The current application gives one additional explicitly named location beyond the already retained closest Squamish boundary: Murrin Provincial Park. It does not provide a per-community result table for all the places in the Explorer in the material recovered by this bounded search.

TDR Table 6.7 (PDF page 146, printed page 36) gives the following Murrin totals including baseline and marine vessels: NO2 50.7 ug/m3 (1 hour), SO2 12.5 (1 hour), PM2.5 17.8 (24 hours), CO 522 (1 hour) and 375 (8 hours). The process-upset case includes both HP and LP flares, the heat medium furnace and thermal oxidizer at full load, LNG carrier and harbour assist tugboats; FortisBC sources are marked N/A (PDF 128–129/printed 18–19; 145/35). These are applicant model results, not measured park or residential exposure.

The NO2/SO2 values follow the report's three-year daily-maximum percentile conventions; PM2.5 follows its annual 98th-percentile daily-mean convention (PDF 115–116/printed 5–6). They are not absolute one-hour peaks during an actual flare event. NO2 uses ARM2 Coastal Sites conversion. PM includes secondary formation and deposition. The fixed baseline values are 41.6 NO2, 11.1 SO2, 17.7 daily PM2.5, 389.3 hourly CO and 338.4 eight-hour CO ug/m3 (PDF 119–120/9–10). This baseline is neither zero nor a synchronized hourly observation.

DMP Table 4.1 (PDF 176/printed 12) provides 16 sensitive-receptor coordinates in UTM Zone 10. sensitive-receptors.csv preserves every original ID, name, coordinate and page reference. Included are Squamish General Hospital (R2), Balsam Montessori Academy (R3), Brackendale Eagles Park (R7), Murrin Park (R9) and the estuary wildlife-management-area point (R12). R8 is expressly absent in the source. The hospital, school, estuary and R7 had no individual concentration rows recovered. R7 cannot stand for all of Brackendale, and Garibaldi Park cannot stand for Garibaldi Highlands.

The Murrin result table does not explicitly say R9, despite the corresponding park name in the receptor list. The closest Squamish boundary result has neither an explicit receptor ID nor coordinates. Those two joins should be confirmed before numerical points are placed on an interactive map.

Appendix D supplies spatial output maps: D.37–D.39 for process-upset NO2, SO2 and PM2.5 (PDF 361–363), and D.43–D.44 for vented H2S concentrations and estimated exceedance frequency (PDF 367–368). The maps have figure numbers rather than printed page numbers. Their contour labels are not named-community measurements or peak point values. In particular, 56.5 is a NO2 contour level in D.37; its appearance there does not resolve the earlier TAR narrative's 56.5 versus Table 6.7's 54.9. No concentrations were inferred from map colours or assigned to communities.

No named-community or sensitive-receptor venting result rows were recovered. The Table 6.9 domain maxima (TRS 278; H2S 160 ug/m3) must remain domain maxima. The venting assessment uses a continuously modelled five-year source and a separate assumed 96 event-hours/year for occurrence estimates (PDF 149–151/39–41). Exact per-receptor ranks, the five-year aggregation, and event/weather assumptions need the electronic output and post-processing.

The highest-value next request is an electronic, receptor-keyed results table plus its receptor definitions. The application itself specifies CONC.DAT concentration output, IQAPLOT receptor/source geometry output and a proposed Excel receptor exceedance list. data-requests.txt identifies the requested files and exact supporting pages. Binary output is documented as g/m3, whereas printed concentrations are ug/m3; retain that distinction when importing.

Coordinate caution: Table 4.1 gives UTM Zone 10 without datum; domain metadata says NAD83, and the CALPUFF input appendix specifies NAR-C. Map notes say NAD 1983 BC Environment Albers. This inventory preserves the original coordinates without conversion or georeferencing. Obtain the actual receptor file and CRS metadata before using a map image as a quantitative grid.

Scope: full-PDF text searches followed by targeted reading of air-report tables, definitions and appendices. Six relevant pages were rendered and visually checked. The remainder of the 4,149-page application largely contains unrelated water and ecological appendices; this was not a manual review of every page. Absence here does not establish that requested electronic files do not exist elsewhere. No simulation or production site changes were made.