Protecting bathing water quality from sewage overflow in Rimini, Italy
During heavy rainfall events, Rimini frequently experienced combined sewage system overflows which caused local surface flooding in the city and direct discharge of untreated, diluted wastewater into the sea. The resultant contamination of sea water was posing health risks and necessitated frequent implementation of bathing bans on the city’s beaches, with negative impacts on tourism.
The Municipality of Rimini set up and continues to implement an Optimized Seawater Protection Plan (Piano di Salvaguardia della Balneazione Ottimizzato – PSBO), which included the creation of a separated sewage collection system, improvement of the sewage treatment system and construction of storage tanks for overflow water. After the finalization of the sewerage system works on Rimini’s northern coast in 2020, the discharges of untreated wastewater into the sea have been drastically reduced. Despite continuing occurrence of heavy rainfall events, the number of bathing bans implemented has decreased.
Public works on the street surfaces, necessary during renovation of the sewage system, provided an opportunity to transform streets and parking areas on the waterfront into an urban park (“parco del mare”) with green areas and space for recreational activity that simultaneously functions as a barrier against coastal flooding.
Case Study Description
Challenges
Poor microbial water quality on recreational beaches can cause a variety of conditions such as gastrointestinal, eye, ear, skin, and respiratory diseases (Haile, et al., 1999; Wade et al., 2003; EEA, 2024).The main sources of bacterial contamination of coastal waters are sewage discharges, including sewage outfalls, sewer overflows, stormwater discharges, sewage network failures, polluted river discharges and agricultural and urban runoff (Penna et al., 2021; Claessens et al., 2014).
In Rimini, heavy precipitation events caused sewage overflows which resulted in contamination of bathing water along the city’s coast on average around 10 times per year (Venier, 2018). The bathing bans usually lasted between 1 and 4 days, and in some cases up to 7 days (ARPAE, 2023). The combined sewage collection system could not keep pace with the growth in population, the number of tourists and the increasing rates of urbanization and soil sealing.
In the northern part of the municipality, several small drainage channels originally used only for collection of rainwater were progressively culverted and integrated into the wastewater collection system. At the end of the channels, watertight floodgates with pumping stations prevented water from flowing into the sea and conveyed it towards the wastewater treatment plant. In cases of heavy rainfall overloading the sewage system, these channels were opened to the sea to avoid local sewage overflows. These occasional discharges of diluted sewage into the sea resulted in temporal bathing bans due to the presence of pollution in the water close to the beaches. Under changing climate conditions, the frequency of intense precipitation events is expected to increase in the region (SNPA, 2021), thereby raising the probability of sewage overflows with negative consequences for bathing water quality.
Objectives
The creation of a separated sewage collection system (where feasible), improvement of the sewage treatment system, and installation of storage tanks for collecting and storing overflow wastewater and storm water (in areas with a combined sewage collection system) aim to reduce or stop contamination of sea water originating from urban sewage overflows during the increasingly frequent and intense rainfall events.
Adaptation Options Implemented In This Case
Solutions
Following the Optimized Seawater Protection Plan, adopted in 2013, the city’s sewage system and the wastewater treatment plant have been renewed and upgraded, increasing and improving collection and treatment capacities in the whole area. The combined sewage system was replaced with a separated system in most parts of the city. In the most densely built-up areas, where the dual system was not possible, a pumping system including storage for the collection of runoff and sewage water was created or expanded.
The system includes an underground plant, completed in 2020, for the collection of runoff water during extreme rainfall events. The runoff water is released successively into the sewage system and conveyed to a treatment plant once the pressure on the urban system has decreased. If storage capacities are reached, the diluted wastewater is released into the sea. The plant consists of two storage tanks located 40 meters below ground; a first tank with a capacity of 14,000 cubic metres collects the initial rainfall water, while the second, with a capacity of 25,000 cubic metres, is dedicated to storage and limiting the amount of mixed wastewater and stormwater conveyed to the sea. This stored water is discharged into the sea 1,000 meters from the shoreline to further reduce any health risks for beach users.
The public works necessary for installing new sewage pipes and underground collectors were used as an opportunity to renew the city’s waterfront, substituting streets and parking lots with a park. The park’s walkways, green areas and sports facilities are slightly elevated to provide protection for the city against storm surges and sea level rise. The pumping plants and the water storage tanks are located beneath an attractive building which is used as a belvedere with an accessible elevated terrace overlooking the beaches.
Relevance
Case mainly developed and implemented because of other policy objectives, but with significant consideration of Climate Change Adaptation aspects
Additional Details
Stakeholder Participation
The renovation of the sewage infrastructure has been managed together by the Municipality of Rimini and the water utility company responsible for the management of wastewater in the city. Collaboration between these entities took place on the basis of the Seawater Protection Plan, developed together with the water utilities, and adopted by the local authority (Municipality of Rimini) in 2013. Scientific support for modelling the hydraulic system and future risks of flooding from extreme precipitation and the definition of the security level was provided by the regional Environment Agency (ARPAE). The security level chosen for dimensioning the system refers to events with an actual return period of 1-in-50 years. The plan for safeguarding bathing waters and the urban park are elements of the wider strategic plan for Rimini, which has been subject to further participative activities.
Prior to the development of the of the urban park area “parco del mare”, the city of Rimini consulted citizens and city users, economic actors as operators of beach establishments (stabilimenti balneari), bars, restaurants and services in the area, as well as environmental groups. The specific needs and expectations voiced by those stakeholders were used to shape the form of the new park. For instance, more space than initially foreseen was reserved for leisure time activities, cycling and walking. The consultation also informed the specifications for the architectural competition launched for the area.
Success and Limiting Factors
Monitoring of bathing water quality as required by the Bathing Water Directive (EC, 2006) is done by the Regional Environment Agency (ARPAE) and takes place close to the shoreline, in a water depth between 80 and 120 centimeters. Monitoring points are pre-defined and correspond to the points where sewage water can potentially be released. The monthly controls of Enterococci and E. coli bacteria during the bathing season (from the beginning of May to the end of September) are complemented by ad-hoc monitoring in cases of extreme precipitation events or discharges from the sewage system into the sea, communicated by the utility company. Such events trigger precautional bathing bans, and additional monitoring activities are carried out to determine the end of the contamination event. From 2020 onwards, when the northern part of the new sewage plant was nearly complete (in the very northern sections some parts of the new system became operative later), the number of sewage discharges into the sea and bathing bans have reduced and, in some places, gone down to zero.
The park, created between the beaches and the waterfront, raises the level of the promenade by 80 centimeters, providing an example of how strongly urbanized sections of the coast can be protected against some level of sea level rise without compromising the touristic use of beaches. At the same time, the level of protection against storm surges will not be sufficient under scenarios of higher sea level rise and additional measures might be needed to protect the city.
The sewage system is protected against overflows for 1-in-50 year rainfall events. Under climate change, less frequent but more intense rainfall is projected for the Emilia Romagna Region (Sabelli, 2023). Therefore, today’s 1-in-50 year events are likely to occur more frequently and bathing bans are not excluded in the future.
Costs and Benefits
The overall costs (until late 2023) for the improvements in the sewage system are approximately 200 M€. Upgrading of the sewage system has been financed by 3 entities: the Municipality of Rimini (33%) using inter alia regional and EU funding, the water utility (33%), and through tariffs paid by water users (33%). Whilst the latter led to some critique (Rimini 2.0, 2018), according to the Italian water pricing regulations, improvements of water and sewage system services can be co-financed by an increase in consumer payments for the water services.
The creation of the urban park has been financed by the municipality which has been able to use, further to the municipal budget, additional national and regional funding.
The completion of the Seawater Protection Plan will benefit the tourism industry, improving the reputation of Rimini as seaside resort and allowing for continuous use of beaches. The economic value of the avoided losses caused by health risks in sea water and consequent bathing bans for the bathing establishments is estimated at about 1.5 M€/year (Venier, 2018, p. 233).
Legal Aspects
In Italy, discharging runoff water into natural water bodies is not allowed according to the national law for water protection, as this water is considered contaminated and needs to be treated (D.Lgs. n. 152 del 2006). For this reason, in the creation of a separated sewage system, mechanisms have been introduced to ensure treatment of runoff water and avoidance of contamination of the near-shore waters with run-off water in case the storage capacities should be reached.
Interventions such as the improvement of the sewage system, according to Italian law, are not subject to environmental assessments.
Implementation Time
The project is being realized successively in different sections of the city’s waterfront, with the northern and central parts of the coastline already completed. The water storage plant has been in operation since 2020. Further sections are under realization. The entire waterfront will be transformed by 2026.
Life Time
The lifetime corresponds to the lifetime of public infrastructure.
Reference Information
Contact
Roberta Frisoni
Deputy Mayor for urban planning, transport and waterfront development
roberta.frisoni@comune.rimini.it
Websites
Reference
ARPAE, 2023, ‘Inconvenienti stagionali’, Arpae Emilia-Romagna (ARPAE) (https://www.arpae.it/it/temi-ambientali/balneazione/rapporti-balneazione/inconvenienti-stagionali) accessed 24 October 2023.
Claessens, J., et al., 2014, ‘The soil-water system as basis for a climate proof and healthy urban environment: opportunities identified in a Dutch case-study.’, The Science of the total environment 485-486, pp. 776-784 (DOI: 10.1016/j.scitotenv.2014.02.120).
EC, 2006, Directive 2006/7/EC of the European Parliament and of the Council of 15 February 2006 concerning the management of bathing water quality and repealing Directive 76/160/EEC.
EEA, 2024 (forthcoming), Responding to climate change impacts on human health in Europe: focus on floods, droughts and water quality, EEA Report No #/2024, European Environment Agency.
Giovanardi, F., et al., 2006, ‘Coastal waters monitoring data: frequency distributions of the principal water quality variables’, Journal of Limnology 66(2), pp. 65-82.
Haile, R. W., et al., 1999, ‘The Health Effects of Swimming in Ocean Water Contaminated by Storm Drain Runoff’, Epidemiology 10(4):p 355-363, July 1999. Free 10(4), pp. 355-363.
Montini, A., 2021, ‘Rimini: Piano di Salvaguardia della Balneazione e Parco del Mare’, presentation given at: Ecomondo, Rimini, 26 October 2021.
Penna, P., et al., 2021, ‘Water quality integrated system: A strategic approach to improve bathing water management’, Journal of Environmental Management 295, p. 113099 (DOI: 10.1016/j.jenvman.2021.113099).
Rimini 2.0, 2018, ‘Scarichi a mare e PSBO, i costi per i cittadini aumentano di 6,5 milioni di euro’, Riminiduepuntozero (https://www.riminiduepuntozero.it/scarichi-a-mare-e-psbo-i-costi-per-i-cittadini-aumentano-di-65-milioni-di-euro/) accessed 24 January 2024.
Sabelli, C., 2023, ‘Examining the role of climate change in the Emilia-Romagna floods’, Nature Italy, pp. d43978-023-00082-z (DOI: 10.1038/d43978-023-00082-z).
SNPA, 2021, Rapporto sugli indicatori di impatto dei cambiamenti climatici – Edizione 2021, Report SNPA No 21/2021, Sistema Nazionale per la Protezione dell’Ambiente (SNPA), Roma (https://www.snpambiente.it/temi/report-intertematici/cambiamenti-climatici/rapporto-sugli-indicatori-di-impatto-dei-cambiamenti-climatici-edizione-2021/).
Venier, S., 2018, ‘Waste Water Management in Seaside Tourism Areas: The Rimini Seawater Protection Plan’, in: A. Gilardoni (ed.), The Italian Water Industry: Cases of Excellence, Springer, pp. 225-235.
Wade, T. J., et al., 2003, ‘Do US Environmental Protection Agency water quality guidelines for recreational waters prevent gastrointestinal illness? A systematic review and meta-analysis.’, Environmental health perspectives 111(8), pp. 1102-1109.
Published in Climate-ADAPT Feb 27 2024 - Last Modified in Climate-ADAPT Apr 18 2024
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