1 of 41

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

2 of 41

Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

Beatrice Cantoni

2/31

3 of 41

Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

Beatrice Cantoni

3/31

4 of 41

Drinking water supply in urban context

WATER SOURCES

TREATMENT

DISTRIBUTION

CONSUMPTION

Beatrice Cantoni

4/31

5 of 41

Drinking water supply: SUSTAINABILITY

[Jungbluth et al., 2014]

Life-Cycle Assessment Comparison

Beatrice Cantoni

5/31

6 of 41

Drinking water supply: SUSTAINABILITY

[Jungbluth et al., 2014]

Life-Cycle Assessment Comparison

Italy is worldwide second country for bottled water consumption

Beatrice Cantoni

6/31

7 of 41

Drinking water supply: CURRENT AND FUTURE CHALLENGES

WATER POLLUTION

CLIMATE CHANGE

SUSTAINABLE CONSUMPTION

Beatrice Cantoni

7/31

8 of 41

Drinking water supply: CURRENT AND FUTURE CHALLENGES

CONTAMINANTS OF EMERGING CONCERN (CECs)

Beatrice Cantoni

8/31

9 of 41

How can we handle emerging contaminants?

  • Assess current CECs risk

  • Prioritize interventions

Beatrice Cantoni

9/31

10 of 41

How can we handle emerging contaminants?

  • Assess current CECs risk

  • Prioritize interventions

Monitoring

Experiments

Risk assessment

Modelling

Beatrice Cantoni

10/31

11 of 41

How can we handle emerging contaminants?

  • Assess current CECs risk

  • Prioritize interventions

Monitoring

Experiments

Risk assessment

Modelling

Beatrice Cantoni

11/31

12 of 41

Risk assessment

EXPOSURE

HEALTH EFFECT

RISK

Beatrice Cantoni

12/31

13 of 41

Risk assessment

Concentration

p

DWTL

C𝑬𝑿𝑷

From deterministic

Chemical Risk Assessment

(CRA)

 

EXPOSURE

HEALTH EFFECT

RISK

>

>

1 🡪 No Risk

1 🡪 Risk

Beatrice Cantoni

13/31

14 of 41

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)

 

Beatrice Cantoni

14/31

15 of 41

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

Beatrice Cantoni

15/31

16 of 41

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)

Beatrice Cantoni

16/31

17 of 41

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

17/31

18 of 41

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

18/31

19 of 41

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

19/31

20 of 41

How can we handle emerging contaminants?

  • Assess current CECs risk

  • Prioritize interventions

Monitoring

Experiments

Risk assessment

Modelling

Beatrice Cantoni

20/31

21 of 41

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

Beatrice Cantoni

21/31

22 of 41

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

Beatrice Cantoni

22/31

23 of 41

Interventions for risk minimization

Italian

Water Utility

DESIGN OF THE STUDY

Beatrice Cantoni

23/31

24 of 41

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

Beatrice Cantoni

24/31

25 of 41

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

Beatrice Cantoni

25/31

26 of 41

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

Beatrice Cantoni

26/31

27 of 41

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

Beatrice Cantoni

27/31

28 of 41

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

Beatrice Cantoni

28/31

29 of 41

NEXT STEPS TOWARDS SAFETY AND SUSTAINABILITY

WHEN MANAGING ACTIVATED CARBON ADSORPTION SHOULD WE MOVE

FROM SINGLE COMPOUNDS BREAKTHROUGH TO THE MIXTURE RISK BREAKTHROUGH

Beatrice Cantoni

29/31

30 of 41

NEXT STEPS TOWARDS SAFETY AND SUSTAINABILITY

INDIVIDUAL GRANT FOR

2-YEARS RESEARCH FUNDING

(09/2023-08/2025)

Climate

change

Beatrice Cantoni

30/31

31 of 41

Acknowledgements

What I like the most about being a researcher:

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

safeWATER Lab

Beatrice Cantoni

31/31

32 of 41

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

33 of 41

Applications of Quantitative Chemical Risk Assessment (QCRA)

Penserini et al., 2022

DOI: 10.1016/j.envint.2022.107294

Beatrice Cantoni

33/31

34 of 41

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

WHO: Alkylphenols (BPA and NP)

NOVELTY: Multiple exposure risk assessment

Beatrice Cantoni

34/31

35 of 41

Applications of Quantitative Chemical Risk Assessment (QCRA)

Penserini et al., 2023

DOI: 10.1016/j.chemosphere.2023.138259

Beatrice Cantoni

35/31

36 of 41

PFAS Risk Assessment

PFAS are always seen as a mixture

PFAS have the same end-point

Traditional method based on EU-DWD

 

Clim, sum PFAS = 0.1 μg/l

Cout, sum PFAS

Beatrice Cantoni

36/31

37 of 41

PFAS Risk Assessment

PFAS are always seen as a mixture

PFAS have the same end-point

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

Beatrice Cantoni

37/31

38 of 41

PFAS Risk Assessment

An example of PFAS Risk assessment application for scenario analysis

Experiments

[Submitted to Process Safety and Environmental Protection]

Beatrice Cantoni

38/31

39 of 41

PFAS Risk Assessment

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

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

 

Beatrice Cantoni

39/31

40 of 41

PFAS Risk Assessment

WHEN MANAGING ACTIVATED CARBON ADSORPTION SHOULD WE MOVE

FROM SINGLE COMPOUNDS BREAKTHROUGH TO THE MIXTURE RISK BREAKTHROUGH

Beatrice Cantoni

40/31

41 of 41

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

41/31