| | Modelling WCA Collection Systems Costs, Performance and |
| | 0,77 | | MB | Outputs |
| | 117 | | stron |
| | 5210 | | ID | Eunomia Research & Consulting Ltd |
| | 2006 | | rok |
| | Contents |
| | 1.0 Executive Summary .1 |
| | 1.1 Selecting Which Services to Investigate1 |
| | 1.2 Study Findings and Recommendations Arising 2 |
| | 1.2.1 Existing Participation Rates are Good2 |
| | 1.2.2 Kerbside Collected Waste Recycling Rates of 50% are Realistic and Affordable 2 |
| | 1.2.3 Reduced Frequency Refuse Collections are Central to High Performing, Low Cost Systems.2 |
| | |
| | 1.2.4 Co-mingled Recycling Services will Offer Limited Performance Gains in Surrey. .3 |
| | 1.2.5 Garden Waste Services Need Not be Provided Free of Charge3 |
| | 1.2.6 Full Alignment of WCA and WDA Interests is Critical and Urgent .4 |
| | 2.0 Model Description and Methodology.5 |
| | 2.1 Introduction .5 |
| | 2.2 Description of Model.5 |
| | 2.2.1 Baseline Modelling.5 |
| | 2.2.2 Scenario Modelling 8 |
| | 2.3 Performance Assumption Guidelines 9 |
| | 2.3.1 General Modelling Assumptions .9 |
| | 2.3.2 Cost Assumptions.11 |
| | 2.4 Notes on Interpretation of Cost & Performance Data 13 |
| | 3.0 Appraisal of System Configurations for Long Term Modelling and Option Selection .15 |
| | 3.1 Introduction .15 |
| | 3.2 Development of a Long List of Fully Optimised, Longer Term Scenarios15 |
| | 3.2.1 Residual waste .15 |
| | 3.2.2 Dry Recyclables 16 |
| | 3.2.3 Organic material.16 |
| | 3.2.4 Service Combinations and Early Stage Short-Listing 17 |
| | 3.3 Shortening the Long List of Options 19 |
| | 3.3.1 Qualitative Appraisal of All Possible Service Combinations – Internal Eunomia Workshop 19 |
| | 3.4 Producing a Final Short List – Scenario Modelling for a Generic Authority 20 |
| | 3.4.1 Results from Generic Authority Modelling20 |
| | 3.4.2 Recycling System Performance Comparisons .21 |
| | 3.4.3 Organic System Performance Comparisons 22 |
| | 3.5 Ranking System Methodology25 |
| | 3.6 Ranking the 19 Long Term Models .26 |
| | 3.7 Ranking System Sensitivity Analysis28 |
| | 3.8 Selecting which Long-Term Options to Model Using the Ranking System and Other Practical |
| | Considerations.28 |
| | 3.8.1 Reasons for Including (and Excluding certain) Scenarios in Further Detailed Modelling.28 |
| | 3.9 Development of Possible Intermediate Scenarios .30 |
| | 4.0 Detailed Modelling Outputs.32 |
| | 4.1 Elmbridge Borough Council 34 |
| | 4.2 Epsom & Ewell Borough Council 39 |
| | 4.3 Guildford Borough Council .42 |
| | 4.4 Mole Valley District Council 45 |
| | 4.5 Reigate & Banstead Borough Council 48 |
| | 4.6 Runnymede Borough Council 51 |
| | 4.7 Spelthorne Borough Council 54 |
| | 4.8 Surrey Heath Borough Council 57 |
| | 4.9 Tandridge District Council . 60 |
| | 4.10 Waverley Borough Council . 63 |
| | 4.11 Woking Borough Council 66 |
| | 5.0 County-wide Implications of Modelling Long-Term Services.69 |
| | 5.1 Costs and Performance under a County-wide Roll-out of any Single System 69 |
| | 5.2 Preferred Scenarios with Cross-County Costs and Performance Outcomes 73 |
| | 5.3 Incentivising the WCAs to make Optimal Service Selections and the Costs of Kitchen Waste |
| | Collections 76 |
| | 5.4 Recycling and Residual Waste Compositions Outputs 77 |
| | 6.0 Long Term Option Sensitivity Analyses83 |
| | 6.1 Weekly Residual Waste . 84 |
| | 6.2 Substitution for Stillage Recyclable Vehicles . 84 |
| | 6.3 AD Treatment of Kitchen Waste 85 |
| | 6.4 Single Pass for Recyclables and Kitchen Waste 85 |
| | 6.5 Changing Waste Growth Rate . 86 |
| | 7.0 Conclusions .90 |
| | 7.1 Doorstep Recycling Performance and Alternate Week Collection of Refuse. 90 |
| | 7.2 Dry Recycling Participation Rates . 91 |
| | 7.3 Co-mingled Collections vs. Kerbside Sort. 91 |
| | 7.4 Green Waste Collections . 92 |
| | 7.5 Kitchen Waste Collections. 92 |
| | 7.6 The Need for Joined up Working. 93 |
| | Appendix 1: Waste Composition Data Used .95 |
| | Appendix 2: Commodity Prices Used 96 |
| | Appendix 3: Description of the Nineteen Scenarios Modelled for a ‘Generic’ Authority98 |