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Risk-based approaches for safe and sustainable Drinking Water production and distribution chain

CS4@DICA, Politecnico di Milano

4th December, 2023

Beatrice Cantoni, PhD

​

Department of Civil and Environmental Engineering, Politecnico di Milano

​

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Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

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Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

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Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

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Drinking water supply: SUSTAINABILITY

[Jungbluth et al., 2014]

Life-Cycle Assessment Comparison

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Drinking water supply: SUSTAINABILITY

[Jungbluth et al., 2014]

Life-Cycle Assessment Comparison

Italy is worldwide second country for bottled water consumption

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Drinking water supply: CURRENT AND FUTURE CHALLENGES

WATER POLLUTION

CLIMATE CHANGE

SUSTAINABLE CONSUMPTION

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Drinking water supply: CURRENT AND FUTURE CHALLENGES

CONTAMINANTS OF EMERGING CONCERN (CECs)

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How can we handle emerging contaminants?

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  • Assess current CECs risk

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​

​

  • Prioritize interventions

​

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How can we handle emerging contaminants?

​

  • Assess current CECs risk

​

​

​

  • Prioritize interventions

​

Monitoring

​

Experiments

Risk assessment

Modelling

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How can we handle emerging contaminants?

​

  • Assess current CECs risk

​

​

​

  • Prioritize interventions

​

Monitoring

​

Experiments

Risk assessment

Modelling

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Risk assessment

EXPOSURE

HEALTH EFFECT

RISK

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Risk assessment

Concentration

p

DWTL

C𝑬𝑿𝑷

From deterministic

​

Chemical Risk Assessment

(CRA)

 

EXPOSURE

HEALTH EFFECT

RISK

>

>

1 🡪 No Risk

1 🡪 Risk

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Risk assessment

Uncertainty on exposure

Uncertainty on hazard

Concentration

p

DWTL

C𝑬𝑿𝑷

From deterministic

​

Chemical Risk Assessment

(CRA)

 

>

>

1 🡪 No Risk

1 🡪 Risk

To probabilistic

​

Quantitative Chemical Risk Assessment (QCRA)

 

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Risk assessment

Uncertainty on exposure

Uncertainty on hazard

Concentration

p

DWTL

C𝑬𝑿𝑷

From deterministic

​

Chemical Risk Assessment

(CRA)

 

>

>

1 🡪 No Risk

1 🡪 Risk

To probabilistic

​

Quantitative Chemical Risk Assessment (QCRA)

 

BQ

P(BQ > 0.1)

P(BQ > 1)

Cantoni et al., 2021

DOI: 10.1016/j.watres.2021.116911

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Risk-based comparison of tap and plastic bottled-water consumption

Target CECs: Alkylphenols and Phthalates

​

​

Collected data: - CECs concentration in tap and bottled water (87 literature papers)

- Worldwide drinking water consumption habits (23 literature papers)

​

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Risk-based comparison of tap and plastic bottled-water consumption

Target CECs: Alkylphenols and Phthalates

​

​

Collected data: - CECs concentration in tap and bottled water (87 literature papers)

- Worldwide drinking water consumption habits (23 literature papers)

​

PHTHALATES

Penserini et al., 2022

DOI: 10.1016/j.envint.2022.107294

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Risk-based comparison of tap and plastic bottled-water consumption

Target CECs: Alkylphenols and Phthalates

​

​

Collected data: - CECs concentration in tap and bottled water (87 literature papers)

- Worldwide drinking water consumption habits (23 literature papers)

​

PHTHALATES

Penserini et al., 2022

DOI: 10.1016/j.envint.2022.107294

Beatrice Cantoni

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Risk-based comparison of tap and plastic bottled-water consumption

Target CECs: Alkylphenols and Phthalates

​

​

Collected data: - CECs concentration in tap and bottled water (87 literature papers)

- Worldwide drinking water consumption habits (23 literature papers)

​

PHTHALATES

Penserini et al., 2022

DOI: 10.1016/j.envint.2022.107294

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How can we handle emerging contaminants?

​

  • Assess current CECs risk

​

​

​

  • Prioritize interventions

​

Monitoring

​

Experiments

Risk assessment

Modelling

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Interventions for risk minimization

Cantoni et al., 2021

DOI: 10.1016/j.scitotenv.2021.148821

WHAT: Performance analysis and optimization of

Granular Activated Carbon treatment

​

CECs: PFAS

​

NOVELTY: From Lab to Full-scale

​

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

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Interventions for risk minimization

Cantoni et al., 2021

DOI: 10.1016/j.watres.2021.116911

Time (t)

COUT/CIN

Some background on Granular Activated Carbon treatment

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Interventions for risk minimization

Italian

Water Utility

DESIGN OF THE STUDY

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Interventions for risk minimization

DESIGN OF THE STUDY

Milled and sieved ACs 🡪 dp, RSSCT (e.g. 110 um)

EBCTRSSCT (6.1 sec) 🡪 Flowrate (5.5 mL/min)

Down-scaling method

Constant diffusivity equation:

EBCT (average: 11 min)

dp,LC (average: 1200 um)

Full scale

RSSCT

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Interventions for risk minimization

Cantoni et al., 2021

DOI: 10.1016/j.scitotenv.2021.148821

Experiments

Modelling

GAC SELECTION

CRITERIA

ONLINE MONITORING SYSTEM

CONFIGURATION SELECTION

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Interventions for risk minimization

WHAT: Evaluation of water-materials contact in drinking water distribution

​

CECs: Bisphenol A (BPA)

​

NOVELTY: Real testing conditions from lab to field

​

​

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

Cantoni et al., 2021

DOI: 10.1016/j.scitotenv.2021.146908

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Interventions for risk minimization

Cantoni et al., 2021

DOI: 10.1016/j.scitotenv.2021.146908

2. BADGE polymerization with polyamines

Free BPA trapped into the lattice

1. BPA + Epichlorohydrin 🡪 BADGE

DWDN pipelines corrosion and need for renovation

Renovation through relining

with epoxy resins

Potential release of

bisphenol-A (BPA)

Potential health risk for BPA in DW

Endocrine disruptor

​

Effects on reproductive system

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Interventions for risk minimization

Cantoni et al., 2021

DOI: 10.1016/j.scitotenv.2021.146908

Experiments

Modelling

Time [h]

BPA concentration [µg/L]

Time (h)

Concentration BPA [µg/L]

A

B

Risk

RESIN SELECTION

TESTING

DRINKING WATER DISTRIBUTION NETWORK MONITORING

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NEXT STEPS TOWARDS SAFETY AND SUSTAINABILITY

WHEN MANAGING ACTIVATED CARBON ADSORPTION SHOULD WE MOVE

​

FROM SINGLE COMPOUNDS BREAKTHROUGH TO THE MIXTURE RISK BREAKTHROUGH

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NEXT STEPS TOWARDS SAFETY AND SUSTAINABILITY

INDIVIDUAL GRANT FOR

2-YEARS RESEARCH FUNDING

(09/2023-08/2025)

Climate

change

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Acknowledgements

What I like the most about being a researcher:

​

Research is collaboration, interdisciplinarity, networking, looking forward, sharing ideas, bringing innovation

safeWATER Lab

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Thank you for your attention!

Beatrice Cantoni, PhD

​

Department of Civil and Environmental Engineering, Politecnico di Milano

​

beatrice.cantoni@polimi.it

​

CS4@DICA, Politecnico di Milano

4th December, 2023

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Applications of Quantitative Chemical Risk Assessment (QCRA)

Penserini et al., 2022

DOI: 10.1016/j.envint.2022.107294

Beatrice Cantoni

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Applications of Quantitative Chemical Risk Assessment (QCRA)

Penserini et al., 2023

DOI: 10.1016/j.chemosphere.2023.138259

WHAT: Risk-based comparison of drinking water and food consumption

​

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WHO: Alkylphenols (BPA and NP)

​

​

​

NOVELTY: Multiple exposure risk assessment

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Applications of Quantitative Chemical Risk Assessment (QCRA)

Penserini et al., 2023

DOI: 10.1016/j.chemosphere.2023.138259

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PFAS Risk Assessment

PFAS are always seen as a mixture

​

PFAS have the same end-point

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Traditional method based on EU-DWD

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​

​

​

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​

 

Clim, sum PFAS = 0.1 μg/l

Cout, sum PFAS

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PFAS Risk Assessment

PFAS are always seen as a mixture

​

PFAS have the same end-point

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Traditional method based on EU-DWD

​

​

​

​

​

But each PFAS has its own toxicity

Advanced method to consider toxicity

Toxicity is represented by the Relative Potency Factors (RPF) as proposed in EU Water Framework Directive

​

INCREASING TOXICITY

[Bill et al., 2021]

 

 

Clim,PFOA

 

Clim, sum PFAS = 0.1 μg/l

Cout, sum PFAS

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PFAS Risk Assessment

An example of PFAS Risk assessment application for scenario analysis

Experiments

[Submitted to Process Safety and Environmental Protection]

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PFAS Risk Assessment

How PFAS risk ranking changes according to the applied risk assessment method?

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1 2 3 4 5 6 7 8 9 10 11 12 13 14

1 2 3 4 5 6 7 8 9 10 11 12 13 14

 

TRADITIONAL

METHOD

ADVANCED METHOD

 

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PFAS Risk Assessment

WHEN MANAGING ACTIVATED CARBON ADSORPTION SHOULD WE MOVE

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FROM SINGLE COMPOUNDS BREAKTHROUGH TO THE MIXTURE RISK BREAKTHROUGH

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Risk assessment

Uncertainty on exposure

Uncertainty on hazard

Concentration

p

DWTL

C𝑬𝑿𝑷

From deterministic

​

Chemical Risk Assessment

(CRA)

 

>

>

1 🡪 No Risk

1 🡪 Risk

To probabilistic

​

Quantitative Chemical Risk Assessment (QCRA)

 

BQ

P(BQ > 0.1)

P(BQ > 1)

Beatrice Cantoni

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