entropy
Article Morphogenesis of Urban Water Distribution Networks: A Spatiotemporal Planning Approach for Cost-Efficient and Reliable Supply
Jonatan Zischg * , Wolfgang Rauch and Robert Sitzenfrei
Unit of Environmental Engineering, University of Innsbruck, Technikerstraße 13, A-6020 Innsbruck, Austria; [email protected] (W.R.); [email protected] (R.S.) * Correspondence: [email protected]; Tel.: +43-512-507-62160
Received: 26 July 2018; Accepted: 13 September 2018; Published: 14 September 2018
Abstract: Cities and their infrastructure networks are always in motion and permanently changing in structure and function. This paper presents a methodology for automatically creating future water distribution networks (WDNs) that are stressed step-by-step by disconnection and connection of WDN parts. The associated effects of demand shifting and flow rearrangements are simulated and assessed with hydraulic performances. With the methodology, it is possible to test various planning and adaptation options of the future WDN, where the unknown (future) network is approximated via the co-located and known (future) road network, and hence different topological characteristics (branched vs. strongly looped layout) can be investigated. The reliability of the planning options is evaluated with the flow entropy, a measure based on Shannon’s informational entropy. Uncertainties regarding future water consumption and water loss management are included in a scenario analysis. To avoid insufficient water supply to customers during the transition process from an initial to a final WDN state, an adaptation concept is proposed where critical WDN components are replaced over time. Finally, the method is applied to the drastic urban transition of Kiruna, Sweden. Results show that without adaptation measures severe performance drops will occur after the WDN state 2023, mainly caused by the disconnection of WDN parts. However, with low adaptation efforts that consider 2–3% pipe replacement, sufficient pressure performances are achieved. Furthermore, by using an entropy-cost comparison, the best planning options are determined.
Keywords: urban transition; EPANET 2; network disconnection; network growth; uncertainties; performance and adaptation; flow entropy
1. Introduction Cities are highly dynamic structures that are experiencing demographic changes with large population growth in most regions of Asia and Africa, whereas a general population decline is taking place in Europe. The shrinking city phenomenon and abandonment of urban districts are gaining in importance worldwide. According to Oswalt and Rieniets [1] every fourth city in the world was shrinking between 1990 and 2000 with a rising trend. One of the most prominent examples is the city of Detroit, USA, where today about one third of the town area is abandoned or demolished due to deindustrialization [2]. Conversely, strong city growth and the expansion of neighborhoods with annual growth rates up to 5% are observed in the last years [3]. These urban transitions stress not only the above-ground infrastructure like streets or public transport, but also the underground water infrastructure due to the necessary modifications in the network’s structure and function. Water supply systems are one of the most important infrastructures in society and its well-functioning is essential. Shifting demand patterns, endeavors from centralized
Entropy 2018, 20, 708; doi:10.3390/e20090708 www.mdpi.com/journal/entropy Entropy 2018, 20, 708 2 of 21 to decentralized techniques [4], network expansions, or connectivity loss are only a few examples for transition processes which stress the ability to perform. Along with the long life span of several decades (in some cases even exceeding 100 years), the influence of a newly constructed pipe in the future system and the interaction with the existing system emphasize the importance of future oriented planning and management [5]. “Network transitioning” describes the pathway from an existing (source) network to a future (destination) network [6]. Usually transition processes of water infrastructure are relatively slow and take place over decades, where the network structure remains nearly constant (see e.g., Ref. [4]). Here we present a method and apply it to a case study to assess fast ongoing transitions, with severe impacts on the network’s structure. Changes of the network structure are densifications, expansions and/or disconnection of network parts caused by climate change, population changes, changes in land use, and shifts in water technology [7–9]. While new network parts must be designed for expected load conditions and spatial constraints, the existing network may need to be adapted to provide sufficient performances at all times of the transition process. In many cases, the detailed future network layout is largely unknown, because decisions on urban transitions are usually made without taking the water infrastructure into account. In summary, transitioning of urban infrastructure systems is characterized by real world complexity and high uncertainties, which is strongly dependent on the urban development. In the field of water distribution system analysis, it is widely accepted that measures for hydraulic capacity reliability and redundancy have to be considered in the design process to account for such uncertainties and unforeseeable events. Among many stochastic and reliability-based methods, flow entropy, based on Shannon’s informational entropy [10], is proven to be a consistent surrogate measure of reliability and failure tolerance [11,12]. High entropy values indicate equally important flow paths, i.e., the absence of dominant supply structures, whose failure could cause a severe system breakdown. Higher entropies are not only dependent on the number of supply sources and alternative flow paths, but also on their scale and spatial location. For example, a loop in the network structure with high flows (e.g., proximity to the supply source) is rated higher than a loop in secondary pipes with lower flows, where potential system failures have smaller impacts on the global performance. Compared to other criteria, this measure has the advantage that it is relatively easy to calculate, non-iterative, and that the data requirements are minimal [11,13]. Previous studies presented methods of designing and evaluating the long-term transition under deep uncertainties of water infrastructure (planning horizon of several decades), as for example shown by Marlow et al. [14], Eggimann et al. [15] and Urich and Rauch [16] whose work emphasized on urban drainage system transitions. Creaco et al. in Refs. [17,18] presented an optimization methodology for the optimal growth of water distribution networks (WDNs) with respect to costs and reliability, also considering demand uncertainties. In their work, they considered the step-by-step connection of pipes and concluded that solely designing one ideal “final state network” is not optimal, neglecting possible deficiencies of the WDN at intermediate states. However, disconnections and uncertainties of the network topology were not considered in their works. Existing studies of complex real world WDN transitions are limited and therefore further research is necessary also with regard to exploring case studies of unspecific methods [19,20]. A promising concept is the creation of many possible future network layouts, rather than assessing a fixed topology. The idea is to use the often available future road network (RN) from city planners as the basis for an automatic WDN planning approach. This concept of so-called “in-silico” or “semi-virtual” networks was already used for network reconstructions [21] or even the approximation of real water infrastructure networks where missing network information is approximated with known surrogate information, such as the co-located road network data [22,23]. In comparison with the work presented in Ref. [22], this study extends transition modeling by the interaction of the existing WDN data and future “in-silico” network data, also taking into account uncertain population developments that allow for future design under a probable range of uncertainties. Furthermore, the work presents a simple local adaptation concept of pipe replacement Entropy 2018, 20, 708 3 of 21 Entropy 2018, 20, x FOR PEER REVIEW 3 of 21 basedbased onon thethe least-least- “monetary”“monetary” costcost pathpath whichwhich isis appliedapplied toto thethe WDN,WDN, inin casecase aa defineddefined criticalcritical performanceperformance can no longer longer be be achieved achieved at at a acertain certain tr transitionansition state. state. After After sufficient sufficient performances performances are areachieved achieved for forall allWDN WDN states, states, we we perform perform a acost-r cost-reliabilityeliability comparison comparison of of different WDNWDN designdesign alternativesalternatives (layout(layout andand designdesign demand).demand). Entropy-costEntropy-cost ratiosratios helphelp decisiondecision makersmakers identifyidentify reliablereliable planningplanning optionsoptions thatthat workwork forfor aa broadbroad rangerange ofof futurefuture conditions,conditions, andand quantifyquantify necessarynecessary costscosts (WDN(WDN layoutlayout andand adaptationadaptation costs)costs) atat an an earlyearly state state of of the the transition. transition. TheThe noveltynovelty ofof thisthis workwork isis toto investigate many planning options with regard to WDN structure, andand toto provideprovide sufficientlysufficiently working,working, reliablereliable andand cost-efficientcost-efficient systemssystems overover time.time. SpecificSpecific problemproblem statesstates cancan bebe well-definedwell-defined andand optimized,optimized, butbut inin reality,reality, transitiontransition processesprocesses areare oftenoften drivendriven byby aa multitudemultitude ofof uncertain uncertain conditions. conditions. Therefore, Therefore, the the proposed proposed approach approach serves serves as aas screening a screening method method for decisionfor decision makers makers to realize to realize a masterplan a masterplan and givesand gives a holistic a holistic view view on network on network dynamics, dynamics, rather rather than focusingthan focusing on one on specific one spec problemific problem or state. or state.
2.2. MaterialsMaterials andand MethodsMethods 2.1. Model Development 2.1. Model Development This section presents the development of the model to assess WDN transitioning, on the basis This section presents the development of the model to assess WDN transitioning, on the basis of of the city masterplan, future network design alternatives and concepts for system adaptation. the city masterplan, future network design alternatives and concepts for system adaptation. Additionally, all planning options are assessed by a variety of scenarios (e.g., demand increase due to Additionally, all planning options are assessed by a variety of scenarios (e.g., demand increase due population growth) during the transition process. In Figure1 the model is shown in a flow chart and to population growth) during the transition process. In Figure 1 the model is shown in a flow chart described in detail in the subsequent sections (see headed associated section numbers). and described in detail in the subsequent sections (see headed associated section numbers).
FigureFigure 1.1. DescriptionDescription ofof thethe modelmodel forfor waterwater distributiondistribution networknetwork (WDN)(WDN) transitioning.transitioning.
Entropy 2018, 20, 708 4 of 21 Entropy 2018, 20, x FOR PEER REVIEW 4 of 21
2.1.1.2.1.1. City City Masterplan Masterplan InIn urban urban planning, planning, the the citycity masterplanmasterplan comprisescomprises a description of of the the futu futurere city’s city’s spatial spatial and and temporaltemporal development, development, defines defines regulatory regulatory changes, changes, and and lays lays out aout strategic a strategic direction direction of future of future visions. Comprehensivevisions. Comprehensive objectives objectives regarding regarding urban landscape urban landscape and water and resource water resource development, development, national andnational public and interests public areinterests specified are specified from a municipality from a municipality perspective perspective and therefore and therefore a masterplan a masterplan is case studyis case specific study specific [24]. Such [24]. aSuch blueprint a blueprint for the for futurethe future is the is the basis basis for for the the successful successful realization realization ofof a transitiona transition process, process, out out of of which which various various planning planning alternatives alternatives cancan be derived for for further further testing testing and and optimization.optimization. Furthermore, Furthermore, it it decreasesdecreases thethe numbernumber of uncertainties and and makes makes the the modeling modeling process process lessless complex complex [25 ,26[25,26].]. The masterplanThe masterplan defines, defines, for example, for example, ambitions ambitions from centralized from tocentralized decentralized to waterdecentralized management water in management the future, the in the disconnection future, the disconnection of abandoned of city abandoned districts duecity todistricts water due quality to problems,water quality expected problems, city densifications expected city or densifications expanding neighborhoods, or expanding neighborhoods, which lead to network which lead growth. to Innetwork the cases growth. where In no the masterplan cases where is available, no masterplan stochastic is available, network stochastic growth models network such growth as random models or fitness-basedsuch as random attachment or fitness-based models canattachment be used model to anticipates can be network used to anticipate development network [27]. development [27]. 2.1.2. Source and Destination Networks 2.1.2. Source and Destination Networks The starting point of this modeling approach is an existing hydraulic model (e.g., EPANET 2 model)The of starting the WDN point (hereinafter of this modeling called sourceapproach network). is an existing It includes hydraulic all water model sources, (e.g., EPANET pipes and 2 junctionsmodel) of with the theirWDN attributes, (hereinafter control called devices source and netw allork). information It includes on spatiallyall water andsources, time pipes dependent and waterjunctions consumption with their andattributes, water control leakage. devices While an thed all source information network on spatially represents and an time existing dependent WDN, thewater future consumptionsystem may and be water fairly leakage. unknown While in terms the so ofurce a detailednetwork networkrepresents layout an existing and future WDN, water the demandfuture system (e.g., duemay tobe cityfairly expansions). unknown in terms Based of on a detailed a city masterplan, network layout a new and future future supplywater demand concept can(e.g., be developed,due to city considering,expansions). e.g.,Based various on a futurecity masterplan, network topologies. a new future In this supply process, concept many can future be systemsdeveloped, (destination considering, networks) e.g., various with different future network graph theoretical topologies. and In this hydraulic process, design many arefuture created systems (e.g., (destination networks) with different graph theoretical and hydraulic design are created (e.g., loop loop degree of the network, design demand and supply redundancy). To account for future demand degree of the network, design demand and supply redundancy). To account for future demand uncertainty in the design process, different pipe capacity factors (hereinafter called “safety factors”) uncertainty in the design process, different pipe capacity factors (hereinafter called “safety factors”) are used. Compared to the source network, the destination network differs in its topology, demand are used. Compared to the source network, the destination network differs in its topology, demand distribution, pipe diameter & roughness, position of water sources and water losses (see Figure2). distribution, pipe diameter & roughness, position of water sources and water losses (see Figure 2).
FigureFigure 2.2. ConceptualConceptual representation representation of an of urban an urban transi transitiontion affecting affecting the water the distribution: water distribution: Source Sourcenetwork network and possible and possible future futuredestination destination networks. networks.
GivenGiven a a defined defined goal goal inin thethe citycity masterplan,masterplan, aa setset ofof destination networks is is created. created. Thereby Thereby partsparts of of the the source source network network and and the the newly newly designed designed “in-silico” “in-silico” WDN WDN parts parts are are combined. combined. The Theidea idea is tois use to use the the often often available available future future road road network network (RN) (RN) from from city city plannersplanners as the basis basis for for an an automatic automatic WDNWDN planning planning approach. approach. PreviousPrevious studies proved the high co-location co-location between between road road and and urban urban infrastructureinfrastructure networks, networks, where where aboutabout 80%80% ofof WDNsWDNs are located below below 50% 50% of of the the RN RN [28,29]. [28,29]. In In the the presented model, it is assumed that 100% of the WDN is co-located with the RN (WDN ⊆ RN). presented model, it is assumed that 100% of the WDN is co-located with the RN (WDN ⊆ RN). However, not all roads may contain pipes; this is mainly due to cost reasons. So there are the two However, not all roads may contain pipes; this is mainly due to cost reasons. So there are the two extreme cases of possible “in-silico” WDN topologies; (1) a branched network, representing the extreme cases of possible “in-silico” WDN topologies; (1) a branched network, representing the minimum spanning tree of the RN, and (2) a highly looped topology, where the WDN layout is minimum spanning tree of the RN, and (2) a highly looped topology, where the WDN layout is identical with the RN. Between these two cases, the loop degree can vary with the cycle index (CI).
Entropy 2018, 20, 708 5 of 21 identicalEntropy 2018 with, 20, thex FOR RN. PEER Between REVIEW these two cases, the loop degree can vary with the cycle index5 of (CI). 21 While a CI of 0 describes a branched layout, a CI > 0 indicates the availability of alternative flow While a CI of 0 describes a branched layout, a CI > 0 indicates the availability of alternative flow paths paths (loops) in the WDN, which is also an indicator for reliability and redundancy. More detailed (loops) in the WDN, which is also an indicator for reliability and redundancy. More detailed information of the CI can be found in Mair et al. [29]. During the generation process of the future WDN information of the CI can be found in Mair et al. [29]. During the generation process of the future parts, different CIs are considered. Furthermore, the digital elevation model (DEM), the existing WDN, WDN parts, different CIs are considered. Furthermore, the digital elevation model (DEM), the (future) demand distribution, the position of (future) water sources and the (future) road network are existing WDN, (future) demand distribution, the position of (future) water sources and the (future) required for model input (see Figure3). The “in-silico” WDN parts can either represent missing data road network are required for model input (see Figure 3). The “in-silico” WDN parts can either of existing systems, or possible future network expansions/densifications. represent missing data of existing systems, or possible future network expansions/densifications.
FigureFigure 3. 3.Example Example of of an an existing existing WDN WDN layout layoutand and thethe approximationapproximation ofof unknownunknown WDN parts using spatialspatial road road network network data data as as surrogate. surrogate.
TheThe WDN WDN creation creation is is performed performed with with DynaMind, DynaMind, anan openopen sourcesource softwaresoftware writtenwritten inin C++C++ and and developeddeveloped at at the the Unit Unit for for Environmental Environmental Engineering Engineering ofof thethe UniversityUniversity ofof Innsbruck.Innsbruck. The software containscontains (1) (1) a a spanning spanning tree tree based based algorithm algorithm forfor designingdesigning aa minimalminimal operating new network network layout, layout, (2)(2) an an algorithm algorithm to to create create a a cyclic cyclic structure structure for for the the purposepurpose ofof networknetwork reliability and (3) an an automated automated pipe-sizingpipe-sizing algorithm algorithm to to create create WDN WDN based based on on geographic geographic information information system system (GIS) (GIS) data data as input as input [30]. To[30]. obtain To aobtain connected a connected network, network, the “in-silico” the “in-silico” parts are parts connected are connected to the closest to the junctionclosest junction of the existing of the WDN,existing unless WDN, other unless connection other connection points are points manually are defined.manually The defined. software The uses software a pipe uses sizing a pipe algorithm sizing foralgorithm selected pipefor selected sets (e.g., pipe all sets unknown (e.g., all WDN unknow parts)n WDN based parts) on a defined based on pressure a defined surface pressure inclination surface at inclination at hourly peak demand (Qh,max) as presented by Saldarriaga et al. [31]. Other WDN design hourly peak demand (Qh,max) as presented by Saldarriaga et al. [31]. Other WDN design optimization algorithmsoptimization might algorithms be more might suitable be more when suitable focusing when on focusing the detailed on the planning detailed planning of small of case small studies. case studies. However, the reasons for choosing this design algorithm are the low computational costs However, the reasons for choosing this design algorithm are the low computational costs and the good and the good approximation of optimal WDN design solutions, even for WDNs with several approximation of optimal WDN design solutions, even for WDNs with several thousands of nodes thousands of nodes and pipes. and pipes.
2.1.3.2.1.3. Intermediate Intermediate State State Networks Networks InIn most most cases, cases, changes changes from from an an existing existing system system toto thethe finalfinal systemsystem are long term processes processes which which cannotcannot be be directly directly implemented implemented at at one one specificspecific timetime step,step, butbut havehave toto bebe successivelysuccessively introduced in in different phases, making the modeling of intermediate transition states unavoidable [18]. During different phases, making the modeling of intermediate transition states unavoidable [18]. During such a transition process the network’s structure and function changes progressively. Parts of the such a transition process the network’s structure and function changes progressively. Parts of the existing system may be taken out of service, while other parts are connected to the existing system or existing system may be taken out of service, while other parts are connected to the existing system the demand pattern changes, e.g., due to changing land use. At the same time, the total water or the demand pattern changes, e.g., due to changing land use. At the same time, the total water consumption and its spatial distribution can change over time. Such stresses can cause a system consumption and its spatial distribution can change over time. Such stresses can cause a system breakdown, where required performance levels cannot be guaranteed anymore. In our analysis breakdown, where required performance levels cannot be guaranteed anymore. In our analysis several transition state models, which represent specific time steps during the investigation period, are automatically created (see Figure 4).
Entropy 2018, 20, 708 6 of 21 several transition state models, which represent specific time steps during the investigation period, are automatically created (see Figure4). Entropy 2018, 20, x FOR PEER REVIEW 6 of 21
FigureFigure 4. 4.Automatic Automatic creation creation ofof intermediateintermediate WDN on basis of of the the source source and and destination destination WDN WDN and and thethe city city masterplan. masterplan.
TheThe basis basis forfor thethe intermediateintermediate statestate modelmodel configurationsconfigurations is is the the source source and and the the destination destination networksnetworks and and the the masterplan, masterplan, whichwhich describesdescribes the spatiotemporal development development of of the the city, city, and and as as wellwell as theas WDN.the WDN. By disconnecting By disconnecting spatially spatia definedlly pipesdefined from pipes the WDN from (“intended the WDN disconnection”), (“intended thedisconnection”), network may bethe splitnetwork into may sub-networks be split into which sub-networks are not connected which are to not the connected water source to the anymore. water Thissource is the anymore. case when This is a the pipe case coincides when a pipe with coincides a bride with or cut-edge a bride or of cut-edge the network, of the network, whose deletionwhose increasesdeletion increases the number the number of connected of connected components compon [32ents]. Resulting[32]. Resulting “unintended” “unintended” disconnections disconnections are are determined through a network connectivity analysis. Unconnected parts are either additionally determined through a network connectivity analysis. Unconnected parts are either additionally removed, or reconnected to the main network, depending on the unintended and intended pipe removed, or reconnected to the main network, depending on the unintended and intended pipe disconnection ratio. Newly connected pipes have the attributes (location, connection points, disconnection ratio. Newly connected pipes have the attributes (location, connection points, diameter) diameter) of the destination network and their year of connection is defined in the masterplan. The of the destination network and their year of connection is defined in the masterplan. The disconnected disconnected nodal demand is shifted to the newly connected parts, and the distribution is assumed nodal demand is shifted to the newly connected parts, and the distribution is assumed to coincide to coincide to the final WDN, while the total demand is scenario dependent (see Section 2.1.4). By the to the final WDN, while the total demand is scenario dependent (see Section 2.1.4). By the fact that fact that in a first step the intermediate WDN state are not individually designed, a “single state in a first step the intermediate WDN state are not individually designed, a “single state design” is design” is followed. With this strategy critical WDN states are identified in space and time. In a followed. With this strategy critical WDN states are identified in space and time. In a second step a second step a WDN re-design based on the least- “monetary” cost path is considered in case a WDNspecified re-design performance based on cannot the least- be assured “monetary” (see Section cost path 2.1.6). is considered in case a specified performance cannot be assured (see Section 2.1.6). 2.1.4. Scenario Analysis 2.1.4. Scenario Analysis Future water demands and their geospatial distributions are highly uncertain [33]. They depend Future water demands and their geospatial distributions are highly uncertain [33]. They depend on multiple factors, including changes in population and consumption behavior, alterations in land onuse, multiple and tourism factors, [34]. including Water loss changes reduction in population is a main challenge and consumption in WDN operation behavior, and alterations management, in land use,saving and valuable tourism [resources34]. Water and loss providing reduction isadditional a main challenge flow capacities in WDN [35]. operation Furthermore, and management, the water savingdemand valuable fraction, resources which is and supplied providing via the additional central distribution flow capacities system, [35 depends]. Furthermore, on the degree the water of demanddecentral fraction, supply which(e.g., rainwater is supplied harvesting) via the centralor the provision distribution of sufficient system, fire depends flow [36]. on theIn this degree work of decentralwe investigate supply possible (e.g., rainwater future developments harvesting) orof thethe provisioncity’s total ofwater sufficient demand fire by flow a scenario [36]. In analysis, this work wewhere investigate the base possible demand future is multiplied developments by time ofdependent the city’s factors total water [37]. demand by a scenario analysis, where the base demand is multiplied by time dependent factors [37]. 2.1.5. Simulation and Performance Assessment 2.1.5. Simulation and Performance Assessment The presented model has an interface to the hydraulic solver EPANET 2 [38] by which every networkThe presented state is simulated model hasfor peak an interface demand toand the a pe hydraulicriod of low solver water EPANET usage. Different 2 [38] by daily which patterns every networkfor domestic state isand simulated industrial for demands peak demand as well and as for a period water losses of low are water applied usage. [39]. Different With the daily simulation patterns forresult, domestic global and performance industrial demands indicators as are well calculated as for water to assess losses arethe appliedhydraulic [39 condition,]. With the the simulation water result,quality global and performancethe reliability indicatorsof the WDN. are calculatedThe follow toing assess performance the hydraulic indicators condition, are calculated: the water Nodal quality andpressure the reliability head at ofpeak the demand, WDN. The maximum following water performance age during indicators a low demand are calculated: period, flow Nodal entropy pressure at headhourly at peak peak demand, demand, maximumand the number water of age elem duringentary a low loops demand of the created period, WDN flow entropy layouts. at hourly peak demand,The and principles the number of global of elementary performance loops indicators of the created (PIs) are WDN briefly layouts. outlined. We use normalized performance indices, where each node i of the WDN is associated with a performance value from 0 (requirements not fulfilled) to 1 (requirements fulfilled), based on predefined threshold limits [40]. Equation (1) shows the calculation of the local nodal performance PIi with the upper and lower threshold values Tu and Tl. The factor α (0 or 1) depends on the performance criterion (minimum pressure or maximum water age), and xi is the performance variable (e.g., nodal pressure). In
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The principles of global performance indicators (PIs) are briefly outlined. We use normalized performance indices, where each node i of the WDN is associated with a performance value from 0 (requirements not fulfilled) to 1 (requirements fulfilled), based on predefined threshold limits [40]. Equation (1) shows the calculation of the local nodal performance PIi with the upper and lower threshold values Tu and Tl. The factor α (0 or 1) depends on the performance criterion (minimum pressure or maximum water age), and xi is the performance variable (e.g., nodal pressure). In addition, a weight wi (e.g., nodal demand) is assigned to the local performances PIi and aggregated to one global representative value PI, where N is the total number of nodes (see Equation (2)).
|0 − α|, x ≤ T i l PI = |1 − α|, xi ≥ Tu (1) i xi−Tl − α , x > T ∧ x < Tu Tu−Tl i l i
∑N w × PI = i=0 i i PI N (2) ∑i=0 wi For the WDN reliability assessment the informational flow entropy E is calculated. The concept is based on Shannon’s entropy function nn S = − ∑ pl ln pl (3) l=1 where S is the entropy; pl is the probability of the l-th outcome; and nn is the number of outcomes [10]. S is zero, if one event is certain and the probabilities of the other events are zero. Tanyimboh and Templeman [41] developed a method to account for entropy in WDNs (Equation (4)).
s N ! Q Q d d Qij Qij E = − ∑ 0k ln 0k − ∑ i ln i + ∑ ln (4) T T T Ti T Ti k=1 i=1 ij∈NDi | {z } | {z } E-supply E-node(s) source(s)
In WDN analysis, E describes the uncertainty of all possible flow paths from the source to every demand node [11,42]. Usually, the number of sources is limited to one or a few supply nodes, confronting many demand nodes and, therefore, inhomogeneity in the flow distribution that exists. Also, the node degree (i.e., connected pipes to a junction) is limited through space [43], which influences entropy maximization. High entropy values indicate that a demand node is connected by many equally important flow paths, which characterizes highly reliable and redundant systems that can cope best with failures, such as pipe breaks [44]. Hence, in terms of WDN design, a high entropy value is sought. The value increases when the system is supplied by more sources of equal importance and when the flow paths have similar flows (absence of a “main” path). E consists of two terms, one describes the entropy related to the supply sources, and the other is related to the nodes. N is the total number of nodes, s denotes the number of sources, T is the total demand (=ˆ total inflow to the WDN), di is the demand at node i, Ti is the total inflow at node i, Qij is the outflow at node i to each successor node j (ij ∈ NDi, the pipe set of successors at node i) and Q0k is the inflow from supply source k [13]. When, e.g., considering only one supply source, the first term in Equation (4) is zero. Moreover, the number of elementary loops in the network is assessed by Γ = E − N + 1, where E is the number of edges (pipes, valves, pumps) and N the number of nodes (junctions, tanks, reservoirs) of the WDN [43]. The various WDN design alternatives are assessed with a simple cost function which depends on the length and diameter of the pipes [13]. This allows for a cost-reliability comparison of different transition strategies, to support decision makers in choosing a reliable layout and design for the new WDN. Any other hydraulic modeling [13], network graph [32], or energy [45] based performance indicators can easily be implemented in the model. Entropy 2018, 20, 708 8 of 21
2.1.6. Critical Performance and Adaptation Existing WDNs can tolerate a certain amount of deviations from the optimum planning state to deal with uncertainties (e.g., demand increase, connectivity loss), whilst still guaranteeing sufficient performance requirements (e.g., sufficient pressure). In case the WDN cannot satisfy all requirements local adaptation measures (e.g., pipe replacement) must be considered to improve the performance to a sufficient level. For cost benefits, an effort is made to leave existing components of the WDN unchangedEntropy 2018 as, 20 much, x FOR asPEER possible. REVIEW Therefore, we focus on the redesign and replacements of the weakest8 of 21 components by a diameter increase and roughness decrease, in case the minimum pressure threshold valuecomponentspcrit is not by met.a diameter To find increase the weak and networkroughness components, decrease, in case pipes the with minimum unusual pressure high friction threshold loss value pcrit is not met. To find the weak network components, pipes with unusual high friction loss (user-defined threshold hcrit) are identified and redesigned on a least- “monetary” cost path from the (user-defined threshold hcrit) are identified and redesigned on a least- “monetary” cost path from the critical node to the supply source. The concept is shown in Figure5 and subsequently described. critical node to the supply source. The concept is shown in Figure 5 and subsequently described. The The WDN can be mathematically represented as weighted graph G(V, E(W)), which consists of a node WDN can be mathematically represented as weighted graph G(V, E(W)), which consists of a node set set V, an edge set E and a set of values W mapped. Dijkstra’s algorithm [46] is used to identify the V, an edge set E and a set of values W mapped. Dijkstra’s algorithm [46] is used to identify the shortest shortest path L in the network from a critical node (e.g., minimum pressure pmin) to a given root node path L in the network from a critical node (e.g., minimum pressure pmin) to a given root node (e.g., (e.g., water source S). water source S).
FigureFigure 5. 5.Local Local adaptation adaptation concept concept basedbased onon the redesign of critical critical pipes pipes along along the the least- least- “monetary” “monetary” costcost path. path.
AllAll edges edgesE Eof of the the graph graphG Gare are thereby thereby weighted weighted withwith thethe monetarymonetary costscosts wij(e(eijij),), wherewhere eeij ijisis the the edgeedge between between node nodei andi andj andj andw wijij> > 0.0. Along the shortest path, path, the the pipes pipes with with unusual unusual high high unit unit head head loss (ho,i,j > crithcrit) are identified and successively redesigned in an iterative process based on Equation loss (ho,i,j > h ) are identified and successively redesigned in an iterative process based on Equation (5), (5), where new and old pipe diameters are denoted with dn,i,j and do,i,j, hn and ho,i,j are the new and old where new and old pipe diameters are denoted with dn,i,j and do,i,j, hn and ho,i,j are the new and old ® unitunit head head loss, loss, respectively respectively [ 47[47].]. The The followingfollowing algorithmalgorithm waswas implemented in in MATLAB MATLAB R2016b R2016b®. .