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effected the static water level in CEC'e monitoring wells. PH Levels The pH levels recorded on pages 6-8 are the data taken from in-house tfield> recordings. Aa you knor, CEC continued to dorn size in 1993; chile this is essential to our operation, inconaiatenciea do occur. It is hard to replace individuals rho are knorledgeable and technically qualified with a multi-assignment, multi-3ob-role individual. While, the field meter calibrations could have been incorrect, I feel that both the meter calibration end the individuals taking the reading need to be more consistent. CEC rill make sure this is corrected in the future. The laboratory pH levels are consistent throughout the year tSee Attached). The field readings should be relatively close to the laboratory analysis varying no more than 1 point. AMW-2 Unlike, AMW-1 rhich is completed correlation to the existing subs located at the south west corner realistically completed directly ground rater. AMW-2 is located farthest easterly, dorn gradient area. in a undisturbed area, with a direct ~rface rater table and SMW-2 which is of the permanent spoil area and is adjacent to the original subsurface in "A" Pit spoil material and ie the monitoring cell in the disturbed Ground-rater floc is to the northeast across the mine site and is largely controlled by the top of bedrock rhich also slopes to the northeast (SEE Section 2.04.7 Permit). Therefore, AMW-2 ie essentially cut-off from the natural subsurface rater migration by "A" Pit to the south and massive disturbed amounts of spoil to the east. Aa the subsurface rater table recharge activities occur in the mined out areas, AMW-2 rill more than likely be the last Well to confirm stabilization of ground-rater. Vecetation CEC hoe solicited Savage and Savage to address permit defects in our Reclamation Plan and to carry out the Vegetation Study for 1994. Mr. Michael Savage discussed our circumatancea with Mr. Waldron directly and came to an agreement over issues that needed to be addressed. (See Savage and Savage Attached)