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Last modified
10/26/2007 12:15:24 PM
Creation date
12/9/2004 7:24:20 AM
Metadata
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Template:
Planning Files
Planning Files - Planning File #
3315
Planning Files - Type
Conditional Use Permit
Address
803 LARPENTEUR AVE W
Applicant
Roselawn Cemetery
Status
Denied
Date Final City Council Action
8/27/2001
Planning Files - Resolution #
9927
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<br />J' <br /> <br />rr <br />~j <br /> <br />Emission Test Report <br />EMCWA-2-08 <br />Section 3 <br />Revision: 0 <br />Date: September 30. 1999 <br />Page 5 of 33 <br /> <br />I <br />I <br /> <br />last duct bend after the secondary combustion chamber, and the Method 23 outlet train was <br />located nearest to the scrubber outlet. More turbulent flow expected at these locations may <br />explain the higher flow results obtained with the Method 23 trains. Because flow was <br />different at each traverse point at any given time across each sampling cross-section and <br />flow varied at each of those points during the course of a run, consistent flow results could <br />not be obtained among the trains used at the inlet or the outlet during any run. <br /> <br />Results of testing for total particulate matter are presented in Table 3-8. As indicated <br />from the data, inlet and outlet concentrations for each run were very similar, regardless of <br />condition thereby indicating that the scrubber had little, or no effect on particulate matter <br />removal. Data from particulate matter testing are found in Appendix H. <br /> <br />: j <br /> <br />~ ~ ] <br /> <br />3.4.2 Hydrogen Chloride Analysis Results <br /> <br />] <br />'"i,' <br />i '\ <br /> <br />Hydrogen chloride emission results are presented in Table 3-9 in units of both grams <br />per minute and pounds per hour. While, emissions appear to be lower at the scrubber <br />outlet than at the inlet for Condition 1, the HCI concentrations are too low at the inlet <br />relative to the outlet locations for removal efficiencies to be meaningful. HCI data are <br />included in Appendix E. <br /> <br />'1 <br />U <br /> <br />3.4.3 Metals Analysis Results <br /> <br />r-l <br />L <br /> <br />Metals results, blank corrected results and emission rates are shown in Tables 3-10 <br />through 3-12. Cadmium and lead emissions tend to increase with secondary combustion <br />chamber temperature increase; mercury emissions were less affected by temperature than <br />the other two metals. The increase in metals emissions with increasing temperatures is not <br />uncommon, however, the amount of cadmium and lead charged during each run may also <br />have contributed. The metals narrative report with analysts' results are included in <br />Appendix F. <br /> <br />u <br /> <br />3.4.4 Dioxin and Furan Results <br /> <br />] <br />[01 <br /> <br />Dioxin and furan results are provided in Tables 3-13 through 3-24, grouped by <br />condition. Tables 3-13 through 3-16 provide results for Condition 1 testing, Tables 3-17 <br />through 3-20 provide results for Condition 2 testing, and Tables 3-21 through 3-24 provide <br />results for Condition 3 testing. Results for each condition are presented first by total <br />amount found within a given homologue, next by the 2,3,7,S-substituted compounds, then <br />by the corresponding equivalent toxicity of 2,3,7 ,S-tetrachloro-dibenzo-dioxin for inlet and <br />outlet. The dioxin and furan narrative report is included in Appendix G. It should be noted <br /> <br />J <br /> <br />MRJ-AED\R49S1~ S3.wpd <br />
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