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<br />      								CLEARWA'TER
<br />  									G  R  O  U  P,   I  N  C
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<br />      								30       	CT'IVI FIELD A  	TIES      					l
<br />   		All  work  was  performed  in  accordance  with  Clearwater  Field  Proceedures
<br />   		(previously submitted) and under the directives and guidelines established by the
<br />   		PHS/EHD and the Regional,Water Quality Control Board
<br />   		The monitoring wells were gauged and sampled on December 28, 1994   Prior to
<br />   		sampling, all wells were purged of a minimum  of three saturated well volumes
<br />  1      	Well purging information is presented in Appendix A   The monitoring wells were,
<br />   		resampled on January 4, 1995, after the project courier failed to keep the samples
<br />   		adequately cool   In accordance with instruction from the PHS/EHD, no additional
<br />  '      	gauging or purging data was generated at this time
<br />   		Groundwater samples were collected from the monitoring ,wells using dedicated
<br />   		polyethylene bailers    Samples were labeled, documented  on a chain-of-custody
<br /> 	Y  	form, and placed in a cooler for transport to PACE, Inc  (PACE), a DHS-certified
<br />    		laboratory located in Novato, California    All groundwater samples were analyzed
<br />    		for  total  petroleum  hydrocarbons  as  gasoline  (TPHg)  by  EPA  Method  8015
<br />    		(modified), and for benzene, toluene, ethylbe'nzene and total xylenes (BTEX) by EPA
<br />    		Method 8020 (modified)
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<br />     							4.0 RESULTS AND DISCUSSION
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<br />    		4.1  Water Level Monitoring Data
<br />       										�°   								II
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<br />    		On December 28, 1994,,the depth to ground water in each of the wells ranged from
<br />    		27 81  to  29.13  'feet  below , grade     Groundwater  flow  was  determined  to  be
<br />`   		northwesterly at an approximate gradient of 0 031 foot/foot across most of the site
<br />  '       	In the northwest corner of the site, downgradient of the former tank excavation, the
<br />    		groundwater  flow  was  to  the  northwest  at  an  approximate  gradient  of' 0 013
<br />    		foot/foot.   Plotted  on the ,Groundwater Contour Map I (Figure 3)  this change in
<br />    		"gradient appears,as a'slight mounding of the water table' u1 the vicuuty of the former
<br /> 1
<br />    		USTs r  A simi"l"ar groundwater mound was apparent in,the same location�duruig the
<br />       	!     previous gauging'evr ent
<br />  						litei  S I   '
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<br />    		The site is unpaved; therefore itis,likelyrtAat; groundwater recharge through the
<br /> I l     r      a      	' I     III I     1 I   i' ' I I ; '     I,';     r 4 	1       I      	1       I ' 	I	!      I
<br />    		vadose 'zone,is''producing,1al cistern-effect'Ein' porous excavation',,backfill' !mater`ial,!`I! 1
<br />    		causing, this" mound  featur'e!;I` The  mounding will  continue  toI Ibe monitored 'in
<br />  '       	future  gauging  events,  and I`the  results  of  these- observations !documented  in
<br />    		subsequent reports
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