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LCE
1
Chaojie Li1, Émile Sylvestre2, Xavier Fernandez Cassi3,Tim Julian2, Tamar Kohn1
1Laboratory of Environmental Chemistry(LCE), EPFL, Lausanne 1015, Switzerland 2Department Environmental Microbiology, Eawag, Überlandstrasse 133, 8600, Dübendorf, Switzerland
3Faculty of Pharmacy and Food Sciences, UB, Av. de Joan XXIII, 27-31, 08028, Barcelona, Spain
LCE
Study site: Lake Geneva
2
Located on the border of
Switzerland and France.
Used as a drinking water
source and recreational
water site by more than
800,000 inhabitants. It
has a surface area of 580
km2 and a maximum
depth of 310 m.
LCE
A schematic view
3
LCE
4
Methods overview
3D Water quality modeling
Sewage virus measurement
and characterization
Environmental virus decay
Simulated virus concentration
LCE
5
Methods overview
3D Water quality modeling
QMRA
Sewage virus measurement
and characterization
Environmental virus decay
Simulated virus concentration
LCE
6
Hydrodynamic and water quality module
Source: http://meteolakes.ch/
Hydrodynamics: Delft3D 4 Based online platform: Δt =1 min, Δx ≈400 m, 100 Z-layers.
Water quality: Delft3D-WAQ, validated with surrogate of total suspended matter. Spatial and temporal
inactivation of virus included.
LCE
7
Environmental inactivation of waterborne virus
𝑙𝑜𝑔10𝑘 = 𝛽0 + ෍
𝑖=1
𝑛
𝛽𝑖𝑥𝑖 + 𝜀
Boehm, A. B., Silverman, A. I., Schriewer, A., & Goodwin, K. (2019). Systematic review and meta analysis of decay rates of waterborne mammalian viruses and coliphages
in surface waters. Water Research, 164, 114898.
Virus type Beta 0 Beta temp Beta solar (surface)
Rotavirus -0.6 0.04 0.51
Norovirus -1.08 0.04 0.43
Adenovirus -1.2 0.07 0.13
Enterovirus -0.25 0.03 1.07
The first-order inactivation rate, k
LCE
8
𝐸𝑥𝑝𝑜𝑛𝑒𝑛𝑡𝑖𝑎𝑙:
𝑃 = 1 − 𝑒(−𝑟∗𝑑𝑜𝑠𝑒)
𝐵𝑒𝑡𝑎 − 𝑃𝑜𝑖𝑠𝑠𝑜𝑛:
𝑃 = 1 − (1 + 𝐷𝑜𝑠𝑒/𝛽)−𝛼
Dose-response models for
different viruses:
Source: http://qmrawiki.org/
𝐵𝑒𝑡𝑎 − 𝐵𝑖𝑛𝑜𝑚𝑖𝑎𝑙:
𝑃 = 1 −
𝛤(𝛼+𝛽)𝛤(𝛽+𝑑)
𝛤(𝛽)𝛤(𝛼+𝛽+𝑑)
Enterovirus
Adenovirus
Rotavirus
Norovirus
LCE
Case studies: Site and scenarios
9
Release sources:
Vidy WWTP and
Morges WWTP.
Site of interest:
Morges recreational
site.
Weekly simulation: 3 days of continuous release of raw sewage + 4 dry days. 24 cases in year 2019.
LCE
10
Measurement of virus concentration in raw sewage
PCR measurements
DNA and RNA Samples from sewage
Rotavirus has higher annual mean concentration then the rest, also shows possible seasonality.
LCE
11
Characterizing virus concentrations in sewage
PLN performs slightly better than the
PGA distribution.
Poisson lognormal
Poisson gamma
Parameter Virus Adenovirus Enterovirus Norovirus Rotavirus (Summer/Winter)
Mean of samples
(GC/ml)
561 482 10488 1041/18446
DICm PLN 179 176 253 114/143
DICm PGA 181 183 247 113/178
1
LCE
Concentration evolvement over one week
12
LCE
Nearshore virus concentration and infection risks
13
Two sources:
Vidy WWTP and
Morges WWTP.
One source:
Vidy WWTP.
LCE
The influence of environmental stressors
14
LCE
The influence of environmental stressors
15
LCE
Stochastic simulations for risk characterization
16
The incoming sewage virus
concentration was considered a
stochastic process. The uncertainties
related to the water intake volume
and the dose-response relationships
were not included in this study.
LCE
Annual risk characterization
17
Eastward wind
Westward wind
Source: NEMS meteroblue
Annual mean Westward wind Eastward wind Eastward/Westward
Adenovirus 0.078 0.089 0.045 51%
Enterovirus 0.0003 0.0003 0.0001 33%
Norovirus 0.685 0.713 0.603 85%
Rotavirus 0.035 0.04 0.021 53%
LCE
18
Norovirus is the most acute species among the viruses studied according to the
case studies while enterovirus poses the least danger.
Summary and outlook
The relative distance to the contamination sources, the season, wind conditions
as well as inactivation rates are essential in determining virus concentrations at
a specific site in lakes.
Stochastic simulations can indicate uncertainties in risk assessment. More
information on the sewage virus concentration and uncertainties related to the
dose-response of viruses would further consolidate the model.
Online visualization of the results, the implement of flexible mesh and hopefully a
better coupling scheme for the inactivation module.
LCE
Acknowledgements
19
Prof. Tamar Kohn
Dr. Tim Julian Dr. Émile Sylvestre Dr. Xavier Fernandez Cassi
&
LCE
Thank you!
20

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DSD-INT 2022 Waterborne virus transport and the associated risks in a large lake - Li

  • 1. LCE 1 Chaojie Li1, Émile Sylvestre2, Xavier Fernandez Cassi3,Tim Julian2, Tamar Kohn1 1Laboratory of Environmental Chemistry(LCE), EPFL, Lausanne 1015, Switzerland 2Department Environmental Microbiology, Eawag, Überlandstrasse 133, 8600, Dübendorf, Switzerland 3Faculty of Pharmacy and Food Sciences, UB, Av. de Joan XXIII, 27-31, 08028, Barcelona, Spain
  • 2. LCE Study site: Lake Geneva 2 Located on the border of Switzerland and France. Used as a drinking water source and recreational water site by more than 800,000 inhabitants. It has a surface area of 580 km2 and a maximum depth of 310 m.
  • 4. LCE 4 Methods overview 3D Water quality modeling Sewage virus measurement and characterization Environmental virus decay Simulated virus concentration
  • 5. LCE 5 Methods overview 3D Water quality modeling QMRA Sewage virus measurement and characterization Environmental virus decay Simulated virus concentration
  • 6. LCE 6 Hydrodynamic and water quality module Source: http://meteolakes.ch/ Hydrodynamics: Delft3D 4 Based online platform: Δt =1 min, Δx ≈400 m, 100 Z-layers. Water quality: Delft3D-WAQ, validated with surrogate of total suspended matter. Spatial and temporal inactivation of virus included.
  • 7. LCE 7 Environmental inactivation of waterborne virus 𝑙𝑜𝑔10𝑘 = 𝛽0 + ෍ 𝑖=1 𝑛 𝛽𝑖𝑥𝑖 + 𝜀 Boehm, A. B., Silverman, A. I., Schriewer, A., & Goodwin, K. (2019). Systematic review and meta analysis of decay rates of waterborne mammalian viruses and coliphages in surface waters. Water Research, 164, 114898. Virus type Beta 0 Beta temp Beta solar (surface) Rotavirus -0.6 0.04 0.51 Norovirus -1.08 0.04 0.43 Adenovirus -1.2 0.07 0.13 Enterovirus -0.25 0.03 1.07 The first-order inactivation rate, k
  • 8. LCE 8 𝐸𝑥𝑝𝑜𝑛𝑒𝑛𝑡𝑖𝑎𝑙: 𝑃 = 1 − 𝑒(−𝑟∗𝑑𝑜𝑠𝑒) 𝐵𝑒𝑡𝑎 − 𝑃𝑜𝑖𝑠𝑠𝑜𝑛: 𝑃 = 1 − (1 + 𝐷𝑜𝑠𝑒/𝛽)−𝛼 Dose-response models for different viruses: Source: http://qmrawiki.org/ 𝐵𝑒𝑡𝑎 − 𝐵𝑖𝑛𝑜𝑚𝑖𝑎𝑙: 𝑃 = 1 − 𝛤(𝛼+𝛽)𝛤(𝛽+𝑑) 𝛤(𝛽)𝛤(𝛼+𝛽+𝑑) Enterovirus Adenovirus Rotavirus Norovirus
  • 9. LCE Case studies: Site and scenarios 9 Release sources: Vidy WWTP and Morges WWTP. Site of interest: Morges recreational site. Weekly simulation: 3 days of continuous release of raw sewage + 4 dry days. 24 cases in year 2019.
  • 10. LCE 10 Measurement of virus concentration in raw sewage PCR measurements DNA and RNA Samples from sewage Rotavirus has higher annual mean concentration then the rest, also shows possible seasonality.
  • 11. LCE 11 Characterizing virus concentrations in sewage PLN performs slightly better than the PGA distribution. Poisson lognormal Poisson gamma Parameter Virus Adenovirus Enterovirus Norovirus Rotavirus (Summer/Winter) Mean of samples (GC/ml) 561 482 10488 1041/18446 DICm PLN 179 176 253 114/143 DICm PGA 181 183 247 113/178 1
  • 13. LCE Nearshore virus concentration and infection risks 13 Two sources: Vidy WWTP and Morges WWTP. One source: Vidy WWTP.
  • 14. LCE The influence of environmental stressors 14
  • 15. LCE The influence of environmental stressors 15
  • 16. LCE Stochastic simulations for risk characterization 16 The incoming sewage virus concentration was considered a stochastic process. The uncertainties related to the water intake volume and the dose-response relationships were not included in this study.
  • 17. LCE Annual risk characterization 17 Eastward wind Westward wind Source: NEMS meteroblue Annual mean Westward wind Eastward wind Eastward/Westward Adenovirus 0.078 0.089 0.045 51% Enterovirus 0.0003 0.0003 0.0001 33% Norovirus 0.685 0.713 0.603 85% Rotavirus 0.035 0.04 0.021 53%
  • 18. LCE 18 Norovirus is the most acute species among the viruses studied according to the case studies while enterovirus poses the least danger. Summary and outlook The relative distance to the contamination sources, the season, wind conditions as well as inactivation rates are essential in determining virus concentrations at a specific site in lakes. Stochastic simulations can indicate uncertainties in risk assessment. More information on the sewage virus concentration and uncertainties related to the dose-response of viruses would further consolidate the model. Online visualization of the results, the implement of flexible mesh and hopefully a better coupling scheme for the inactivation module.
  • 19. LCE Acknowledgements 19 Prof. Tamar Kohn Dr. Tim Julian Dr. Émile Sylvestre Dr. Xavier Fernandez Cassi &