Over the recent years, managers of the Algerian National Sanitation Office (ONA) have been worrying about the degraded state of their Urban Drainage Systems (UDS). This infrastructure failure is due essentially to the lack of funding and absence of adequate structured methodology for diagnosis and maintenance. As a result, ONA's managers found it very interesting to get a tool that allows them to assess their management of UDS operation. The aim of this paper is therefore to provide an assessment tool to managers for a good network operation. The adopted approach is participative and takes into account the specific local context. Six performance indicators, grouped into two criteria, have been constructed to achieve this objective. These indicators have been chosen for their effectiveness; they are scaled to get their performance scores according to a scaling constructed here based on standards when available and to the ONA expert's recommendations. The developed tool is applied to the UDS of Bejaia City, in north-eastern Algeria. The assessment and the analysis of the performance evolution of these indicators for the period 2017–2021 are carried out. The results highlighted successes that can be maintained as well as weaknesses that need to be improved.

  • A participative approach is adopted to assess and to analyse the operation of the Urban Drainage Systems (UDS).

  • Performance indicators are selected according to the availability and reliability of practical data.

  • Performance scales are constructed for the performance indicators with the help of managers and researchers.

  • The proposed methodology is applied to the UDS of Bejaia City for the period 2017–2021.

Graphical Abstract

Graphical Abstract
Graphical Abstract

The main function of the operation of Urban Drainage Systems (UDS) is to ensure the integrity and the capacity of pipe materials to support dead and live loads. It is supposed to operate properly during its service life (Ramos-Salgado et al. 2022). However, the UDS inevitably ages and degrades. In fact, managers of the Algerian National Sanitation Office (ONA) have been worrying about the degraded state of their UDS (Igroufa et al. 2020). This infrastructure failure is essentially due to the absence of adequate structured methodology of maintenance (Benzerra et al. 2012; Bedjou et al. 2019). In addition, the installation of appropriate management for the proper UDS operation has been constrained by several aspects such as lack of human and financial resources, lack of motivation and awareness, and limited data collection capacity. Consequently, ONA managers have been managing their assets without estimating quantitatively their performance gaps. As a result, ONA found it very interesting to get a tool that allows them to assess their management of UDS operation.

Performance Indicators (PI) constitute one of the most useful tools for quantifying the efficiency and the effectiveness of actions, and for supporting the monitoring of services over time (Santos et al. 2019). This tool has been successfully applied in the water field, mainly for water supply and wastewater services. In fact, several studies have been published in the field of water service management using performance indicators (Matos et al. 2003; Haider et al. 2015; Silva et al. 2016; Jensen & Wu 2018; Nam et al. 2019). Those authors have developed the PI in several aspects, such as: water resource management, operational and environmental practices, personal training, physical infrastructure, customer service, water quality, public health, and financial issues. Its application would be beneficial in terms of: collection of information, detection of problems, definition of priority objectives, and support of the decision-making process. This tool should be adapted to local specificities and should take into account the available information.

Recently, several authors have applied the assessment framework using a protocol based on PI. Examples are Collivignarelli et al. (2021) and Santos et al. (2022), who aimed to evaluate the wastewater service. Collivignarelli et al. (2021) used and calculated performance indices to analyse the performance of sewer systems and wastewater treatment plants. The tool allows to report the factual state of the system in order to improve the quality of services offered to the public. Santos et al. (2022) built a system of objectives, criteria, and performance metrics for two Portuguese water utilities. The main purpose is to identify the main strengths and weaknesses of the system's functioning, and to support the decision-making. Another research was carried out by Vanegas et al. (2022), who used two performance indicators to evaluate the deterioration model of sediment deposit. The aim is to prioritise inspections of sewer pipes based on self-cleansing criteria.

Within the Algerian context, the research study conducted by Benzerra et al. (2012) was the first that introduced and implemented the notion of PI for UDS. In fact, a hierarchical structure of objectives, criteria and PI was developed to measure the sustainability of Algerian urban drainage systems. Recently, Bedjou et al. (2019) proposed two operating indicators to evaluate the performance of ONA maintenance practices. The PI were calculated and then compared between two Algerian cities during the years 2011–2016. Another research was achieved by Igroufa et al. (2020), who developed an assessment framework for support infrastructure asset management. Two main objectives, six criteria, and 31 PI were constructed with the consultation of experts. The assessment tool takes into account the financial capacities of managers and the local context. The performance assessment of the two identified objectives was performed during the year 2018. Finally, Mezhoud et al. (2022) were interested in the evaluation and the prioritisation of the defects of the UDS using decision support methods. The objective is to support the ONA in its decision-making challenge on priority defects for maintenance work.

In view of the above considerations, this paper aims to answer some specific questions so that managers can take actions relating to the management of the UDS operation. It mainly seeks to achieve two main targets. The first one is to assess the operation of the UDS using PI during the period 2017–2021. The PI used in the assessment tool are defined from the regional works mentioned above. The indicators are then evaluated using performance scales, which are constructed with the help of experts. This performance assessment will help managers to identify the different elements and actions that need improvement. The second target is to analyse the performance evolution of each PI from 2017 to 2021. The interpretation of this evolution will provide answers to two questions: How could managers improve their actions? And what resources will be mobilised to achieve a good operation of the UDS? An example of application is shown on the UDS of Bejaia, a city in north-eastern Algeria.

Performance indicators can be defined as metrics used to quantify the productivity of an activity. They constitute a fundamental component of any performance assessment system. In general, the PI are expressed as ratios between variables, and these ratios may be commensurate (e.g., %) or non-commensurate (e.g., €/m3) (Santos 2021). They provide valuable information on whether the performance of the infrastructure is improving or worsening (Berg 2020). Their main objective is to provide insights into the behaviour of systems in order to make their management easier (Santos 2021).

To satisfy the objective of a good operation of the studied UDS, two criteria were found essential. The first one concerns the maintenance practices, and the second deals with the rehabilitation actions. These actions are performed to maintain the function of an asset and extend its service life (Okwori et al. 2020), to guarantee proper transfer of sewage to the wastewater treatment (Tomczak & Zielińska 2017), to keep existing capital assets in serviceable condition, to improve the service provided to users, and to ensure the reliability and the resilience of the system. To reach an effective maintenance and rehabilitation, it is essential to create a database containing historical data and information about the network. The two criteria also represent the link between the objective and the PI, on the one hand. On the other hand, they constitute reference indices in order to facilitate the management improvement to ONA. The two criteria are composed of a set of PI, which are selected from the works of Igroufa et al. 2020 (Figure 1). The use and the choice of these PI are highly affected by data availability, quality and accuracy. In fact, the data available in the ONA agency allow to successfully implement the indicators in the case of Bejaia City. Moreover, these PI provided the following features:
  • (1)

    They are representative: the indicators are truly reflective of the quantities and characteristics they are intended to represent;

  • (2)

    They are presented quantitatively: the indicators provide information which can be used by decision-makers;

  • (3)

    They are verifiable: the accuracy of the values of the indicators can be checked;

  • (4)

    They are clear: the indicators are easily understood and interpreted;

  • (5)

    They are finalised: the indicators are linked into the system to allow feedback of information for the decision-making process.

Figure 1

The summary of criteria and indicators (based on Igroufa et al. 2020).

Figure 1

The summary of criteria and indicators (based on Igroufa et al. 2020).

Close modal

The definition, the unit, and the processing rule of each PI are detailed in Table 1.

Table 1

Description of performance indicators identified

Performance IndicatorUnitDefinition and processing rule
PI11 Number of black spots per km of the network Nbr/km Number of points per km of the sewerage. These spots present sites with structural sensitivities, they are characterised by the repetition of the problem and the need to treat them at least twice per year (e.g., counter slope, root intrusion, … etc.). 
PI12 Rate of preventive curing on surface structure Number of manholes and inlets curated preventively divided by the total number of manholes and inlets during the assessment period.
 
  With:
: Rate of preventive curing on surface structure;
: Number of manholes and inlets curated preventively;
: Total number of manholes and inlets. 
PI13 Rate of restorative curing on surface structure Number of manholes and inlets curated restoratively divided by the total number of manholes and inlets during the assessment period.

With:
: Rate of restorative curing on surface structure;
: Number of manholes and inlets curated restoratively;
: Total number of manholes and inlets. 
PI21 Rate of replaced pipes Length of defective pipes replaced divided by the total pipe length during the assessment period

With:
: Rate of replaced pipes;
: Length of pipes replaced;
: Total length of pipes. 
PI22 Rate of repaired pipes Length of defective pipes repaired divided by the total pipe length during the assessment period

With:
: Rate of repaired pipes;
: Length of pipes repaired;
: Total length of pipes. 
PI23 Rate of renovated pipes Length of defective pipes renovated divided by the total pipe length during the assessment period

With:
: Rate of renovated pipes;
: Length of pipes renovated;
: Total length of pipes. 
Performance IndicatorUnitDefinition and processing rule
PI11 Number of black spots per km of the network Nbr/km Number of points per km of the sewerage. These spots present sites with structural sensitivities, they are characterised by the repetition of the problem and the need to treat them at least twice per year (e.g., counter slope, root intrusion, … etc.). 
PI12 Rate of preventive curing on surface structure Number of manholes and inlets curated preventively divided by the total number of manholes and inlets during the assessment period.
 
  With:
: Rate of preventive curing on surface structure;
: Number of manholes and inlets curated preventively;
: Total number of manholes and inlets. 
PI13 Rate of restorative curing on surface structure Number of manholes and inlets curated restoratively divided by the total number of manholes and inlets during the assessment period.

With:
: Rate of restorative curing on surface structure;
: Number of manholes and inlets curated restoratively;
: Total number of manholes and inlets. 
PI21 Rate of replaced pipes Length of defective pipes replaced divided by the total pipe length during the assessment period

With:
: Rate of replaced pipes;
: Length of pipes replaced;
: Total length of pipes. 
PI22 Rate of repaired pipes Length of defective pipes repaired divided by the total pipe length during the assessment period

With:
: Rate of repaired pipes;
: Length of pipes repaired;
: Total length of pipes. 
PI23 Rate of renovated pipes Length of defective pipes renovated divided by the total pipe length during the assessment period

With:
: Rate of renovated pipes;
: Length of pipes renovated;
: Total length of pipes. 

To classify performance, it is necessary to compare PI values against reference values. This may be undertaken by defining performance scales for each PI. In fact, these functions establish a relation between the PI values and a scale of classification (Santos 2021). By comparing the result of the indicators with pre-set reference values, it is possible to assign a judgment to the result, e.g., good, acceptable, or unsatisfactory (Brito et al. 2022). These performance scales can be set from the literature review, regulations standards, available assessment frameworks, benchmarking of a representative sample, or expert opinions (Brito et al. 2022). By monitoring the result of PI over time, it is possible to assess whether the implemented actions are having the expected impact.

In the present work, the construction of performance scales for each PI is based on a participatory approach. In fact, it was necessary to organise several meetings and discussions between the ONA agency experts and the researchers from the Laboratory of Applied Hydraulics and Environment (LRHAE) at the University of Bejaia. Ten experts were consulted to this aim: five from ONA and five from LRHAE. All these experts and researchers have from 10 to 20 years of experience in managing the UDS and conducting research works in the field of asset management and performance assessment. During this process, it was required to take into account the functional requirements of the UDS and the specific local context. Indeed, particular attention was paid to the type of defects appearing in the UDS, and the rate of recorded defects.

It was agreed to choose a scale from 0 to 1; with 1 representing the best performance and 0 the worst. This range of variation makes easy a detailed distinction of the performance evolution. For all the indicators, the principal adopted performance ranges are: very good, good, weak, and bad. As an example, the performance scale of the number of black spots per km of the network is between 0.5 and 1, when the rate is less than or equal to 20%, but if the percentage exceeds the threshold of 40%, the performance is, in this case, zero. Figure 2 shows the performance functions constructed for all the indicators.
Figure 2

Performance scales constructed for each PI.

Figure 2

Performance scales constructed for each PI.

Close modal

The developed assessment tool is applied to the UDS of Bejaia City. The latter is located about 220 km east of Algiers. It has 185.000 inhabitants covering an area of 120.22 km2. Based on the report of ONA (2018), 91.9% of pipes have a diameter between 200 and 650 mm, 7.6% have a large diameter varying from 700 to 1,500 mm, and 0.5% have a diameter less than 200 mm. It has been noted that 99.4% of the network operates in gravity mode, of unitary type and of circular shape (Mezhoud et al. 2022). Based on the review of the available documents and the results of the survey, 79.56% of the pipes are made from concrete, 13.52% from PVC, and the rest are not indicated. Approximately 88.32% of the network pipes are aged but without precision about their age, 8.67% were constructed before 1996, 1.78% between 1997 and 1999, and 1.23% from 2000 to now (Igroufa et al. 2020). According to the inspections carried out by ONA, several anomalies have been noticed in the UDS: presence of sand in pipe, clogging, root intrusion into pipe, chemical attacks on pipe, crack, joint displacement, collapse,…etc. The UDS is thus poorly maintained and presents several black spots. In order to save the lifetime of the network, the managers have to make an adequate structured methodology to maintain and rehabilitate the defected pipes. More information about the study area can be found in Igroufa et al. (2020).

The measures collection of the PI from 2017 to 2021 has required several meetings with the managers. These meetings consisted of a deep research in the registers of data. For each year, the following data were collected:

  • The length of the network: this length increased from year to year according to the investment projects carried out by the locality;

  • The number of inlets and manholes: it also increased over time depending on the length of the extended pipes;

  • The number of black spots: it varies from year to year according to the types of problems, and to the frequency of maintenance.

In addition to these data, a survey containing a set of questions was addressed to the staff of the maintenance department of ONA. It aims to determine the number of manholes and inlets curated preventively and restoratively, and the length of pipes repaired, replaced, and renovated. This allowed us to obtain the values of the indicators for all the years 2017, 2018, 2019, 2020, and 2021; they are reported in Table 2.

Table 2

Measurements of the identified indicatorsa

Years/IndicatorPI11PI12PI13PI21PI22PI23
2017 21.00 04.34 20.05 01.67 00.67 00.00 
2018 21.00 04.63 31.64 01.60 00.96 00.00 
2019 23.00 10.52 44.17 03.96 02.44 00.61 
2020 21.00 07.22 36.26 05.65 03.87 02.08 
2021 21.00 08.34 39.44 06.02 04.58 03.72 
Years/IndicatorPI11PI12PI13PI21PI22PI23
2017 21.00 04.34 20.05 01.67 00.67 00.00 
2018 21.00 04.63 31.64 01.60 00.96 00.00 
2019 23.00 10.52 44.17 03.96 02.44 00.61 
2020 21.00 07.22 36.26 05.65 03.87 02.08 
2021 21.00 08.34 39.44 06.02 04.58 03.72 

aRefer to Table 1 for the description of indicators.

In this section, the performance assessment of the UDS operation is evaluated during five years for the case of Bejaia City in Algeria. The performance evolution from 2017 to 2021 of each indicator is analysed. The performance functions constructed for the indicators lead to the performance scores plotted in Figure 3. According to these results, all the indicators showed a bad or a weak performance during the five years. The exceptions concerning PI23 during 2017 and 2018, and PI13 during 2019 are noticed. The first one presented a nil performance, whereas the second a good performance. The low quality of performance displayed by most of PI demonstrates the various problems that exist, which can be summarised as follows:
  • Weakness of the budget allocated to the operation of the network;

  • Absence of cooperation between ONA agency and the university (No agreements for a fruitful exchange of new methodology and technology used in the management of UDS);

  • Lack of qualified and specialised personnel in the operational management of UDS;

  • Absence of training for the employees regarding the best practices of maintenance and rehabilitation;

  • Absence of an organisation that ensures the link between the researchers and the managers (so that managers can communicate their problems to the researchers and exploit the results of the research carried out).

Figure 3

Performance of indicators during the years 2017–2021. (a) Performance of indicators during the year 2017. (b) Performance of indicators during the year 2018. (c) Performance of indicators during the year 2019. (d) Performance of indicators during the year 2020. (e) Performance of indicators during the year 2021.

Figure 3

Performance of indicators during the years 2017–2021. (a) Performance of indicators during the year 2017. (b) Performance of indicators during the year 2018. (c) Performance of indicators during the year 2019. (d) Performance of indicators during the year 2020. (e) Performance of indicators during the year 2021.

Close modal

Improving the performance of these indicators will require:

  • More financial and material means;

  • More training for the employees;

  • More coordination and communication between the managers and the owner of the network;

  • More accordance of actions between all stakeholders.

Figure 4 displays the curves of performance evolution of each PI over the five years' period. Analysis of these curves indicates that:
  • The performance curves of PI21, PI22, and PI23 follow an ascending trend during the five years. This can be explained by the material tools implemented by the managers to replace, renovate and repair the defected pipes. However, the performance increase for the three PI is very small. For example, the performance of PI21 rises only from 0.04 in 2017 to 0.13 in 2021. This slight evolution remains not enough to reach a good performance. It is thus essential to invest more in the field of rehabilitation to save the life time of pipes.

  • The performance curves of PI12 and PI13 follow an ascending trend during the first three years. In 2020, the rate of preventive and restorative curing on surface structures has decreased compared to 2017, 2018 and 2019. In fact, ONA, like all companies, has been affected in one way or another by the COVID-19 crisis. Many employees in charge of curing have caught the disease. This has significantly reduced the workforce. In 2021, the performance of both indicators has increased again. This shows that ONA managers have been compelled to reconsider aligning their curing operations with the COVID-19 context to maintain their missions;

  • The performance curve of PI11 follows an ascending trend during 2017 and 2018. In 2019, the performance decreased, then it increased again in 2020 and 2021. This performance fluctuation is due to the characteristics of the rate of black spots per km of the network. In fact, there is a lack of effective treatment of black spots. The managers should adopt a specific program to reduce the number of the existing black spots.

Figure 4

Evolution of performance during the years 2017–2021.

Figure 4

Evolution of performance during the years 2017–2021.

Close modal

In the present work, the performance of the UDS operation has been assessed using a set of performance indicators. An assessment tool has been established and applied to the case of Bejaia City for a period of years ranging from 2017 to 2021. The performance comparison of each indicator over the five years is thus carried out.

The application of the assessment tool has required scheduling multiple meetings with the experts of the UDS management. The discussions aimed to build the performance scales for each PI already defined. In fact, these functions transform the initial measurement of indicators into scores between 0 and 1. The obtained results showed the need for investment in rehabilitation and maintenance of pipes. It was found that except two indicators over two years, all the measured performances were bad or weak. Based on the results of this study, it appears that there are many challenges facing the operation practice in Algeria. In fact, UDS maintenance and rehabilitation are usually carried out only in the event of malfunctions (no operation plan is followed). Moreover, the lack of adequate technological tools and the weakness of the allocated budget constitute the main obstacles to carrying out all these tasks. This also indicates a large divergence in the actions of the stakeholders. Gathering these actors for strategic partnership becomes thus an urgent priority.

Regarding the performance evolution of each indicator, it differs from one PI to another. Three of them, PI21, PI22, and PI23, displayed performance improvement over the considered years. This motivates the ONA's managers to reinforce their actions to achieve their goals. The remaining indicators, PI11, PI12, and PI13, show an increased performance in the first years. Then, the performance relapses for one year, and rises again in the following year. This performance analysis will help ONA's managers to understand the reasons for the performance drop. Consequently, they will manage better the UDS operation by improving their actions.

The assessment tool based on performance indicators provided interesting and useful information to the managers. They can use the results of this study to help them to formulate policy and implement plans which are relevant to the problems that have been exposed. Analysis of indicators' performances gives more details about possible failures and guides ONA's managers to act in order to improve the overall performance. In a future perspective, for the completion of the analysis of the performance of UDS operation, the tool could be extended to identify further criteria and PI applicable to the context of Bejaia City.

The authors would like to express their gratitude to the ONA, which facilitated this research by providing the required data.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

Bedjou
A.
,
Boudoukha
A.
&
Bosseler
B.
2019
Assessment of wastewater asset management effectiveness in the case of rare data and low investments
.
International Journal of Environmental Science and Technology
16
(
7
),
3781
3792
.
http://dx.doi.org/10.1007/s13762-018-2005-3
.
Benzerra
A.
,
Cherrared
M.
,
Chocat
B.
,
Cherqui
F.
&
Zekiouk
T.
2012
Decision support for sustainable urban drainage system management: a case study of Jijel, Algeria
.
Journal of Environmental Management
101
(
10
),
46
53
.
http://dx.doi.org/10.1016/j.jenvman.2012.01.027
.
Berg
S. V.
2020
Performance assessment using key performance indicators (KPIs) for water utilities: a primer
.
Water Economics and Policy
6
(
2
), 2050001.
https://doi.org/10.1142/S2382624X20500010
.
Brito
R. S.
,
Almeida
M. C.
,
Silva
N.
,
Barreto
S.
&
Verissimo
F.
2022
Assessing intermittent saline inflows in urban water systems
.
Water Science & Technology
85
,
90
103
.
Collivignarelli
M. C.
,
Todeschini
S.
,
Abbà
A.
,
Ricciardi
P.
,
Carnevale Miino
M.
,
Torretta
V.
,
Rada
E. C.
,
Conte
F.
,
Cillari
G.
,
Calatroni
S.
,
Lumia
G.
&
Bertanza
G.
2021
The performance evaluation of wastewater service: a protocol based on performance indicators applied to sewer systems and wastewater treatment plants
.
Environmental Technology
.
https://doi.org/10.1080/09593330.2021.1922509
.
Haider
H.
,
Sadiq
R.
&
Tesfamariam
S.
2015
Inter-utility performance benchmarking model for small-to-medium-sized water utilities: aggregated performance indices
.
Journal of Water Resources Planning and Management
142
(
1
).
http://dx.doi.org/10.1061/(ASCE)WR.1943-5452.0000552
.
Igroufa
M.
,
Benzerra
A.
&
Seghir
A.
2020
Development of an assessment tool for infrastructure asset management of urban drainage systems
.
Water Science & Technology
82
(
3
),
537
548
.
http://dx.doi.org/10.2166/wst.2020.356
.
Jensen
O.
&
Wu
H.
2018
Urban water security indicators: development and pilot
.
Environmental Science and Policy
83
,
33
45
.
https://doi.org/10.1016/j.envsci.2018.02.003
.
Matos
R.
,
Cardoso
A.
,
Ashley
R.
,
Duarte
P.
,
Molinari
A.
&
Schulz
A.
2003
Performance Indicators for Wastewater Services. Manual of Best Practice Series
.
IWA Publishing
,
London
, p.
192
,
ISBN 9781900222907
.
Mezhoud
C.
,
Berreksi
A.
,
Bedjou
A.
&
Bosseler
B.
2022
Prioritization of maintenance work in wastewater networks using decision support methods
.
Journal of Water, Sanitation & Hygiene for Development
12
(
2
),
186
199
.
https://doi.org/10.2166/washdev.2022.165
.
Nam
S. N.
,
Nguyen
T. T.
&
Oh
J.
2019
Performance indicators framework for assessment of a sanitary sewer system using the analytic hierarchy process (AHP)
.
Sustainability
11
(
10
),
2746
.
https://doi.org/10.3390/su11102746
.
Okwori
E.
,
Viklander
M.
&
Hedström
A.
2020
Performance assessment of Swedish sewer pipe networks using pipe blockage and other associated performance indicators
.
H2Open Journal
3
(
1
),
46
57
.
https://doi.org/10.2166/h2oj.2020.027
.
ONA
2018
Etudes de diagnostic et de réhabilitation des réseaux d'assainissement lot 2 – villes de Tizi Ouzou et Bejaia, Rapport de synthèse, ville de Bejaia (sous mission B7)
, p.
355
.
Ramos-Salgado
C.
,
Muñuzuri
J.
,
Aparicio-Ruiz
P.
&
Onieva
L.
2022
A comprehensive framework to efficiently plan short and long-term investments in water supply and sewer networks
.
Reliability Engineering and System Safety
219
,
108248
.
https://doi.org/10.1016/j.ress.2021.108248
.
Santos
L. F.
2021
Proposal and Validation of a Performance Assessment Framework for Urban Storm Water Systems
.
PhD Thesis
,
University of Lisbon
, Portugal, p.
251
.
Santos
L. F.
,
Galvao
A. F.
&
Cardoso
M. A.
2019
Performance indicators for urban storm water systems: a review
.
Water Policy
21
(
1
),
221
244
.
Santos
L. F.
,
Cardoso
M. A.
&
Galvao
A. F.
2022
Storm water systems’ performance: assessment framework application to Portuguese water utilities
.
International Journal of Water Resources Development
.
https://doi.org/10.1080/07900627.2021.2004882
.
Silva
C.
,
Saldanha Matos
J.
&
Rosa
M. J.
2016
A comprehensive approach for diagnosing opportunities for improving the performance of a WWTP
.
Water Science & Technology
74
(
12
),
2935
2945
.
http://dx.doi.org/10.2166/wst.2016.432
.
Tomczak
E.
&
Zielińska
A.
2017
Example of sewerage system rehabilitation using trenchless technology
.
Ecological Chemistry and Engineering S
24
(
3
),
405
416
.
doi:10.1515/eces-2017-0027
.
Vanegas
S.
,
Montes
C.
&
Saldarriaga
J.
2022
Prioritizing inspection of sewer pipes based on self-cleansing criteria
.
Urban Water Journal
.
https://doi.org/10.1080/1573062X.2022.2035408
.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY-NC-ND 4.0), which permits copying and redistribution for non-commercial purposes with no derivatives, provided the original work is properly cited (http://creativecommons.org/licenses/by-nc-nd/4.0/).