Hannouche, A.; Chebbo, G.; Joannis, C. Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? SPN7 – Sheffield,

Slides:



Advertisements
Similar presentations
Statistical basics Marian Scott Dept of Statistics, University of Glasgow August 2008.
Advertisements

Irene Seco Manuel Gómez Alma Schellart Simon Tait Erosion resistance and behaviour of highly organic in-sewer sediment 7th International Conference on.
Joongdae Choi, Chulhee Won and Dongkoun Yun Kangwon National University, Korea Rural Research Institute, Korea ICID 2012, Adelaide, Australia.
Integrated urban wastewater systems: Prediction of particle settling velocity distributions Thibaud Maruéjouls, Paul Lessard and Peter A. Vanrolleghem.
Transport of nitrogen and phosphorus from Rhode River watersheds during storm events David Correll, Thomas Jordan, and Donald Weller Water Resources Research,
What’s Mud Got to Do With It? Stephen J. Klaine, Ph.D. Department of Biological Sciences Clemson University
Metropolitan Observatory of Urban Hydrology in Port-au-Prince Dr Evens EMMANUEL Laboratoire de Qualité de l’Eau et de l’Environnement Université Quisqueya.
1 CE 548 Analysis and Selection of Wastewater Flowrates and Constituent Loading.
ADRICOSM-EXT PROJECT (ADRIatic sea integrated COastal areaS and river basin Management system pilot project - EXTension) WP2 – INTEGRATED CATCHMENT SIMULATOR.
STUDY OF THE STORM DRAIN SEWER OF THE URBAN CATCHMENT OF LA RIERETA, SAN BOI DE LLOBREGAT, SPAIN TEAM 3: 1. Aline Veról 2. José Rivero 3. Pedro Ramos 4.
4 th International Symposium on Flood Defence Generation of Severe Flood Scenarios by Stochastic Rainfall in Combination with a Rainfall Runoff Model U.
Distribution of Nitrate in Ground Water Under Three Unsewered Subdivisions Erin P. Eid Mike Trojan Jim Stockinger Jennifer Maloney Minnesota Pollution.
Investigation of Acid Deposition Trends in the United States March 2014.
Additional Questions, Resources, and Moving Forward Science questions raised in the development of a science assessment Effect of Conservation Tillage.
Applications of Scaling to Regional Flood Analysis Brent M. Troutman U.S. Geological Survey.
The evaluation of rainfall influence on CSO characteristics: the Berlin case study S. Sandoval*, A. Torres*, E. Pawlowsky-Reusing **, M. Riechel*** and.
Watershed Characteristics and Polycyclic Aromatic Hydrocarbons in Urban Lake Sediments EVAN DART.
SENSORS, CYBERINFRASTRUCTURE, AND WATER QUALITY IN THE LITTLE BEAR RIVER Jeffery S. Horsburgh David K. Stevens, Amber Spackman Jones, David G. Tarboton,
UC Marine Council Santa Barbara Coastal LTER - NSF Nutrient Export Coefficient Modeling in Mediterranean Coastal Streams Timothy H. Robinson, Al Leydecker,
Nutrient Concentrations in Coastal Streams, Variation with Land Use in the Carpinteria Valley (Santa Barbara Coastal LTER) Timothy H. Robinson John M.
Characterizing Baseline Water Body Conditions. What? Confirm impairments and identify problems Statistical summary Spatial analysis Temporal analysis.
Monitoring and Pollutant Load Estimation. Load = the mass or weight of pollutant that passes a cross-section of the river in a specific amount of time.
NSF - CREST Center for the Integrated Study of Coastal Ecosystem Processes and Dynamics in the Mid-Atlantic Region Sub – Theme #1 Land Use and Climate.
Building risk indicators of surface water contamination by pesticides at the small catchment scale. Taking into account spatial and temporal dimensions.
URBAN STORMWATER QUALITY AND LOAD ESTIMATION FROM URBAN RESIDENTIAL AREA IN SKUDAI, JOHOR, MALAYSIA Siti Nazahiyah Bte Rahmat Faculty of Civil and Environmental.
Northwest hydraulic consultants 2NDNATURE Geosyntec Consultants September 11, 2007 Urban Upland / Groundwater Source Category Group (UGSCG) Overview Presentation.
Satellite based mapping of lakes and climatic variations in the Ruizi and Katonga Catchments, Uganda Bernard Barasa December, 2014.
The University of MississippiNational Center for Computational Hydroscience and Engineering Rainfall runoff modeling in agricultural watershed using 2D.
Contents Interpolated Rainfall :« simple to complexe » methods
1 of 35 The EPA 7-Step DQO Process Step 4 - Specify Boundaries (30 minutes) Presenter: Sebastian Tindall Day 2 DQO Training Course Module 4.
URANS A PPROACH FOR O PEN - C HANNEL B IFURCATION F LOWS M ODELLING Adrien Momplot, Gislain Lipeme Kouyi, Emmanuel Mignot, Nicolas Rivière and Jean-Luc.
Biofilm in combined sewer:  a wet weather pollution source ? and / or  a dry weather pollution indicator ? Sewer Processes and Networks France
Comparative analysis of climatic variability characteristics of the Svalbard archipelago and the North European region based on meteorological stations.
Water quality and river plume monitoring in the Great Barrier Reef: an overview of methods based on ocean colour satellite data Michelle Devlin 1, Caroline.
Unit of Environmental Engineering – University of Innsbruck, Austria Do we measure the right parameters in the right place(s)? Günther LEONHARDT M. Kleidorfer.
Urban Storm Drain Design: Rainfall-Runoff relations.
1 Drainage and Environment, Results of the Monitoring of Non Point Source Pollution Viesturs Jansons Department of Environmental Engineering and Water.
1 II. Sewer Networks and Facilities Topic II.1. Kinds of Wastewater. General Scheme of Sewerage. Kinds of Sewerage Schemes (Patterns) Sewerage Definition:
Applications of Regression to Water Quality Analysis Unite 5: Module 18, Lecture 1.
1 Factors influencing the dynamics of excessive algal blooms Richard F. Ambrose Environmental Science and Engineering Program Department of Environmental.
Assessing Metaldehyde Concentrations in Surface Water Catchments and Implications for Drinking Water Abstraction Alemayehu Asfaw, PhD student - University.
Assessment of Runoff, Sediment Yield and Nutrient Load on Watershed Using Watershed Modeling Mohammad Sholichin Mohammad Sholichin 1) Faridah Othman 2)
Source waters and flow paths in an alpine catchment, Colorado, Front Range, United States Fengjing Liu, Mark W. Williams, and Nel Caine 2004.
Watershed Monitoring and Modeling in Switzer, Chollas, and Paleta Creek Watersheds Kenneth Schiff Southern California Coastal Water Research Project
The influence of local calibration on the quality of UV-VIS spectrometer measurements in urban stormwater monitoring N. Caradot, H. Sonnenberg, M. Riechel,
Impact of rainstorm-triggered landslides on high turbidity in a mountain reservoir Impact of rainstorm-triggered landslides on high turbidity in a mountain.
Surface Water Surface runoff - Precipitation or snowmelt which moves across the land surface ultimately channelizing into streams or rivers or discharging.
Water quality sensors provide insight into the suspended solids dynamics during high flow events in the Lamprey River, NH Nicholas K. Shonka and William.
Sources of Bacteria and their Variability in Urban Watersheds Robert Pitt Cudworth Professor Urban Water Systems Department of Civil, Construction, and.
Chowan River TMDL Development Blackwater Area 09/07/04.
Intro to Psychology Statistics Supplement. Descriptive Statistics: used to describe different aspects of numerical data; used only to describe the sample.
The Examination of Streamflow from an Ice Covered Pond Presented By:
Watershed Monitoring and Modeling in Switzer, Chollas, and Paleta Creek Watersheds Kenneth Schiff Southern California Coastal Water Research Project
Chowan River TMDL Development Nottoway Area 08/31/04.
Ron Fleming and Malcolm MacAlpine University of Guelph Ridgetown Campus, Ridgetown, ON, N0P 2C0 Paper No. CSBE
Tim Cohn USGS Office of Surface Water Reston, Virginia Flood Frequency Analysis in Context of Climate Change.
Surface water and Barton Springs What do we know? –After a storm –The rest of the time Current study objectives TCEQ – USGS study approach Additional research.
Maximum Liquid Manure Spreading Rates on Sloping Land Ron Fleming and Malcolm MacAlpine University of Guelph Ridgetown Campus CSBE
M. Walaszek 1, P. Bois 1, J. Laurent 1, A. Wanko 1 1 Ecole Nationale du Génie de l’Eau et de l’Environnement de Strasbourg (ENGEES) Laboratoire des Sciences.
Characteristics of the overflow pollution of storm drains with inappropriate sewage entry Zuxin XU Hailong YIN College of Environmental Science and Engineering,
Graduate Students, CEE-6190
Bayesian model averaging approach for urban drainage water quality modelling Gabriele Freni Università degli Studi di Enna “Kore”
Continuous Surrogate Monitoring for Pollutant Load Estimation in Urban Water Systems Anthony A. Melcher, USU Civil and Environmental.
Impacts of Urbanization and Event Magnitude on Runoff Contributing Area and Runoff Coefficients 13th International Conference on Urban Drainage, 7-12 September.
URBAN NON-POINT SOURCE NUTRIENT IMPACTS
Estimation of Loadings for Nonpoint Sources and Stormwater
Hydrology CIVL341.
Hydrology CIVL341 Introduction
Scottish Water Catchment Conference, 06/09/2018
Presentation transcript:

Hannouche, A.; Chebbo, G.; Joannis, C. Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? SPN7 – Sheffield, UK – August 2013

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 2 Context Importance of urban wet weather pollution; Negative impact of TSS ( main vector of certain contaminants ); High temporal variability of TSS concentrations and fluxes not only during event but also between events; Some studies have observed some spatial homogeneity between sites, as regards fluxes and concentrations (Kafi Benyahia et al. 2008: Spatial variability of the characteristics of combined wet weather pollutant loads in Paris. Water Research 42, ) Conventional sampling methods on samples collected during rain events:  limited number of samples per event  some events can be sampled Continuous turbidity measurement in sewer systems:  indirect access to the dynamics of particulate pollution

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 3 SOERE URBIS databases Statistically representative databases for continuous water flow and turbidity measurements at the outlet of:  two embedded catchments in Paris (Quais and Clichy)  one in Lyon (Ecully)  hundreds of rainfall events and dry weather days Aim of this study  Assessment of the variability of TSS fluxes and concentrations observed at the outlet of these catchments during both wet and dry weather periods (A long-term Observation System for research and Experimentation on urban environment)Lyon Paris

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 4   Quais catchment is totally embedded in the Clichy catchment complementary fraction of the “Quais” catchment denoted “Outside Quais”   Ecully’s characteristics are quite different vs. Parisian sites: low population density, residential area with steep slopes, and no street cleaning   Paris sewer network is known for its high deposit level but this is not the case for Ecully Description of the sites CatchmentsQuaisClichyOutside QuaisEcully Land usesDense urban residential Surface area (ha) Runoff coefficient (-) Active surface (ha) Median slope (%)

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 5  each site: 2 redundant turbidity sensors, 1 flow-rate sensor & 1 conductivity sensor   Flow-rate, turbidity and conductivity measurements: time step: 1 Quais & Clichy (2006), 2 Ecully (2004  2008))   Turbidity-TSS average relationship was applied   Available data set Equipments and available data set

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 6 RESULTS AND DISCUSSION Volumes, masses and concentrations at the level of rainfall events and dry days Wet weather Dry weather Distributions “Tukey box plots”

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 7 RESULTS AND DISCUSSION Volumes, masses and concentrations at the level of rainfall events Correlations between sites for common rainfall events

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 8 CONTRIBUTION OF SOURCES Contribution of different sources to mass results for each rain event 3 distinct origins of event load during a rain event (M Outlet ) :  Wastewater (M WW ),  Surface runoff (M SR )  Sewer deposits (M SD )  M SD =M Outlet -M WW -M SR TSS (mg/l) Turbidity (FAU) C runoff (mg/l)

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 9 RESULTS AND DISCUSSION Contribution of different sources to mass results for all rainfall events Absolute contribution Relative contribution Absolute contribution Relative contribution Distributions d 10 -mean-d 90

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 10 RESULTS AND DISCUSSION Contribution of different sources to mass results for common rainfall events Correlations between sites (Quais & Clichy)

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 11 Conclusions The results confirmed obtained for other Paris sites with similar land uses; Masses and concentrations for different rain events are correlated between sites with similar land uses The correlation between the concentrations is unexpected and may be a clue for some deterministic processes Regarding urban water discharges, wastewater is a decisive factor for two reasons:  Wastewater generates straightforwardly a significant part of the total event load  deposits contribution is also comparatively substantial; substantial contribution of sewer deposits is not specific to sewer systems like the Paris sewer network (low slope, coarse sewer deposits)

Ali Hannouche – SPN7- Wednesday 28 - Friday 30 August 2013-Sheffield, UK Dynamics of pollutant discharge in combined sewer systems during rain events: chance or determinism? 12 THANK YOU FOR YOUR ATTENTION Questions?