Laserfiche WebLink
conductivity values. This well has historically exhibited relatively higher conductivities and TD5 <br />• concentrations than other Wadge wells: This may be attributable to the influence of spoil water at this site <br />as the well is located downgradient of reclaimed surface mined areas. Seven measured parameters at well <br />91M006 returned values outside of previously established ranges during 1994, again however, none are <br />believed to evidence mine impacts as the relatively short period of record available for this site contributes <br />to this result. Specifically at well 91M006, new minimum field wnductivity, alkalinity, and TDS values <br />along with new maximum field temperature and dissolved iron values were recorded in May. New minimum <br />pH, alkalinity, TDS, and sulfate values with new maximum dissolved lead and iron values were recorded <br />in October. <br />-~ Twentymile Sandstone: During 1994, two Twentymile Sandstone wells (006-BRDH-7 and 91M005) required <br />~` 1 monitoring for water levels and field parameters on asemi-annual basis. Monitoring requirements were <br />r''~yS completed with the exception of a water level measurement omission occurring in May 1994 at well 006- <br />BRDH-7. Field parameters obtained from the site but the water level was inadvertently not recorded. Well <br />006-BRDH-7 has historically exhibited extremely low pressure heads and it is unlikely significant variation <br />from the norm occurred in May. Tables 5 and 6 provide summaries of the 1994 Water Year data collected <br />at each site. Figures 11 through 14 provide graphical representations of water levels and selected water <br />quality parameters recorded at each site. <br />• The potentiomettic surface in the Twentymile Sandstone is also generally observed to slope from south to <br />north in monitored wells. During 1994, water levels were observed to remain stable with no mine impacts <br />apparent. However, a markedly lower water level is noted in well 91M005 relative to well 006-82-48A. <br />Well 91M005 was established in 1993 to replace well 006-82-48A which was mined through during 1993. <br />Although not required, full suite analyses on water quality samples drawn from we1191M005 were conducted <br />during 1994. Results are presented in Table 6. Field parameter measurements on both Twentymile <br />Sandstone wells monitored during 1994 returned values within anticipated ranges with no mine related <br />impacts evident. <br />Trout Creek Sandstone: During 1994, three Trout Creek Sandstone wells (001-83-106, 001-83-107, and <br />/ ~ FCM A'2) required monitoring for water levels and field parameters on asemi-annual basis. An additional <br />`\.t~ l well (008-75-EFC) required an annual water level measurement. Wells 001-83-106 and FCM N2 also <br />~~h required water quality sampling on a semi-annual basis. Three water level monitoring omissions occurred <br />during 1994. Field parameters were obtained in May from wells 001-83-106 and 001-83-107, however, <br />water levels were inadvertently not recorded. In addition, the required annual water level measurement at <br />well 008-75-EFC was not obtained. Changes in personnel during the latter part of 1993 and early 1994 <br />contributed to the inadvertent failure to monitor this location. TCC has identified this omission and taken <br />steps to ensure that required data will be obtained from this site in the future. Completion work on well <br />FCM Jl2 occurred during the summer of 1994. A subsequent water level measurement was obtained <br />September. Tables 7 through 10 provide summaries of the 1994 Water Year data collected at each site. <br />-3- <br />