Characterization of Current Conditions
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Philadelphia Combined Sewer Overflow Long Term Control Plan Update 3 CHARACTERIZATION OF CURRENT CONDITIONS As prescribed by the 1997 LTCP, PWD has committed to a detailed watershed-based monitoring program in the Cobbs and Tookany/Tacony-Frankford (TTF) Creek Watersheds. This monitoring program includes chemical, biological and physical assessments to characterize the current state of the watershed and identify existing problems and their sources. The need for this detailed watershed monitoring program was rooted in the fact that insufficient physical, chemical and biological information existed on the nature and causes of water quality impairments, sources of pollution, and appropriate remedial measures prior to PWD’s watershed based assessment. Through this assessment process, PWD has sought to gain a good understanding of the physical, chemical and biological conditions of the water bodies, understand the character of the watershed land uses that will drive wet weather water quality conditions, and build a common understanding of these factors among all stakeholders. A compendium document is produced following the analysis of all collected data; this Comprehensive Characterization Report (CCR) assessment serves to document the watershed baseline health prior to implementation of any plan recommendations, allowing for the measure of progress as implementation takes place upon completion of the plan. The CCR is shared with watershed partners for comments and feedback. CCRs have been completed for the Cobbs Creek Watershed in 2004, the TTF Creek Watershed in 2005 and the Pennypack Creek Watershed in 2009 (Section 1, Table 1.4). These CCR documents are available on the partnership website at www.phillyriverinfo.org. Data related to the Cobbs and TTF Watersheds within this section have been pulled from these CCRs. Data related to the Schuylkill and Delaware River Watersheds have been assembled from a number of sources including PWD sampling locations, the United States Geological Survey (USGS) gage stations and the Delaware River Basin Commission (DRBC) monitoring locations. In order to further understand the complex nature and causes of water quality impairments, PWD has continued to monitor and model the collection system within Philadelphia. This section additionally presents information characterizing Philadelphia’s network of sewer systems, regulating structures, drainage districts, contributing watersheds and outlying community municipalities, precipitation data collection and analysis and the collection of water quantity and quality information. 3.1 MONITORING AND DATA COLLECTION Data collection and monitoring is an essential component to appropriately develop and analyze alternatives for the LTCPU. The collected data is organized, assessed for errors and analyzed using a variety of models, tools and methods. The sections below present data necessary to the LTCPU development process and how it was collected. More information specific to the models, methods and tools used to analyze the data is available in Section 5. 3.1.1 Overview of Input Data Collection The development of the LTCPU required extensive data collection and analysis. The data collection and analysis included characterization of the City’s local climate through precipitation data sources; analysis, collection and correct representation of existing infrastructure data; analysis of the contribution of contaminants and flow data with established flow metering programs; analysis of the Section 3 • Characterization of Current Conditions 3-1 Philadelphia Water Department. September 2009 Philadelphia Combined Sewer Overflow Long Term Control Plan Update topography through extensive use of Geographic Information Systems analyses; analysis and collection of socioeconomic status and the cost for improving the infrastructure. The following sections discuss how this data was collected and the sources used to characterize the City for the LTCPU. 3.1.2 Meteorological Monitoring Data Precipitation data are a fundamental component of a Combined Sewer System monitoring program required to calibrate and validate CSO models and develop design conditions needed for characterizing the CSS and estimating CSO statistics. Both long-term temporal rainfall data and event based rainfall data synchronized with CSS flow monitoring are needed to appropriately calibrate and characterize the CSS. There are three primary sources of precipitation data used in the CSO Program. • National Weather Service (NWS) operated Philadelphia International Airport (PIA) surface observation station • PWD’s city-wide rain gage network • Calibrated radar rainfall estimates 3.1.2.1 PIA Precipitation Data Sources NWS gage at the Philadelphia International Airport (PIA), located in southwestern Philadelphia, has over 100 years of hourly precipitation data; the period of record runs from January 3, 1902 through the present. An annual online subscription is maintained by PWD for the Philadelphia International Airport station (PIA) that allows the download of monthly Edited Local Climatological Data published by the National Oceanic and Atmospheric Administration (NOAA) National Climatic Data Center. The reports are downloaded on a monthly basis when made available - typically four to six weeks behind the end of the current month. Along with hourly rainfall data, the report includes snowfall, temperature, wind speed, atmospheric pressure and other relevant and useful climatological data. 3.1.2.2 PIA Precipitation Data Processing and QA/QC The NWS applies quality assurance procedures to the PIA data internally prior to its release, therefore, no quality assurance protocols are proposed for the PIA data. 3.1.2.3 PWD Precipitation Data Sources PWD maintains a rain gage network consisting of 24 tipping bucket rain gages located throughout the City that record rainfall depths (minimum recorded depth of 0.01 inches) in 2.5-minute increments. The PWD data is considered reliable from 1990-present, with all 24 gages replaced with heated units beginning in the year 2004 in order to allow for accurate measurement of frozen precipitation events. The raw 2.5-minute tipping bucket rain gage data is extracted from a link to the PWD Collector System’s real-time control unit (RTU) database which collects data directly via automatic telephone polling of the gages. The approximate locations of the 24 PWD rain gages are presented in Figure 3-1. The total number of rain gages within each watershed is shown in Table 3-1. Section 3 • Characterization of Current Conditions 3-2 Philadelphia Water Department. September 2009 Philadelphia Combined Sewer Overflow Long Term Control Plan Update Figure 3-1 PWD Rain Gage Locations and Combined Sewer Drainage Areas Section 3 • Characterization of Current Conditions 3-3 Philadelphia Water Department. September 2009 Philadelphia Combined Sewer Overflow Long Term Control Plan Update Table 3-1 Number of PWD Rain Gages within each Watershed Watershed Total Number of Rain Gages Delaware River 10 Schuylkill River 7 Darby-Cobbs Creek 2 Tookany/Tacony Frankford Creek 5 3.1.2.4 PWD Precipitation Data Processing and QA/QC The PWD raw 2.5-minute data are summed to fixed 15-minute intervals. QA/QC of this data is performed on a monthly basis by visual inspection using comparison of data across the network in order to identify and flag missing or questionable data. Flagged data are then filled with coincident data from the six nearest gages using inverse distance squared weighting. On an annual basis, daily rainfall totals for each gage are compared to the network mean using double mass and cumulative residual time series plots in order to identify changes in non-climatic biases at the gages. In this way, gage malfunctions not readily apparent from initial visual inspection of the raw gage data can be identified. Furthermore, bias adjustment periods are identified for each gage and along with comparisons to radar rainfall estimates obtained for a 15-month period of the gage record, a bias adjusted rainfall record is produced for each gage location. Detailed descriptions of the tools and methods of the precipitation bias adjustment are available in Section 5. 3.1.2.5 Calibrated Radar Rainfall Data Sources Due to the fact that storm events are inherently variable and do not evenly distribute rainfall spatially or temporally, PWD obtained discrete measurements of rainfall intensity during storm events targeted for wet weather sampling. For each 15-minute interval, RADAR tower-mounted equipment measured high frequency radio wave reflection in the atmosphere as a series of relative reflectivity measurements for individual 1 km2 blocks. This information was used along with PWD rain gage network data to generate gage calibrated RADAR rainfall estimates and provided to PWD and is further discussed in Section 5.2.1. The National Weather Service’s Next Generation Weather Radar (NEXRAD) program generates products used for estimating spatially variable rainfall data. Several vendors offer gage adjusted radar-rainfall data. PWD rain gage data are used to calibrate NEXRAD data in order to create a detailed and accurate rainfall record that preserves the total rainfall volume reported at the gages while incorporating the spatial variability provided by the NEXRAD data. Detailed rainfall records for areas outside of the City are required for calibration of rainfall dependent inflow and infiltration (RDII) from sanitary sewers contributing flows to the CSS, as well as for watershed modeling performed as part of Phase