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FIRST HALF 2006 SUBSIDENCE REPORT <br />IV. Vegetation Monitoring: <br />Vegetation monitoring (riparian survey) for the 16- and 17--Right Panel was performed <br />during athree-day period from August 30, 2005 through September 1, 2005. The <br />vegetation monitoring report, which evaluates any changes in riparian vegetation <br />conditions and chazacteristics for Fish Creek, relative to the measured baseline <br />conditions, is presented as an Appendix to this report. <br />V. Hvdrologic Monitoring: <br />During the first half of 2006, water quality data was collected from established sites along <br />Fish Creek in areas underlain by gate-roads or longwall panels, as well as from <br />representative downstream sites located away from the subsidence azea. <br />Hydrologic monitoring of potential subsidence impacts from the 17 and 18-Right Panels <br />utilizes three alluvial wells and three neazby surface sites. These sites aze shown on the <br />attached First Half 2006 Subsidence Map. These include alluvial Well AVF-14 and <br />associated surface Site SW-14 (upstream of 17-Right subsidence zone). Also utilized aze <br />alluvial Well 008-AU3 and associated surface Site 305 (downstream of 17-Right <br />subsidence zone). Note that Sites 305 and 008-AU3, were designated under TR03-42 as <br />subsidence monitoring sites. <br />Alluvial Well AVF-15 and associated surface site SW-15 are located between the two <br />sets of upstream and downstream sites, presently within a ponded subsidence zone. <br />Localized ponding occurred in this area in September/early-October of 2004, and has <br />persisted through the first half of 2006. <br />Hydrologic monitoring did not indicate significant water quality impacts to Fish Creek. <br />Summary tables of monitoring data for the subject surface sites and alluvial wells aze <br />attached. Note that seasonal fluctuations in the concentrations of some analytical <br />parameters (e.g. iron, conductivity, TDS, etc.) do occur at the surface sites. Increases in <br />iron concentration are often related to accumulation and leaching of iron-beating <br />strata/sediments during spring runoff erosion. Some elevated iron concentrations may <br />also be related to ponding effects (e.g. increased solids in ponded samples). <br />V. Conclusions: <br />Structures remained essentially unaffected during the period, with the exception of the <br />predicted impacts to the powerlines pazallel to the 19-Right Panel. No adverse impacts, <br />i.e. imminent failure of structures, were evident with regard to these structures. <br />2006_lstl-IaltSubReport.doc Page 2 of 3 11/14/2006 <br />