additional six-month lag compared to the concentration increases detected in the source zone, as expected due to the ten meter downgradient location of the sampling control plane and the low groundwater flow. The higher concentrations were detected throughout the center of the transect at MLS-10, and in the upper region of MLS-9. Table 3-3. Sages downgradient transect natural gradient concentrations. Values are molar sum of all chlorinated species in mM. Transect is MLS-9, MLS-10, MLS-11. Well Depth 12/1998 01/1999 05/1999 05/2000 03/2001 02/2002 10/2002 10/2003 06/2004 m bgs (mM) (mM) (mM) (mM) (mM) (mM) (mM) (mM) (mM) MLS-9 8.08 0.2487 0.3321 0.1325 0.0144 0.0682 0.4730 0.5224 0.0172 0.2264 8.69 0.2908 0.3424 0.3014 0.3758 0.3553 0.3399 0.4522 0.2790 0.0711 9.07 0.0360 0.0406 0.0847 0.0139 0.1896 0.1892 0.1187 0.7385 0.0261 9.45 0.0301 0.0114 0.0168 0.0105 0.0142 0.0295 0.0553 0.2308 0.0268 9.91 0.0063 0.0025 0.0180 0.0097 0.0650 0.0999 0.1349 0.1573 0.0474 12.2 0.0059 0.0008 0.0347 0.0037 0.0016 0.0096 0.0083 0.0031 0.0000 Mean 0.103 0.122 0.098 0.071 0.116 0.190 0.215 0.238 0.066 Std Dev 0.130 0.168 0.109 0.149 0.135 0.184 0.217 0.269 0.082 MLS-10 8.08 8.69 9.07 9.45 9.91 12.2 Mean Std Dev MLS-11 8.08 8.69 9.07 9.45 9.91 12.2 Mean Std Dev 0.0070 0.1904 0.3861 0.2835 0.1959 0.0019 0.176 0.168 0.0114 0.0476 0.0790 0.0381 0.1354 0.0011 0.060 0.050 0.0110 0.0062 0.0000 0.2140 0.1545 0.2046 0.3862 0.3280 0.8048 0.1855 0.3198 0.5237 0.3883 0.2352 0.4606 0.0017 0.0758 0.0109 0.195 0.194 0.361 0.190 0.143 0.348 0.0124 0.0127 0.0029 0.0765 0.0864 0.1447 0.1708 0.1518 0.2466 0.1396 0.1761 0.2332 0.1426 0.1107 0.1645 0.0009 0.0173 0.0016 0.106 0.108 0.158 0.068 0.062 0.098 0.0890 0.0410 0.0233 0.4228 0.4413 0.4515 0.3789 1.0312 0.0149 0.4049 0.3772 0.9959 0.4518 0.3887 0.8137 0.0063 0.0744 0.9836 0.249 0.376 0.566 0.224 0.405 0.505 0.0043 0.0060 0.0205 0.0718 0.1064 0.0815 0.1527 0.1344 0.0000 0.1724 0.2121 0.1235 0.1079 0.0948 0.0849 0.0005 0.0000 0.1363 0.101 0.110 0.085 0.068 0.076 0.053 In Figure 3-3, Surfer visualizations are presented. In most of the control plane, increases in detected concentrations were observed until peaking in year four, 2002, at 1.03 mM. Reductions in aqueous chlorinated concentrations were observed from in the peak in 2002 until the end of the sampling period in 2004, concluding at 0.33 mM. These changes will be further examined through mass discharge evaluation in the next section. 0.2877 0.1516 0.0016 0.0000 0.0320 0.0000 0.010 0.014 0.0157 0.0086 0.0164 0.0545 0.3002 0.0074 0.077 0.126 0.0004 0.2157 0.0000 0.3330 0.0088 0.0030 0.069 0.148 0.0002 0.0027 0.0102 0.0314 0.0058 0.0000 0.010 0.013