DISCO ROAD BIOGAS UTILIZATION PROJECT. Modifications Document
|
|
- Sophie Atkinson
- 7 years ago
- Views:
Transcription
1 December 2016 DISCO ROAD BIOGAS UTILIZATION PROJECT Modifications Document Submitted to: Ministry of the Environment and Climate Change Director, Environmental Approvals Access and Service Integration Branch 135 St. Clair Ave. W, 1st Flr. Toronto, ON M4V 1P5 REPORT Report Number: Distribution: 3 copies - Ministry of the Environment and Climate Change 1 copy - Toronto Solid Waste Management Services 1 copy - Golder Associates Ltd.
2 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT Table of Contents 1.0 INTRODUCTION CONTACT INFORMATION SUMMARY OF PROPOSED PROJECT CHANGES RATIONALE FOR PROPOSED CHANGES SUMMARY OF NEW POTENTIAL ENVIRONMENTAL EFFECTS EFFECTS ON RENEWABLE ENERGY APPROVAL APPLICATION REPORTS NEW DOCUMENTS REQUIRED SITE PLAN CONCLUSIONS... 8 TABLES Table 1: Proposed Scenarios for Biogas Consumption... 3 Table 2: Summary of Amendments to Renewable Energy Approval Application Reports and Studies... 5 Table 3: Amendments to Renewable Energy Approval Application Reports and Studies... 6 FIGURES Figure 1: Project Location APPENDICES APPENDIX A Revised Air Emission Tables (ESDM Report Tables I, 4 and 5 and Design & Report Table 3) December 2016 Report No i
3 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT 1.0 INTRODUCTION This Modifications Document has been prepared by Golder Associates Ltd. (Golder), on behalf of the City of Toronto (the City) in support of a Renewable Energy Approval (REA) application for the proposed Disco Road Biogas Utilization Project (the Project). The Project is located at 150 Disco Road in Toronto, Ontario, adjacent to the Disco Road Waste Management Facility (DRWMF), which is located at 120 Disco Road, as shown on Figure 1. The draft REA for the Project was issued by the Ontario Ministry of the Environment and Climate Change (MOECC) on March 29, Upon review of the draft approval, it was identified that approval for three additional operating scenarios (contingency scenarios) for the consumption of is required to provide operational flexibility to meet heating demands of the Disco Road Organics Processing Facility (DROPF) at 120 Disco Road under extreme cold weather conditions and to allow for all foreseeable temporary operating scenarios that could arise. The MOECC has classified this amendment as a Technical Change. The purpose of this Modifications Document is to outline the Technical Change by describing the proposed contingency scenarios, assessing the environmental effects of these changes, and summarizing how these additional scenarios affect reports previously submitted as part of the REA application. December 2016 Report No
4 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT 2.0 CONTACT INFORMATION Applicant The Proponent for the City of Toronto and the contact for the Project is as follows: Silvio Abate, Project Manager Toronto Solid Waste Management Services Infrastructure Development and Asset Management Capital Delivery 35 Vanley Crescent Building 275 Toronto, Ontario, Canada M3J 2B7 Phone: (416) sabate@toronto.ca Project website: Consultant The Proponent has retained Golder Associates Ltd. (Golder) to prepare the Modifications Document for the REA Application under O. Reg. 359/09. Contact information for the Golder REA Manager is as follows: James Francis, REA Manager Golder Associates Ltd. 141 Adelaide Street West Suite #910 Toronto, Ontario, Canada M5H 3L5 Phone: (416) x jfrancis@golder.com December 2016 Report No
5 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT 3.0 SUMMARY OF PROPOSED PROJECT CHANGES Three contingency scenarios are proposed to be added to the REA. These scenarios are in addition to the two scenarios already included in the REA. These three contingency scenarios are required to provide operational flexibility to meet heating demands of the DROPF at 120 Disco Road under extreme cold weather conditions and to allow for all foreseeable temporary operating scenarios that could arise. The proposed operating scenarios for consumption are identified in Table 1. Table 1: Proposed Scenarios for Biogas Consumption Source Description Biogas Generators DRWMF Biogas Flare DRWMF Biogas Boilers Included in Draft REA Scenario A Two generators at maximum of 1064 m³/hour at a consumption rate of 418 m³/hour Not Scenario B One generator at maximum of 532 m³/hour at a consumption rate of 656 m³/hour Not Proposed Contingency Scenarios to be Added to the REA Scenario C One generator at maximum of 532 m³/hour at a consumption rate of 418 m³/hour on 497 m³/hour Scenario D One generator at maximum of 532 m³/hour at a consumption rate of 656 m³/hour on 248 m³/hour Scenario E Two generators at maximum of 1064 m³/hour Not on 66 m³/hour Scenario A (normal operations) and Scenario B (maintenance operations) both represent the primary operations for the Project, while Scenarios C through E will be temporary operational conditions. Each of the Scenarios account for consumption of at least the maximum amount of that can be produced by the digesters (1,130 m³/hour). Note that the operating conditions encompassing (1) no generators, one boiler and flare and (2) no generators, two boilers and no flare have been previously approved under the Amended Environmental Compliance Approval EHPAN, issued February 12, December 2016 Report No
6 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT 4.0 RATIONALE FOR PROPOSED CHANGES The additional scenarios are required to meet heating demands of the DROPF at 120 Disco Road under extreme cold weather conditions and to cover all foreseeable temporary operating scenarios that could arise. 5.0 SUMMARY OF NEW POTENTIAL ENVIRONMENTAL EFFECTS No new environmental effects are anticipated to result from the proposed changes to the Project. The proposed changes could result in minor increases in the magnitude of predicted contaminant concentrations previously assessed in the REA Application. These changes are as follows: maximum nitrogen oxide emissions in any modelled operating scenario increase from 46.9% of the MOECC Point of Impingement (POI) limit under Scenario A to 47.8% of the limit under Scenario E; and maximum sulphur dioxide emissions in any modelled operating scenario increase from 96.8% of the MOECC POI limit under Scenario A to 98.7% of the limit under Scenario E. Given that the predicted emissions remain within MOECC POI limits, no additional mitigation is required. Details of the updated air quality modelling are provided in Table 3 with updated results for all scenarios included in Appendix A. December 2016 Report No
7 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT 6.0 EFFECTS ON RENEWABLE ENERGY APPROVAL APPLICATION REPORTS Table 2 provides a summary of the amendments/updates to each REA application report as a result of the three additional operating scenarios (contingency scenarios). Table 2: Summary of Amendments to Renewable Energy Approval Application Reports and Studies Report Description of Amendment/Update Explanation of whether the report is impacted by the change Project Description Report No amendments required No impacts to report Construction Plan Report No amendments required No impacts to report Design and Report Amendment to describe the three additional operating scenarios and provide air emissions summary tables for the additional scenarios Updates to the description of operation Decommissioning Plan Report No amendments required No impacts to report Cultural Heritage Report No amendments required No impacts to report Natural Heritage Report No amendments required No impacts to report Water Assessment Report No amendments required No impacts to report Emission Summary and Dispersion Modelling (ESDM) Report Amendment requiring modelling of the additional operating scenarios. The ESDM amendments include updating the Emission Summary Table (Table I and Table 5), adding additional Dispersion Modelling Source Summary tables for the three additional operating scenarios, updating the text throughout to mention the additional scenarios, and including the modelling files for the additional scenarios No impact to the conclusions of the report. The assessment demonstrates that the Project can operate in compliance with section 20 of O. Reg. 419/05 under each assessed Scenario. Noise Study Report No amendments required No impacts to report Odour Study Report No amendments required No impacts to report Consultation Report No amendments required No impacts to report Table 3 outlines the amendments/updates required to each REA application report as a result of the three additional operating scenarios (contingency scenarios). December 2016 Report No
8 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT Table 3: Amendments to Renewable Energy Approval Application Reports and Studies Report Design and Report Description of Amendment Addition of information on operating scenarios C through E Section # and Page # Affected Section Page 12 Original Text It is not feasible for all equipment to operate at maximum concurrently; therefore, two maximum operating scenarios have been defined: the normal operations scenario and the maintenance operations scenario. Revised Text or Location of Revised Text It is not feasible for all equipment to operate at maximum concurrently; therefore, five maximum operating scenarios for consumption have been defined as follows: Source Description Biogas Generators Scenario A Two generators at maximum of 1064 m³/hour Scenario B One generator at maximum of 532 m³/hour Scenario C One generator at maximum of 532 m³/hour Scenario D One generator at maximum of 532 m³/hour Scenario E Two generators at maximum of 1064 m³/hour DRWMF Biogas Flare at a consumption rate of 418 m³/hour at a consumption rate of 656 m³/hour at a consumption rate of 418 m³/hour at a consumption rate of 656 m³/hour Not Section Page 12 A summary of the modelling results is provided in Table 3 for the normal operations scenario and Table 4 for the maintenance operations scenario. DRWMF Biogas Boilers Not Not on 497 m³/hour on 248 m³/hour on 66 m³/hour Scenario A is considered normal operations, while the remaining four operations provide flexibility for various heating demands as well as maintenance of the system. A summary of the modelling results is provided in Table 3 for all scenarios. Revised table 3 is provided in Appendix A (Emissions Summary Table.). Addition of reference to additional tables Section Page 22 These include emission of the contaminants listed in Tables 3 and 4 (see Section 4.4.3). These include emission of the contaminants listed in Table 3 (see Section 4.4.3). ESDM Report Revision of text regarding additional operating scenarios Executive Summary Page i The assessment has been completed for two scenarios, normal operations and maintenance operations. The assessment has been completed for five scenarios of consumption: normal operations, maintenance operations, and three contingency operation scenarios. Revision of header title Revision of header title Section Page 2 Section Page Normal Conditions Scenario A (Normal Conditions) Maintenance Scenario B (Maintenance Conditions) Addition of sections describing Page Scenario C December 2016 Report No
9 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT Report Description of Amendment Section # and Page # Affected Original Text Revised Text or Location of Revised Text operating scenarios C through E If required during off-peak hours due to heating demands of 120 Disco Road, the two dual fuel boilers may be operated on. If this is required, sufficient would be available to run one of the generators at maximum. Remaining not consumed by the two boilers and single generator would be directed to the flare Scenario D If required during off-peak hours due to heating demands of 120 Disco Road, one of the two dual fuel boilers may be operated on. If this is required, sufficient would be available to run one of the generators at maximum. Remaining not consumed by the single boiler and single generator would be directed to the flare Scenario E If required during on-peak hours due to heating demands of 120 Disco Road, the two generators would be operating to provide power and heat to the Joint Facility. Remaining not consumed by the two generators would be consumed by one of the dual fuel boilers. No would be directed to the flare. Addition of information on operating scenarios C through E Section 4.1 Page 7 Table A: Scenarios Source Description Maximum Capacity Normal Maintenance Table A: Scenarios Source Description Maximum Capacity Scenario A Scenario B Scenario C Scenario D Scenario E Biogas Generators Natural Gas Combustion Equipment Dust Collector DRWMF 1,426 kw each (24 hours per day, 7 days per week) 16 hours per day, 5 days per week 24 hours per day, 7 days per week Described in Appendix A Two generators at maximum All units operating at maximum except boiler H4 Maximum Maximum One generator at maximum All units operating at maximum except boiler H4 Maximum Maximum Biogas Generators Natural Gas Combustion Equipment Dust Collector DRWMF Flare DRWMF Biogas Boilers (H4) All other DRWMF Sources 1,426 kw each (24 hours per day, 7 days per week) 16 hours per day, 5 days per week Two generators at maximum All units operating at maximum except boiler H4 One generator at maximum All units operating at maximum except boiler H4 Maximum at a consumption rate of 656 m³/hour 24 hours per day, 7 days per week Maximum 24 hours per day, 7 at a days per week consumption rate of 418 m³/hour 24 hours per day, 7 days per week Not Not Described in Appendix A Maximum Maximum One generator at maximum All units operating at maximum except boiler H4 Maximum at a consumption rate of 418 m³/hour on at 497 m³/hour Maximum One generator at maximum All units operating at maximum except boiler H4 Maximum at a consumption rate of 656 m³/hour on at 248 m³/hour Maximum Two generators at maximum All units operating at maximum except boiler H4 Maximum Not on at 66 m³/hour Maximum December 2016 Report No
10 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT In the ESDM, the Emissions Summary Table (Table I and Table 5) also requires revision to reflect updated results based on the modelling completed for the additional operating scenarios. The revised table can be found in Appendix A of this document, along with a revised Table 4 (Dispersion Modelling Source Summary Table) which reflects the emission rates and modelling parameters of all five operating scenarios. Additionally, the dispersion modelling files for Conditions A through E have been provided to MOECC. 7.0 NEW DOCUMENTS REQUIRED No new documents are expected to be required with respect to the proposed amendment. 8.0 SITE PLAN No changes to the site plan are required with respect to the proposed amendment. The Project Location, as shown in Figure 1, is unchanged. 9.0 CONCLUSIONS The proposed amendment does not affect the conclusions of the REA application reports. Revisions to the text in the Design and Report have been provided in this Modifications Document to describe the additional three operating scenarios. Modelling of the additional three operating scenarios was completed to update the ESDM Report. Revisions to the text in the ESDM Report reflecting the additional three operating scenarios have been provided in this Modifications Document. The conclusions of the ESDM Report remain unchanged. The proposed amendment does not result in an increase in Project Location size, does not result in a change to the overall impact at receptors, does not require additional lands, does not require an archaeological assessment, and has no impact on cultural heritage or natural heritage features. December 2016 Report No
11 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT Report Signature Page GOLDER ASSOCIATES LTD. James Francis, M.Sc., B.Eng.Soc. REA Manager Mark Greenhill, P.Eng. Project Manager AVW/KSA/JF/MG/ng Golder, Golder Associates and the GA globe design are trademarks of Golder Associates Corporation. n:\active\2013\1155\ city of toronto-landfill& util.study\ rea application\19 draft rea approval\technical change\version 3\ rpt dec 2016 disco rd util mod doc.docx December 2016 Report No
12 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT FIGURES December 2016 Report No
13 HIGHWAY LEGEND ³ Railways Watercourse Waterbody Wetland North Mimico Valley Park Municipal Boundary Underground Biogas Pipes 150 Disco Road Property 120 Disco Road Property Disco Road Waste Management Facility Toronto West Detention Centre Project Location 1 Biogas Facility Footprint (Included in the Project Location) CITY OF TORONTO NOTE: 1. The Project Location includes the Biogas Facility Footprint. ATTWELL DRIVE Boiler Room New SSO Processing Facility ^_ Mississauga!. Whitby!. Toronto!. Lake Ontario Cambridge!. Hamilton!. INDEX MAP G:\Projects\2013\ \GIS\MXDs\Reporting\ProjectLocationMap.mxd CITY OF MISSISSAUGA NORTHWEST DRIVE Approximately 1.6 km To Pearson Airport? DISCO ROAD Mimico Creek HIGHWAY 409 CARLINGVIEW DRIVE REFERENCE Base Data - MNR LIO, obtained 2009 Produced by Golder Associates Ltd under licence from Ontario Ministry of Natural Resources, Queens Printer 2012 Imagery - ESRI World Imagery WMS, 2014 Projection: Transverse Mercator Datum: NAD 83 Coordinate System: UTM Zone 17 PROJECT TITLE SCALE 1:8,000 METRES CITY OF TORONTO DISCO ROAD BIOGAS UTILIZATION PROJECT PROJECT LOCATION PROJECT NO SCALE AS SHOWN DESIGN ME 14 Mar GIS ME 14 Mar CHECK IC 14 Mar Mississauga, Ontario REVIEW IC 14 Mar REV. FIGURE: 1
14 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT APPENDIX A Revised Air Emission Tables (ESDM Report Tables I, 4 and 5 and Design & Report Table 3) December 2016 Report No
15 DISCO ROAD BIOGAS UTILIZATION PROJECT - MODIFICATIONS DOCUMENT ESDM Report Table I, 4 and 5 December 2016 Report No
16 December (5000) Source Information Previously Approved Significant Modelled Rationale if Not Significant or Not Source Description Expected Contaminants Source ID General Location Under Existing ECA (Yes or No)? (Yes or No)? Modelled or Title 150_S1 Generator 1 Main Building No Products of combustion Yes Yes N/A 150_S2 Generator 2 Main Building No Products of combustion Yes Yes N/A 150_BA Building A (103) Natural Gas Combustion Equipment Building A (103) No Products of combustion Yes Yes 150_BB 150_BC Building B (101) Natural Gas Combustion Equipment Building C (102) Natural Gas Combustion Equipment Building B (101) No Products of combustion Yes Yes Building C (102) No Products of combustion Yes Yes 150_BD Building D (100) Natural Gas Combustion Equipment Building D (100) No Products of combustion Yes Yes 150_DC Dust Collector Building B No Particulate matter Yes Yes N/A MW Maintenance Welding Building B No Particulate matter No No Negligible source as per Table B-3 of FT Fuel Tanks Building B No 120_S-1 Biofilter 120 Disco Road Yes Volatile compounds from diesel fuel VOCs, odour, total reduced sulphur compounds No No No No the ESDM Procedure Document. Negligible source as per Table B-3 of the ESDM Procedure Document. No contaminants in common with the Project. Odour is not expected to be emitted from the Project. An analysis of odour emissions from 120 Disco Road is documented in the Odour Study Report, submitted under separate cover in support of the REA application. 120_S-2 Biogas Flare 120 Disco Road Yes Products of combustion Yes Yes N/A 120_S-4 Natural Gas Fired Heating Equipment Transfer Station and SSO Facility Sources H1-H6 Table 1 Sources and Contaminants Identification Table Yes Products of combustion Yes Yes 120_S-5 4 Dust Collectors S5a-S5d Yes Particulate matter and odour Yes Yes 120_FP Fire Pump 120 Disco Road Yes Products of combustion Yes Yes Only NOx has been assessed as per section of the ESDM Guidance Document. Only NOx has been assessed as per section of the ESDM Guidance Document. SO2 has been assessed at the request of the MOECC. Only particulate matter has been assessed. Odour is not expected to be emitted from the Project. An analysis of odour emissions from 120 Disco Road is documented in the Odour Study Report, submitted under separate cover in support of the REA application. Only NOx has been assessed as per section of the ESDM Guidance Document. SO2 has been assessed at \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 1 of 15 Golder Associates Made by: EKL Checked by: KSA
17 December (5000) Table 1 Sources and Contaminants Identification Table Source ID Source Information Source Description or Title General Location Previously Approved Under Existing ECA Expected Contaminants Significant (Yes or No)? Modelled (Yes or No)? Rationale if Not Significant or Not Modelled 120_S-6a-e Transfer Station General Exhausts Transfer Station Yes Odour No No 120_S-7 LFG Collection System Exhaust 120 Disco Road Yes Odour No No 120_S-8 Leaf and Yard Waste 120 Disco Road Yes Odour No No 120_N/A Roads, Parking Lot 120 Disco Road Yes Dust No No Odour is not expected to be emitted from the Project. An analysis of odour emissions from 120 Disco Road is documented in the Odour Study Report, submitted under separate cover in support of the REA application. Not listed in Table 7-2 or 7-3 of Section 7.4 of the ESDM Procedure Document (although waste disposal Facility, is not a landfill) \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 2 of 15 Golder Associates Made by: EKL Checked by: KSA
18 December (5000) Source Identifier Source Description Stack Volumetric Flow Rate [Am³/s] Stack Exit Gas Temperature [ C] Stack Inner Diameter Source Parameters Stack Height Stack Height Above Grade Above Roof X-Coordinate Y-Coordinate Contaminant CAS No. Table 2 Source Summary Table Normal (Operation A) 150_S1 Generator N/A Nitrogen oxides E E E E E-01 1,24 EF Average 40% 65% 59% 62% 39% Vinyl Chloride E E E E E EC Average 50% 100% 100% 100% 50% Methylene Chloride E E E E E EC Average 50% 100% 100% 100% 50% Hexane E E E E E EC Average 50% 100% 100% 100% 50% cis-1,2-dichloroethene E E E E E EC Average 50% 100% 100% 100% 50% Benzene E E E E E-04 24, annual EC Average 50% 100% 100% 100% 50% Trichloroethylene E E E E E EC Average 50% 100% 100% 100% 50% Toluene E E E E E EC Average 50% 100% 100% 100% 50% Tetrachloroethylene E E E E E EC Average 50% 100% 100% 100% 50% Ethylbenzene E E E E E EC Average 50% 100% 100% 100% 50% Xylenes E E E E E min, 24 EC Average 50% 100% 100% 100% 50% 1,2,4-Trimethylbenzene E E E E E EC Average 50% 100% 100% 100% 50% 1,1-Dichloroethane E E E E E EC Average 50% 100% 100% 100% 50% Cyclohexane E E E E E EC Average 50% 100% 100% 100% 50% Particulate matter N/A 5.25E E E E E EF Average 16% 20% 18% 19% 16% Sulphur dioxide E E E E E EC Average 44% 72% 67% 66% 44% Carbon monoxide E E E E E EF Average 28% 39% 38% 38% 28% 150_S2 Generator N/A Nitrogen oxides E E E E E-01 1,24 EF Average 40% <1% <1% <1% 39% Vinyl Chloride E E E E E EC Average 50% <1% <1% <1% 50% Methylene Chloride E E E E E EC Average 50% <1% <1% <1% 50% Hexane E E E E E EC Average 50% <1% <1% <1% 50% cis-1,2-dichloroethene E E E E E EC Average 50% <1% <1% <1% 50% Benzene E E E E E EC Average 50% <1% <1% <1% 50% Trichloroethylene E E E E E EC Average 50% <1% <1% <1% 50% Toluene E E E E E EC Average 50% <1% <1% <1% 50% Tetrachloroethylene E E E E E EC Average 50% <1% <1% <1% 50% Ethylbenzene E E E E E EC Average 50% <1% <1% <1% 50% Xylenes E E E E E EC Average 50% <1% <1% <1% 50% 1,2,4-Trimethylbenzene E E E E E EC Average 50% <1% <1% <1% 50% 1,1-Dichloroethane E E E E E EC Average 50% <1% <1% <1% 50% Cyclohexane E E E E E EC Average 50% <1% <1% <1% 50% Particulate matter N/A 5.25E E E E E EF Average 16% <1% <1% <1% 16% Sulphur dioxide E E E E E EC Average 44% <1% <1% <1% 44% Carbon monoxide E E E E E EF Average 28% <1% <1% <1% 28% 150_BA Building A (103) Natural Gas Combustion N/A N/A N/A N/A N/A Nitrogen oxides E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Equipment 150_BB Building B (101) Natural Gas Combustion N/A N/A N/A N/A N/A Nitrogen oxides E E E E E-02 1,24 EF Above average 3% 5% 4% 5% 3% Equipment 150_BC Building C (102) Natural Gas Combustion N/A N/A N/A N/A N/A Nitrogen oxides E E E E E-02 1,24 EF Above average 1% 2% 2% 2% 1% Equipment 150_BD Building D (100) Natural Gas Combustion N/A N/A N/A N/A N/A Nitrogen oxides E E E E E-02 1,24 EF Above average 2% 3% 2% 3% 2% Equipment 150_DC Dust Collector N/A N/A N/A N/A N/A N/A N/A Particulate matter N/A 1.00E E E E E-01 1 EF Average 31% 38% 35% 36% 31% H1 Transfer Station Boiler Nitrogen oxides E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Sulphur dioxide E E E E E-05 1,24 EF Above average <1% <1% <1% <1% <1% H2 Transfer Station Roof Top Unit Nitrogen oxides E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Sulphur dioxide E E E E E-06 1,24 EF Above average <1% <1% <1% <1% <1% H3 Hot Water Heater Nitrogen oxides E E E E E-04 1,24 EF Above average <1% <1% <1% <1% <1% Sulphur dioxide E E E E E-06 1,24 EF Above average <1% <1% <1% <1% <1% H4 SSO Facility Boiler Nitrogen Oxides E E E E E-03 1,24 EF Above average <1% <1% 10% 5% <1% Carbon Monoxide E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Particulate matter N/A 0.00E E E E E-03 1,24 EF Above average <1% <1% 6% 3% <1% Sulphur dioxide E E E E E-02 1,24 EF Above average <1% <1% 16% 8% 1% Maintenance (Operation B) Emission Rate One Engine, Two Boilers and Flare (Operation C) One Engine, One Boiler and Flare (Operation D) Two Engines plus One Boiler (reduced ) (Operation E) Emission Data Averaging Period [hours] Emission Estimating Technique Emissions Data Quality Normal (Operation A) Maintenance (Operation B) Percentage of Overall Emissions [%] One Engine, Two Boilers and Flare (Operation C) One Engine, One Boiler and Flare (Operation D) Two Engines plus One Boiler (reduced ) (Operation E) \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 3 of 15 Golder Associates Made by: EKL Checked by: KSA
19 December (5000) Source Identifier Source Description Stack Volumetric Flow Rate [Am³/s] Stack Exit Gas Temperature [ C] Stack Inner Diameter Source Parameters Stack Height Stack Height Above Grade Above Roof X-Coordinate Y-Coordinate Contaminant CAS No. Table 2 Source Summary Table Normal (Operation A) Maintenance (Operation B) Emission Rate One Engine, Two Boilers and Flare (Operation C) One Engine, One Boiler and Flare (Operation D) Two Engines plus One Boiler (reduced ) (Operation E) Emission Data Averaging Period [hours] Emission Estimating Technique Emissions Data Quality Normal (Operation A) Maintenance (Operation B) Percentage of Overall Emissions [%] H5 Hot Water Heater Nitrogen oxides E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Sulphur dioxide E E E E E-05 1,24 EF Above average <1% <1% <1% <1% <1% H6 Hot Water Heater Nitrogen oxides E E E E E-03 1,24 EF Above average <1% <1% <1% <1% <1% Sulphur dioxide E E E E E-05 1,24 EF Above average <1% <1% <1% <1% <1% S2 Biogas Flare NA Nitrogen Oxides E E E E E-01 1,24 EF Average 14% 23% 20% 21% 14% Carbon Monoxide E E E E E+00 1 EF Average 44% 61% 61% 61% 44% Particulate matter N/A 6.29E E E E E EF Marginal 20% 24% 22% 23% 20% Sulphur dioxide E E E E E-01 1,24 EF Above-Average 11% 28% 17% 26% 11% S5a Transfer Station Dust 3.2 above roof x Collector (tier 1) Particulate matter N/A 1.51E E E E E EC Average 5% 6% 5% 5% 5% S5b Transfer Station Dust 3.2 above roof x Collector (tier 1) Particulate matter N/A 1.01E E E E E EC Average 3% 4% 4% 4% 3% S5c Transfer Station Dust 3.2 above roof x Collector (tier 1) Particulate matter N/A 1.01E E E E E EC Average 3% 4% 4% 4% 3% S5d Transfer Station Dust Collector x above roof (tier 1) One Engine, Two Boilers and Flare (Operation C) One Engine, One Boiler and Flare (Operation D) Particulate matter N/A 1.51E E E E E EC Average 5% 6% 5% 5% 5% Two Engines plus One Boiler (reduced ) (Operation E) Notes: "V-ST" - Validated Source Test, "ST" - Source Test, "EF" - Emission Factor, "MB" Mass Balance, "EC" - Engineering Calculation Data Quality Categories: "Highest"; "Above-Average"; "Average"; and "Marginal" \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 4 of 15 Golder Associates Made by: EKL Checked by: KSA
20 December (5000) Relevant Section of the Regulation Section 8 Section 9 Section 10 Section 11 Section 12 Section 13 Section 14 Section 15 Section 16 Section 17 Section Title Negligible Sources of Contaminants Same Structure Contamination Conditions Source of Contaminant Emission Rates Combined Effect of Assumptions for Conditions and Emission Rates Meteorological Conditions Area of Modelling Coverage (receptor locations) Stack Height for Certain New Sources of Contaminant Terrain Data Averaging Periods Table 3 Dispersion Modelling Input Summary Table Summary of How the Approved Dispersion Model Was Used Sources and contaminants that were considered negligible were explicitly identified, and therefore were not modelled in accordance with s.8 of O.Reg.419/05. Not applicable as the Facility is the only tenant occupying the building, and does not have a child care facility, health care facility, senior's residence, long-term care facility or an education facility located at the on-site. All equipment was assumed to be operating at the maximum production rates, simultaneously. The emission rate for each significant contaminant emitted from a significant source was estimated. The methodology for the calculation is documented in Table 2 - Source Summary Table. The Conditions were estimated in accordance with s.10(1) 1 and s.11(1) 1 of O.Reg.419/05 and are therefore considered to result in the highest POI concentration that the Facility is capable of for each contaminant emitted. The MOECC Regional Urban Dataset for Toronto Region was used. Modelling coverage based on s.14 of O. Reg. 419/05. Not applicable as s.15 of O.Reg.419/05 does not apply to the Facility. Terrain data obtained from the MOECC website was assessed for sources and receptors at the Facility using AERMAP. The appropriate averaging periods, as defined by the regulatory limits outlined in Schedule 3, were used. Location of Supporting Documentation in ESDM Report Section 3.0, Table 1 N/A Section 4.0, Table 4 Section 4.0, Table 2 Section 4.0 Section 6.3 Section 6.0, Figure 6 N/A Section 6.0, Figure 5 Section 6.7 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 5 of 15 Golder Associates Made by: EKL Checked by: KSA
21 December (5000) Modelling ID Source(s) Included for Modelling Source Type Stack Volumetric Flow Rate [Am³/s] Stack Height Above Grade Table 4a Dispersion Modelling Source Summary Table - Normal (Operation A) Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] Averaging Period [hours] 150_S1 150_S1 Point Nitrogen oxides E-01 1,24 150_S1 Vinyl Chloride E _S1 Methylene Chloride E _S1 Hexane E _S1 cis-1,2-dichloroethene E _S1 Benzene E-04 24, annual 150_S1 Trichloroethylene E _S1 Toluene E _S1 Tetrachloroethylene E _S1 Ethylbenzene E _S1 Xylenes E min, _S1 1,2,4-Trimethylbenzene E _S1 1,1-Dichloroethane E _S1 Cyclohexane E _S1 Particulate matter N/A 5.25E _S1 Sulphur dioxide E _S1 Carbon monoxide E _S2 150_S2 Point Nitrogen oxides E-01 1,24 150_S2 Vinyl Chloride E _S2 Methylene Chloride E _S2 Hexane E _S2 cis-1,2-dichloroethene E _S2 Benzene E _S2 Trichloroethylene E _S2 Toluene E _S2 Tetrachloroethylene E _S2 Ethylbenzene E _S2 Xylenes E _S2 1,2,4-Trimethylbenzene E _S2 1,1-Dichloroethane E _S2 Cyclohexane E _S2 Particulate matter N/A 5.25E _S2 Sulphur dioxide E _S2 Carbon monoxide E H1 H1 Point Nitrogen oxides E-03 1,24 H1 Sulphur dioxide E-05 1,24 H2 H2 Point Nitrogen oxides E-03 1,24 H2 Sulphur dioxide E-06 1,24 H3 H3 Point Nitrogen oxides E-04 1,24 H3 Sulphur dioxide E-06 1,24 H5 H5 Point Nitrogen oxides E-03 1,24 H5 Sulphur dioxide E-05 1,24 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 6 of 15 Golder Associates Made by: KSA Checked by: BSC
22 December (5000) Modelling ID Source(s) Included for Modelling Source Type Stack Volumetric Flow Rate [Am³/s] Stack Height Above Grade Table 4a Dispersion Modelling Source Summary Table - Normal (Operation A) Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] H6 H6 Point Nitrogen oxides E-03 1,24 H6 Sulphur dioxide E-05 1,24 S2 S2 Point Nitrogen Oxides E-01 1,24 S2 Carbon Monoxide E+00 1 S2 Particulate matter N/A 6.29E S2 Sulphur dioxide E-01 1,24 S5a S5a Horizontal Point x Particulate matter N/A 1.51E S5b S5b Horizontal Point x Particulate matter N/A 1.01E S5c S5c Horizontal Point x Particulate matter N/A 1.01E S5d S5d Horizontal Point x Particulate matter N/A 1.51E Averaging Period [hours] Source ID Source ID(s) Source Type Building Area Building Height Release Height Initial Lateral Dimension Initial Vertical Dimension X-coordinate Y-Coordinate Contaminant CAS No. Maximum Emission Rate [g/s] Averaging Period [hours] 150_BA 150_BA Volume Nitrogen oxides E-03 1,24 150_BB 150_BB Volume Nitrogen oxides E-02 1,24 150_BB 150_DC Particulate matter N/A 1.00E-01 1,24 150_BC 150_BC Volume Nitrogen oxides E-02 1,24 150_BD 150_BD Volume Nitrogen oxides E-02 1,24 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 7 of 15 Golder Associates Made by: KSA Checked by: BSC
23 December (5000) Modelling ID Source(s) Included for Modelling Source Type Stack Volumetric Flow Rate [Am³/s] Table 4b Dispersion Modelling Source Summary Table - Maintenance (Operation B) Stack Height Above Grade Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] 150_S2 150_S2 Point Nitrogen oxides E-01 1,24 150_S2 Vinyl Chloride E _S2 Methylene Chloride E _S2 Hexane E _S2 cis-1,2-dichloroethene E _S2 Benzene E _S2 Trichloroethylene E _S2 Toluene E _S2 Tetrachloroethylene E _S2 Ethylbenzene E _S2 Xylenes E _S2 1,2,4-Trimethylbenzene E _S2 1,1-Dichloroethane E _S2 Cyclohexane E _S2 Particulate matter N/A 5.25E _S2 Sulphur dioxide E _S2 Carbon monoxide E H1 H1 Point Nitrogen oxides E-03 1,24 H1 Sulphur dioxide E-05 1,24 H2 H2 Point Nitrogen oxides E-03 1,24 H2 Sulphur dioxide E-06 1,24 H3 H3 Point Nitrogen oxides E-04 1,24 H3 Sulphur dioxide E-06 1,24 H5 H5 Point Nitrogen oxides E-03 1,24 H5 Sulphur dioxide E-05 1,24 H6 H6 Point Nitrogen oxides E-03 1,24 H6 Sulphur dioxide E-05 1,24 S2 S2 Point Nitrogen Oxides E-01 1,24 S2 Carbon Monoxide E+00 1 S2 Particulate matter N/A 6.29E S2 Sulphur dioxide E-01 1,24 S5a S5a Horizontal Point x Particulate matter N/A 1.51E S5b S5b Horizontal Point x Particulate matter N/A 1.01E S5c S5c Horizontal Point x Particulate matter N/A 1.01E S5d S5d Horizontal Point x Particulate matter N/A 1.51E Averaging Period [hours] Source ID Source ID(s) Source Type Building Area Building Height Release Height Initial Lateral Dimension Initial Vertical Dimension X-coordinate Y-Coordinate Contaminant CAS No. Maximum Emission Rate [g/s] Averaging Period [hours] 150_BA 150_BA Volume Nitrogen oxides E-03 1,24 150_BB 150_BB Volume Nitrogen oxides E-02 1,24 150_BB 150_DC Particulate matter N/A 1.00E-01 1,24 150_BC 150_BC Volume Nitrogen oxides E-02 1,24 150_BD 150_BD Volume Nitrogen oxides E-02 1,24 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 8 of 15 Golder Associates Made by: KSA Checked by: BSC
24 December (5000) Modelling ID Source(s) Included for Modelling Source Type Table 4c Dispersion Modelling Source Summary Table - Operation of One Engine, Two Boilers and Flare (Operation C) Stack Volumetric Flow Rate [Am³/s] Stack Height Above Grade Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] Averaging Period [hours] 150_S1 150_S1 Point Nitrogen oxides E-01 1,24 150_S1 Vinyl Chloride E _S1 Methylene Chloride E _S1 Hexane E _S1 cis-1,2-dichloroethene E _S1 Benzene E-04 24, annual 150_S1 Trichloroethylene E _S1 Toluene E _S1 Tetrachloroethylene E _S1 Ethylbenzene E _S1 Xylenes E min, _S1 1,2,4-Trimethylbenzene E _S1 1,1-Dichloroethane E _S1 Cyclohexane E _S1 Particulate matter N/A 5.25E _S1 Sulphur dioxide E _S1 Carbon monoxide E H1 H1 Point Nitrogen oxides E-03 1,24 H1 Sulphur dioxide E-05 1,24 H2 H2 Point Nitrogen oxides E-03 1,24 H2 Sulphur dioxide E-06 1,24 H3 H3 Point Nitrogen oxides E-04 1,24 H3 Sulphur dioxide E-06 1,24 H4 H4 Point Nitrogen Oxides E-02 1,24 H4 Carbon Monoxide E-02 1,24 H4 Particulate matter N/A 1.84E-02 1,24 H4 Sulphur dioxide E-01 1,24 H5 H5 Point Nitrogen oxides E-03 1,24 H5 Sulphur dioxide E-05 1,24 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 9 of 15 Golder Associates Made by: KSA Checked by: BSC
25 December (5000) Modelling ID Source(s) Included for Modelling Source Type Table 4c Dispersion Modelling Source Summary Table - Operation of One Engine, Two Boilers and Flare (Operation C) Stack Volumetric Flow Rate [Am³/s] Stack Height Above Grade Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] H6 H6 Point Nitrogen oxides E-03 1,24 H6 Sulphur dioxide E-05 1,24 S2 S2 Point Nitrogen Oxides E-01 1,24 S2 Carbon Monoxide E+00 1 S2 Particulate matter N/A 6.29E S2 Sulphur dioxide E-01 1,24 S5a S5a Horizontal Point x Particulate matter N/A 1.51E S5b S5b Horizontal Point x Particulate matter N/A 1.01E S5c S5c Horizontal Point x Particulate matter N/A 1.01E S5d S5d Horizontal Point x Particulate matter N/A 1.51E Averaging Period [hours] Source ID Source ID(s) Source Type Building Area Building Height Release Height Initial Lateral Dimension Initial Vertical Dimension X-coordinate Y-Coordinate Contaminant CAS No. Maximum Emission Rate [g/s] Averaging Period [hours] 150_BA 150_BA Volume Nitrogen oxides E-03 1,24 150_BB 150_BB Volume Nitrogen oxides E-02 1,24 150_BB 150_DC Particulate matter N/A 1.00E-01 1,24 150_BC 150_BC Volume Nitrogen oxides E-02 1,24 150_BD 150_BD Volume Nitrogen oxides E-02 1,24 \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 10 of 15 Golder Associates Made by: KSA Checked by: BSC
26 December (5000) Modelling ID Source(s) Included for Modelling Source Type Table 4d Dispersion Modelling Source Summary Table - Operation of One Engine, One Boiler and Flare (Operation D) Stack Volumetric Flow Rate [Am³/s] Stack Height Above Grade Stack Exit Gas Temperature [K] Modelling Source Data Stack Exit Velocity [m/s] Stack Inner Diameter X-Coordinate Y-Coordinate Contaminant CAS No. Emissions Data Maximum Emission Rate [g/s] 150_S2 150_S2 Point Nitrogen oxides E-01 1,24 150_S2 Vinyl Chloride E _S2 Methylene Chloride E _S2 Hexane E _S2 cis-1,2-dichloroethene E _S2 Benzene E _S2 Trichloroethylene E _S2 Toluene E _S2 Tetrachloroethylene E _S2 Ethylbenzene E _S2 Xylenes E _S2 1,2,4-Trimethylbenzene E _S2 1,1-Dichloroethane E _S2 Cyclohexane E _S2 Particulate matter N/A 5.25E _S2 Sulphur dioxide E _S2 Carbon monoxide E H1 H1 Point Nitrogen oxides E-03 1,24 H1 Sulphur dioxide E-05 1,24 H2 H2 Point Nitrogen oxides E-03 1,24 H2 Sulphur dioxide E-06 1,24 H3 H3 Point Nitrogen oxides E-04 1,24 H3 Sulphur dioxide E-06 1,24 H4 H4 Point Nitrogen Oxides E-02 1,24 H4 Carbon Monoxide E-03 1 H4 Particulate matter N/A 9.18E H4 Sulphur dioxide E-01 1,24 H5 H5 Point Nitrogen oxides E-03 1,24 H5 Sulphur dioxide E-05 1,24 H6 H6 Point Nitrogen oxides E-03 1,24 H6 Sulphur dioxide E-05 1,24 S2 S2 Point Nitrogen Oxides E-01 1,24 S2 Carbon Monoxide E+00 1 S2 Particulate matter N/A 6.29E S2 Sulphur dioxide E-01 1,24 S5a S5a Horizontal Point x Particulate matter N/A 1.51E S5b S5b Horizontal Point x Particulate matter N/A 1.01E S5c S5c Horizontal Point x Particulate matter N/A 1.01E S5d S5d Horizontal Point x Particulate matter N/A 1.51E Averaging Period [hours] \\golder.gds\gal\mississauga\active\2013\1155\ City of Toronto-landfill& util.study\ Response to MOECC Questions\01 Air\To MOECC September 2016\Updated Tables 4 and 5.xlsm Page 11 of 15 Golder Associates Made by: KSA Checked by: BSC
A GUIDANCE NOTE ON THE BEST PRACTICABLE MEANS FOR ELECTRICITY WORKS BPM 7/1 (2014)
A GUIDANCE NOTE ON THE BEST PRACTICABLE MEANS FOR ELECTRICITY WORKS (COAL-FIRED PLANT, GAS-FIRED GAS TURBINE, AND OIL-FIRED GAS TURBINE (PEAK LOPPING PLANT)) BPM 7/1 (2014) Environmental Protection Department
More informationYou have applied in accordance with Section 9 of the Environmental Protection Act for approval of:
Ministry of the Environment Ministère de l Environnement ISP Canada Corp. 34 Industrial Street Toronto, Ontario M4G 1Y9 AMENDED CERTIFICATE OF APPROVAL AIR NUMBER 0275-864JR4 Issue Date: April 1, 2011
More informationEmission Testing February 2015 LMS Energy Pty Ltd - Jilliby Plant
Page: 1 of 6 1/132 Ross Court Cleveland QLD 4163 Emission Testing February 2015 - Jilliby Plant Dear Nathan McClelland, Tests were performed 11 February 2015 to determine emissions to air from Unit 1 at
More informationTORONTO MUNICIPAL CODE CHAPTER 423, ENVIRONMENTAL REPORTING AND DISCLOSURE. Chapter 423 ENVIRONMENTAL REPORTING AND DISCLOSURE
423-1. Definitions. TORONTO MUNICIPAL CODE 423-2. Duty to report. Chapter 423 ENVIRONMENTAL REPORTING AND DISCLOSURE ARTICLE I Interpretation ARTICLE II Duty to Report 423-3. Exemptions from reporting
More informationGUIDELINE FOR THE INSTALLATION AND OPERATION OF CONTINUOUS EMISSION MONITORING SYSTEMS (CEMS) AND THEIR USE FOR REPORTING UNDER THE PROVISIONS OF
GUIDELINE FOR THE INSTALLATION AND OPERATION OF CONTINUOUS EMISSION MONITORING SYSTEMS (CEMS) AND THEIR USE FOR REPORTING UNDER THE PROVISIONS OF REGULATION O.Reg. 127/01 Ontario Ministry of the Environment
More informationHackney Biomass Boiler Information Request Form
Hackney Biomass Boiler Information Request Form In common with other types of combustion appliances, biomass boilers are potentially a source of air pollution. Pollutants associated with biomass combustion
More informationConrex Steel Ltd. ite468 Rideau Street. Kingston, Ontario K7K 3B1. 468 Rideau Street
Ministry of the Environment and Climate Change Ministère de l Environnement et de l Action en matière de changement climatique ENVIRONMENTAL COMPLIANCE APPROVAL NUMBER 9418-A9CSB9 Issue Date: May 17, 2016
More informationOil and Gas Air Quality Regulations and Permitting
Oil and Gas Air Quality Regulations and Permitting Adam Berig Olsson Associates Colorado Springs Oil and Gas Committee Presentation February 2012 Who Regulates Air Quality? United States Environmental
More informationDillon Consulting Limited. Invenergy Solar Canada ULC. Woodville Solar Farm Renewable Energy Approval (REA) Draft Project Description Report
Renewable Energy Approval (REA) 10-3523 Prepared by Dillon Consulting Limited Submitted by Invenergy Solar Canada ULC Table of Contents Page 1.0 INTRODUCTION... 1 2.0 CONTACT INFORMATION... 1 3.0 AUTHORIZATIONS
More informationStatement of Basis SCA Tissue North America, LLC. 701-0055
Statement of Basis SCA Tissue North America, LLC. 701-0055 On December 26, 2012, the Department received SCA Tissue North America, LLC renewal Title V application. SCA is considered a major source for
More informationLANDFILL GAS TO ENERGY- COMBINED ENGINE AND ORC-PROCESS
LANDFILL GAS TO ENERGY- COMBINED ENGINE AND ORC-PROCESS Dr Petri Kouvo Helsinki Region Environmental Services Authority THIRD INTERNATIONAL SYMPOSIUM ON ENERGY FROM BIOMASS AND WASTE Venice, Italy 8-11
More informationPOTENTIAL TO EMIT SUMMARY FIBERIGHT, LLC HAMPDEN, MAINE
POTENTIAL TO EMIT SUMMARY FIBERIGHT, LLC HAMPDEN, MAINE s (Ton/Year) Thermal Flare Oxidizer Boiler#1 Boiler #2 Scrubber #1 Scrubber #2 Total Carbon Monoxide (CO) 6.91 2.90 43.59 24.90 78.3 Oxides of Nitrogen
More informationCONTENT COPY OF ORIGINAL
Halton Healthcare Services Corporation 1 Princess Anne Drive, Georgetown Halton Hills, Ontario L7G 2B8 Ministry of the Environment and Climate Change Ministère de l Environnement et de l Action en matière
More informationCAT CG132. Series Gas Generator Sets
CAT CG132 Series Gas Generator Sets CAT CG132 SMARTER ENERGY SOLUTIONS COMMERCIAL AND INDUSTRIAL FACILITIES Facilities such as manufacturing plants, resorts, shopping centers, office or residential buildings,
More informationDRAFT White Paper Asphalt (non-permitted) Strategy Evaluation Portland Air Toxics Solutions
DRAFT White Paper Asphalt (non-permitted) Strategy Evaluation Portland Air Toxics Solutions Table of Contents Introduction... 2 I. SOURCE CATEGORY: Asphalt (non-permitted)... 3 A. Source Category Description...3
More informationAMENDED ENVIRONMENTAL COMPLIANCE APPROVAL NUMBER 2152-A3YN6H Issue Date: November 13, 2015 L. & G. General Auto Body Limited. ite4656 Yonge Street
Ministry of the Environment and Climate Change Ministère de l Environnement et de l Action en matière de changement climatique AMENDED ENVIRONMENTAL COMPLIANCE APPROVAL NUMBER 2152-A3YN6H Issue Date: November
More information2014 Aamjiwnaang Air Monitoring Station Results. Ministry of the Environment and Climate Change April 19, 2016
2014 Aamjiwnaang Air Monitoring Station Results Ministry of the Environment and Climate Change April 19, 2016 Outline Key Results Parameters Measured Benchmarks 2014 Report Results Mobile Monitoring Results
More informationFUEL QUALITY REPORT BIOCNG GAS ANALYSIS NOVEMBER 2012
FUEL QUALITY REPORT BIOCNG GAS ANALYSIS NOVEMBER 2012 Prepared by: Mark J. Torresani, P.E. and Joseph J. Falle IV, P.E. 8413 Excelsior Drive, Suite 160 Madison, WI 53717 Rev. 0, 12/4/12 Project (enter
More informationBirmingham City University / Students Union Aspects and Impacts Register. Waste. Impacts description
Birmingham City University / Students Union and Impacts Register Waste Production of non - hazardous waste Production of hazardous waste Storage of non - hazardous waste Potential for waste to be disposed
More informationAs a minimum, the report must include the following sections in the given sequence:
5.2 Limits for Wind Generators and Transformer Substations In cases where the noise impact at a Point of Reception is composed of combined contributions due to the Transformer Substation as well as the
More informationCHAPTER 9 PERMITTING. 9.2 Scotland 102 9.2.1 Exemption 102 9.2.2 Waste management licence 102 9.2.3 PPC permit 102
CHAPTER 9 PERMITTING 9.1 England and Wales 100 9.1.1 T24 exemption for on-farm AD 100 9.1.2 T25 exemption for off-farm AD 100 9.1.3 Standard rules environmental permits 100 9.1.4 Standard rules for on-farm
More informationClean Up Your Fleet. Introducing a practical approach to cleaner, more efficient fleet operation
Clean Up Your Fleet Introducing a practical approach to cleaner, more efficient fleet operation The value of clean fleet management Reduce air pollution from your fleet Reduce greenhouse gas emissions
More informationConsultation response: PPC Technical Guidance Note 35 Anaerobic Digestion
Consultation response: PPC Technical Guidance Note 35 Anaerobic Digestion The Anaerobic Digestion and Biogas Association ( ADBA ) is the trade association that represents the range of interests and matters
More informationGuidance for developments requiring planning permission and environmental permits. October 2012 UNCLASSIFIED
Guidance for developments requiring planning permission and environmental permits October 2012 UNCLASSIFIED We are the Environment Agency. We protect and improve the environment and make it a better place
More informationTips from the Help Desk
Tips from the Help Desk Questions & Answers from the Source Registration (SR) Help Desk for some common problems and unusual situations Contents CTRL+Click the questions below to go to the answers. Tips
More informationEnergy from waste. Introduction. Legal status of this guideline. What is energy from waste? Draft guideline
Draft guideline Energy from waste Publication 1549 September 2013 Authorised and published by EPA Victoria, 200 Victoria Street, Carlton Introduction As outlined in Getting full value: the Victorian Waste
More informationEmission Facts. The amount of pollution that a vehicle emits and the rate at which
Average Annual Emissions and Fuel for Gasoline-Fueled Passenger Cars and Light Trucks The amount of pollution that a vehicle emits and the rate at which it consumes fuel are dependent on many factors.
More information5. State the function of pulveriser. The pulverisers are the equipments which are used to powdered coal.
413 POWER PLANT ENGINEERING PART-A 1. Define Power. Power is the rate at which energy is used (or) Energy/time. 2. What are the types of fuels? Solid fuel Liquid fuel Gaseous fuel (Any one among the above
More informationPennsylvania Marcellus Shale Short- Term Ambient Air Sampling Project
Pennsylvania Marcellus Shale Short- Term Ambient Air Sampling Project Marcellus Shale Conference November 16, 2011 Nick Lazor Chief, Air Quality Monitoring Division Bureau of Air Quality PA Department
More informationThermal Mass Flow Meters
Thermal Mass Flow Meters for Greenhouse Gas Emissions Monitoring Natural Gas Measurement for Emissions Calculations Flare Gas Monitoring Vent Gas Monitoring Biogas and Digester Gas Monitoring Landfill
More informationAssessment of Air Emissions Martin Marietta Materials Facilities on Highway 34, Weld County, Colorado Project No.: 4572.003
April 1, 2015 Mr. James Sharn 10170 Church Ranch Way, Suite 201 Westminster, Colorado 80021 Subject: Assessment of Air Emissions Facilities on Highway 34, Weld County, Colorado Project No.: 4572.003 Dear
More informationState of New Jersey. General Permit. For. Boilers and Heaters [Individually Less Than 10 MMBTU/HR]
State of New Jersey Department of Environmental Protection Air Quality Permitting General Permit For This General Permit allows for the construction, installation, reconstruction and operation of single
More informationTesoro Savage Vancouver Energy Distribution Terminal August 2013 Application No. 2013-01 Page 2-162
Crude Oil Storage Tanks The Facility includes six 360,000-bbl capacity crude oil storage tanks, each with a working capacity of approximately 340,000 bbl These tanks are subject to an NSPS that applies
More informationMBJ Environmental Programmes
MBJ Airports Limited Environmental Policy The following is MBJ Airports Limited s (MBJ) Environmental Policy for Sangster International Airport (SIA): Integrate environmental management measures with planning,
More informationA STUDY OF ENVIRONMENTAL BENEFITS OF INDUSTRIAL INTEGRATION
A STUDY OF ENVIRONMENTAL BENEFITS OF INDUSTRIAL INTEGRATION Presented to Hydrocarbon Upgrading Task Force Calgary, Alberta Presented By: AMEC EARTH & ENVIRONMENTAL Edmonton, Alberta June 2007 Objectives
More informationSIX REASONS TO DRY BIOGAS To A LOW DEWPOINT BEFORE COMBUSTION IN A CHP ENGINE STEVEN SCOTT MARKET DEVELOPMENT MANAGER ALTERNATIVE ENERGIES
SIX REASONS TO DRY BIOGAS To A LOW DEWPOINT BEFORE COMBUSTION IN A CHP ENGINE STEVEN SCOTT MARKET DEVELOPMENT MANAGER ALTERNATIVE ENERGIES Filippo Turra Product Manager Cooling Technology INTRODUCTION
More informationGENERATOR REGISTRATION REPORT. Part 1 Generator Identification
Part 1 Generator Identification Ministry of the Environment This report is (check one): An initial generator registration report An annual generator registration report A supplementary generator registration
More informationApproved baseline and monitoring methodology AM0056
Approved baseline and monitoring methodology AM0056 Efficiency improvement by boiler replacement or rehabilitation and optional fuel switch in fossil fuel-fired steam boiler systems I. SOURCE AND APPLICABILITY
More informationTips for a Successful Diesel Retrofit Project
Tips for a Successful Diesel Retrofit Project Tips for a Successful Diesel Retrofit Project Transportation and Climate Division Office of Transportation and Air Quality U.S. Environmental Protection Agency
More informationDate: 12 th December 2013
Mr Ross Taylor Parsons Brinckerhoff Amber Court William Armstrong Drive Newcastle Upon Tyne NE4 7YQ Our ref: EPR/FP3838EB/A001 Your ref: EPR/FP3838EB/RFI Date: 12 th December 2013 Dear Mr Taylor We need
More informationATTACHMENT B California Energy Commission Air Quality Self-Certification Checklist for Simple-Cycle Gas Turbine Generation Units
ATTACHMENT B California Energy Commission Air Quality Self-Certification Checklist for Simple-Cycle Gas Turbine Generation Units License Application for: [ X ] New Emissions Unit(s) at a New Stationary
More informationPEAK DISTRICT NATIONAL PARK AUTHORITY ENVIRONMENTAL MANAGEMENT ANNUAL PERFORMANCE REPORT 2013/2014
2009/10 2010/11 2011/12 2012/13 2013/14 2014/15 2015/16 2016/17 Carbon emissions (kgco2) Page 1 PEAK DISTRICT NATIONAL PARK AUTHORITY ENVIRONMENTAL MANAGEMENT ANNUAL PERFORMANCE REPORT 2013/2014 1. INTRODUCTION
More informationTransfer of 497 Richmond Street West to Build Toronto
STAFF REPORT ACTION REQUIRED Transfer of 497 Richmond Street West to Build Toronto Date: June 3, 2013 To: From: Government Management Committee Chief Corporate Officer Wards: Ward 20 Reference Number:
More information4. The role of fleets and fleet managers Role of REC?
4. The role of fleets and fleet managers Role of REC? 79% 5% 44% To grow by 50% by 2010 over 1998 Role of Fleets - Changing operating environment: national, local government incentives, disincentives -
More informationTorino Nord. Cogeneration Plant. The gas turbine. The steam generator. The Torino Nord cogeneration plant produces electricity and heat for district
PLANT TORINO NORD Iren Energia is the company in the Iren Group whose core businesses are the production and distribution of electricity, the production and distribution of thermal energy for district
More informationAddition of general construction conditions applicable to the portable emergency turbine because they were omitted from the original Part 70 Permit.
Ms. Heather N. Frosch Midwestern Gas Transmission P.O. Box 2511 Houston, Texas 77252-2511 Re: 153-11686 First Significant Permit Modification to Part 70 No.: T153-5975-00006 Dear Ms. Frosch: Midwestern
More informationContinuous flow direct water heating for potable hot water
Continuous flow direct water heating for potable hot water An independently produced White Paper for Rinnai UK 2013 www.rinnaiuk.com In the 35 years since direct hot water systems entered the UK commercial
More informationHolcim EMR List of EN Standards and VDI Guidelines usable for Discontinuous Measurements in Cement Plants
Holcim EMR List of EN Standards and VDI Guidelines usable for Discontinuous Measurements in Cement Plants Version 2004-01 / August 2004 (HGRS-JW-04-25s) HGRS-CTS/MT J. Waltisberg SUMMARY ( ) shall not
More informationControl Device Requirements Charts For Oil and Gas Handling and Production Facilities
Device Charts For Oil and Gas Handling and Production Facilities Purpose/Scope: The purpose of this document is to provide standardized guidance for use by the regulated community and air permit reviewers,
More informationWellington Inner City Improvements National War Memorial Park (Pukeahu) Certification Review
Wellington Inner City Improvements National War Memorial Park (Pukeahu) Air Quality (Dust) Certification Review 22 November 2012 [CAQMP1 TR] Prepared in association with: Document produced by: Apecx PO
More informationUnited States SECURITIES AND EXCHANGE COMMISSION Washington, D.C. 20549 FORM 8-K
United States SECURITIES AND EXCHANGE COMMISSION Washington, D.C. 20549 FORM 8-K CURRENT REPORT Pursuant to Section 13 or 15(d) of the Securities Exchange Act of 1934 January 19, 2006 Date of report (date
More informationSustainable Resource Management Ltd
6.0 Predicted nvironmental Impacts 6. Stages and Impacts Considered An nvironmental Impact Analysis has been carried out whereby all the possible environmental, socio economic and health & safety aspects
More informationBuilding Permit Application
Building Permit Application CBO: Don Reed / Inspector: Scott Richardson -All applications must be filled out in full -Residential applications will be issued or denied within 10 working days -Multi-residential
More informationENVIRONMENTAL STANDARDS FOR PETROLEUM OIL REFINERIES EMISSIONS. Standards for emissions from furnaces, boilers and Power Plant
ENVIRONMENTAL STANDARDS FOR PETROLEUM OIL REFINERIES EMISSIONS Standards for emissions from furnaces, boilers and Power Plant S. Parameter Limiting concentration in mg/nm 3, unless stated Existing refineries
More informationIn-Situ Remediation Strategies as Sustainable Alternatives to Traditional Options. Ryan Bernesky, B.Sc., P.Ag. February 26, 2013
In-Situ Remediation Strategies as Sustainable Alternatives to Traditional Options Ryan Bernesky, B.Sc., P.Ag. February 26, 2013 Outline Introduction to Contaminated Sites and Remediation Strategies In-Situ
More informationAir quality and biomass installations. A briefing for local authorities
Air quality and biomass installations A briefing for local authorities March 2011 Published by BioRegional Development Group BedZED Centre, 24 Helios Road, Wallington, Surrey SM6 7BZ. www.bioregional.com
More informationDavid Mezzacappa, P.E. SCS Engineers Contractor to U.S. EPA on LMOP
LMOP Workshop: LFG Collection & LFG Energy Technologies David Mezzacappa, P.E. SCS Engineers Contractor to U.S. EPA on LMOP Introduction Goal convert LFG into a useful energy form Technologies include:
More information4. The role of fleets and fleet managers
4. The role of fleets and fleet managers 79% 5% 44% To grow by 50% by 2010 over 1998 Role of Fleets - Changing operating environment: national, local government incentives, disincentives - Economies of
More informationElectrical infrastructure serving the city of London CITY OF LONDON. 2012 Corporate Energy Consumption Report
Electrical infrastructure serving the city of London CITY OF LONDON 2012 Corporate Energy Consumption Report September 2013 TABLE OF CONTENTS CORPORATE ENERGY MANAGEMENT - UPDATE... 3 1 CORPORATE ENERGY
More informationHalf the cost Half the carbon
Half the cost Half the carbon the world s most efficient micro-chp What is BlueGEN? The most efficient small-scale electricity generator BlueGEN uses natural gas from the grid to generate electricity within
More informationVogt Power Emission Control Solutions
ONE SOURCE ONE PURPOSE MANY SOLUTIONS Vogt Power Emission Control Solutions Kelly Flannery Kristen Cooper Andrew Heid Chief Thermal Engineer Simple Cycle Design Lead Emission Catalyst Design Lead Presented
More informationSustainable Schools 2009. Renewable Energy Technologies. Andrew Lyle RD Energy Solutions
Sustainable Schools 2009 Renewable Energy Technologies Andrew Lyle RD Energy Solutions RD Energy Solutions Energy efficiency and renewable energy consultancy Project management of installations Maintenance
More informationClean Diesel versus CNG Buses: Cost, Air Quality, & Climate Impacts
CONCORD, MA - MANCHESTER, NH - WASHINGTON, DC 1000 ELM STREET, 2 ND FLOOR MANCHESTER, NH 03101 603-647-5746 www.mjbradley.com DATE February 22, 2012 TO FROM RE: Conrad Schneider, Clean Air Task Force Dana
More informationAddition of general construction conditions applicable to the portable emergency turbine because they were omitted from the original Part 70 Permit.
Ms. Heather N. Frosch Midwestern Gas Transmission P.O. Box 2511 Houston, Texas 77252-2511 Re: 125-11685 First Significant Permit Modification to Part 70 No.: T 125-5976-00004 Dear Ms. Frosch: Midwestern
More informationVOCs Ambient Air Monitoring Report
VOCs Ambient Air Monitoring Report Pollution Control Department and Department of Environmental Quality Promotion Ministry of Natural Resources and Environment 2 List of abbreviations BKK ERTC GC/MS HAP
More informationCity of Bath Maine. A Small Landfill s Preliminary Evaluation of Carbon Credits and Renewable Energy Projects. December 11, 2008
City of Bath Maine A Small Landfill s Preliminary Evaluation of Carbon Credits and Renewable Energy Projects December 11, 2008 Presented by Michael Booth P.E. Presentation Background Bath s Approach to
More informationSite Identification No.: 197809AAO Application No.: 15030051
Project Summary for a Construction Permit Application from Midwest Generation for a Natural Gas Conversion Project for the Joliet Electric Generating Station Joliet, Illinois Site Identification No.: 197809AAO
More informationBP Texas City Refinery
BP Texas City Refinery ENVIRONMENTAL STATEMENT FOR YEAR 2010 (Review of Y2009 Performance) Introduction Recognizing the complex nature of petroleum refining operations and to ensure that we meet our stated
More informationWaste to Energy in Düsseldorf. for a clean city.
Waste to Energy in Düsseldorf for a clean city. Waste Management in Düsseldorf. Düsseldorf s public utilities company known as Stadtwerke Düsseldorf operates a waste to energy plant (WtE) that has been
More informationMonitoring of Total Suspended Particles & Toxic Gasses in Stationary Combustion Systems
ENGINEER - Vol. XXXXIV, No. 04, pp, [36-44], [37-45], 2011 The Institution of Engineers, Sri Lanka Monitoring of Total Suspended Particles & Toxic Gasses in Stationary Combustion Systems K T Jayasinghe
More informationEPA Requirements for Diesel Standby Engines In Data Centers. Bob Stelzer / CTO / Safety Power Inc. For 7x24 Fall 2014 Conference. 1.
EPA Requirements for Diesel Standby Engines In Data Centers Bob Stelzer / CTO / Safety Power Inc For 7x24 Fall 2014 Conference 1.0 Introduction In order to get the Air Emissions Permit for facilities that
More informationLandfill Gas In Ireland - The Facts
Landfill Gas In Ireland - The Facts Almost two million tonnes of municipal solid waste (MSW) were generated in Ireland in 1998, over 90% of which was consigned to landfill. At landfill, bacteria cause
More informationSulfur Tail Gas Thermal Oxidizer Systems By Peter Pickard
Sulfur Tail Gas Thermal Oxidizer Systems By Peter Pickard Introduction SRU s (Sulfur Recovery Units) are critical pieces of equipment in refineries and gas plants. SRUs remove sulfur compounds from certain
More informationVENTURA COUNTY AIR POLLUTION CONTROL DISTRICT 669 County Square Drive, Ventura CA 93003 805/ 645-1401 FAX 805/ 645-1444 www.vcapcd.
VENTURA COUNTY AIR POLLUTION CONTROL DISTRICT 669 County Square Drive, Ventura CA 93003 805/ 645-1401 FAX 805/ 645-1444 www.vcapcd.org AB 2588 COMBUSTION EMISSION FACTORS Emission factors for combustion
More informationPopulation Density, Traffic Density and Nitrogen Oxides (NOx) Emission Air Pollution Density in Major Metropolitan Areas of the United States
Population Density, Traffic Density and Nitrogen Oxides (NOx) Emission Air Pollution Density in Major Metropolitan Areas of the United States This report summarizes the latest Environmental Protection
More informationCongratulations! Your unique solar monitor ID is located on your monitoring unit as seen on this page.
Congratulations! Your unique solar monitor ID is located on your monitoring unit as seen on this page. To access your unique solar monitoring website, simply type: www.welserver.com/welxxxx/ into your
More informationSolar Thermal Systems
Solar Thermal Systems Design and Applications in the UAE Murat Aydemir Viessmann Middle East FZE General Manager (M.Sc. Mech.Eng., ASHRAE) Dubai Knowledge Village Congress Centre, Dubai 20.4.2009 Viessmann
More informationPE9.4 Corrected Report
PE9.4 Corrected Report STAFF REPORT ACTION REQUIRED Toronto s 2013 Greenhouse Gas Inventory Date: December 17, 2015 To: From: Wards: Reference Number: Parks and Environment Committee Chief Corporate Officer
More informationCombined Heat and Power: Local Authorities
Combined Heat and Power: Air Quality HP Guidance for Local Authorities About Environmental Protection UK Environmental Protection UK s vision is of a cleaner, quieter, healthier world. We seek changes
More informationIn 2012 the commercial sector natural gas demand was 201 billion cubic feet (bcf) or 2.01e + 23 thousand British thermal units (kbtu).
ENVIRONMENTAL SETTING The Southern California Gas Company (SoCalGas) provides natural gas to the City of Malibu. The City lies within the boundaries of the South Coastal distribution division. SoCalGas
More informationSAP 2012 IN A NUTSHELL
SAP 2012 IN A NUTSHELL The consultation version of the SAP 2012 methodology was published by the Department of Energy and Climate Change (DECC) on January 4th 2012. This article from Dyfrig Hughes of National
More informationSOIL-MAT ENGINEERS & CONSULTANTS LTD.
SOIL-MAT ENGINEERS & CONSULTANTS LTD. 130 LANCING DRIVE, HAMILTON, ONTARIO L8W 3A1 PHONE (905) 318-7440 FAX (905) 318-7455 E-MAIL: info@soil-mat.on.ca PROJECT NO.: SM 145464-E JANUARY 16, 2014 1371975
More informationWolverine Clean Energy Venture
Prepared for: Wolverine Power Supply Cooperative Cadillac, Michigan Supplement to CAA Section 112(g) MACT Auxiliary Boiler Amended Application No. 317-07 Wolverine Clean Energy Venture Rogers City, MI
More informationElement D Services Plumbing
Medical Vacuum and Gas PART 1 - GENERAL 1.01 OVERVIEW A. This section addresses medical vacuum, waste anesthetic gas disposal, compressed air, oxygen, nitrous oxide, nitrogen and carbon dioxide systems.
More informationErP made easy What does it mean to merchants? What does it mean to installers?
ErP made easy What does it mean to merchants? What does it mean to installers? On 26th September 2015, changes were introduced which affect space and water heaters sold and installed here in the UK and
More informationDraft Case Study for xx CDM Landfill Gas Project presented at a World Bank Workshop Page 1 of 16 BANDEIRANTES-SAO PAULO-BRAZIL FOR CASE STUDIES
Draft Case Study for xx CDM Landfill Gas Project presented at a World Bank Workshop Page 1 of 16 BANDEIRANTES-SAO PAULO-BRAZIL FOR CASE STUDIES OF CDM - LANDFILL GAS PROJECTS PRESENTED AT A WORKSHOP IN
More informationGuide to Applying for an Environmental Compliance Approval
Guide to Applying for an Environmental Compliance Approval ontario.ca/environment MINISTRY OF THE ENVIRONMENT Guide to Applying for an Environmental Compliance Approval This is a guide for persons applying
More informationDescription of Thermal Oxidizers
Description of Thermal Oxidizers NESTEC, Inc. is a full service equipment supplier specializing in solutions for plant emission problems. The benefit in working with NESTEC, Inc. is we bring 25+ years
More informationSolid Waste: Opportunities for Greenhouse Gas Emission Reduction in Sonoma County. Community Climate Action Plan
Solid Waste: Opportunities for Greenhouse Gas Emission Reduction in Sonoma County Community Climate Action Plan Prepared by Ken Wells For the Climate Protection Campaign www.climateprotectioncampaign.org
More informationThe Pipelines Regulations, 2000
PIPELINES, 2000 P-12.1 REG 1 1 The Pipelines Regulations, 2000 being Chapter P-12.1 Reg 1 (effective April 1, 2000) as amended by the Statutes of Saskatchewan, 2014, c.21. NOTE: This consolidation is not
More informationEffect of Self-Heat Circulation on VOCs Decomposition in Regenerative Thermal Oxidizer
Effect of Self- Circulation on VOCs Decomposition in Regenerative Thermal Oxidizer Shinsuke Iijima 1, Katsuya Nakayama 1, Koichi Ushiroebisu 1 Mitsuhiro Kubota 2 and Hitoki Matsuda 2 1. Engineering Division,
More informationThe regulators requirements for the operation of an AD facility. Gitty Ankers Senior Environment Officer Devon and Cornwall
The regulators requirements for the operation of an AD facility Gitty Ankers Senior Environment Officer Devon and Cornwall Cornwall Renewable Energy Show 27 July 2012 Introduction Waste past and present
More informationLatornell. Experiments in Climate Change Response in a Rapidly Urbanizing Region. November 20, 2008. By Brian Denney Chief Administrative Officer
Latornell Experiments in Climate Change Response in a Rapidly Urbanizing Region November 20, 2008 By Brian Denney Chief Administrative Officer Toronto has an ecological footprint 280 times its Eric Krause
More informationCHAIR AND MEMBERS CIVIC WORKS COMMITTEE MEETING ON MARCH 29, 2016 JAY STANFORD, M.A., M.P.A. DIRECTOR, ENVIRONMENT FLEET & SOLID WASTE
1 TO: FROM: SUBJECT: CHAIR AND MEMBERS CIVIC WORKS COMMITTEE MEETING ON MARCH 29, 2016 JAY STANFORD, M.A., M.P.A. DIRECTOR, ENVIRONMENT FLEET & SOLID WASTE LANDFILL GAS UTILIZATION STATUS OF OPPORTUNITIES
More informationPROPOSED EXCESS SOIL MANAGEMENT POLICY FRAMEWORK
PROPOSED ECESS SOIL MANAGEMENT POLICY FRAMEWORK TABLE OF CONTENTS 1.0 INTRODUCTION... 3 1.1 CONTET... 3 1.2 ENVIRONMENTAL BILL OF RIGHTS REVIEW... 4 2.0 NEED FOR A REVISED POLICY FRAMEWORK... 6 2.1 SUMMARY
More informationSULFUR RECOVERY UNIT. Thermal Oxidizer
SULFUR RECOVERY UNIT Thermal Oxidizer BURNERS FLARES INCINERATORS PARTS & SERVICE SULFUR RECOVERY UNIT Thermal Oxidizer Tail Gas Thermal Oxidizer designed and built to GOST-R requirements. Zeeco can meet
More informationBiomass Boiler House Best Practices. Irene Coyle & Fernando Preto CanmetENERGY
Biomass Boiler House Best Practices Irene Coyle & Fernando Preto CanmetENERGY Growing the Margins London, Ontario March 2010 The Biomass & Renewables Group of Industrial Innovation Group (IIG) of CanmetENERGY
More informationHot Water Heating: Technologies and Use
Hot Water Heating: Technologies and Use Skip Hayden Integrated Energy Systems CanmetENERGY Better Buildings by Design 2010 Burlington Vermont February 2010 Natural Resources Canada Ressources naturelles
More informationLower Hunter Ambient Air Quality Review of Available Data
Lower Hunter Ambient Air Quality Review of Available Data 2012 ACKNOWLEDGEMENTS The Australian Nuclear Science and Technology Organisation, ConPorts, GrainCorp, Newcastle City Council, BHP Billiton, Hunter
More informationLife-Cycle Assessment of McCarty Landfill Gas to CNG in California San Diego Metropolitan Transit System
Life-Cycle Assessment of McCarty Landfill Gas to CNG in California San Diego Metropolitan Transit System October 21 st, 2014; Updated August 25 th, 2015 Submitted to: BP Natural Gas and Power Prepared
More information