Loading...
The URL can be used to link to this page
Your browser does not support the video tag.
Home
My WebLink
About
ID2919-Installation-of-Trash-Capture-Devices-7-23-12
City of Palo Alto (ID # 2919) City Council Informational Report Report Type: Informational Report Meeting Date: 7/23/2012 July 23, 2012 Page 1 of 6 (ID # 2919) Council Priority: Environmental Sustainability Title: Info Report on Short-Term Trash Reduction Plan Subject: Informational Report on Installation of Trash Capture Devices in the Municipal Storm Drain System as Part of Palo Alto's Short-Term Trash Reduction Plan From:City Manager Lead Department: Public Works Executive Summary Palo Alto is installing two trash capture devices in the storm drain system as part of a program to meet regulatory requirements through a Trash Load Reduction Program specified by the State and a region-wide permit program. Because the State has provided substantial (but not full)funding for the devices,the project falls below the financial triggers requiring Council approval. However, staff is providing this informational staff report because of the importance of the new State requirements for trash reduction. Background In October 2009, the San Francisco Bay Regional Water Quality Control Board (Water Board) issued a new regional National Pollutant Discharge Elimination System (NPDES) storm water permit to the City of Palo Alto and 76 other Bay Area entities for discharge of municipal storm water to local creeks and San Francisco Bay. This Municipal Regional Permit (MRP) specifies programs and measures to be conducted by local agencies to minimize storm water pollution through the year 2014. One of the new areas of focus in the MRP is control of trash in local waterways. The MRP contains progressively stringent requirements for implementation of trash control measures over the life of the permit. The MRP requires permittees to develop and implement a Short-Term Trash Load Reduction Plan (Short-Term Plan) that will prevent or remove trash loads from municipal storm drain systems in order to attain a 40% reduction in trash loads by July 23, 2012 Page 2 of 6 (ID # 2919) July 1, 2014 (measured from a 2009 baseline trash loading rate). Furthermore, the permittees are required to develop and begin implementation of a Long-Term Trash Load Reduction Plan to attain a 70% reduction in trash loads from their storm drain systems by 2017 and 100% by 2022. The trash load reduction plans are mandated to include implementation of a number of specified actions, such as a mandatory minimum level of trash capture from storm drains,periodic cleanup and abatement of a mandatory minimum number of designated trash hot spots in local creeks; and implementation of other appropriate control measures and best management practices. A summary of the trash load reduction requirements contained in the MRP is provided in Attachment A. Discussion Short-Term Trash Load Reduction Plan (Short-Term Plan) Bay Area municipalities worked cooperatively through their countywide storm water programs and the Bay Area Stormwater Management Agencies Association (BASMAA) to develop a uniform methodology for establishing baseline trash loading rates and a system of trash load reduction credits used to measure progress towards the required trash reduction goals. Palo Alto staff interacted with other Santa Clara County municipalities through the Santa Clara Valley Urban Runoff Pollution Prevention Program (SCVURPPP) on trash reduction strategies. Palo Alto and the other MRP permittees submitted their Short-Term Plans to the Water Board on February 1, 2012. Palo Alto’s Short-Term Plan includes an assortment of trash control measures that achieve a cumulative load reduction of 51% (Attachment B). The Short-Term Plans, and their underlying baseline trash loading rates and load reduction credits, are currently under review by Water Board staff and are likely subject to future change and refinement. Palo Alto was able to exceed the short-term 40% trash load reduction goal without having to implement many new measures and programs because the trash load reduction credit strategy devised by BASMAA on behalf of all Bay Area municipalities gave ample credit for early adoption of effective measures like enhanced street sweeping and plastic bag and expanded polystyrene product bans, which Palo Alto has already embraced. The most significant new control measure in Palo Alto’s Short-Term Plan is the installation of trash capture devices in the municipal storm drain system, which is described in greater detail below. The key elements of Palo Alto’s Short-Term Plan are summarized below: 1.Single-use Carryout Plastic Bag Ban (5.0% trash reduction credit) (existing July 23, 2012 Page 3 of 6 (ID # 2919) measure) Palo Alto has adopted an ordinance banning distribution of single-use carryout plastic bags at large supermarkets. 2.Polystyrene Foam Food Service Ware Ban (6.6% trash reduction credit) (existing measure) Palo Alto has adopted an ordinance banning distribution of polystyrene foam food service ware by all food vendors. 3.Public Education and Outreach Programs (4.9% trash reduction credit) (continuing measure) Palo Alto participates in regional advertising campaigns, outreach to youth, and media relations activities with a focused trash reduction message. 4.Activities to Reduce Trash from Uncovered Vehicle Loads (4.2% trash reduction credit) (continuing measure) Palo Alto ensures that its local trash hauler covers its refuse collection trucks, has a local ordinance and enforcement actions prohibiting uncovered vehicle loads on City streets, and is a partner in the Sunnyvale Materials Recovery and Transfer (SMaRT) Station, which requires drivers of vehicles with uncovered loads to purchase tarps to cover their loads. 5.Improved Trash Bin/Container Management (5.3% trash load reduction) (continuing measure) Palo Alto has ordinances and enforcement actions requiring residents and businesses to use and maintain appropriately-sized, covered trash containers and uses the Downtown Streets Team to hand-sweep the downtown business district. 6.Enhanced Street Sweeping (17.5% trash load reduction) (continuing measure) Palo Alto sweeps its streets more frequently than the baseline level of service identified for Bay Area communities (3 times per week in commercial districts [Baseline = weekly]; weekly in residential districts [Baseline = 2 times per month]). July 23, 2012 Page 4 of 6 (ID # 2919) 7.Installation of Full-Capture Treatment Devices (2.8% trash load reduction) (new measure) Palo Alto will be installing two large trash-capture devices along Park Boulevard to filter and capture trash from the municipal storm drain system (see detailed discussion below). 8.Installation of Litter Booms (0.6% trash reduction credit) (continuing measure) Palo Alto has installed a seasonal trash boom across Matadero Creek upstream of Highway 101 to capture trash before the creek flows into the Palo Alto Flood Basin in the Baylands. 9.Volunteer Creek Clean-Ups (4.7% trash reduction credit) (continuing measure) Palo Alto coordinates creek clean-ups by volunteers two times per year at two designated trash hot spots (Matadero Creek downstream of Highway 101 and Adobe Creek downstream of Highway 101). Trash Capture Devices The MRP requires the City to install devices in its municipal storm drain system that will capture and allow for the removal of all trash (down to five millimeters – the approximate diameter of a cigarette butt) from a tributary watershed area of at least 84 acres. Water Board staff reviewed available trash capture devices on the market and identified those that will meet the five millimeter capture standard. Approved devices include small screens or baskets installed at individual storm drain inlets or large underground vault-based devices installed inline along storm drain pipelines. Staff elected to use large vault-based devices because of the significantly lower maintenance costs incurred in servicing a smaller number of centralized devices. After reviewing the performance and cost of various devices, staff selected the Continuous Deflective Separator (CDS) unit manufactured by Contech Construction Products, Inc. In order to determine the optimum locations for trash capture devices in Palo Alto, staff reviewed the layout of the City’s storm drain system in search of locations with the following characteristics: ·Not connected to a storm water pump station (pump stations have trash racks that currently capture a significant portion of incoming trash and July 23, 2012 Page 5 of 6 (ID # 2919) debris). ·Tributary to commercially-zoned land use areas (where there is a higher likelihood of trash, as compared to residential areas). ·Easily accessible for maintenance using simple traffic control measures. ·Junction points where multiple storm drain pipelines converge. Using these criteria, staff decided to install trash capture devices at the two locations listed below: Park Boulevard at Ventura Avenue ·Tributary area of 40 acres (see map -Attachment C) ·Includes runoff from El Camino Real between Wilton Avenue and Los Robles Avenue ·Flows to Barron Creek 4040 Park Boulevard (east of Maclane Avenue) ·Tributary area of 127 acres (see map –Attachment D) ·Includes runoff from El Camino Real between Los Robles Avenue and Dinah’s Court ·Flows to Barron Creek In order to assist municipalities with permit compliance, the Association of Bay Area Governments (ABAG) secured a grant from the United States Environmental Protection Agency to provide funding for the purchase of trash capture devices and negotiated volume-based pricing for each of the approved devices. Palo Alto’s $58,227 share of the grant proceeds was supplemented with capital improvement program funds to pay for the project. The following is a summary of the costs and funding for the installation of the trash capture devices: Project Revenues Association of Bay Area Governments grant $ 58,227 City Capital Improvement Program $133,486 TOTAL $191,713 Project Expenditures Purchase of Two (2) Contech CDS Trash Capture Devices $ 98,998 Contract for Installation of Trash Capture Devices $ 92,715 July 23, 2012 Page 6 of 6 (ID # 2919) TOTAL $191,713 Installation of the two trash capture devices was advertised for competitive bids. A contract was awarded to Casey Construction, Inc, who submitted the low bid of $92,715. The devices will be installed during the month of July 2012. Installation of the two CDS trash capture devices will satisfy the MRP’s trash capture requirements through 2014. Public Works’Public Services Division staff will be responsible for removing the accumulated trash from the devices as part of their routine maintenance of the storm drain system and submitting reports to the Water Board on the amount of trash captured on an annual basis. Resource Impact The majority of the funds required for the puchase and installation of the two trash capture devices was available in Capital Improvement Program Project SD- 06101, Storm Drain System Replacement and Rehabilitation. The remaining project funds was provided through an Association of Bay Area Governments grant. Environmental Review This project is categorically exempt from the provisions of the California Environmental Quality Act (CEQA) under Section 15301 of the CEQA Guidelines as repair, maintenance and/or minor alteration of existing facilities and no further environmental review is necessary. Courtesy Copies Storm Drain Oversight Committee Attachments: ·A -Summary of MRP Trash Load Reduction Requirements (PDF) ·B -City of Palo Alto Short-Term Trash Load Reduction Plan (PDF) ·C -Tributary Area for Park Blvd/Ventura Ave Trash Capture Device (PDF) ·D -Tributary Area for 4040 Park Blvd Trash Capture Device (PDF) Prepared By:Joe Teresi, Senior Engineer Department Head:J. Michael Sartor, Director City Manager Approval: James Keene, City Manager 1 Attachment A Summary of Trash Load Reduction Requirements in the Municipal Regional Storm Water Discharge Permit (MRP) The Municipal Regional Storm Water Discharge Permit (MRP) contains a provision (Provision C.10) that mandates the implementation of measures that control trash entering local creeks from municipal storm drain systems. Provision C.10 requires Co-permittees to implement control measures and other actions to reduce trash loads to local urban creeks from the storm drainage system by 40 percent by 2014, which will set the course for additional load reductions in future years. To achieve this goal, Co-permittees are required to develop and implement a Short-Term Trash Loading Reduction Plan, which includes the installation and maintenance of trash full-capture devices, designed to treat a mandatory minimum level of land area, and implementation of other control measures and best management practices (i.e., trash reduction ordinances) to prevent or remove trash loads. To address longer-term goals of trash reduction, Co-permitees are also required to develop a Long-Term Trash Loading Reduction Plan near the end of the Permit term in preparation for the next Permit. Descriptions of specific Provision C.10 requirements that are being addressed at the Co- permittee and regional levels are provided below. Short-Term Trash Loading Reduction Plan Provision C.10.a.i of the MRP requires each Co-permittee to submit a Short-Term Trash Loading Reduction Plan (Short-Term Plan) to the Water Board by February 1, 2012. The Short- Term Plan must describe control measures and best management practices that are currently being implemented and the current level of implementation, and the planned new or enhanced control measures and best management practices that will be implemented to attain a 40 percent trash load reduction by July 1, 2014. Baseline Trash Loading Rates Provision C.10.a.ii of the MRP requires Co-permittees to develop and report on baseline trash loads from their municipal storm drain systems by February 1, 2012. Baseline trash loading estimates were developed on a regional basis via the Bay Area Storm Water Management Agencies Association’s (BASMAA) Baseline Trash Generation Rates Project. Approximately 160 storm drain inlets were installed with full-capture devices throughout the Bay Area to monitor trash loads during wet and dry periods. Monitoring sites were selected to test the effect that land use and other factors (e.g., economic profile and population density) may have on trash loading rates. Trash and other debris were removed and characterized an average of three times from each device over the course of one year. Trash generation rates derived through the BASMAA project are being used by Co-permittees to develop Co-permittee-specific trash baseline loads. Trash Load Reduction Tracking Method Provision C.10.a.ii of the MRP requires Co-permittees to develop a method by which they will demonstrate progress towards the MRP trash load reduction goal (i.e., 40 percent by 2014). A preliminary Trash Load Reduction Tracking Method Technical Report was developed collectively by the Co-permittees and submitted to the Water Board on February 1, 2012 by BASMAA. The report describes the load reduction tracking method selected for each potential 2 control measure, and the process by which load reduction tracking will take place. Full Capture Treatment Devices Provision C.10.a.iii of the MRP requires each Co-permittee to treat runoff from an acreage equal to 30% of its wholesale-retail land use with full capture treatment devices. All devices meeting the full capture definition that are installed prior to July 1, 2014 can be applied towards this requirement. Trash Hot Spot Cleanup and Assessment Provision C.10.b of the MRP requires each Co-permittee to identify and select a required number of trash hot spots in creeks or shorelines within their jurisdictions that will be the focus of required annual trash assessments and cleanups. Provision C.10.b(ii) of the MRP requires Co-permittees to clean up trash hot spots to a level of “no visual impact” at least one time per year for the term of the permit (December 1, 2009 through November 30, 2014). Long-Term Trash Load Reduction Plan Provision C.10.c requires the Co-permittees to develop and submit a Long-Term Trash Load Reduction Plan by February 1, 2014. The Long-Term Plan must describe the control measures that are being implemented and what additional control measures will be implemented to achieve a 70% trash load reduction by July 1, 2017 and a 100% load reduction by July 1, 2022. Baseline Trash Load and Short‐Term Trash Load Reduction Plan Submitted by: City of Palo Alto 250 Hamilton Avenue Palo Alto, CA 94301 In compliance with Provisions C.10.a(i) and C.10.a(ii) of Order R2‐2009‐0074 February 1, 2012 ii Page Intentionally Left Blank City of Palo Alto iv TABLE OF CONTENTS CERTIFICATION STATEMENT .................................................................................................................... III TABLE OF CONTENTS......................................................................................................................................... IV LIST OF TABLES .................................................................................................................................................. V LIST FIGURES..................................................................................................................................................... VI ABBREVIATIONS............................................................................................................................................... VII PREFACE .............................................................................................................................................................8 1.0 INTRODUCTION .....................................................................................................................................1 BASELINE TRASH GENERATION RATES PROJECT....................................................................................................................1 TRASH LOAD REDUCTION TRACKING METHOD SUMMARY......................................................................................................2 SHORT‐TERM TRASH LOAD REDUCTION PLAN .....................................................................................................................2 2.0 BASELINE TRASH LOADING ESTIMATE ....................................................................................................4 PERMITTEE CHARACTERISTICS...........................................................................................................................................4 DEFAULT TRASH GENERATION RATES (REGIONAL APPROACH)................................................................................................5 JURISDICTIONAL AND EFFECTIVE LOADING AREAS.................................................................................................................5 PERMITTEE‐SPECIFIC BASELINE TRASH LOADING RATES.........................................................................................................6 Baseline Street Sweeping .....................................................................................................................................6 Baseline Storm Drain Inlet Maintenance..............................................................................................................7 Baseline Stormwater Pump Station Maintenance ...............................................................................................7 BASELINE TRASH LOADING ESTIMATE.................................................................................................................................7 3.0 LOAD REDUCTION CALCULATION PROCESS ..........................................................................................10 STEP #1: EXISTING ENHANCED STREET SWEEPING..............................................................................................................10 STEP #2: TRASH GENERATION REDUCTION CONTROL MEASURES..........................................................................................11 STEP #3: ON‐LAND INTERCEPTION CONTROL MEASURES.....................................................................................................11 STEP #4: CONTROL MEASURES THAT INTERCEPT TRASH IN THE MS4.....................................................................................12 STEP #5: CONTROL MEASURES THAT INTERCEPT TRASH IN WATERWAYS................................................................................12 STEP #6: COMPARISON TO BASELINE TRASH LOAD.............................................................................................................12 4.0 ENHANCED TRASH CONTROL MEASURES .............................................................................................13 CR‐1: SINGLE‐USE CARRYOUT PLASTIC BAG POLICY ...........................................................................................................14 Baseline Level of Implementation ......................................................................................................................14 Enhanced Level of Implementation....................................................................................................................14 Reduction from Implementing Control Measure................................................................................................15 CR‐2: POLYSTYRENE FOAM FOOD SERVICE WARE POLICY ...................................................................................................16 Baseline Level of Implementation ......................................................................................................................16 Enhanced Level of Implementation....................................................................................................................16 Percent Reduction from Enhancements.............................................................................................................17 CR‐3: PUBLIC EDUCATION AND OUTREACH PROGRAMS ......................................................................................................18 Baseline Level of Implementation ......................................................................................................................18 Enhanced Level of Implementation....................................................................................................................18 Baseline Level of Implementation ......................................................................................................................21 Enhanced Level of Implementation....................................................................................................................21 Percent Reduction from Enhancements.............................................................................................................22 CR‐6: IMPROVED TRASH BIN/CONTAINER MANAGEMENT...................................................................................................23 Baseline Level of Implementation ......................................................................................................................23 Enhanced Level of Implementation....................................................................................................................23 Baseline Trash Load and Short‐Term Trash Load Reduction Plan v Percent Reduction from Enhancements.............................................................................................................24 QF‐2: ENHANCED STREET SWEEPING ..............................................................................................................................25 Baseline Level of Implementation ......................................................................................................................25 Enhanced Level of Implementation....................................................................................................................25 Percent Reduction from Enhancements.............................................................................................................26 QF‐3: PARTIAL‐CAPTURE TREATMENT DEVICES.................................................................................................................30 Baseline Level of Implementation ......................................................................................................................30 Enhanced Level of Implementation....................................................................................................................30 Percent Reduction from Enhancements.............................................................................................................31 QF‐5: FULL‐CAPTURE TREATMENT DEVICES .....................................................................................................................33 Baseline Level of Implementation ......................................................................................................................33 Enhanced Level of Implementation....................................................................................................................33 Percent Reduction from Enhancements.............................................................................................................33 QF‐6: CREEK/CHANNEL/SHORELINE CLEANUPS ................................................................................................................35 Baseline Level of Implementation ......................................................................................................................35 Enhanced Level of Implementation....................................................................................................................35 Percent Reduction from Enhancements.............................................................................................................35 5.0 SUMMARY OF TRASH CONTROL MEASURE ENHANCEMENTS................................................................36 5.1 ANNUAL REPORTING AND PROGRESS TOWARDS TRASH LOAD REDUCTION GOAL(S)........................................................38 5.2 CONSIDERATIONS OF UNCERTAINTIES.....................................................................................................................38 6.0 IMPLEMENTATION SCHEDULE..............................................................................................................39 7.0 REFERENCES ........................................................................................................................................41 LIST OF TABLES Table 1.1: Trash Control Measures for which Load Reduction Quantification Credits or Formulas Were Developed to Track Progress towards Trash Load Reduction Goals Table 2‐1: Regional Default Annual Trash Generation Rates by Land Use Category Table 2‐2: Jurisdictional Areas and Effective Loading Areas in the City of Palo Alto by Land Use Classes Identified by ABAG (2005) Table 2 3: Preliminary Trash Baseline Load for the City of Palo Alto Table 4.1: Trash Control Measures that will be implemented by the City of Palo Alto to reach the 40% Trash Load Reduction Table QF‐2‐1: Planned Enhanced Street Sweeping Program in the City of Palo Alto Table QF‐3‐1: Partial Capture Treatment Devices Installed or Planned to be installed within the City of Palo Alto Prior to July 1, 2014 Table QF‐5‐1: Trash Full‐Capture Treatment Devices within the Jurisdictional Boundaries of the City of Palo Alto that are planned for installation by July 1, 2014 Table 5‐1: Planned Enhanced Trash Control Measure Implementation within the Jurisdictional Boundaries of the City of Palo Alto and Associated Trash Loads Reduced Table 6‐1: Preliminary Implementation Schedule for Enhanced Trash Control Measures in the City of Palo Alto City of Palo Alto vi LIST FIGURES Figure 2 1: Estimated Trash Baseline Loading Rates for Geographical Areas in the City of Palo Alto Figure QF‐2‐1: Planned Enhanced Street Sweeping Program in the City of Palo Alto Baseline Trash Load and Short‐Term Trash Load Reduction Plan vii ABBREVIATIONS BASMAA Bay Area Stormwater Management Agencies Association BID Business Improvement District CalRecycle California Department of Resources Recycling and Recovery Caltrans California Department of Transportation CASQA California Stormwater Quality Association CDS Continuous Deflection Separator CEQA California Environmental Quality Act CY Cubic Yards EIR Environmental Impact Report EPA Environmental Protection Agency GIS Geographic Information System MRP Municipal Regional Stormwater NPDES Permit MS4 Municipal Separate Storm Sewer System NGO Non‐Governmental Organization NPDES National Pollutant Discharge Elimination System Q Flow SFRWQCB San Francisco Regional Water Quality Control Board SWRCB State Water Resource Control Board TMDL Total Maximum Daily Load USEPA United States Environmental Protection Agency Water Board San Francisco Regional Water Quality Control Board WDR Waste Discharge Requirements City of Palo Alto viii PREFACE This Baseline Trash Load and Short‐Term Trash Load Reduction Plan (Plan) is submitted in compliance with provision C.10.a(i) and C.10.a(ii)of the Municipal Regional Stormwater NPDES Permit (MRP) for Phase I communities in the San Francisco Bay (Order R2‐2009‐0074). This Plan was developed using a regionally consistent format developed by the Bay Area Stormwater Management Agencies Association (BASMAA). Based on new information that becomes available during the implementation of this Short‐ Term Plan (e.g., revisions to baseline loading estimates or load reduction credits of quantification formulas), the City of Palo Alto may chose to amend or revise this Plan. If revisions or amendments are necessary, a revised Short‐Term Plan will be submitted to the Water Board via the City of Palo Alto’s annual reporting process. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 1 1.0 INTRODUCTION The Municipal Regional Stormwater NPDES Permit for Phase I communities in the San Francisco Bay (Order R2‐2009‐0074), also known as the Municipal Regional Permit (MRP), became effective on December 1, 2009. The MRP applies to 76 large, medium and small municipalities (cities, towns and counties) and flood control agencies in the San Francisco Bay Region, collectively referred to as Permittees. Provision C.10 of the MRP (Trash Load Reduction) requires Permittees to reduce trash from their Municipal Separate Storm Sewer Systems (MS4s) by 40 percent before July 1, 2014. Required submittals to the San Francisco Bay Regional Water Quality Control Board (Water Board) by February 1, 2012 under MRP provision C.10.a (Short‐Term Trash Loading Reduction Plan) include: 1. (a) Baseline trash load estimate, and (b) description of the methodology used to determine the load level. 2. A description of the Trash Load Reduction Tracking Method that will be used to account for trash load reduction actions and to demonstrate progress and attainment of trash load reduction levels. 3. A Short‐Term Trash Loading Reduction Plan that describes control measures and best management practices that will be implemented to attain a 40 percent trash load reduction from its MS4 by July 1, 2014; This Short‐Term Trash Load Reduction Plan (Short‐Term Plan) is submitted by the City of Palo Alto in compliance with the portions of MRP provision C.10.a.i listed as 1a and 3 above. In compliance with 1b, BASMAA submitted a progress report on behalf of Permittees that briefly describes the methodologies used to develop trash baseline loads (BASMAA 2011a). These methods are more fully described in BASMAA (2011b, 2011c). Lastly, the Trash Load Reduction Tracking Method Technical Report (BASMAA 2012a) was submitted by BASMAA on behalf of Permittees in compliance with submittal 2 described above. The Baseline Loading Rates and Tracking Method projects are briefly described below. Baseline Trash Generation Rates Project Through approval of a BASMAA regional project, Permittees agreed to work collaboratively to develop a regionally consistent method to establish baseline trash loads from their MS4s. The project, also known as the BASMAA Baseline Trash Generation Rates Project assists Permittees in establishing a baseline to demonstrate progress towards MRP trash load reduction goals (i.e., 40 percent). The intent of the project was to provide a scientifically‐sound method for developing (default) baseline trash generation rates that can be adjusted, based on Permittee/site specific conditions; and used to develop baseline loading rates and loads. Baseline loads form the reference point for comparing trash load reductions achieved through control measure implementation. Baseline trash loading rates are quantified on a volume per unit area basis and based on factors that significantly affect trash generation (e.g., land use, population density, and economic profile). The method used to the establish baseline trash loads for each Permittee builds off “lessons learned” from previous trash loading studies conducted in urban areas (Allison and Chiew 1995; Allison et al. 1998; Armitage et al. 1998; Armitage and Rooseboom 2000; Lippner et al. 2001; Armitage 2003; Kim et al. 2004; County of Los Angeles 2002, 2004a, 2004b; Armitage 2007). The method is based off a conceptual model developed as an outgrowth of these studies (BASMAA 2011b). Baseline trash loading rates were developed through the quantification and characterization of trash captured in Water Board recognized City of Palo Alto 2 full‐capture treatment devices installed in the San Francisco Bay area. Methods used to develop trash baseline loading rates are more fully described in BASMAA (2011b, 2011c, and 2012). Trash Load Reduction Tracking Method Summary The trash load reduction tracking method, described in the Trash Load Reduction Tracking Method Technical Report, assists Permittees in demonstrating progress towards reaching trash load reduction goals defined in the MRP (e.g., 40 percent). The tracking method is based on information gained through an extensive literature review and Permittee experiences in implementing stormwater control measures in the San Francisco Bay Area. The literature review was conducted to evaluate quantification methods used by other agencies to assess control measure effectiveness or progress towards quantitative goals. Results are documented in the Trash Load Reduction Tracking Method: Technical Memorandum # 1 – Literature Review (BASMAA 2011d). Methods attributable to specific trash control measures fall into two categories: 1) trash load reduction quantification formulas; and 2) load reduction credits (BASMAA 2012a). Quantification formulas were developed for those trash control measures that were deemed feasible and practical to quantify load reductions at this time. Load reduction credits were developed for all other control measures included in the methodology development. Both categories of methods assume that as new or enhanced trash control measures are implemented by Permittees, a commensurate trash load reduction will occur. Progress towards load reduction goals will be demonstrated through comparisons to established trash baseline load estimates developed through the BASMAA Baseline Generation Rates Project. Short‐Term Trash Load Reduction Plan The purpose of this Short‐Term Plan is to describe the current level of implementation of control measures and best management practices, and identify the type and extent to which new or enhanced control measures and best management practices will be implemented to attain a 40 percent trash load reduction from their MS4 by July 1, 2014. The Short‐Term Plan was developed using a template created by BASMAA through a regional project. New and enhanced trash control measures (i.e., Best Management Practices) that Permittees may implement to demonstrate trash load reduction goals are included in Table 1.1. This list was developed collaboratively through the BASMAA Trash Committee, which included participation from Permittee, stormwater program, Water Board and non‐governmental organization (NGO) staff. The list of control measures is based on: 1) the potential for Permittees to implement; 2) the availability of information required to populate formulas and develop credits; and 3) the expected benefit of implementation. Load reductions associated with each control measure are demonstrated either through a quantification formula (QF) or credits (CR) described in the Trash Load Reduction Tracking Method Technical Report (BASMAA 2012a). In efforts to reduce trash discharged from MS4s, Permittees may choose to implement control measures that are not included in Table 1.1 or described more fully in BASMAA (2011e). If a Permittee chooses to do so, methods specific to calculating trash load reductions for that control measure would need to be developed. Additionally, at that point, consideration should be given to updating this Short‐Term Plan. Additionally, based on new information that becomes available during the implementation of this Short‐ Term Plan (e.g., revisions to baseline loading estimates or load reduction credits of quantification formulas), the City of Palo Alto may amend or revise this Plan. If revisions or amendments are necessary, Baseline Trash Load and Short‐Term Trash Load Reduction Plan 3 a revised Short‐Term Plan will be submitted to the Water Board via the City of Palo Alto’s annual reporting process. Table 1.1. Trash control measures for which load reduction quantification credits or formulas were developed to track progress towards trash load reduction goals. Load Reduction Credits Single-use Carryout Plastic Bag Ordinances Polystyrene Foam Food Service Ware Ordinances Public Education and Outreach Programs Activities to Reduce Trash from Uncovered Loads Anti-Littering and Illegal Dumping Enforcement Activities Improved Trash Bin/Container Management Activities Single-Use Food and Beverage Ware Ordinances Quantification Formulas On-land Trash Pickup (Volunteer and/or Municipal) Enhanced Street Sweeping Partial-Capture Treatment Devices Enhanced Storm Drain Inlet Maintenance Full-Capture Treatment Devices Creek/Channel/Shoreline Cleanups (Volunteer and/or Municipal) This Short‐Term Plan is organized into the following sections: • Introduction; • Baseline Trash Loading Estimate; • Load Reduction Calculation Process • Enhanced Trash Control Measures • Summary of Trash Control Measure Enhancements • Implementation Schedule; and • References City of Palo Alto 4 2.0 BASELINE TRASH LOADING ESTIMATE Note: Tables and information presented in this section are subject to change based on the results of a third monitoring event of the BASMAA Baseline Trash Generation Rates Project. Therefore, this section of the Short‐Term Plan may be updated with revised trash generation rates, baseline loading rates, and baseline loads. This section provides the estimated annual trash baseline load from the City of Palo Alto’s Municipal Separate Storm Sewer System (MS4). In compliance with Provision C.10.a.ii of the MRP, the City of Palo Alto worked collaboratively with other MRP Permittees through BASMAA to develop data and the process necessary to establish baseline trash loading estimate from our MS4. The collaborative project was managed through the BASMAA Trash Committee and included a series of steps described in BASMAA (2012) and listed below. The approach was intended to be cost‐effective and consistent, but still provide an adequate level of confidence in trash loads from MS4s, while acknowledging that uncertainty in trash loads still exists. The approach entailed the following steps: 1. Conduct literature review; 2. Develop conceptual model; 3. Develop and implement sampling and analysis plan; 4. Test conceptual model; 5. Develop and apply default trash generation rates to Permittee effective loading areas; 6. Adjust default trash generation rates based on baseline levels of control measure implementation by the Permittee to develop trash baseline loading rates; and, 7. Calculate Permittee‐specific annual trash baseline load. Through the collaborative BASMAA project, default baseline trash generation rates (volume per area) were developed for a finite set of categories, based on factors that significantly affect trash loads (e.g., land use). These trash generation rates were then applied to effective loading areas in applicable jurisdictional areas within the City of Palo Alto. Trash generation rates were then adjusted based on baseline street sweeping, storm drain inlet maintenance, and stormwater pump station maintenance conducted in each applicable area. The sum of the trash loads (i.e., rate multiplied by area) from each effective loading area represents the City of Palo Alto’s baseline trash load from its MS4. A full description of the methods by which trash baseline loads were developed is included in BASMAA (2012a) and is summarized below. Permittee Characteristics Incorporated in 1894, the City of Palo Alto is located in Santa Clara County, and has a jurisdictional area of 15,569 acres. According to the 2010 Census, it has a population of 64,403, with a population density of 2,497.5 people per square mile, and average household size of 2.41. Of the 64,403 who call the City of Palo Alto home, 23.4% are under the age of 18, 4.9% are between 18 and 24, 26.6% are between 25 and 44, 28.0% are between 45 and 64, and 17.1% are 65 or older. Companies such as Hewlett‐Packard, Vmware, Tesla Motors, Ning, IDEO, Palantire Technologies, and Facebook are located in the City of Palo Alto. The median household income was $119,046 in 20001. 1 From the 2000 Census. The median household income for the City of Palo Alto from the 2010 Census is not currently available. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 5 Default Trash Generation Rates (Regional Approach) A set of default trash generation rates was developed via the BASMAA regional collaborative project (BASMAA 2012b). Default generation rates were developed based on a comparison between trash characterization monitoring results, land uses, economic profiles, and other factors that were believed to possibly affect trash generation. Three trash characterization monitoring events were scheduled via the Trash Generation Rates Project. Due to the compliance timeline in the MRP, only two of three trash characterization monitoring events were used to develop trash generation rates described in BASMAA (2012a) and presented in this section. Following the completion of the third characterization event (Winter 2011/12), this section of the Short‐Term Plan may be updated to reflect the most up‐to‐date trash generation and loading rates available. Trash generation rates based on the results of two of the three characterization events are shown in Table 2‐1 for each trash loading category. Table 2‐1: Regional Default Annual Trash Generation Rates by Land Use Category. Land Use Category Generation Rates (Gallons/Acre) Retail and Wholesale 29.99 High Density Residential 17.04 K‐12 Schools 13.14 Commercial and Services/ Heavy, Light and Other Industrial 7.08 Urban Parks 2.14 Low Density Residential 1.25 Rural Residential 0.17 Jurisdictional and Effective Loading Areas Default trash baseline generation rates presented in Table 2‐1 were applied to effective loading areas with jurisdictional areas within the City of Palo Alto. The City of Palo Alto’s jurisdictional areas includes all urban land areas within the City of Palo Alto boundaries that are subject to the requirements in the MRP. Land use areas identified by a combination of the ABAG 2005 land use dataset and Permittee knowledge that were not included within the City’s jurisdictional areas include: • Federal and State of California Facilities and Roads (e.g., Interstates, State Highways, Military Bases, Prisons); • Roads Owned and Maintained by Santa Clara County; • Colleges and Universities (Private or Public); • Non‐urban Land Uses (e.g., agriculture, forest, rangeland, open space, wetlands, water); • Communication or Power Facilities (e.g., PG & E Substations); • Water and Wastewater Treatment Facilities; and • Other Transportation Facilities (e.g., airports, railroads, and maritime shipping ports). City of Palo Alto 6 Once the City of Palo Alto’s jurisdictional area was delineated, an effective trash loading area was developed by creating a 200‐foot buffer on each side of the streets within the City’s jurisdictional area. The purpose of the effective loading area is to eliminate land areas not directly contributing trash to the City’s MS4 (e.g., large backyards and rooftops). Both the jurisdictional and the effective loading areas for the City of Palo Alto are presented in Table 2‐2. Table 2‐2: Jurisdictional areas and effective loading areas in the City of Palo Alto by land use classes identified by ABAG (2005). Land Use Category Jurisdictional Area (Acres) Effective Loading Area (Acres) % of Effective Loading Area High Density Residential 701 652 11 Low Density Residential 4,004 3,502 62 Rural Residential 179 101 2 Commercial and Services/ Heavy, Light and Other Industrial 1,563 752 13 Retail and Wholesale 365 308 5 K‐12 Schools 230 102 2 Urban Parks 1,689 260 5 TOTAL 8,732 5,677 100% Permittee‐Specific Baseline Trash Loading Rates Regional default trash generation rates developed through the BASMAA regional collaborative project were applied to effective loading areas within the City of Palo Alto based on identified land uses. These generation rates were then adjusted based on the calculated effectiveness of baseline street sweeping, storm drain inlet maintenance and pump station maintenance implemented by the City. These adjustments were conducted in GIS due to the site specificity of baseline generation rates and baseline control measure implementation. The following sections describe the baseline level of implementation for these three control measures. A summary of trash baseline generation and loading rates for the City of Palo Alto are provided in Table 2‐3 and areas associated with these rates are illustrated in Figure 2‐1. Baseline Street Sweeping A "baseline" street sweeping program is defined as the sweeping frequency and parking enforcement implemented by the City of Palo Alto prior to effective date of the MRP. Baseline street sweeping differs from "enhanced" street sweeping, which includes increased parking enforcement and/or sweeping conducted at a frequency greater than baseline ceiling (i.e., once per week for retail land uses and twice per month for all other land uses). The baseline ceiling was created to not penalize implementers of enhanced street sweeping programs prior to the effective date of the MRP. For those Permittees that sweep less frequent than the baseline ceiling, their current sweeping frequency serves as their baseline. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 7 The City of Palo Alto's baseline street sweeping program includes sweeping streets in residential areas and arterial roads twice per month, and sweeping retail areas once per week. The City’s current street sweeping program includes sweeping residential areas and arterial roads once per week, and retail areas three times per week. Posting of parking enforcement signs for street sweeping is limited to a residential area north of downtown. Parking enforcement equivalent exists on many arterial roads throughout the City. The estimated trash load reduced via baseline street sweeping is presented in Table 2‐3. Baseline Storm Drain Inlet Maintenance Within the City of Palo Alto, storm drain inlets were cleaned at a baseline level of one time per year prior to the effective date of the MRP. Based on this baseline frequency and the effectiveness rating developed in BASMAA (2012b), the baseline storm drain maintenance program in the City of Palo Alto has an annual effectiveness rating of 5%. The estimated trash load reduced via baseline storm drain inlet maintenance is presented in Table 2‐3. Baseline Stormwater Pump Station Maintenance The City of Palo Alto owns and maintains eight stormwater pump stations. Of these stations, four have trash racks that capture trash and allow for removal during maintenance. For those pump stations with trash racks, the estimated volume of trash removed annually from each pump station prior to the effective date of the MRP is considered the baseline level of implementation. To determine the baseline volume of trash removed from pump stations, an effectiveness rating of 25% removal of the baseline trash load attributable to the area draining to the pump station is assumed. This effectiveness rating is based on methods developed in BASMAA (2012b). The estimated trash load reduced via baseline pump station maintenance is presented in Table 2‐3. Baseline Trash Loading Estimate The estimated baseline trash load from the City of Palo Alto was calculated as the sum of the loads from the City’s effective loading area, adjusted for baseline implementation of street sweeping, storm drain inlet maintenance, and pump station maintenance. The preliminary annual trash baseline load for the City of Palo Alto is presented in Table 2‐3. Preliminary baseline trash loading rates are presented in Figure 2‐1 to provide a geographical illustration of areas with estimated low, moderate, high and very high trash loading rates. City of Palo Alto 8 Table 2‐3: Preliminary annual trash baseline load for the City of Palo Alto. Category Annual Load (gallons) Preliminary Generation Trash Load 31,955 Load Removed via Baseline Street Sweeping 14,443 Load Removed via Baseline Storm Drain Inlet Maintenance 876 Load Removed via Baseline Stormwater Pump Station Maintenance 1,710 Preliminary Trash Baseline Load 14,926 Baseline Trash Load and Short‐Term Trash Load Reduction Plan 9 Figure 2‐1: Estimated trash baseline loading rates for geographical areas in the City of Palo Alto. City of Palo Alto 10 3.0 LOAD REDUCTION CALCULATION PROCESS Using the guiding principles and assumptions described BASMAA (2011e), a stepwise process for calculating trash load reductions was developed collaboratively through BASMAA. This process is fully described in Trash Load Reduction Tracking Method Technical Report (BASMAA 2012a) and is briefly summarized in this section. The process takes into at what point in the trash generation and transport process a trash control measure: 1) prevents trash generation, 2) intercepts trash in the environment prior to reaching a water body, or 3) removes trash that has reached a water body. In doing so, it avoids double‐counting of trash load reductions associated with specific control measures. To demonstrate trash load reductions, baseline trash loading rates will be adjusted using the following process: Step #1: Existing Enhanced Street Sweeping Step #2: Trash Generation Reduction Step #3: On‐land Interception Step #4: Trash Interception in the Stormwater Conveyance System Step #5: Trash Interception in Waterways Step #6: Comparison to Baseline Trash Load Reductions calculated in Steps 2 and 5 are assumed to be implemented at a constant rate on an “area‐ wide” basis. For example, if a new region‐wide public education strategy is implemented within the San Francisco Bay area, all Permittees can apply load reduction credits associated with this control measure. In contrast, Steps 1, 3 and 4 are “area‐specific” reductions that only apply to specific areas within a Permittee’s jurisdiction. Area‐specific control measures include full‐capture treatment devices and enhanced street sweeping. Area‐specific reductions may require the use of a Geographic Information System (GIS) to calculate. Reductions are generally applied in the sequence as described below, although some reductions may be applied “in‐parallel” and calculated during the same sub‐step in the process. Step #1: Existing Enhanced Street Sweeping Trash load reductions due to existing enhanced street sweeping implemented prior to the effective date of the MRP and conducted at levels above baseline levels are not incorporated into each Permittee’s trash baseline load. Therefore, load reductions associated with existing enhanced are accounted for first in the trash load reduction calculation process. Existing enhanced street sweeping includes street sweeping conducted at a frequency greater than 1x/week for streets within retail land use areas or greater than 2x/month for streets in all other land use areas. The result of adjustments made to trash baseline loads due to the implementation of existing enhanced street sweeping is a set of current baseline loading rates and a current baseline load. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 11 Step #2: Trash Generation Reduction Control Measures Trash generation reduction control measures prevent or greatly reduce the likelihood of trash from being deposited onto the urban landscape. They include the following area‐wide control measures: CR‐1: Single‐Use Carryout Plastic Bag Ordinances CR‐2: Polystyrene Foam Food Service Ware Ordinances CR‐3: Public Education and Outreach Programs CR‐4: Reduction of trash from uncovered loads CR‐5: Anti‐Littering and Illegal Dumping Enforcement CR‐6: Improved Trash Bin/Container Management CR‐7: Single‐Use Food and Beverage Ware Ordinances Load reductions associated with trash generation reduction control measures are applied on an area‐ wide basis.2 Therefore, reductions in current baseline loading rates are adjusted uniformly based on the implementation of the control measure and the associated credit claimed. Baseline loading rate adjustments for all generation reduction controls measures implemented may be applied in‐parallel, but should be applied prior to calculating on‐land interception measures discussed in Step #3. The result of adjustments to trash baseline loading rates due to the implementation of these enhanced control measures will be a set of street loading rates. The street load is the volume of trash estimated to enter the environment and available for transport to the MS4 if not intercepted via on‐land control measures described in Step #3 Step #3: On‐land Interception Control Measures Once trash enters the environment, it may be intercepted and removed through the following control measures prior to reaching the stormwater conveyance system: QF‐1: On‐land Trash Cleanups (Volunteer and/or Municipal) (Area‐wide) QF‐2: Enhanced Street Sweeping (Area‐specific) Since on‐land trash cleanups can affect the amount of trash available to street sweepers, load reductions associated with their implementation will be quantified first, followed by street sweeping enhancements. On‐land trash cleanups will be applied as an area‐wide reduction and all effective loading rates will be adjusted equally. Enhanced street sweeping, however, is an area‐specific control measure and only those effective loading rates associated with areas receiving enhancements will be adjusted. Due to the spatial nature of enhanced street sweeping, GIS may be needed to conduct this step. The result of adjustments to effective loading rates due to the implementation of these enhanced control measures will be a set of conveyance system loading rates. The conveyance load is the volume of trash estimated to enter the stormwater conveyance system (e.g., storm drains). 2 The only exception to this statement are load reductions associated with the establishment of Business Improvement Districts (BIDs) or equivalent, which are specific to geographic areas and considered “area‐specific”. City of Palo Alto 12 Step #4: Control Measures that Intercept Trash in the MS4 Control measures that intercept trash in the stormwater conveyance system are area‐specific. Therefore, they only apply to land areas and associated trash loads reduced. Conveyance system loading rates developed as a result of Step #3 should be adjusted in‐parallel for the following control measures: QF‐3a: Partial‐capture Treatment Device: Curb Inlet Screens (Area‐specific) QF‐3b: Partial‐capture Treatment Device: Stormwater Pump Station Trash Racks Enhancements (Area‐specific) QF‐4: Enhanced Storm Drain Inlet Maintenance (Area‐specific) QF‐5: Full‐Capture Treatment Devices (Area‐specific) Load reductions for these control measures are calculated in‐parallel because they are applied to independent geographical areas. Reductions from all control measures described in this step are area‐specific and may require the use of GIS to calculate a set of waterway loading rates. Once waterway loading rates have been determined, a waterway load will be developed and used as a starting point for calculating load reductions associated with trash interception in waterways discussed in Step #5. Step #5: Control Measures that Intercept Trash in Waterways The load of trash that passes through the stormwater conveyance system without being intercepted may still be removed through interception in waterways. There are two control measures associated with interception in waterways: QF‐3c: Partial‐capture Treatment Device: Litter Booms/Curtains (Area‐wide) QF‐7: Creek/Channel/Shoreline Cleanups (Volunteer and/or Municipal) (Area‐wide) As these control measures are implemented, load reduction estimates can be calculated in‐parallel for these two measures. Step #6: Comparison to Baseline Trash Load Applying the five steps described in the processes above will provide an estimated trash load (volume) remaining after trash control measures are implemented. As depicted in the following equation, the relative percent difference between the baseline load and the load remaining after control measures are implemented is the percent reduction that will be used to assess progress towards MRP trash load reduction goals. •100 Baseline Load – Remaining Load Baseline Load = % Reduction Baseline Trash Load and Short‐Term Trash Load Reduction Plan 13 4.0 ENHANCED TRASH CONTROL MEASURES This section describes the new or enhanced trash control measures planned for implementation by the City of Palo Alto. The enhanced control measures described are designed to reach a 40% reduction by July 1, 2014. New and enhanced control measures that will be implemented by the City of Palo Alto include those listed in Table 4.1. Table 4.1. Trash control measures that will be implemented by the City of Palo Alto to reach the 40% trash load reduction. Control Measure Single-use Carryout Plastic Bag Ordinances Polystyrene Foam Food Service Ware Ordinances Public Education and Outreach Programs Activities to Reduce Trash from Uncovered Loads Improved Trash Bin/Container Management (Municipally or Privately-Controlled) Enhanced Street Sweeping Partial-Capture Treatment Devices Full-Capture Treatment Devices Creek/Channel/Shoreline Cleanups (Volunteer and/or Municipal) City of Palo Alto 14 CR‐1: Single‐use Carryout Plastic Bag Policy Single‐use plastic carryout bags have been found to contribute substantially to the litter stream and to have adverse effects on marine wildlife (United Nations 2009, CIWMB 2007, County of Los Angeles 2007). The prevalence of litter from plastic bags in the urban environment also compromises the efficiency of systems designed to channel storm water runoff. Furthermore, plastic bag litter leads to increased clean‐up costs for the Permittees and other public agencies. Based on recent experiences of municipalities throughout the State, the process Permittees must go through to enact a single‐use carryout plastic bag policy/ordinance is difficult due to intense scrutiny and opposition from not only public interest groups and lobbyists, but also merchants and community members. In most cases, most opposition groups are pressing for the development of Environmental Impact Reports (EIRs) in accordance with the California Environmental Quality Act (CEQA). Baseline Level of Implementation Prior to adoption of the MRP, Permittees within the Bay area have enacted policies or ordinances on Single‐use Carryout Plastic Bags. To avoid penalizing these early implementers, an applicable control measure implemented by a Permittee prior to the effective date of the MRP will be credited equally to a control measure implemented after the effective date. Therefore, the baseline level of implementation is not applicable for this control measure. Enhanced Level of Implementation The City of Palo Alto has adopted an ordinance (Palo Alto Municipal Code Chapter 5.35) prohibiting the distribution of single‐use carryout plastic bags at large supermarkets (those with gross annual sales of $2 million or more). The ordinance provides that supermarkets may provide only reusable bags or recyclable paper bags to their customers. The ordinance also strongly encourages supermarkets to educate their staff to promote reusable bags as the best option for checkout bags and to post signs encouraging customers to use reusable bags. The ordinance became effective on September 18, 2009. City of Palo Alto staff members promote the use of reusable bags by giving out free bags and other promotional items (e.g. stickers and magnets reminding folks to bring their reusable bags to the store) prior to and during the initial days of the bag ban and on an ongoing basis at public outreach events, participation in the regional Bring Your Own Bag (BYOB) advertising campaign, and by assisting regulated stores with public outreach through use of in‐store promotional materials (e.g. signs, reusable bag displays, etc.). City of Palo Alto staff members have verified through periodic site visits that 100% of regulated supermarkets are in full compliance with the provisions of the ordinance. The total percent trash reduced from MS4s as a result of implementing a single‐use carryout plastic bag ordinance will be reported in the Annual Report submitted each September to the Water Board. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 15 Reduction from Implementing Control Measure The City of Palo Alto will receive a 6 (six) percent3 reduction credit for implementing specific enhanced control measures described in Enhanced Level of Implementation section above. The 6 (six) percent reduction credit will be applied to the City of Palo Alto’s baseline trash load. This percent reduction credit is consistent with methods presented in the BASMAA (2011e). A summary of all load reductions anticipated through the implementation of this plan are included in Section 5.0. 3 The actual trash load reduction realized for the City of Palo Alto’s Single‐use Carryout Plastic Bag Policy is 5.0 percent due to the effects of the trash load reduction derived from the City’s existing enhanced street sweeping program. City of Palo Alto 16 CR‐2: Polystyrene Foam Food Service Ware Policy Polystyrene foam is used as food ware in the food service industry. According to the USEPA, floatable debris in waterways, such as products made of polystyrene, is persistent in the environment and has physical properties that can have serious impacts on human health, wildlife, the aquatic environment and the economy (USEPA 2002). Due to its properties, polystyrene foam used as food ware is typically not recycled. Since 1990, over 100 government agencies within the United States, including over twenty within the Bay area have enacted full or partial bans on polystyrene foam food service ware. Baseline Level of Implementation Prior to adoption of the MRP, over twenty agencies within the Bay area enacted full or partial bans on polystyrene foam food service ware. To avoid penalizing these early implementers, an applicable control measure implemented by a Permittee prior to the effective date of the MRP will be credited equally to a control measure implemented after the effective date. Therefore, the baseline level of implementation is not applicable for this control measure. Enhanced Level of Implementation The City of Palo Alto has adopted an ordinance (Palo Alto Municipal Code Chapter 5.30) banning food vendors from providing prepared food in disposable food service containers made from expanded polystyrene or non‐recyclable plastic. Food vendors are defined as any establishments which provide prepared and ready‐to‐consume food or beverages for public consumption, including but not limited to any store, supermarket, delicatessen, restaurant, retail food vendor, sales outlet, shop, cafeteria, catering truck or vehicle, sidewalk or other outdoor vendor, or caterer. The ordinance also prohibits all city facilities, city‐managed concessions, city‐sponsored events, and city‐permitted events from using disposable food service containers made from expanded polystyrene or non‐recyclable plastic. The ordinance became effective on April 22, 2010. Foods prepared or packaged outside the City of Palo Alto and coolers and ice chests that are intended for reuse are exempt from the ordinance, although purveyors of food prepared or packaged outside the City are encouraged to follow the provisions of the ordinance. City of Palo Alto staff members notified the affected facility owners in advance about the polystyrene ban by conducting two informational public meetings, notifying individual owners by mailed post card, placing paid advertisements in local newspapers, and site visits to a majority of food service facilities within the city. Through follow‐up site visits, food service facility source control inspections, and customer referrals, City of Palo Alto staff members have verified that approximately 95% of regulated food vendors are in full compliance with the provisions of the ordinance. The percent trash reduction from MS4s as a result of implementing a polystyrene foam food service ware ordinance will be reported in the Annual Report submitted each September. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 17 Percent Reduction from Enhancements The City of Palo Alto will receive an 8 (eight) percent4 reduction credit for implementing specific enhanced control measures described in Enhanced Level of Implementation section above. The 8 (eight) percent reduction credit will be applied to the City of Palo Alto’s baseline trash load. This percent reduction credit is consistent with methods presented in the BASMAA (2011e). A summary of all load reductions anticipated through the implementation of this plan are included in Section 5.0. 4 The actual trash load reduction realized for the City of Palo Alto’s Polystyrene Foam Food Service Ware Policy is 6.6 percent due to the effects of the trash load reduction derived from the City’s existing enhanced street sweeping program. City of Palo Alto 18 CR‐3: Public Education and Outreach Programs Permittees in the San Francisco Bay Area have implemented public education and outreach programs to inform residents about stormwater issues relating to pollutants of concern, watershed awareness and pollution prevention. Public education and outreach efforts include developing and distributing brochures and other print media; posting messages on websites and social networking media (Facebook, Twitter etc.), attending community outreach events, and conducting media advertising. In recent years, some municipal agencies have implemented anti‐ litter campaigns to increase public awareness about the impacts of litter on their communities and water quality; and to encourage the public to stop littering. Baseline Level of Implementation Beginning prior to the effective date of the MRP and continuing into the future, the City of Palo Alto (both as an individual entity and in conjunction with SCVURPPP and/or BASMAA) has implemented and will continue to implement a number of robust public education and outreach control measures related to source control and stormwater pollution prevention. Although these control measures included trash reduction messages, they are considered baseline measures because they are not focused specifically on trash reduction. Enhanced Level of Implementation The City of Palo Alto will implement the following public education and outreach control measures in conjunction with SCVURPPP and/or BASMAA prior to July 1, 2014. In addition, although not specifically listed below, the City of Palo Alto will increase emphasis on the trash reduction message in its own ongoing source control and pollution prevention programs. Litter Reduction Advertising Campaigns BASMAA Youth Outreach Campaign (Regional) Through participation and funding of the regional BASMAA Youth Outreach Campaign, the City of Palo Alto will implement an outreach campaign designed to reduce littering from the target audience in the Bay Area. The Youth Outreach Campaign was launched in September 2011 (post‐MRP effective date) and aims to increase the awareness of Bay Area Youth (ages 16‐24) on litter and stormwater pollution issues, and eventually change their littering behaviors. Combining the ideas of Community Based Social Marketing with traditional advertising, the Youth Campaign aims to engage youth to enable the peer‐to‐peer distribution of Campaign messages. The Campaign will at least run from FY 11‐12 through FY 13‐14. A brief description of the Campaign activities is provided below: o Raising Awareness: The Campaign will begin by raising awareness of the target audience on litter and stormwater pollution issues. Partnerships with youth commissions, high schools, and other youth focused organizations will be developed to reach the target audience. Messages targeted to youth will be created and distributed via paid advertising, email marketing, Campaign website and social networking sites (e.g,, Facebook and Twitter). o Engage the Youth ‐ The advertisements will encourage the audience to participate in the Youth Campaign by joining a Facebook page, entering a contest, taking an online quiz, etc., and providing their contact information. At the beginning of FY 12‐13, a video Baseline Trash Load and Short‐Term Trash Load Reduction Plan 19 contest will be launched to get Bay Area youth further involved in the Campaign. An online voting system will be used to select the winning entry. Media advertising will be conducted to promote the winning entry. o Change Behaviors: To move the audience along the behavior change continuum, the Campaign will use electronic platforms such as email marketing and social networking sites to encourage participants to engage in increasingly more difficult behavior changes, such as participating in a clean‐up, organizing a clean‐up, etc. o Maintain Engagement: The Campaign will continue to interact with the target audience through email marketing and social media websites. The Youth Campaign will include a pre and post campaign survey to evaluate the effectiveness of outreach. The pre‐campaign survey will be conducted in FY 11‐12 and the post campaign survey in FY 13‐14. Other evaluation mechanisms, such as website hits, number of youth engaged in the Campaign’s social networking website, etc. will also be used to evaluate its effectiveness in increasing awareness and changing behavior. Watershed Watch Campaign (Countywide) In addition to the BASMAA Campaign, the City of Palo Alto will continue to implement the countywide Watershed Watch Campaign through active participation and funding of the Santa Clara Valley Urban Runoff Pollution Prevention Program (SCVURPPP). This Campaign conducts media advertising that includes anti‐litter messages. Anti‐litter advertisements for television, print, transit and radio have been developed and are used each year and will continue in the future. A telephone survey is conducted every five years to measure the effectiveness of outreach and increase in awareness about liter and stormwater related messaging. Outreach to School‐age Children or Youth ZunZun (Countywide) Through participation and funding of the SCVURPPP countywide ZunZun Program, the City of Palo Alto plans to continue to implement litter reduction outreach to elementary school‐age children. Up to 50 ZunZun assemblies at elementary schools are conducted in the Santa Clara Valley each year. These bilingual musical assemblies educate elementary school students and their teachers on watersheds and urban runoff pollution prevention, including litter. ZunZun performances use physical comedy, audience participation and musical instruments to educate teachers and children. Handouts, including teacher and student activity sheets, are distributed following the assembly. The SCVURPPP Schools and Youth Education and Outreach Work Group provides a list of schools for ZunZun to contact. In addition to schools with high Hispanic populations, the list includes schools with high Asian/Pacific Islander populations. ZunZun assemblies are evaluated using postage‐paid evaluation cards that are distributed to all teachers present at the performances. Teachers mail the completed evaluation cards to SCVURPPP, and results are compiled by SCVURPPP staff. Based on the teacher feedback, changes are made to future assemblies and/or handouts. City of Palo Alto 20 Media Relations BASMAA Regional Media Relations Project (Regional) Through participation and funding of the BASMAA Regional Media Relations Project, the City of Palo Alto plans to continue to implement a media relations project partially designed to reduce littering from target audiences in the Bay Area. The goal of the BASMAA Media Relations Project is to generate media coverage that encourages individuals to adopt behavior changes to prevent water pollution, including littering. At least two press releases or PSAs focus on litter issues each year (e.g., creek clean‐up activities, preventing litter by using reusable containers, etc.). Percent Reduction from Enhancements The City of Palo Alto will receive a total of 6 (six) percent reduction credit for implementing specific enhanced control measures described in Enhanced Level of Implementation section above. This percent reduction is comprised of the following credits, consistent with the Load Reduction Tracking Method: • Litter Reduction Advertising Campaigns – 3% • Outreach to School‐age Children or Youth – 2% • Media Relations – 1% These 6 (six) percent5 reduction credits will be applied against the City of Palo Alto’s baseline trash load. This percent reduction credit is consistent with methods presented in the BASMAA (2011e). A summary of all load reductions anticipated through the implementation of this plan are included in Section 5.0. 5 The actual trash load reduction realized for the City of Palo Alto’s Public Education and Outreach Programs is 4.9 percent due to the effects of the trash load reduction derived from the City’s existing enhanced street sweeping program. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 21 CR‐4: Reduction of Trash from Uncovered Loads Although it is currently illegal to operate a vehicle that is improperly covered and which its’ contents escapes6, vehicles remain an important trash source to MS4s and local waterways. Specifically, vehicles that do not secure or cover their loads when transporting trash and debris have a high risk of contributing trash to MS4s. Land areas that generate trash from vehicles include roads, highways (on/off ramps, shoulders or median strips) and parking lots. To help address the dispersion of trash from unsecured or uncovered vehicles destined for landfills and transfer stations, Permittees may require municipally‐contracted trash haulers to cover or secure loads or work with municipal or private landfill and transfer station operators to educate waste haulers on securing loads and/or to enhance enforcement of existing regulations. Baseline Level of Implementation The baseline trash load described in Section 2.0, assumes that prior to adoption of the MRP the City of Palo Alto had not adopted control measures to reduce trash from vehicles with uncovered loads. Therefore, implementation of any of the control measures described in this section is considered to be enhanced implementation. Enhanced Level of Implementation The City of Palo Alto has implemented the following enhanced control measures to reduce trash from vehicles with uncovered loads: 1) The City’s contract with its municipal trash hauler (Green Waste) contains language requiring covered loads when transporting trash and debris to the transfer station. 2) Palo Alto Municipal Code Section 5.20.160 requires that all solid waste and recyclable materials hauled by any person over public streets in the city shall be securely tied and covered during hauling thereof so as to prevent leakage, spillage, or blowing and prohibits any person from allowing any solid waste or recyclable materials of any kind whatsoever to leak, spill, blow or drop from any vehicle on any public street within the city. This Code section is enforced by the Palo Alto Police Department. Violators are subject to an administrative penalty of $250. 3) The City of Palo Alto is a partner agency in the Sunnyvale Materials Recovery and Transfer (SMaRT) Station. The SMaRT Station has a tarp distribution program which requires vehicles that arrive with uncovered loads to purchase a tarp at a cost of $15.00. Each subsequent visit to the transfer station with an uncovered load will result in an additional fee for a tarp, prompting haulers to change their behavior by covering their loads in order to avoid additional tarp fees. 6 In accordance with the California Vehicle Code Sections 23114 and 23115, it is against the law to operate a vehicle on the highway which is improperly covered, constructed, or loaded so that any part of its contents or loads spills, drops, leaks, blows, or otherwise escapes from the vehicle. Exempted materials include hay and straw, clear water and feathers from live birds. Additionally, any vehicle transporting garbage, trash, or rubbish, used cans or bottles, waste papers, waste cardboard, etc. must have the load covered to prevent any part of the load from spilling on the highway (CVC 2011). Significant fines are possible for non‐compliance. City of Palo Alto 22 Percent Reduction from Enhancements The City of Palo Alto will receive a 5 (five) percent7 reduction credit for implementing specific enhanced control measures described in Description of Enhanced Level of Implementation section above. The 5 (five) percent reduction credit will be applied to the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. This percent reduction credit was obtained from the Trash Load Reduction Tracking Method Report (BASMAA 2012a) and is presented in the Trash Load Reduction Summary Table included in Section 5.0. 7 The actual trash load reduction realized for the City of Palo Alto’s Efforts to Reduce Trash from Uncovered Loads is 4.2 percent due to the effects of the trash load reduction derived from the City’s existing enhanced street sweeping program. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 23 CR‐6: Improved Trash Bin/Container Management Receptacles used to place/store trash or recyclables prior to collection by a public agency or private waste hauler reduce the potential for littering and trash loading to stormwater conveyance systems and receiving waters (City of Los Angeles 2004). For the purposes of assigning trash load reduction credits, receptacles fall into the following two categories: • Private Trash/Recycling Bins: A receptacle for placing trash or recyclables generated from a household, business, or other location that is serviced by a trash hauler. Bins are specifically‐designed, heavy‐duty plastic wheeled containers with hinged lids; or large multi‐yard metal or plastic containers rectangular in shape. • Public Area Trash Containers: A receptacle for placing incidental trash generated in public spaces that provides people with a convenient and appropriate place to dispose of trash. The design and size of public area trash containers vary widely, depending on their setting and use. The effectiveness of bins/containers and bins in reducing trash in the environment is likely dependent upon: the location and density of the receptacles, size of the bin/container in relationship to the size needed to service users, frequency of maintenance, and the ability of the bin/container to capture and contain the trash deposited. Baseline Level of Implementation The baseline trash load described in Section 2.0, assumes that the City of Palo Alto has not implemented enhanced trash bin/container management practices prior to effective date of the MRP. Therefore, implementation of any of the control measures described in this section is considered to be enhanced implementation. Enhanced Level of Implementation The City of Palo Alto has implemented the following improved trash bin/container management practices. The City of Palo Alto has a number of municipal ordinances regulating the maintenance of trash/recyclables containers by private residents and businesses. Palo Alto Municipal Code Sections 5.20.040, 5.20.080, 5.20.130, and 5.20.180 require residents and businesses to 1) utilize the trash/recyclables collection services of the City’s contracted hauler; 2) procure a sufficient number of containers to hold all solid waste created, produced or accumulated on the premises during a one‐week period, unless a more frequent collection schedule has been arranged; 3) maintain the trash/recyclables bins, boxes, and containers on their premises, and the area in which they are located, in a good, usable, clean and sanitary condition, and ensure that the lid or cover on the bin, box, or container is kept fully closed in a manner that prevents leakage, spillage and the escape of odors, and that no solid waste or recyclable materials are placed outside of the bin, box, or container; and 4) keep their premises in a clean and sanitary condition and not cause, suffer or permit any solid waste to accumulate in, on or about such premises for a period in excess of one calendar week, respectively. In order to ensure that trash/recyclables containers for residents and businesses are properly sized, the City’s trash hauler (Green Waste) works with customers during the establishment of new refuse collection services to recommend a suitably‐sized container based on the occupant load and use of the premises. Language in the City’s municipal trash hauling contract requires Green Waste staff to monitor and take corrective actions in response to missing/overflowing trash & City of Palo Alto 24 recyclables bins. Problem locations identified by collection vehicle drivers in the field are conveyed to Green Waste office staff for investigation and resolution. Green Waste staff work with customers to ensure that missing containers are replaced and/or that undersized containers are replaced with larger units in order to prevent future overflow conditions. The Palo Alto Downtown Business and Professional Association is a Business Improvement District (BID) serving the City of Palo Alto’s University Avenue Business District. The Association, funded through annual dues paid by businesses with the District, conducts various activities on behalf of its members that benefit the businesses within the BID. One of the Association’s most successful programs is the Downtown Streets Team. The Downtown Street Team is an innovative program that provides meaningful community‐based employment opportunities for local homeless individuals. The Association pays the Downtown Streets Team to hand sweep parking lots, garages, alleys, and plaza areas throughout the District on a daily basis. In addition, City of Palo Alto staff members use blowers to push trash and debris from District sidewalks and from behind parking stops and tree wells into the street on street sweeping days in order to allow the sweepers to pick up sidewalk‐based debris as well as street‐based debris. Lastly, the District sidewalks are mechanically swept and vacuumed by City staff on a daily basis using a small‐scale sweeper known as the Green Machine. Together these various elements comprise a highly effective trash reduction program in Palo Alto’s Downtown Business District. Percent Reduction from Enhancements The City of Palo Alto will receive a 6.5 percent8 reduction credit for implementing specific enhanced control measures described in Description of Enhanced Level of Implementation section above. The 6.5 percent reduction credit will be applied to the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. This percent reduction credit was obtained from the Trash Load Reduction Tracking Method Report (BASMAA 2012a) and is presented in the Trash Load Reduction Summary Table included in Section 5.0. 8 The actual trash load reduction realized for the City of Palo Alto’s Improved Trash Bin/Container Management Program is 5.3 percent due to the effects of the trash load reduction derived from the City’s existing enhanced street sweeping program. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 25 QF‐2: Enhanced Street Sweeping Street sweeping is conducted by most, if not all, Bay Area municipalities to remove trash and debris that collect in the gutters at the edge of streets. Parked cars and large storms that produce significant runoff can impact the effectiveness of street sweepers. However, increasing parking enforcement or more frequent street sweeping (as compared to the frequency of storm events) may increase the trash load reduced to MS4s. Permittees who choose to enhance street sweeping may do so to demonstrate trash load reductions to their MS4s and progress towards trash load reduction goals required by the MRP. Baseline Level of Implementation The baseline trash load described in Section 2.0 incorporates the trash load reductions due to baseline street sweeping. The City of Palo Alto’s baseline street sweeping program includes sweeping at a frequency of once time per week on average in retail areas and two times per month on average in all other areas, coupled with the parking enforcement program described below. The City of Palo Alto uses multiple parking prohibition strategies to enhance the effectiveness of street sweeping by ensuring that sweepers have clear access to the curb during sweeping operations. The first strategy is to perform street sweeping in selected districts at a specific time of day when parked cars are typically not present. The strategy of sweeping commercial districts during the early morning hours (prior to the operating hours for adjacent businesses) is particularly effective. Although not by specific intent, sweeping efficiency is nevertheless also enhanced along the multiple stretches of roadway within the City of Palo Alto where parking is prohibited 24/7 by signage for traffic management purposes. Lastly, the City of Palo Alto also has one street sweeping district in the Downtown North residential neighborhood where a “No Parking on Sweeping Day” program has been implemented due to an historical problem with a chronically high volume of parked cars. Streets in this neighborhood have been posted with permanent “No Parking on Sweeping Day” signs in order to improve street sweepers’ access to the curb. All of the streets in the City of Palo Alto where parked cars are not present during street sweeping due to the implementation of one of the strategies described above have been entered into a GIS database. Increased street sweeping efficiency rates have been applied to these streets when calculating the trash reduction achieved through the City’s baseline street sweeping program. Enhanced Level of Implementation Enhancements to street sweeping frequencies and parking enforcement (or equivalent measures) control measures will be used to calculate loads reduced from enhanced street sweeping, consistent with the trash load reduction tracking method (BASMAA 2012a). A list of planned enhancements is included in Table QF‐2‐1 and illustrated in Figure QF‐2‐1. Enhancements include: The City of Palo Alto sweeps its streets more frequently than the Baseline level. Actual sweeping frequencies are three times per week in retail (business district) areas and one time per week in all other areas. City of Palo Alto 26 Percent Reduction from Enhancements The total estimated annual volume of trash that will be reduced by July 1, 2014 as a result of enhanced street sweeping is 2,618 gallons. As described in Trash Load Reduction Summary Table included in Section 5.0, this volume is equal to approximately a 17.5 percent reduction in the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 27 Table QF‐2‐1. Planned enhanced street sweeping program in the City of Palo Alto. Baseline Enhanced Route ID Approximate Length Swept (curb miles) Frequency Parking Enforcement Frequency Parking Enforcement A1 15.14 2x per month “No Parking” on selected streets 1x per week Unchanged from Baseline A2 13.90 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A3 11.13 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A4 19.94 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A5 26.18 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A5 IND 10.70 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A6 15.17 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline A7 19.61 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B1 14.82 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B2 11.93 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B3 16.33 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline City of Palo Alto 28 Baseline Enhanced Route ID Approximate Length Swept (curb miles) Frequency Parking Enforcement Frequency Parking Enforcement B4 24.78 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B5A 18.40 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B5B 18.49 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B6 21.72 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B7 18.82 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B8 RES 3.80 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B8 IND 8.80 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline B9 3.03 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline BA 23.92 1x per week “No Parking” on selected streets 3x per week Unchanged From Baseline D1 18.68 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline D2 RES 7.60 2x per month “No Parking” on Sweeping Day Program 1x per week Unchanged From Baseline D2 IND 9.70 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline D3 20.39 2x per month “No Parking” on selected streets 1x per week Unchanged From Baseline Baseline Trash Load and Short‐Term Trash Load Reduction Plan 29 Figure QF‐2‐1: Planned enhanced street sweeping program in the City of Palo Alto. City of Palo Alto 30 QF‐3: Partial‐Capture Treatment Devices Partial‐capture devices are treatment devices that have not been approved as full‐capture by the San Francisco Bay Regional Water Quality Control Board, but capture trash at a known effectiveness value. Partial‐capture devices may be similar to full‐capture devices, but do not meet the full capture definition due to engineering challenges; or they may be completely different types of devices. Partial‐capture devices include curb inlet screens (e.g., automated retractable screens), litter booms/curtains and stormwater pump station track racks. Trash loads reduced via partial‐capture devices within a Permittee’s jurisdictional boundaries may be used to demonstrate attainment of trash load reduction goals. Baseline Level of Implementation Curb Inlet Screens and Litter Booms/Curtains Prior to effective date of the MRP, some Permittees within the Bay area have installed and maintained curb inlet screens and litter booms/curtains. To avoid penalizing these early implementers, the applicable control measure implemented by a Permittee prior to the effective date of the MRP will be credited equally to a control measure implemented after the effective date. Furthermore, the trash load removed via these devices installed prior to the MRP is not accounted for in baseline trash loads. Therefore, the baseline level of implementation is not applicable for this control measure, as devices installed prior to the effective date of the MRP and associated loads reduced will be grandfathered in as enhanced measures. Stormwater Pump Station Racks Similar to the devices described above, some Permittees within the Bay area have installed and maintained trash racks on their stormwater pump stations. Existing pump station trash racks are assumed to remove roughly 25% of the trash that enters the pump station (BASMAA 2012a). The baseline trash load removed via these devices is accounted for in baseline trash loads. Trash racks are installed at the following stormwater pump stations owned and maintained by the City of Palo Alto: Matadero Creek Stormwater Pump Station (Colorado Ave. near West Bayshore Rd.), Adobe Creek Storm Water Pump Station (East Meadow Drive near Fabian Way), Airport Storm Water Pump Station (Embarcadero Rd. at Palo Alto Airport), and San Francisquito Creek Stormwater Pump Station (East Bayshore Rd. at San Francisquito Creek). Enhanced Level of Implementation A total of one partial‐capture treatment device has been installed in the City of Palo Alto. Since June 2009, a litter boom has been deployed annually during the dry season across Matadero Creek upstream of West Bayshore Road. City staff worked cooperatively with the Santa Clara Valley Water District to obtain an encroachment permit allowing seasonal placement of the boom. In accordance with the permit, the boom must be removed each year prior to the start of the rainy season so as not to cause potential flow blockages during storm events. The boom floats on the surface of the water and has a suspended curtain that captures near‐surface debris. The amount of debris trapped by the boom is monitored periodically by City staff, and the debris is photographed, removed and measured on an as‐ needed basis. This partial‐capture device is included in Table QF‐3‐1 as an enhanced trash control measure. Calculation of loads reduced from this partial‐capture device will be consistent with the approach described in the Trash Load Reduction Tracking Method Report (BASMAA 2012a). Baseline Trash Load and Short‐Term Trash Load Reduction Plan 31 Percent Reduction from Enhancements The total estimated annual volume of trash that will be reduced by July 1, 2014 as a result of deploying the partial‐capture treatment device listed in Table QF‐3‐1 is 90 gallons. This volume is equal to approximately a 0.6 percent reduction in the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. Both values provided within this section are included in Trash Load Reduction Summary Table included in Section 5.0. City of Palo Alto 32 Table QF‐3‐1. Partial capture treatment devices installed or planned to be installed within the City of Palo Alto prior to July 1, 2014. Device ID Public or Private Device Name Location (Cross Streets) Installation Date/Anticipated Installation Date Total Area Treated (acres) Trash Load Reduced (gallons) 1 Public Matadero Creek litter boom Matadero Creek upstream of West Bayshore Road June 8, 2009 N/A 90 Baseline Trash Load and Short‐Term Trash Load Reduction Plan 33 QF‐5: Full‐Capture Treatment Devices As defined by the Municipal Regional Stormwater Permit (MRP), a full‐capture system or device is any single device or series of devices that traps all particles retained by a 5 mm mesh screen and has a design treatment capacity of not less than the peak flow rate (Q) resulting from a one‐year, one‐hour, storm in the sub‐drainage area. A list of the full‐capture systems and devices recognized by the San Francisco Bay Regional Water Quality Control Board (Water Board) is included in Trash Load Reduction Tracking Method Report (BASMAA 2012a). Trash loads reduced via publically or privately owned and operated devices within a Permittee’s jurisdictional area that have been recognized by the Water Board as full‐capture may be used to demonstrate attainment of trash load reduction goals. Baseline Level of Implementation Prior to adoption of the MRP, some Pemittees installed and maintained full capture devices. To avoid penalizing these early implementers, an applicable control measure implemented within a Permittee’s jurisdictional area prior to the effective date of the MRP will be credited equally to a control measure implemented after the effective date. Therefore, the baseline level of implementation is no trash full‐ capture devices have been installed. Enhanced Level of Implementation A total of two trash full‐capture treatment devices will be installed in the City of Palo Alto prior to July 1, 2014. A list of these full‐capture devices is included in Table QF‐5‐1. All devices listed within this table are enhanced trash control measures. Table QF‐5‐1 also includes the area treated and the calculated trash load reduced from each full‐capture treatment device. These calculations are consistent with the approach described in the Trash Load Reduction Tracking Method Report (BASMAA 2012a). Percent Reduction from Enhancements The total estimated annual volume of trash that will be reduced by July 1, 2014 as a result of implementing full capture devices is 414 gallons. This volume is equal to approximately a 2.8 percent reduction in the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. Both values provided within this section are included in Trash Load Reduction Summary Table included in Section 5.0. City of Palo Alto 34 Table QF‐5‐1. Trash full‐capture treatment devices within the jurisdictional boundaries of the City of Palo Alto that are planned for installation by July 1, 2014. Device ID Public or Private Device Name Location (Cross Streets) Installation Date/Anticipated Installation Date Total Area Treated (acres) Estimated Trash Load that will be Reduced 1 Public Contech CDS 3875 Park Boulevard (at Ventura Avenue) October 1, 2012 126.08 258 2 Public Contech CDS 4032 Park Boulevard (at Maclane Street) October 1, 2012 41.91 155 Baseline Trash Load and Short‐Term Trash Load Reduction Plan 35 QF‐6: Creek/Channel/Shoreline Cleanups Creek/channel/shoreline cleanups have been successful in removing large amounts of trash from San Francisco Bay area creeks and waterways; and increasing citizen's awareness of trash issues within their communities. Creek/channel/shoreline cleanups are conducted as single‐day events or throughout the year by volunteers and municipal agencies. Since volunteers and municipal agencies have the common goal of clean creeks and waterways, their efforts sometimes overlap. This is apparent with some municipal agencies using volunteers to help assess and clean designated trash hot spots during single‐ day volunteer events. Baseline Level of Implementation Trash reduced via creek/channel/shoreline cleanups was not accounted for in the City of Palo Alto’s baseline trash load described in Section 2.0. Therefore, implementation of any of the control measures described in this section is considered to be an enhancement and can be used to demonstrate progress towards load reduction goals. Enhanced Level of Implementation Prior to July 1, 2014, the City of Palo Alto will conduct the MRP‐required9 creek/channel/shoreline cleanups listed below. These cleanups will be conducted each year and the volume of trash removed will be tracked to demonstrate trash loads reduced. National River Clean‐Up Day (annually on the third Saturday in May) • Matadero Creek downstream of East Bayshore Road • Adobe Creek downstream of East Bayshore Road Coastal Clean‐Up Day (annually on the third Saturday in September) • Matadero Creek downstream of East Bayshore Road • Adobe Creek downstream of East Bayshore Road These annual creek clean‐up events are conducted with volunteers coordinated by City of Palo Alto staff members. Staff conduct outreach to attract volunteers, provide the bags/equipment needed for the clean‐ups, supervise the volunteers during the clean‐ups, and measure and document the amount of trash collected during each clean‐up event. Percent Reduction from Enhancements The total estimated annual volume of trash that will be reduced by July 1, 2014 as a result of implementing creek/channel/shoreline cleanups is 700 gallons. This volume is equal to approximately a 4.7 percent reduction in the baseline trash load to urban creeks from the municipal separate storm sewer system (MS4) owned and operated by the City of Palo Alto. Both values provided within this section are included in Trash Load Reduction Summary Table included in Section 5.0. 9 Creek/channel/shoreline cleanups conducted in accordance with Permit Provision C.10.b. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 36 5.0 SUMMARY OF TRASH CONTROL MEASURE ENHANCEMENTS The City of Palo Alto is committed to reducing the potential for trash impacts in local water bodies in the San Francisco Bay Area. The planned enhanced trash control measures described in Section 4.0 are also listed in Table 5‐1. The enhancements are intended to comply with the 40% trash load reduction goal in MRP provision C.10. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 37 Table 5‐1. Planned enhanced trash control measure implementation within the jurisdictional boundaries of the City of Palo Alto and associated trash loads reduced. Trash Control Measure Summary Description Control Measure Action % Reduction (Credits) Trash Load Reduced Cumulative % Reduction (Compared to Baseline) Single‐use Carryout Plastic Bag Ordinance (CR‐1) Local ordinance banning distribution of single‐use carryout plastic bags at large supermarkets 6 738 5.0 Polystyrene Foam Food Service Ware Ban (CR‐2) Local ordinance banning distribution of polystyrene foam food service ware by all food vendors 8 985 11.6 Public Education and Outreach Programs (CR‐3) Participation in regional advertising campaigns, outreach to youth, and media relations 6 738 16.5 Activities to Reduce Trash from Uncovered Loads (CR‐4) Regulation of local trash hauler; ordinance and enforcement actions prohibiting uncovered loads; distribution of tarps at transfer station 5 615 20.7 Improved Trash Bin/Container Management (Municipally or Privately‐Controlled) (CR‐6) Tier 2 Private Program: ordinance and enforcement actions requiring proper trash containers; Downtown Streets Team performs hand sweeping in downtown business district 6.5 799 26.0 Enhanced Street Sweeping (QF‐2) – (Existing and Future Enhanced) Commercial : 3x per week Residential: 1x per week NA 2,618 43.5 Full‐capture Treatment Devices (QF‐5) Two large full‐capture devices (Contech CDS) to be installed on Park Blvd. NA 414 46.3 Litter Booms (Partial‐capture Treatment Device) (QF‐3c) Matadero Creek litter boom NA 90 46.9 Creek/Channel/Shoreline Cleanups (Volunteer and/or Municipal) (QF‐6) Semi‐annual clean‐up events at Matadero & Adobe Creek trash hot spots NA 700 51.6 Baseline Trash Load and Short‐Term Trash Load Reduction Plan 38 5.1 Annual Reporting and Progress Towards Trash Load Reduction Goal(s) Consistent with MRP Provision C.10.d (i), the City of Palo Alto intends to report on progress towards MRP trash load reduction goals on an annual basis beginning with the Fiscal Year 2011‐2012 Annual Report. Annual reports will include: 1. A brief summary of all enhanced trash load reduction control measures implemented to‐date; 2. The dominant types of trash likely removed via these control measures; 3. Total trash loads removed (credits and quantifications) via each control measure implementation; and 4. A summary and quantification of progress towards trash load reduction goals. Similar to other MRP provision, annual reporting formats will be consistent region‐wide. Annual reports are intended to provide a summary of control measure implementation and demonstrate progress toward MRP trash reduction goals. For more detailed information on specific control measures, the City of Palo Alto will retain supporting documentation on trash load reduction control measure implementation. These records should have a level of specificity consistent with the trash load reduction tracking methods described in the BASMAA Trash Load Reduction Tracking Method Technical Report (BASMAA 2012a). 5.2 Considerations of Uncertainties Baseline trash loading and load reduction estimates are based on the best available information at the time this Short‐Term Plan was developed. As with any stormwater loading and reduction estimate, a number of assumptions were used during calculations and therefore uncertainty is inherent in the baseline trash load estimate presented in Section 2.0 and the load reduction estimate presented in this section. For these reasons, the baseline loading estimates presented in this plan should be considered first‐order estimates. During the implementation of this Short‐Term Plan and subsequent plans, additional information may become available to allow the calculation of a more robust baseline load. 39 6.0 IMPLEMENTATION SCHEDULE Implementation of enhanced trash control measures by the City of Palo Alto is currently planned to occur in a timeframe consistent with MRP requirements. A preliminary implementation schedule for all planned enhancements is described in Table 6‐1. This schedule provides a timeframe for reducing trash discharged from the City of Palo Alto’s MS4 by 40%. Based on new information that becomes available during the implementation of this Short‐Term Plan (e.g., revisions to baseline loading estimates or load reduction credits of quantification formulas), the City of Palo Alto may chose to amend or revise this Plan and/or the associated implementation schedule. If revisions or amendments occur, a revised Short‐Term Plan and implementation schedule will be submitted to the Water Board via the City of Palo Alto’s annual reporting process. Baseline Trash Load and Short‐Term Trash Load Reduction Plan 40 Table 6‐1. Preliminary implementation schedule for enhanced trash control measures in the City of Palo Alto. Trash Control Measure Beginning Date of Implementation Single‐use Carryout Plastic Bag Ordinance (CR‐1) September 18, 2009 Polystyrene Foam Food Service Ware Ban (CR‐2) April 22, 2010 Public Education and Outreach Programs (CR‐3) December 2009 Activities to Reduce Trash from Uncovered Loads (CR‐4) Pre‐MRP Improved Trash Bin/Container Management (Municipally or Privately‐Controlled) (CR‐6) Pre‐MRP Enhanced Street Sweeping (QF‐2) Pre‐MRP Full‐capture Treatment Devices (QF‐5) October 2012 Litter Booms (Partial‐capture Treatment Device) (QF‐3c) June 2009 Creek/Channel/Shoreline Cleanups (Volunteer and/or Municipal) (QF‐6) May 2010 Baseline Trash Load and Short‐Term Trash Load Reduction Plan 41 7.0 REFERENCES Allison R.A. and F.H.S. Chiew 1995. Monitoring stormwater pollution from various land uses in an urban catchment. Proceedings from the 2nd International Symposium on Urban Stormwater Management, Melbourne, 551‐516. Allison, R.A., T.A. Walker, F.H.S. Chiew, I.C. O’Neill and T.A McMahon 1998. From Roads to rivers: Gross pollutant removal from urban waterways. Report 98/6. Cooperative Research Centre for Catchment Hydrology. Victoria, Australia. May 1998. Armitage, N. 2001. The removal of Urban Litter from Stormwater Drainage Systems. Ch. 19 in Stormwater Collection Systems Design Handbook. L. W. Mays, Ed., McGraw‐Hill Companies, Inc. ISBN 0‐07‐135471‐9, New York, USA, 2001, 35 pp. Armitage, N. 2003. The removal of urban solid waste from stormwater drains. Prepared for the International Workshop on Global Developments in Urban Drainage Management, Indian Institute of Technology, Bombay, Mumbai India. 5‐7 February 2003. Armitage, N. 2007. The reduction of urban litter in the stormwater drains of South Africa. Urban Water Journal Vol. 4, No. 3: 151‐172. September 2007. Armitage N., A. Rooseboom, C. Nel, and P. Townshend 1998. “The removal of Urban Litter from Stormwater Conduits and Streams. Water Research Commission (South Africa) Report No. TT 95/98, Prestoria. Armitage, N. and A. Rooseboom 2000. The removal of urban litter from stormwater conduits and streams: Paper 1 – The quantities involved and catchment litter management options. Water S.A. Vol. 26. No. 2: 181‐187. BASMAA (Bay Area Stormwater Management Agencies Association). 2011a. Progress Report on Methods to Estimate Baseline Trash Loads from Bay Area Municipal Stormwater Systems and Track Loads Reduced. February 2011. BASMAA (Bay Area Stormwater Management Agencies Association). 2011b. Method to Estimate Baseline Trash Loads from Bay Area Municipal Stormwater Systems: Technical Memorandum #1. Prepared by EOA, Inc. April 2011. BASMAA (Bay Area Stormwater Management Agencies Association). 2011c. Sampling and Analysis Plan. Prepared by EOA, Inc. April 2011. BASMAA (Bay Area Stormwater Management Agencies Association). 2011d. Trash Load Reduction Tracking Method: Technical Memorandum #1 – Literature Review. Prepared by EOA, Inc. May 2011. BASMAA (Bay Area Stormwater Management Agencies Association). 2012a. Trash Load Reduction Tracking Method: Technical Report. Prepared by EOA, Inc. February. BASMAA (Bay Area Stormwater Management Agencies Association). 2012b. Trash Baseline Generation Rates: Technical Report. Prepared by EOA, Inc. February. County of Los Angeles. 2002. Los Angeles County Litter Monitoring Plan for the Los Angeles River and Ballona Creek Trash Total Maximum Daily Load. May 30, 2002. County of Los Angeles. 2004a. Trash Baseline Monitoring Results Los Angles River and Ballona Creek Watershed. Los Angeles County Department of Public Works. February 17, 2004. City of Palo Alto 42 County of Los Angeles 2004b. Trash Baseline Monitoring for Los Angles River and Ballona Creek Watersheds. Los Angeles County Department of Public Works. May 6, 2004. County of Los Angeles, Department of Public Works, Environmental Programs Division. 2007. An Overview of Carryout Bags in Los Angeles County: A Staff Report to the Los Angeles County Board of Supervisors. Alhambra, CA. http://dpw.lacounty.gov/epd/PlasticBags/PDF/PlasticBagReport_08‐2007.pdf. August 2007. Kim, L.H, M. Kayhanian, M.K. Stenstrom 2004. Event mean concentration and loading of litter from highways during storms. Science of the Total Environment Vol 330: 101‐113. SECOND STREET MACLANE WILKIE WAY WEST MEADOW DRIVE EL CAMINO WAY EL C WEST MEADOW DRIVE ALMA STREET ALMA STREET EMERSON STREET PARK BOULEVARD MACLANE EAST MEADOW EAST MEADOW DRIVE RAMONA EMERSON STREET RAMONA STREET EL VERA RRON AVENUE RTH WAY VENTURA AVENUE EL CAMINO REAL EL CAMINO REAL EL CAMINO REAL LA SELVA DRIVE RIVE SOUTH A REAL (PRIVATE) VILLA VISTA (PRIVATE) VISTA AVENUE WISTERIALANE VILLA VISTA (PRIVATE) ORINDA STREET MATADERO AVENUE MARGARITA AVENUE WILTON AVENUE MATADERO AVENUE BA R R O N A V E N U E CURTNER AVENUE WILTON AVENUE KENDALL AVENUE MATADERO AVENUE EL CAMINO REAL EL CAMINO REAL ALMA STREET ALMA STREET VENTURA COURT VENTURA AVENUE CURTNER AVENUE T EMERSON STREET RAMONA STREET LOMA VERDE AVENUE EL VERANO AVENUE RAMONA STREET MARGARITA AVENUE PARK BOULEVARD RD PARK BOULEVARD PARK BOULEVARD MADELINE COURT EET CYPRESS LANE JACOBS COURT (PRIVATE) 66 LANE 66 LA SELVA DRIVE WERS BOARD PENINSULA CORRIDOR JOINT POWERS BOARD PENINSULA CORRIDOR JOINT POWERS BOARD EL EL CAMINO REAL EL CAMINO REALEL CAMINO REAL 3700 3800 3900 3800 300 3100 3300 4000 200 4000 4100 200 3500 100 100 3600 3700 200 3500 3200 200 400 IN IN SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SDSD SD SD SD SD SD SD SD SD SD SD OF OF OF OF OF OF OF OFOF OF OF OF OF OF OF Tributary Area = 40.50 Acres Proposed Installation Site SD This map is a product of the City of Palo Alto GIS This document is a graphic representation only of best available sources. 0' 385' Pro j e c t S i t e O v e r v i e w Ve n t u r a A v e & P a r k B l v d . CITY OF PALO ALTOINCORPORATED CALI FORNIA P a l o A l t oT h e C i t y o f APRIL 1 6 1894 The City of Palo Alto assumes no responsibility for any errors. ©1989 to 2010 City of Palo Alto rhada, 2011-08-04 11:43:06 (\\cc-maps\gis$\gis\admin\Personal\Storm.mdb) FLORALES DRIVE VENUE RO ROADIRVEN COURT ALTA MESA AVENUE EL CAMINO REAL WAY EL CAMINO REAL McKELLAR LANE EL CAMINO REAL SECOND STREET MACLANE WILKIE WAY WEST MEADOW DRIVE VICTORIA PLACE EL CAMINO WAY EL CAMINO REAL CAMINO CT EL CAMINO WAY THAIN WAY THAIN WAY EL CAMINO REAL MAYBELL AVENUE PENA COURT WEST MEADOW DRIVE DAVENPORT WAY JAMES ROAD WILKIE WAY WILKIE COURT TENNESSEE LANE WEST CHARLESTON ROAD ALMA STREET PARK BOULEVARD TENNESSEE LANE WILKIE WAY CAROLINA LANE WEST CHARLESTON ROAD WILKIE WAY DULUTH CIRCLE WILKIE WAY WHITCLEM CT WHITCLEM WAY CHARLESTON ROAD CAROLINA LANE PARK BOULEVARD WEST CHARLESTON ROAD RUTHELMA AVENUE LUNDY LANE PARK BOULEVARD NEWBERRY COURT EDLEE AVENUE WRIGHT PLACE ALMA STREET CR WHITCLEM DRIVE ALMA STREETGREENMEADOW WAY ELY PLACE ALMA STREET ELY PLACE GREENMEADOW PARKSIDE DRIVE ELY DIXON PLACE TREET ALMA STREET EMERSON STREET MACLANE EAST MEADOW DR EAST MEADOW DRIVE RAMONA STREET RAMONA STREET YANT STREET REAL VILLA VERA VILLA REAL (PRIVATE) VILLA VISTA (PRIVATE) LOS ROBLES AVENUE CAMPANA DRIVE DE DRIVE VERDOSA DRIVE VISTA AVENUE WISTERIA LANE VILLA VISTA (PRIVATE) CREEKSIDE DRIVE PARK BOULEVARD DARLINGTON COURT BARCLAY COURT GEORGE HOOD LANE WEST CHARLESTON ROAD WHITCLEM PLACE ALMA STREET EL CAMINO REAL DRISCOLL PLACE CAMPANA DRIVE VERDOSA DRIVE JACOBS COURT (PRIVATE) INTERDALE WY RABELLE COURT LINDERO DRIVE ROOSEVELT CIRCLE STARR KING CIRCLE EDLEE AVENUE WHITCLEM DRIVE PENINSULA CORRIDOR JOINT POWERS BOARD PENINSULA CORRIDOR JOINT POWERS BOARD PENINSULA CORRIDOR JOINT POWERS BOARD PENINSULA CORRIDOR JOI DEODAR STREET DEODAR STREET ALDER LANE SPRUCE LANE RICKEY'S LANE JUNIPER WAY RICKEY'S WAY RICKEY'S WAY RICKEY'S WAY JUNIPER LANE Hettinger Ln Pratt Ln Noble St Cashel St EL CAMINO REAL EL CAMINO REAL O REAL EL CAMINO REAL EL CAMINO REAL 4000 600 600 4000 500 500 4200 200 500 4100 41004100 4000 400 4100 3600 4100 4200 300 200 4100 100 3700 3900 200 3600 3500 100 500 500 400 4200 400 400 400 400 4200 4200 4200 IN IN IN IN IN IN IN IN IN IN IN IN IN IN IN SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SD SDSD SD SD SD SD SD SDSD SD SDSD SD SD SD SD SD SD SDSD SD SD SD SD SD SD SD OF OF OF OF OF OF OF OF OF OF Tributary Area = 127 Acres PROPOSEDINSTALLATIONSITE This map is a product of the City of Palo Alto GIS This document is a graphic representation only of best available sources. 0' 475' Pro j e c t S i t e O v e r v i e w W. M e a d o w D r . & P a r k B l v d . CITY OF PALO ALTOINCORPORATED CALI FORNIA P a l o A l t oT h e C i t y o f APRIL 1 6 1894 The City of Palo Alto assumes no responsibility for any errors. ©1989 to 2010 City of Palo Alto rhada, 2011-08-04 15:11:27 (\\cc-maps\gis$\gis\admin\Personal\Storm.mdb)