pipe defect vicinity (Karpf, 2012;Peche, 2019). After the occurrence of a pipe defect, high sewer exfiltration rates continue until an equilibrium pressure height between insewer and soil conditions is reached. ...
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Increasing evidence from studies in urban wastewater systems proves that sewer exfiltration may present a profound threat for rising levels of toxic substances and microbial pollution in groundwater. New and innovative methods for monitoring sewage exfiltration are continuously developed, which provide a solicit ground for a better understanding of key processes and influencing characteristics of sewer exfiltration to support the development of mathematical equations and models worldwide. However, modelling of sewer exfiltration and its associated impacts on groundwater are still constrained and not fully understood in large urban systems. This paper reviews the knowledge advancements and challenges of sewer exfiltration modelling. Based on the present review, we define five key research domains for developing more generic framework of large-scale models. These domains inquire to advance the representation of hydraulic modelling (e.g. testing exfiltration models coupled with biofilm growth models), modelling of solutes originating from sewer leakages (e.g. heavy metals), define the practical values of key model parameters of main model components and sub-processes for calibration and uncertainty evaluations, develop upscaling approaches for integrated multi-dimensional sewer exfiltration models, and incorporation of sewer exfiltration from private sewers.
... 2). This factor incorporates the two parameters hydraulic conductivity and thickness of the colmation layer, which are difficult to determine and often unknown in practice (Karpf et al. 2009;Peche 2019). This leads to the reformulation of Eq. 1 for calculation of exfiltration rates under the swf condition (which is the case of CSs in this study): ...
... Studies on sewer exfiltration at pipe scales indicate that the leakage process is ruled by a number of key parameters, including leakage area, depth of wastewater in the pipe, clogging layer, hydraulic permeability and soil characteristics, and hydraulic gradient from pipe surface to the groundwater (Wolf and Hötzl 2007;Karpf et al. 2009;Peche et al. 2017). These parameters describe structural and dynamic components of sewer exfiltration processes, which data demand at the catchment scale is often not available or subject to large uncertainties (Rutsch et al. 2008;Karpf and Krebs 2011;Peche 2019). The common approach for large-scale studies is so far based on mapping analysis of sewer network deteriorations (structural condition, distribution of pipes), surveying and indirectly correlating with population-based sewer discharge, or simplified assumptions of nationwide fixed rates of water loss from defective sewer pipes (e.g. ...
... Besides, incorporating process-based approaches for important model parameters (such as wastewater level or the properties of the colmation layer) in the sewer exfiltration model to replace simplified assumptions of constant parameters, or test the timevariant leakage function instead of using the equation of a fixed sewer exfiltration rate might help to better represent the exfiltration dynamics and its spatial distribution (e.g. Peche et al. 2017;Peche 2019). This will require a more detailed identification and inventory of exfiltration susceptible areas in major cities under real sewer conditions. ...
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... A coupled simulation is not required, because the time steps of surface flow are much smaller than those in the soil layer. The leakage of water from the pipe system to the soil is negligible for single events, because the leakage rate is tiny [Peche, 2019]. However, for continuous injection spill problems, the coupling of surface, pipe and soil flow would be a way to forecast the plume of pollutants in the soil and groundwater domain before it reaches surface waters or drinking water wells. ...
... A coupling of the pollution tracking and the runoff routing must be established in both directions. This can be done via an iteration of both models, like described in Peche [2019]: A master model (volume runoff routing) calculates one time step and calls the client (pollution transport) model to process the same amount of time. The result of the transport time step is analysed by the master model to adapt volume fluxes before the next time step is processed. ...
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... Additionally to the conductive heat transport, leakage of wastewater yields a noticeable heat input (Benz et al., 2015;Ford & Tellam, 1994). Leakages of sewer pipes are challenging to detect and quantify and are strongly varying regionally (Peche, 2019). While the temperature of wastewater depends on several factors (Kretschmer et al., 2016), for Central European cities it is generally around 12-22 C (Benz et al., 2015;Cipolla & Maglionico, 2014;Schmid, 2008;Tissen et al., 2021). ...
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