Collecting Data: Benchmarking Experience in Portugal Jaime Melo Baptista, ERSAR, Portugal
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1 Collecting Data: Benchmarking Experience in Portugal Jaime Melo Baptista, ERSAR, Portugal Water Utility Regulatory Benchmarking: Performance Assessment and Improvement Pristina, Kosovo, February 23, 2015
2 The importance of water
3 The importance of water "The Earth is blue", Yuri Gagarin, aboard the Soyuz-R-7, 1961
4 The importance of water The view of Yuri Gagarin seemed to indicate that Earth has almost limitless reserves of water. But the reality is different, especially if we talk of fresh water. Total water (salt + fresh) Fresh water Fresh water of rivers
5 The importance of water What s the Earth Worth? (TV Chanel History, 2015) 4,600 million years
6 The importance of water What s the Earth Worth? (TV Chanel History, 2015) Water: 5,618 x USD Fossil fuels (crude and shale oil, coal, gas): 716 x USD Timber: 270 x USD Base metals (iron, copper, zinc): 135 x USD Rock (granite, limestone): 93 x USD (17) Rare hearth elements (Scadium...): 24 x USD Precious metals (gold, silver, platinum): 15 x USD Food (meat, fish, vegetables): 2,5 x USD Diamonds: 0,5 x USD Total 6,874 x USD Note: 1 x = 1,000,000,000,000 USD = 1 trillions USD Water is the most valuable tangible resource in Earth!
7 The importance of water Why people have so different water supply and sanitation conditions around the world?
8 The importance of water The public water services: Essential for the social and economic development. They have major implications for the quality of life, environment and public health. Several international initiatives: Millennium Development Goals and the anticipated Sustainable Development Goals. UN resolution 64/292 of 2010 recognizing water and sanitation as a human right. The IWA Lisbon Charter for Guiding the Public Policy and Regulation of Drinking Water Supply, Sanitation and Wastewater Management Services. Governments must create a public policy with the necessary conditions to attend the population.
9 The importance of water IWA approved the "Lisbon Charter for Guiding The Public Policy and Regulation of Drinking Water Supply, Sanitation and Wastewater Management Services": With the principles for good public policy and effective regulation of water services; Proclaiming the responsibilities of the governments and public administration, regulatory authorities, service providers, and users.
10 The importance of water All stakeholders should have an ongoing and open dialogue. They should share information on the provision of water services. Policies on access to information should be formulated and agreed. Balance confidentiality versus wide-ranging, reliable and comprehensive information available to the public.
11 What regulatory model for the water services?
12 Regulatory model for water services We can approach regulation of the water services in different ways. In Portugal we decided to implement regulation: With an integrated (holistic) approach. Operating at national level (mainland). Regulating all the utilities, regardless the governance model (State-owned, municipalowned and private). Adopting a collaborative and pedagogic regulation.
13 REGULATORY MODEL Regulatory model for water services Regulatory model RITA-ERSAR: Structural regulation of the sector Regulation of operator behavior Contribution to the organisation of the sector Legal and contractual regulation Contribution to the legislation of the sector Contribution to the information of the sector Contribution to the capacity building of the sector Economic regulation Quality of service regulation Drinking water quality regulation User interface regulation
14 The success of regulation depends on the ability to manage the implementation of its components, ensuring an effective regulatory integrated approach Regulatory model for water services
15 Regulatory model for water services Articulation with third party entities: Articulation with the environmental authority. Articulation with the water resources authority. Articulation with the public health authority. Articulation with the consumer protection authority. Articulation with the competition authority. Articulation with the sectors stakeholders. Cooperation with other regulatory authorities. Good articulation and common understanding of the boundaries are part of the success.
16 Quality of service assessment system
17 REGULATORY MODEL Quality of service assessment system Regulatory model RITA-ERSAR: Structural regulation of the sector Regulation of operator behavior Contribution to the organisation of the sector Legal and contractual regulation Contribution to the legislation of the sector Contribution to the information of the sector Contribution to the capacity building of the sector Economic regulation Quality of service regulation Drinking water quality regulation User interface regulation
18 Quality of service assessment system The quality of service assessment system has the following characteristics: The system is fed with data: Internal, relating to the utility and system. External, relating to the region of the utility. These data can progress into: Performance indicators; Profile of the utility. Profile of the system. Contextual factors. The system requires reference values and brackets: Desirable levels of service for each quality of service indicator. Defined according to area (ex. areas which are mainly urban, those moderately urban and those mainly rural).
19 Quality of service assessment system The quality of service assessment system: Quality of service assessment system Quality of service indicators Data necessary for assessment Profile of the utility Profile of the system Reference values and brackets Contextual factors Interpretation of the indicators to assess the quality of the service
20 Quality of service assessment system Assessment of the quality of the service is carried out based on the interpretation of the indicators: Comparing the values with the reference values and brackets. Attributing good, average or unsatisfactory performance. Receiving support from the profile of the utility, the system profile and contextual factors, for better interpretation. Based on information validated, the regulator should process the definitive data, and produce: An individual assessment of each utility for the various indicators, with meaningful symbols. An assessment for each indicator at a national level and metric benchmarking comparing groups of similar utilities. Assessment of the evolution of each indicator at the national level (clusters) of utilities, and at the level of each utility.
21 Quality of service indicators
22 Quality of service indicators The most important component of this system is the quality of service indicators: Quality of service indicators are quantitative assessment measures of efficiency and effectiveness for certain aspects of the service: Efficiency measures the extent to which available resources are used in an optimised manner for service creation. Effectiveness measures the extent to which realistically defined management objectives are met. As a whole, the indicators should cover the most important aspects of quality of service in a way that is intended to be correct and balanced.
23 Quality of service indicators The quality of service indicators may cover three major assessment areas: Social sustainability: service accessibility to users and quality of service provided to users. Sustainability of service management: economic sustainability of the service, infrastructural sustainability of the service and productivity of its human resources. Environmental sustainability: efficiency in the use of environmental resources and prevention of pollution.
24 Quality of service indicators It should be the responsibility of the regulator: To define the assessment system, according to the country s context and its level of development. To define the quality of service indicators. To define reference values or brackets that reflect realistic objectives to be achieved. The indicators are important regulation instruments, as they enable: Standardize the collection of information. Assess performance based on clear definitions in a common language. Analyse the evolution over time. Improve the quality of service and greater effectiveness and efficiency of the utilities. Express a right of the users of having access to reliable and easily interpreted information.
25 Quality of service indicators The selection of proposed indicators should take into account: Requirements regarding each indicator, individually. Requirements relating to the set of indicators. Individually, each indicator requires: Rigorous definition, attributing concise meaning and unequivocal interpretation; Possibility to be calculated in total by the utilities without significant additional effort; Possibility to be verified during audits; Simplicity and easy to interpret.
26 Quality of service indicators Collectively, the indicators should be defined so as to ensure the following requirements: Suitability regarding the representation of the main aspects of quality of service, enabling global representation; Absence of any overlapping meaning or objectives between indicators; Reference to the same period of time (ex. one calendar year); Reference to the same geographical area served by the utility; Applicable to utilities with varied characteristics and level of development.
27 Quality of service indicators The aim is to simplify an analysis which by its nature is complex, but please note: Each indicator contributes to the quantification of performance within a given perspective, within a given area and for a given period of time. It is only a partial vision of the global reality and in does not incorporate all of its complexity. Its use out of context may lead to incorrect interpretations. It is necessary to analyse indicators as a whole, with knowledge of cause, and linked to their context.
28 Quality of service indicators Quality of service indicators are expressed by ratios between data from the utility: Each indicator is the result of a processing rule, with: The data necessary for the calculation. The unit in which it should be expressed. The respective algebraic combination. They may be undimensional (ex. in %) or dimensional (ex. in /m3). The denominator for the calculation must represent one dimension of the system or utility (ex. the number of service connections). It must be avoided the use of denominators which may vary significantly from one year to another year due to factors external to the utility.
29 In Portugal: ERSAR defined, in partnership with the LNEC, one set of 16 indicators for each service. They are applied to all operators of water services regardless the ownership and their management model. They are described in Technical Guide 19, Guide for assessing the quality of water and waste services provided to users - 2nd generation assessment system, 2014 edition. Quality of service indicators
30 Quality of service indicators Quality of service indicators for the water supply service: Social sustainability Physical accessibility of the service (%) Economic accessibility of the service (%) Occurrence of supply interruptions [No. / (1000 connections x year)] Quality of supplied water (%) Reply to written suggestions and complaints (%) Service management sustainability Coverage of total expenses (-) Effective connection to the service (%) Non-revenue water (%) Adequacy treatment capacity (%) Mains rehabilitation (%/year) Mains failures [No./(100 km x year)] Adequacy of human resources (No./1000 connections) Environmental sustainability Water losses [l/(water connection x day) ] Fulfilment of the water intake licensing (%) Energy efficiency of pumping installations [kwh/(m3 x 100 m)] Disposal of sludge from the water treatment (%)
31 Quality of service indicators Some of those indicators relates with efficiency: Coverage of total expenses Non-revenue water Adequacy treatment capacity Mains rehabilitation Adequacy of human resources Water losses Energy efficiency of pumping installations. The others are related with effectiveness: Physical accessibility of the service Economic accessibility of the service Occurrence of supply interruptions Quality of supplied water Reply to written suggestions and complaints Effective connection to the service Mains failures Fulfilment of the water intake licensing Disposal of sludge from the water treatment.
32 Quality of service indicators Quality of service indicators for the waste water management service: Social sustainability Physical accessibility of the service (%) Economic accessibility of the service (%) Flooding occurrence [No./(1000 connections x year)] Reply to written suggestions and complaints (%) Service management sustainability Coverage of total expenses (-) Effective connection to the service (%) Adequacy of treatment capacity (%) Sewerage rehabilitation (%/year) Sewer collapses [No./(100 km x year)] Adequacy of human resources [No./(100 km x year)] Environmental sustainability Energy efficiency of pumping installations [(kwh/(m3 x 100 m)] Appropriate disposal of collected wastewater (%) Emergency control discharges (%) Wastewater analysis (%) Compliance with discharge parameters (%) Disposal of sludge from the wastewater treatment (%)
33 Quality of service indicators Some of those indicators relates with efficiency: Coverage of total expenses Adequacy of treatment capacity Sewerage rehabilitation Adequacy of human resources Energy efficiency of pumping installations. The others are related with effectiveness: Physical accessibility of the service Economic accessibility of the service Flooding occurrence Reply to written suggestions and complaints Effective connection to the service Sewer collapses Appropriate disposal of collected wastewater Emergency control discharges Wastewater analysis Compliance with discharge parameters Disposal of sludge from the wastewater treatment
34 Data necessary for assessment
35 Data necessary for assessment Data necessary for assessment: Data form the basic component of a quality of service assessment system. The utility needs to collect, compile and send to the regulator a set of internal data. The regulator should supplement these data with any necessary external data. Each item of data should be in accordance with the definitions published by the regulator. Self-evaluation by the utility of the quality of the database is indispensable. The quality of the data should be defined in terms of: the accuracy of data; the reliability of the information source.
36 Data necessary for assessment Accuracy of data: Scale and Error associated with the data supplied 0-5% Less than or equal to ± 5% 5-20% Greater than ± 5%, but better than or equal to ± 20% 20-50% Greater than ± 20%, but better than or equal to ± 50% % Greater than ± 50%, but better than or equal to ± 100% % Greater than ± 100%, but better than or equal to ± 300% > 300 % Greater than ± 300% Reliability of the information source: Scale and Concept associated (***)Data based on exhaustive measurements, faithful recordings, procedures, research and investigations which are suitably documented and recognised as being the best calculation method. (**) Generically as before, but with some non-significant gaps in the data, such as part of the documentation being missing, calculations being old, or based on unconfirmed records, or also some extrapolated data. (*) Data based on estimates and extrapolations from a limited sample.
37 Data necessary for assessment "Golden rules" for the regulatory authorities: Do not ask the utilities excessive or insufficient data. You should explain the utilities the reason for the demand and the deliverable you want to produce. Do not ask the utilities data you are not able to use and transform it in useful information and knowledge. You only succeed if you are able to transform: Data Information Dissemination to stakeholders Knowledge
38 Data necessary for assessment Data for drinking water supply quality of service: Identification of the utility Identification of the utility (-) Model of governance (-) Bulk system(s) used (-) Typology of the area served (-) Shareholder composition (-) Contract term (-) Dwellings Dwellings with effective service (No.) Dwellings with non-effective available service (No.) Existing dwellings (No.) Complaints Complaints and suggestions (No./year) Replies to complaints and suggestions (No./year) Failures and malfunctions Failures in supply (No./year) Failures in main pipes (No./year) Water balance/water volumes Water which entered into the system (m3/year) Authorised consumption (m3/year) Revenue water (m3/year) Non-revenue water (m3/year)
39 Data necessary for assessment Actual losses (m3/year) Abstracted water in licensed abstractions (m3/year) Abstracted water (m3/year) Treated water exported (m3/year) Control of water quality Mandatory analyses carried out on water quality (No./year) Analyses carried out on parameters with a parametric value (No./year) Mandatory regulatory analyses on water quality (No./year) Analysis carried out in compliance with the parametric value (No./year) Energy Energy consumption for pumping (kwh/year) Standardisation factor (m3/year x 100 m) Own production of energy (kwh/year) Energy consumption (kwh/year) Infrastructures and their use Total size of main pipes (km) Average length of main pipes (km) Main pipes rehabilitated in the last five years (km) Connection pipes (No.) Groundwater abstractions (No.) Surface water abstractions (No.) Pumping stations (No.) Water treatment plants (No.) Other treatment plants (No.) Storage tanks (No.)
40 Data necessary for assessment Reserve water capacity for supply and distribution (m3) Overuse of treatment plants (m3) Underuse of treatment plants (m3) Total capacity of treatment plants (m3) Management and infrastructure knowledge index (-) Treatment sludge Sludge with suitable destination (t/year) Initial stored sludge (t/year) System produced sludge (t/year) Sludge from other systems (t/year) Final stored sludge (t/year) Economics Income and total gains ( /year) Total costs ( /year) Average cost for water supply service ( /year) Average disposable family income ( /year) Tariff approved ( /m3) Certifications Environmental management system certification (-) Quality management system certification (-) Occupational health and safety management system certification (-) Other certifications (-) Human resources Water supply service staff (No.) Outsourced water supply service staff (No.)
41 Data necessary for assessment Data for waste water management quality of service: Identification of the utility Identification of the utility (-) Model of governance (-) Bulk system(s) used (-) Typology of the area served (-) Shareholder composition (-) Contract term (-) Dwellings Dwellings with effective service (No.) Dwellings with non-effective available service (No.) Dwellings serviced by individual waste water solutions (No.) Dwellings with available untreated drainage (No.) Existing dwellings (No.) Equivalent population Equivalent population with satisfactory treatment (valid discharge licence) (e.p.) Equivalent population with satisfactory treatment (expired discharge licence) (e.p.) Equivalent population serviced by treatment plants (e.p.) Complaints Complaints and suggestions (No./year) Replies to complaints and suggestions (No./year) Failures and malfunctions Flooding (No./year)
42 Data necessary for assessment Outflows functioning unsatisfactorily (No.) Structural collapses in main pipes (No./year) Control of water quality Analyses requested (No./year) Analyses carried out (No./year) Waste water and energy Invoiced waste water (m3/year) Collected waste water (m3/year) Volume of waste water treated and supplied to another body (m3/year) Volume of waste water treated and for own use (m3/year) Flow rate measurement index (-) Own production of energy (kwh/year) Energy consumption (kwh/year) Energy consumption for pumping (kwh/year) Standardisation factor (m3/year x 100 m) Infrastructures and their use Total length of main pipes (km) Average length of main pipes (km) Main pipes rehabilitated in the last five years (km) Connection lines (No.) Pumping stations (No.) Waste water treatment plants (No.) Collective septic tanks (No.) Treatment plants with valid discharge licence (No.) Overuse of treatment plants (m3) Underuse of treatment plants (m3)
43 Data necessary for assessment Total capacity of treatment plants (m3) Submarine outfalls (No.) Outflow pipes (No.) Unmonitored outflow pipes (No.) Management and infrastructure knowledge index (-) Treatment sludge Sludge with suitable destination (t/year) Initial stored sludge (t/year) System produced sludge (t/year) Sludge from other systems (t/year) Final stored sludge (t/year) Economics Income and total gains ( /year) Total costs ( /year) Average cost of waste water service ( /year) Average disposable family income ( /year) Tariff approved ( /m3) Certifications Environmental management system certification (-) Quality management system certification (-) Occupational health and safety management system certification (-) Other certifications (-) Human resources Waste water staff (No.) Outsourced waste water staff (No.)
44 Profile of the utility
45 Profile of the drinking water supply utility: Identification of the utility (-) Governance model (-) Contract term (-) Shareholder composition (-) Existing dwellings (No.) Activity volume (m3/year) Typology of the area served (-) Bulk system(s) used (-) Environmental management system certification (-) Certification of quality management systems (-) Other certifications (-) Profile of the waste water management utility: Identification of the utility (-) Model of governance (-) Contract term (-) Shareholder composition (-) Existing dwellings (No.) Dwellings serviced by individual waste water solutions (No.) Activity volume (106 m3/year) Typology of the area served (-) Bulk system(s) used (-) Environmental management system certification (-) Certification of quality management systems (-) Occupational health and safety management system certification (-) Other certifications (-) Profile of the utility
46 System profile (infrastructures)
47 System profile Profile of the drinking water supply systems: Surface water abstractions (No.) Groundwater abstractions (No.) Water treatment plants (No.) Network length (km) Density of connection branches (No. of connection /km network) Pumping stations (No.) Water towers (No.) Treated water reserve capacity (days) Own production of energy (%) Index of all infrastructural knowledge and management of patrimony (-) Profile of the waste water management systems: Waste water treatment plants (No.) Total length of main pipes (km) Submarine outfalls (No.) Pumping stations (No.) Own production of energy (%) Use of treated waste water (%) Discharge licensing (%) Index of all infrastructural knowledge and management of patrimony (-) Index of flow rate measurement (-)
48 System profile Index of all infrastructural knowledge and management of patrimony (-) for water supply utilities: Lack of knowledge area Knowledge area Index of all infrastructural knowledge and management of patrimony (-) for waste water management utilities: Lack of knowledge area Knowledge area
49 System profile Profile of the drinking water supply systems: Surface water abstractions (No.) Groundwater abstractions (No.) Water treatment plants (No.) Network length (km) Density of connection branches (No. of connection /km network) Pumping stations (No.) Water towers (No.) Treated water reserve capacity (days) Own production of energy (%) Index of all infrastructural knowledge and management of patrimony (-) Profile of the waste water management systems: Waste water treatment plants (No.) Total length of main pipes (km) Submarine outfalls (No.) Pumping stations (No.) Own production of energy (%) Use of treated waste water (%) Discharge licensing (%) Index of all infrastructural knowledge and management of patrimony (-) Index of flow rate measurement (-)
50 Contextual factors
51 Contextual factors Contextual factors: The contextual factors are important component in quality of service assessment system. The utility and system profiles already take into account the main contextual factors. However, the assessment system should foresee the possibility of including other contextual factors. They do not affect the assessment, but may be taken into account in the forming of judgment. Utilities should identify, for any indicator, additional contextual factors determinant in the interpretation. The contextual factors to be specified should not be subject to any predefined format, but should refer to auditable information.
52 Reference values and brackets
53 Reference values and brackets The regulator must: Specify quality levels and brackets for quality of service. Adjust the goals of the indicators to address the evolution of the situation and new emerging challenges. Use of ex. semaphore codes for easier perception: Ex 1. AR02 - Economic accessibility of the service (%) Ex 2. AR01 - Physical accessibility of the service (%) APR - rural area; AMU - moderately urban area e APU - urban area Specify compensations in the event of non-compliance.
54 Reference values and brackets Levels and brackets for the quality of service indicators of drinking water supply: Physical accessibility of the service (%): For mainly urban areas served: Good quality of service [95; 100] Average quality of service [80; 95[ Unsatisfactory quality of service [0; 80[ For moderately urban areas served: Good quality of service [90; 100] Average quality of service [80; 90[ Unsatisfactory quality of service [0; 80[ For mainly rural areas served: Good quality of service [80; 100] Average quality of service [70; 80[ Unsatisfactory quality of service [0; 70[ Economic accessibility of the service (%) Good quality of service [0; 0.50] Average quality of service ]0.50; 1.00] Unsatisfactory quality of service ]1.00; + [ Occurrence of supply interruptions [No. / (1000 connections x year)] Good quality of service [0.0; 1.0] Average quality of service ]1.0; 2.5] Unsatisfactory quality of service ]2.5; + [
55 Reference values and brackets Quality of supplied water (%) Good quality of service [98.50; ] Average quality of service [94.50; 98.50[ Unsatisfactory quality of service [00.00; 94.50[ Reply to written suggestions and complaints (%) Good quality of service 100 Average quality of service [85; 100[ Unsatisfactory quality of service [0; 85[ Coverage of total expenses (-) Good quality of service [1.0; 1.1] Average quality of service [0.9; 1.0[ or ]1.1; 1.2] Unsatisfactory quality of service [0.0; 0.9[ or ]1.2; + [ Effective connection to the service (%) Good quality of service 100,0 Average quality of service [90; 95[ Unsatisfactory quality of service [0; 90[ Non-revenue water (%) Good quality of service [0.0; 20.0] Average quality of service ]20.0; 30.0] Unsatisfactory quality of service ]30.0; 100.0] Adequacy treatment capacity (%) Good quality of service [90,100] Average quality of service [70,90[ Unsatisfactory quality of service [0,70[
56 Mains rehabilitation (%/year) Good quality of service [1.0; 4.0] Average quality of service [0.8; 1.0[ or [4.0; 100[ Unsatisfactory quality of service [0.0; 0.8[ Mains failures [No./(100 km x year)] Good quality of service [0; 30] Reference values and brackets Average quality of service ]30; 60] Unsatisfactory quality of service ]60; + [ Adequacy of human resources (No./1000 branch connections) For mainly urban areas served: Good quality of service [2.0; 3.0] Average quality of service [1.5; 2.0[ or ]3.0; 3.5] Unsatisfactory quality of service [0; 1.5[ or ]3.5; - ] For moderately urban areas served: Good quality of service [2.0; 3.5] Average quality of service [1.5; 2.0[ or ]3.5; 4.3] Unsatisfactory quality of service [0; 1.5[ or ]4.3; - ] For mainly rural areas served: Good quality of service [2.0; 4.0] Average quality of service [1.5; 2.0[ or ]4.0; 6.0] Unsatisfactory quality of service [0; 1.5[ or ]6.0; - ] Water losses [l/(water connection x day)] Good quality of service [0; 100] Average quality of service ]100; 150] Unsatisfactory quality of service ]150; + ]
57 Reference values and brackets Fulfilment of the water intake licensing (%) Good quality of service 100 Average quality of service [90,100[ Unsatisfactory quality of service [0.90[ Energy efficiency of pumping installations [kwh/(m3 x 100 m)] Good quality of service [0.27; 0.40] average efficiencies between 68 and 100%) Average quality of service ]0.40; 0.54] (average efficiencies between 50 and 68%) Unsatisfactory quality of service ]0.54; + [ (average efficiencies below 50%) Disposal of sludge from the water treatment (%) Good quality of service 100 Average quality of service [95, 100[ Unsatisfactory quality of service [0, 95[
58 Reference values and brackets Levels and brackets for the quality of service indicators of waste water management: Physical accessibility of the service (%): For mainly urban areas served Good quality of service [90; 100] Average quality of service [80; 90[ Unsatisfactory quality of service [0; 80[ For moderately urban areas served Good quality of service [85; 100] Average quality of service [70; 85[ Unsatisfactory quality of service [0; 70[ For mainly rural areas served Good quality of service [70; 100] Average quality of service [60; 70[ Unsatisfactory quality of service [0; 60[ Economic accessibility of the service (%): Good quality of service [0; 0.50] Average quality of service ]0.50; 1.00] Unsatisfactory quality of service ]1.00; + [ Flooding occurrence [No./(1000 connections x year)]: Good quality of service [0; 0.25[ Average quality of service [0.25; 1.0[ Unsatisfactory quality of service [1.0; + [
59 Reference values and brackets Reply to written suggestions and complaints (%): Good quality of service 100 Average quality of service [85; 100[ Unsatisfactory quality of service [0; 85[ Coverage of total expenses (-): Good quality of service [1.0; 1.1] Average quality of service [0.9; 1.0[ or ]1.1; 1.2] Unsatisfactory quality of service [0.0; 0.9[ or ]1.2; + [ Effective connection to the service (%) Good quality of service ]99; 100] Average quality of service [95.0; 99.0[ Unsatisfactory quality of service [0; 95] Adequacy of treatment capacity (%): Good quality of service [80; 100] Average quality of service [60; 80[ Unsatisfactory quality of service [0; 60[ Sewerage rehabilitation (%/year): Good quality of service [1.0; 4.0] Average quality of service [0.8; 1.0[ or ]4.0; 100[ Unsatisfactory quality of service [0.0; 0.8[ Sewer collapses [No./(100 km x year)]: Good quality of service 0.0 Average quality of service ]0.0; 2.0] Unsatisfactory quality of service ]2.0; + [
60 Reference values and brackets Adequacy of human resources [No./(100 km x year)]: For mainly urban areas served Good quality of service [5.0; 10.0] Average quality of service [2.5; 5.0[ or ]10.0; 12.5] Unsatisfactory quality of service [0; 2.5[ or ]12.5; + [ For moderately urban areas served Good quality of service [5.0; 11.0] Average quality of service [2.5; 5.0[ or ]11.0; 14.0] Unsatisfactory quality of service For mainly rural areas served Good quality of service [5.0; 12.0] [0; 2.5[ or ]14.0; + [ Average quality of service [2.5; 5.0[ or ]12.0; 15.5] Unsatisfactory quality of service [0; 2.5[ or ]15.5; + [ Energy efficiency of pumping installations [kwh/(m3 x 100 m)] Good quality of service [0.27; 0.45] average efficiencies between 60 and 100%) Average quality of service ]0.45; 0.68] (average efficiencies between 40 and 60%) Unsatisfactory quality of service ]0.68; + [ (average efficiencies below 40%) Appropriate disposal of collected wastewater (%) Good quality of service 100 Average quality of service ]100; 95] Unsatisfactory quality of service ]95; 0]
61 Reference values and brackets Emergency control discharges (%): Good quality of service ]90; 100] Average quality of service ]80; 90] Unsatisfactory quality of service [0; 80] Wastewater analysis (%): Good quality of service 100 Average quality of service [95; 100[ Unsatisfactory quality of service [0; 95[ Compliance with discharge parameters (%): Good quality of service 100 Average quality of service [95; 100[ Unsatisfactory quality of service [0; 95[ Disposal of sludge from the wastewater treatment (%): Good quality of service 100 Average quality of service [95; 100[ Unsatisfactory quality of service [0; 95[
62 Activities, procedures and instruments
63 Activities, procedures and instruments Regulatory activities and procedures: The regulator should ensure the existence of a suitable system to assess quality of service. Based on that system, it should annually carry out a quality of service regulation annual cycle. In this cycle, the regulator should follow a specific, clear and rational regulatory procedure. This regulatory activity should be carried prior, during and after the year of reference.
64 Activities, procedures and instruments Prior the reference year: The regulator specifies the "quality of service assessment system". During the reference year: The utility carry out collection of the internal and external data necessary to assess its quality of service. After the reference year: The utility send to the regulator the data. The regulator carry out a first validation (cross analysis). The regulator carry out the final validation (local audit). The regulator process the data and interpret it, with regard to the reference values and brackets and the existing contextual factors.
65 Activities, procedures and instruments The regulator open a contradictory period. The regulator process the definitive data and interpret the results, with: Individual assessment of all the indicators for each utility with ex. semaphoric codes; Global assessment for groups of utilities per each indicator, or metric benchmarking, also with ex. semaphoric codes; Assessment of the evolution of the indicators by each utility, region and country. The regulator publicly disclose the results of this regulatory component. If justified, the regulator open infringement proceedings against the utility if they do not provide data on time.
66 Activities, procedures and instruments Stages of quality of service regulation annual cycle
67 Regulatory synergies
68 Regulatory synergies Quality of service regulation articulates closely with other components of the regulation model. Contributes to the legal and contractual regulation: Identify any need for strategic reforms. Identify any need to modify legislation. Identify contractual incompliances. Contributes to the economic regulation: Identify the need for investment to improve quality of service. Cross checked for validation, interpretation and analysis. Contribute to the drinking water quality regulation: Cross checked for validation, interpretation and analysis. Contributes to the user interface regulation: Cross checked for validation, interpretation and analysis.
69 Information as a regulatory tool
70 Information as a regulatory tool Information available in the Annual Report of the Water and Waste Services in Portugal, in paper and digital format ( 5 volumes every year
71 Annual benchmarking for all the operators for each performance indicator Information as a regulatory tool Information available in the Annual Report of the Water and Waste Services in Portugal, in paper and digital format (
72 Information as a regulatory tool Information available in the Annual Report of the Water and Waste Services in Portugal, in paper and digital format ( Geographical distribution for each performance indicator
73 Information as a regulatory tool Information available in the Annual Report of the Water and Waste Services in Portugal, in paper and digital format ( Time evaluation for each performance indicator (ex. Water losses)
74 Information as a regulatory tool Information available in the Annual Report of the Water and Waste Services in Portugal, in paper and digital format ( Increase in the number of responses from operators Improvement in data collection quality and quantity had an impact on quality of service assessment
75 Information as a regulatory tool Information available in the site of ERSAR, digital format (
76 Information as a regulatory tool Information available in the site of ERSAR, digital format ( Annual assessment of the quality of service provided by each utility
77 Information as a regulatory tool Information available in the site of ERSAR, digital format ( Annual assessment of tariffs, quality of service, water quality and complaints for each utility
78 Information available in the smartphone ( Information as a regulatory tool
79 Awards of Quality of Service
80 Preamble: Awards of Quality of Service ERSAR has the statutory obligation to: Disseminate information concerning high performance cases; Raise the community awareness to quality issues. ERSAR & other partners assign annually the "Awards of Quality of Service in Water and Waste".
81 Preconditions to an effective performance benchmarking system
82 Preconditions Preconditions to an effective performance benchmarking system: Institutional background: Independent administrative authority (bylaw of the ERSAR approved by Law 10/2014 of the parliament, on 6 March). Legal background: Mandate for regulation of quality of service provided to users by (500) utilities, promoting improvement in levels of service, assessing the performance of those utilities, comparing the utilities and rewarding best practices. Staff: 8 engineers 6 month/year + 30 auditors 3 month/year. Cost: 500,000 euros / year (1,000 euros/utility/year). Global budget of ERSAR: 8,000,000 euros / year.
83 Preconditions Information technology (IT): It is essential for the regulator to structure and implement an integrated information system that enables it to perform its duties properly, including quality of service.
84 Final remarks
85 Final remarks Based on 12 years of experience in Portugal, we can identify positive impacts of regulation: It is a modern and powerful tool for an effective public policy of the water services. It promotes or controls most of the components of the public policy. It promotes short / medium / long term technical approach to water services instead of (in general) short term politic approach. It guaranties stability across time. It introduces efficiency and effectiveness. It guaranties more harmonization in the sector. It guaranties independence from stakeholders. It guaranties more transparency in the sector.
86 Final remarks Quality of service regulation is one important component of the regulation model: Portuguese experience demonstrates it is a powerful regulatory instrument. A Regulatory Integrated Approach with a collaborative and pedagogic environment can be an effective model. Portugal and ERSAR ( invite you all for closed cooperation between regulators and other stakeholders in improving the provision of sustainable water services.
87 Thanks for your attention
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