STORM WATER QUALITY IN THE CASCINA SCALA (PAVIA, ITALY) EXPERIMENTAL CATCHMENT



Similar documents
Pollution in storm water runoff. Two cases: an urban catchment and a highway toll gate area.

Sewerage Management System for Reduction of River Pollution

CSO Modelling Considering Moving Storms and Tipping Bucket Gauge Failures M. Hochedlinger 1 *, W. Sprung 2,3, H. Kainz 3 and K.

Maine Department of Environmental Protection Program Guidance On Combined Sewer Overflow Facility Plans

Total Suspended Solids: The Hows & Whys of Controlling Runoff Pollution

Risk and vulnerability assessment of the build environment in a dynamic changing society

HOW-TO GUIDE FOR STORMWATER MONITORING

Hydrological and Material Cycle Simulation in Lake Biwa Basin Coupling Models about Land, Lake Flow, and Lake Ecosystem

A water quality monitoring network for environmental management of port areas An example from the Port of Venice

WATER QUALITY MODELING TO SUPPORT THE ROUGE RIVER RESTORATION

Module 6 : Quantity Estimation of Storm Water. Lecture 6 : Quantity Estimation of Storm Water

Application for Controlled Trade Waste Discharge Approval

Improper storage of fuel on construction sites will increase the risk of water pollution that may occur as a result of leaks or spills.

URBAN STORMWATER GUIDELINES AND BEST MANAGEMENT PRACTICES FOR PROTECTION OF FISH AND FISH HABITAT DRAFT DISCUSSION DOCUMENT

Evaluating Drain Inlet Cleaning as a Storm Water Best Management Practice

Burnsville Stormwater Retrofit Study

Stormwater management around the world Lessons from Novatech 2010 Dennis Corbett and Marion Urrutiaguer

Havnepromenade 9, DK-9000 Aalborg, Denmark. Denmark. Sohngaardsholmsvej 57, DK-9000 Aalborg, Denmark

Pollution Control NEW! NEW! Stormwater Attenuation Systems Sustainable Urban Drainage Solutions for Domestic & Commercial Applications. klargester.

Pervious Pavers. By: Rich Lahren. Hebron Brick & Block Supply

User s Manual for the BMPTRAINS Model

Improper storage of potential pollutants will increase the risk of water pollution that may occur because of spills.

Hydraulic efficiency of macro-inlets

Sustainable Drainage Systems (SUDS) A guide for developers

WATER QUALITY MONITORING AND APPLICATION OF HYDROLOGICAL MODELING TOOLS AT A WASTEWATER IRRIGATION SITE IN NAM DINH, VIETNAM

DESIGN OF STORM WATER DETENTION POND

Toxic Municipal Waste Water Treatment

City of Toronto Wet Weather Flow Monitoring Network: Baseline Conditions

Stormwater Best Management Practices (BMP) Performance Analysis

Computing Stormwater Runoff Rates and Volumes

Eau de pluie, pollution source non-ponctuelle, modèle de bassin versant MGEP (SWMM), pollutogramme, contrôle automatique

TEXAS: SAN ANTONIO San Antonio Protects Edwards Aquifer

Natural and Advanced Treatment Systems for Wastewater Management at Municipal Solid Waste Disposal Site in Developing Countries

Guidelines for on-line monitoring of wastewater and stormwater quality

Planning, Health and Environment Division

Highway Runoff in Ireland and Management with a French Drain System

City of Mebane Wastewater Collection and Treatment Facility

Permeable Pavement Treatment Capacity

LANDSCAPING AQUA SPORT. Rainwater treatment using filter substrate channel. DIBt approval applied for

Vision-based sensors for water cycle

The Rational Method. David B. Thompson Civil Engineering Deptartment Texas Tech University. Draft: 20 September 2006

Stormwater Quality Monitoring Report


Phosphorus. Phosphorus Lake Whatcom Cooperative Management.

Retention/Irrigation. Design Considerations. Soil for Infiltration Area Required Slope Environmental Side-effects

89 Avenue Road GP Ltd. Functional Servicing and Stormwater Management Report for 89 Avenue Road Re-Development City of Toronto

C.3 Workshop Track 2: Sizing Calculations and Design Considerations for LID Treatment Measures

NAJAFGARH DRAIN-SAMPLING AND ANALYSIS

Package Treatment Plant Policy and Procedure

BY-LAW CONCERNING DISCHARGES AT PURIFICATION WORKS ON THE TERRITORY OF THE URBAN AGGLOMERATION OF MONTRÉAL

Melbourne, Australia. Melbourne: The city as a catchment approach. The importance of holistic urban water management

Micromanagement of Stormwater in a Combined Sewer Community for Wet Weather Control The Skokie Experience

Computer Assisted Procedure for the Design and Evaluation of Wastewater Treatment Systems

DRAINAGE DISCHARGE AGREEMENTS A WAY OF MANAGING RISK Mr. Sam Green Goulburn-Murray Water

TREATMENT OF SANITARY SEWER OVERFLOW

MONITORING AND MODEL CALIBRATION FOR THE SEWER NETWORK IN OSLO

10/4/ slide sample of Presentation. Key Principles to Current Stormwater Management

SOUTHERN CALIFORNIA Regional Hydrology IMPACTS ON REGULATORY APPROACHES FOR THE FUTURE. Monitoring & Modeling

HYDRAULIC ANALYSIS OF OIL SPILL CONTROL SYSTEMS AT ELECTRICAL TRANSFORMER STATIONS

Chapter 3 : Reservoir models

Procedia Environmental Science, Engineering and Management

1.3 Wastewater and Ambient Water Quality

RÉSUMÉ ABSTRACT KEYWORDS

Climate vulnerability assessment Risks from urban flooding Interactive science and policy assessment

ENGINEERING REPORT Sewage Treatment System

Kansas City s Overflow Control Program

Outdoor Storage of Raw Materials SC-33

Flood risk assessment through a detailed 1D/2D coupled model

Guidance on the use of sustainable drainage systems (SUDS) and an overview of the adoption policy introduced by

Waste Handling & Disposal

STAFF REPORT TO COMMITTEE OF THE WHOLE

How do storm water and wastewater networks function together with the wastewater treatment plant? Theo G. Schmitt, Kaiserslautern University (Germany)

STORMWATER POLLUTION PREVENTION PLAN TEMPLATE. 1.0 SITE DESCRIPTION 1.1 Project Name and Location Date

TALLINN WATER TREATMENT AND SEWERAGE Tuuli Myllymaa

Module 7: Hydraulic Design of Sewers and Storm Water Drains. Lecture 7 : Hydraulic Design of Sewers and Storm Water Drains

ANALYSIS OF RAINFALL AND ITS INFLOW INTO MOBILE, ALABAMA S, ESLAVA SEWER SHED SYSTEM

Permeable Interlocking Concrete Pavements. The Stormwater Problem

Permeable Interlocking Concrete Pavements

16. Storm water drainage

COMPREHENSIVE PLAN SECTION B, ELEMENT 4 WATER RESOURCES. April 20, 2010 EXHIBIT 1

A web system for display and analysis of real-time monitoring observations of small urbanized catchments in Lahti, Finland

Stormwater Ponds. c ıty of a bı le ne st or m wat e r utı lıty dıv ısı on

STORM WATER MANAGEMENT PLAN (SWMP)

A Developer s Guide: Watershed-Wise Development

Temporary Batch Plants

Creating the environment for business

SILA Sistema Integrato di Laboratori per l Ambiente

Guidelines for Performing Infiltration/Inflow Analyses And Sewer System Evaluation Survey

To meet our acceptance criteria, we may require you to partially treat your wastewater before it discharges to sewer.

Water attenuation performance of experimental green roofs at Ruislip Gardens London Underground Depot Report 1 - July 2013

6 Chemicals from human settlements

CWSRF Project Descriptions and Examples for Green Project Reserve

DRAFT Guidelines for Manually Diverting Outdoor Wastewater to the Sanitary Sewer

Re: Proposal for Innovative Options for Providing Stormwater Infrastructure and Services

Water and Wastewater. Sample Collection and Analysis

Flash Flood Science. Chapter 2. What Is in This Chapter? Flash Flood Processes

A strategy for Bremen s adaptation to extreme climate change-related rainfall events the KLAS project

POLLUTION PREVENTION FACT SHEETS: CATCH BASINS. Description

4 Water supply description

Rainfall-Storage-Drain(RSD) model for Runoff Control Rainwater Tank System Design in Building Rooftop

Transcription:

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 STORM WATER QUALITY IN THE CASCINA SCALA (PAVIA, ITALY) EXPERIMENTAL CATCHMENT C. Ciaponi*, M. Mutti**, S. Papiri*** * Dipartimento di Ingegneria Idraulica, Università degli Studi di Pavia, Via Ferrata,, 700 Pavia, Italy, Tel (+9) 0, Fax (+9) 09, Email ciaponi@unipv.it ** Dipartimento di Ingegneria Idraulica, Università degli Studi di Pavia, Via Ferrata,, 700 Pavia, Italy Tel (+9) 076, Fax (+9) 09, Email matteo.mutti@unipv.it *** Dipartimento di Ingegneria Idraulica, Università degli Studi di Pavia, Via Ferrata,, 700 Pavia, Italy Tel (+9) 0, Fax (+9) 09, Email papiri@unipv.it KEYWORDS: experimental catchment, storm water, water quality SUMMARY This paper aims at presenting the first results of an experimental research taking place in the Cascina Scala (Pavia, Italy) experimental catchment. The purpose of the research consists in leading to a better knowledge of the phenomena ruling the pollutant dynamics during storm water runoff from urban areas. The results of two experimental campaigns, concerning both quantity and quality aspects of storm water discharges during meteorological events, have been reported. Quality analyses have been carried out for each of the 6 collected samples, thus making available the values of the following constituents: specific conductivity, COD, BOD, suspended solids, settleable solids, total nitrogen, ammonium nitrogen, phosphorus, lead, zinc and hydrocarbons. Moreover, information on the characteristics of dry weather flows in the sewer network has been provided by samples which have been collected at different times during a dry day. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 INTRODUCTION Several studies (Weibel et al., 96; De Filippi and Shih, 97; Sartor et al., 97; Wanielista et al., 977; Lindholm and Balmèr, 97; Novotny and Chester, 9; Reinertsen, 9; Berndtsson et al., 990; Bujon and Herremans, 990) have stated that urban storm waters must be considered a major source of pollution for receiving waters due to the presence of both conventional (suspended solids, COD, BOD, NH, PO, etc.) and toxic contaminants (Pb, Cu, Zn, hydrocarbons, etc.). Experimental researches aiming at a better definition of wastewater and rainwater characteristics have been carried out in Italy as well. Nonetheless so far published results (Veltri, 9; La Loggia and Viviani, 99; Artina et al., 997) are scarce and certainly not fully representative of the different climatic, urban, social and economical Italian situations. At the present time, the design and the construction of urban stormwater management systems in Italy are planned according to technical criteria based on the experience of other countries where the meteorological and urban features may be quite different. It is therefore evident that data on sewer system flow rates and waste water quality, under both dry weather and wet weather conditions for the Italian situations, can contribute to a better solution of many technical problems. With these aims, systematic investigations to collect storm water quality data in the Cascina Scala (Pavia, Italy) experimental catchment started in June 000. The first results are presented in this paper. THE EXPERIMENTAL CATCHMENT OF CASCINA SCALA (PAVIA) The Cascina Scala experimental catchment is a residential district situated on the northern outskirts of Pavia. The total contributing area adds up to m. 6% of the total area is impervious (.% roofs and.% streets and paved surfaces) while % of the total area is pervious and not connected to the sewer system. The combined sewerage network has a total length of 0 m; the slope of the sewer pipes ranges between 0.% and.0% with an average value weighted on the length of 0.%. All the sewers are made of standard concrete pipes. Research activities on the hydrologic and hydraulic behaviour of the basin have been started in 99 (Papiri, 99). More details on the physical characteristics of the basin and the drainage system are reported in another paper (Ciaponi and Papiri, 99). The rainfall on the basin is measured with two SIAP tipping bucket rain gauges with a 0. mm accuracy and a UM 70 precipitation sensor. The distance between the two rain gauges is 0 m, therefore the spatial uniformity of the precipitation can be checked and the meteorological volume can be evaluated accurately. Storm water runoff in the final reach of the sewer network is measured using a Venturi flume and a ISCO 0 bubbler flow meter. Temperature and conductivity in the final reach of the sewer network are measured on site with a YSI 0 multiparameter sonde ( measurement every minutes), while storm water Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 runoff sampling is collected by means of a ISCO 6700 SR refrigerated sampler equipped with bottles. The samples are collected according to programmable enable controls and laboratory analyses are then carried out. EXPERIMENTAL DATA Quantity and quality data concerning the drainage flows in the sewer network during wet weather have been recorded in the period JuneJuly 000 and MarchApril 00. The data collection refers to meteorological events during which 6 samples have been collected and analysed. The main characteristics of the events are reported in Table. The number of samples is strongly variable for each event, since the sampler enable condition has been programmed so as to depend on a fixed minimum water level in the final reach of the sewer network, therefore an adequate number of samples has been gathered only for events with a certain precipitation intensity. In addition, during the first period of the June 000 campaign there have been some problems in programming the sampling sequence, since the equipment had to be regulated. The results of the analyses for each sample are reported in Table and the range and the mean value of the constituents are reported in Table. Aiming at the characterisation of the dry weather flows, in February 00, samples have been collected ( sample every hours), so as to cover a whole day. The results obtained for the analysed samples are reported in Table and the range and the mean value of the constituents are reported in Table. Comparing the values reported in Table and in Table, it can be observed that the fluctuations of the values of suspended solids, COD and BOD during wet weather are more noticeable than during dry weather. The maximum values of the constituents during wet weather are greater than during dry weather. A list of symbols and abbreviations is reported in Table 6. Many attempts have been made to establish correlation relationships between the concentrations of different constituents. Correlation relationships have been searched particularly between suspended solids and the other contaminants, since suspended solids are assumed as a reference parameter in many mathematical models simulating the pollutant dynamics during storm water runoff. Comparing the results of the two sampling campaigns (JuneJuly 000 and MarchApril 00), the connection between the concentration of COD and BOD and the concentration of suspended solids appears to be markedly evident, thus justifying the assumptions made in many simulation models. However, it must be outlined that the correlation relationships are quite different for the samples of the two campaigns. The difference of statistical behaviour for the two series of experimental data can be essentially explained considering the role played by the temperature in the degradation kinetics of the BOD associated to the suspended solids. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 The correlation relationships between the other constituents and the importance of the temperature will be extensively analysed in a still unpublished paper. ACKNOWLEDGEMENTS This research has been financed by MIUR 000. Special thanks are due to Paola Boriani for the contribution given to this research while working on her degree s thesis. Table. Characteristics of the events. Event Date Rainfall Rainfall Maximum Measured Number of Dry Time Length Depth Flow Rate Volume Collected day min mm l/s m³ Samples 0/06/000. 969 (*) 6 (*). /06/000. 99 (*) 6 (*) 0. /06/000 97. 90 0. /06/000 0.0 6 0. /06/000 0 6. 76 0. 6 /06/000.6 0 7. 7 0/07/000 0 7.0. 0/07/000 6.0 76. 9 /07/000 0.6 90 66 0.9 0 /0/00 7. 0. 7/0/00 7 6. 6.9 /0/00.6 6 9.0 0/0/00 0. 7 6. 0/0/00. 7 6 0.0 (*) The value has been evaluated through numerical simulation because the sewer reaches pressure flow conditions. Table. Results of the quality analyses for the samples collected in the combined sewer system during storms. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Sample SC µs/cm COD mg/l BOD mg/l HC mg/l SS mg/l Set S ml/l TN mg/l AN mg/l P mg/l Pb mg/l Zn mg/l EVENT : 0/06/000 9 0 6. 9.0 9.0 9.00 0.70.00 EVENT : /06/000 9 7 0 90.0 0.70.76 0.06 0. 6 7.0 9.70.97 0.06 0.99 6 0.. 7.70 0. 0.0 0.9 7 7 6 0.7. 7.00 0.7 0.00 0.079 6 9 7 0. 90.0.07 0. 0.0 0.6 EVENT : /06/000 9 0 0..0.. 0.0 0.6 00 0. 0 7.00 0. 0.0 0.00 9 7.07 0.0.0 0. 0.09 0.066 EVENT : /06/000 7.0 70.0.70.0 0.0 0. EVENT : /06/000 0 00 0. 0.0.0.6 0.6 0.9 6 90 76 0.90 90 70.0 6.00.0 0.0.0 900 0 6.0 0.0..9 0.0.00 6 76 0. 0.0.70. 0.0 0.9 69 7.0 0.0..9 0.70 0.0 6 0 0 0.00 70 0..76. 0.0 0.0 7 7 0.0 0 0.0.77.7 0.90 0. 7 70.0 0 9.0 7.7.07 0..0 9 7 6.0 0 0..90.9 0.0. 0 0.90 0 6...77 0.0 0. 7 7.0...9 0. 0. 0.0 70..0.6 0.. 0.00 0.9 0.0 0.09 0 9 6.0... 0.00 0.7.00.0.7.0 0.00 0.0 6 9 0.0.0.0.0 0.0 0.07 7 6 9. 00.6. 0.97 0.00 0.0 99 <0.0.. 0.9 0.09 0.00 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 EVENT 6: /06/000 76 0.0 6.6.0 0.70.6 0.00 0.70 00 7 00.70..00 7.0.6 0.07 0.670 96 7.0 0...0. 0.00 0.96 0 0. 0..0.6.6 0.09 0.6 70. 9 7. 6.90.. 0.079 0. 6 06 69 0. 0.0..00 0.7 0.0 0. 7 0..0. 0.9 0.7 0.0 0.7 0.90 70 7..7 0.69 0. 0.0 0. 9 6 0.90 70.0.00 0.9 0.76 0.0 0. 0 9 0. 0.0.79.6 0. 0.06 0.90 9 0 0.70 6.0.7.6 0.6 0.0 0. 0. 0.. 0.6 0.00 0. EVENT 7: 0/07/000 0 0 7. 0 7.0.0...0 00 0. 0.0 6.0 7.7 0.90. 6 06 0.0 0 6.0 6.0.77 0..0 9 0.90.0.70.6 0.90 0. 007 00 0. 6.0 7.70. 0.. 6 0 7.0.0 7.0.9 0..0 7 0 0 90.0 0.0.0. 0.0.90 7 7.0 0.0.90.9 0.0 0.70 EVENT : 0/07/000 0 6. 6.0.00 0.90.0 0.0 0. 7 6 6. 000.0... 0.0 0.6 6 7..0.0.. 0.06 0.6 0.0 9.0.7..6 0.00 0..0 0 7.0 7. 0..0 0.0 0.90 6.70.0...9 0.00 0.0 7 9 0.00.7...7 0.00 0. 00 07 0.0..00. 0.0 0.00 0.0 9 0 0.00.. 0.69 0. 0.007 0.0 0 9.90.0 6..00 0.69 0.00 0.00 6 9..0.6. 0. 0.00 0.0 0.0 0... 0.9 0.00 0.0 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 6

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 EVENT 9: /07/000 7 90..70.7. 0.066 0.0. 9..0..9 0.00 0. 9.0. 7.97.6.7 0.00 0.0 06 7.0. 7..76. 0.0 0. EVENT 0: /0/00 7 9 0 0.90 0.0 6. 0.00.0 0. 0.90 7 0 0.7.00.0..0 0.70 60 0.0.0.70 7.0.09 0. 0.. 7.0.0 7.0.7 0. 0.0 9 679.70 0.0. 6.0.6 0. 0.0 6 0 6 90. 0.0 7.0 6..9 0. 0.0 7 0 066 0. 0 66.0 0.0 7..96 0.00 0.70 0.0 0.0.0. 0.0 0.0 9 0 0.. 0.6 0.00 0. 0 9 0 70..0 0.6 0.0 0. 0 70 90. 7.90.0 0.6 0.0 0. 9 96.0. 7.0.0 0.6 0.090 0.0 EVENT : 7/0/00 7 70 90.0 0.0 6.70.90.9 0. 0.0 6. 00 0. 9.00 6. 0.70 0.60 7 7.90.0 7.0 0.0 0.90 0.0 6 70. 00.0. 9.0 7.0.0 0.7 90. 6 9.0 7.00 6.90.9 0.0 0. 6 970. 7 6.0 6.90.6 0. 0.0 7 00 9.97.0 7.00 6.00 0. 0.0 0 6.0 0.0 9..0.6 0. 0.6 9 7 90.0 0.0.00.. 0.09 0.00 0 6 0 0 0. 0 6.0 7.0..69 0.0 0.70 7 90.0 0 9.0 7..6.9 0.07 0.0 0...0.77 0.06 0.0 0.70 0 6.0 0... 0.0 0. 0.90 00.0 0.00.00. 0.07 0.0 0 70 0.70.0 7.00. 0.70 0.06 0.70 6 0 7 0..0.0 0. 0.0.770 7 9..0.0.0 0.0 0.0 0.0 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 7

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 9..70.0 0. 0.06 0. 9 07 9 0. 00. 6.90.70 0.0 0.0 0.0 0 0 0 <.0.70. 0.6 0.009 0. 96 0 0 <.0..77 0. 0.00 0. <.0.7.07 0. 0.00 0. 06 0 <.0.00. 0. 0.00 0. 00 6.0 <.0... 0.067 0.0 EVENT : /0/00 6 0.00 00.0 0.0 0. 6. 70 0.0.0.0. 0.00 0. 9 7.0 00.0 6..0. 0..00 90 97 0.0 6 7 66.00. 9. 0. 0.9 6 0.0 00.0 6.70 9.0.0 0.0 0.0 6 00 90 770..0.0 7.. 0.0 0.70 7 6 7. 7 0.0.. 0.07 0.90 7 70 0.0 7.0 9. 7.00 0..00 9 90.7 00.0.0 7..0 0.07 0.70 0 7 0..0 7.00 7.00.0 0.0 0.70 0 0.79 6 0.0.0.0. 0.06 0.790 0 7 0 0. 00 0.0 9.00 7.00.66 0.06 0.770 67.6 0. 6.90.00 0.0 0.0 0 9 00.0 0.0.00 6..77 0.70 0.790 9 0.7 00.0 6.0.0 0.0 0.0 6 9 0.7 90.00 7.0 0.9 0.0 0.6 7 0 0 0.9 00.0.90 0.9 0.0 0.7 7 90 0. 70 6.0.0.. 0.0 0.0 9 0 97 0.99.0. 6.0.0 0.06 0.9 0 7 0.0..70.0 0.0 0.0 00 0 0 6.0.0. 0.96 0.067 0.90 0 6 00.70.70 0..0 0. 0 7 6 90.0.0. 0. 0.07 0.90 00 66 0.0...0 0.09 0. EVENT : 0/0/00 77 76 7.0 6. 6.0.9 0. 0.60 6 67 70 90.0 6..00 7.9 0.0 0.0 0 0 900 0 7 6. 0.0 7. 0.90 0. 0 9 90 7.70 9.00. 0.0 0.7 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 9 6 7 9 0 6 77 67 7 9 7 0 9 0 6 76 6 6 9 07 7 9 0 0 6 6 90 6 0 0 00 670 70 0 0 70 70 0 70.0 7.0.0.0.0 9.0 7..0 9.0.0.0 6.0 6.0 7.0 6.0.0 9.0.0.00..90..90.90. 0.00 0.00 0.0 9.0.0 0.70 6.00 9.0.00 6.00.70 7..9.06.99.67.9..6. 0.6 0.79. 0. 0. 0.06 0.09 0.06 0.066 0.0 0.06 0.0 0.06 0.0 0.790 0.90 0. 0. 0. 0.0 0.690 0. 0. 0.0 0.0 0. EVENT : 0/0/00 6 7 9 0 6 7 9 0 70 6 0 69 6 90 7 9 7 9 6 0 6 07 07 67 99 0 76 0 0 9 7 0 69 9 00 0 6 7 70 6 76 90 0 70 9 0 0 70 70 00 0.0.0.0.0 6.0.0 6.0..0.0.0 7.0 0.0.0.0.0.0.0.0.0.0 6..70 6.70 9.00.0..70.0 9. 7..0 6.70.70....0 9.0..0.0 9..70.0 9.00.70 9.0 9.00 9. 9.90. 7.00 9.90 0..0.90.0 7.70 6..70..90.00.9 6. 6. 6.7... 0.67 0.76 0..0..0.0 0.70.7.06.9.0 0.. 0..90 0. 0.0 0.0 0.00 0.06 0.0 0.0 0.00 0.00 0.07 0.07 0.00 0.0 0.07 0.0 0..0 0.0 0.0 0.0 0.09 0.0 0.670 0.770 0.70 0.0 0. 0. 0. 0. 0.0 0.0 0.0 0.90 0.70 0. 0. 0. 0.0 0.0 0. 0.0 0.00

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Table. Range and mean values of the quality constituents for the 6 samples collected during storms. Constituent Unit of Mean Minimum Maximum Measure Value Value Value Specific Conductivity µs/cm 0 6 77 COD mg/l BOD mg/l 7 Hydrocarbons mg/l.7 0.. Suspended Solids mg/l 0 0 Settleable Solids ml/l. 0. 00.0 Total Nitrogen mg/l.. 6. Ammonium Nitrogen mg/l.6 0. 9. Phosphorus mg/l.70 0..0 Lead mg/l 0.0 0.00.00 Zinc mg/l 0. 0.00.90 Table. Results of the quality analyses for the samples collected during dry weather ( February 00). Hour SC COD BOD HC SS Set S TN AN P Pb Zn µs/cm mg/l mg/l mg/l mg/l ml/l mg/l mg/l mg/l mg/l mg/l 0 70 0 0 0.7 0 9.0.70..9 0.0 0.0 6 667. 6.0. 9.0.6 0.0 0.7 70 7 6. 0.0 6. 0.0.6 0.0 0. 6 7 76.7 6.0..0.67 0.00 0.90 670 00.0.0.. 0.07 0. 0 770 6 0.76 0.0.70.70.7 0.0 0.70 07 70.0 6 6.0..0 6. 0.06 0.0 7..0.0.70. 0.0 0. 0 670 9.0 <.0.0 0.0. 0.0 0. 0 0 6. <.0 7. 0..0 0.0 0. 06 00 0. 0 <.0.00.0.7 0.0 0.00 0 9 79 6.7 0.0 99.00 7.00 7.9 0.00 0.6 Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 0

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Table. Range and mean values of the quality constituents for the samples collected during dry weather. Constituent Unit of Mean Minimum Maximum Measure Value Value Value Specific Conductivity µs/cm 7 0 9 COD mg/l 6 07 BOD mg/l 6 70 Hydrocarbons mg/l.90 0..76 Suspended Solids mg/l 00 0 6 Settleable Solids ml/l.0 <.0 6.0 Total Nitrogen mg/l. 7. 99.00 Ammonium Nitrogen mg/l 0. 9.0 7.00 Phosphorus mg/l.0.0 7.9 Lead mg/l 0.0 0.0 0.0 Zinc mg/l 0.0 0.00 0.7 Table 6. List of symbols and abbreviations. LEGEND SC COD BOD HC SS Set S TN AN P Pb Zn Specific Conductivity Chemical Oxygen Demand Biochemical Oxygen Demand Hydrocarbons Suspended Solids Settleable Solids Total Nitrogen Ammonium Nitrogen Phosphorus Lead Zinc Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure. Hyetograph, hydrograph and samples for event. Figure. Hyetograph, hydrograph and samples for event. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure. Hyetograph, hydrograph and samples for event. Figure. Hyetograph, hydrograph and samples for event. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure. Hyetograph, hydrograph and samples for event. Figure 6. Hyetograph, hydrograph and samples for event 6. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure 7. Hyetograph, hydrograph and samples for event 7. Figure. Hyetograph, hydrograph and samples for event. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure 9. Hyetograph, hydrograph and samples for event 9. Figure 0. Hyetograph, hydrograph and samples for event 0. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 6

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure. Hyetograph, hydrograph and samples for event. Figure. Hyetograph, hydrograph and samples for event. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 7

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 Figure. Hyetograph, hydrograph and samples for event. Figure. Hyetograph, hydrograph and samples for event. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page

New Trends in Water and Environmental Engineering for Safety and Life: Ecocompatible Solutions for Aquatic Environments Capri (Italy), June, 00 REFERENCES Artina S., Maglionico M., Marinelli A. (997). Le misure di qualità nel bacino urbano Fossolo. Modelli qualiquantitativi del drenaggio urbano, p. 7, Centro Studi Deflussi Urbani, Milan. Berndtsson R., Hogland W., Larson M. (990). Field measurements and mathematical modelling of pollution buildup and pipedeposit washout in combined sewers. Proceedings of the Fifth International Conference on Urban Storm Drainage, Osaka, Japan, p.. Bujon G., Herremans L. (990). FLUPOL Modèle de prévision des débits et des flux polluants en réseaux d assainissement par temps de pluie: calage et validation. La Houille Blanche, n.. Ciaponi C., Papiri S. (99). Bacino di Cascina Scala Codice IT0. Le misure di pioggia e di portata nei bacini sperimentali urbani in Italia, p. 7, Centro Studi Deflussi Urbani, Milan. De Filippi J.A., Shih C.S. (97). Characteristics of separated storm and combined sewer flows. Journal of Water Pollution Control Federation, vol.. La Loggia G., Viviani G. (99). Misure delle caratteristiche di qualità delle acque di pioggia nel bacino di Parco D Orleans. Analisi dei primi risultati. Atti del III Seminario sui Sistemi di Drenaggio Urbano, Ancona, Italy. Lindholm O., Balmér P. (97). Pollution in storm runoff and combined sewer overflows. Proceedings of the First International Conference on Urban Storm Drainage, Southampton, Great Britain, p. 7. Novotny V., Chester G. (9). Handbook of nonpoint pollution: sources and management. Van Nostrand Reinhold Co., New York. Papiri, S. (99). Precipitazioni e deflussi nel bacino urbano sperimentale di Cascina Scala (Pavia). Pubblicazione del Dipartimento di Ingegneria Idraulica e Ambientale, Università di Pavia, n. 66. Veltri P. (9). La qualità delle acque nelle fognature urbane. Tecniche per la difesa dall inquinamento; Atti del Corso di Aggiornamento, p. 79, BIOS, Cosenza. Reinertsen T.R. (9). Quality of stormwater runoff from streets. Proceedings of the First International Conference on Urban Storm Drainage, Southampton, Great Britain, p. 07. Sartor J.D., Boyd G.B., Agardy F.J. (97). Water pollution aspects of street surface contaminants. Journal of Water Pollution Control Federation, vol. 6. Wanielista M.P., Yousef Y.A., McLellon W.M. (977). Nonpoint sources effects on water quality. Journal of Water Pollution Control Federation, vol. 9. Weibel S.R., Anderson R.J., Woodward H.L. (96). Urban land runoff as a factor in stream pollution. Journal of Water Pollution Control Federation, vol. 6. Storm Water Quality in the Cascina Scala (Pavia, Italy) Experimental Catchment Page 9