Evaluation and Reporting on Contaminant Hydrogeological
12-12-01
Conditions at the Tajiguas Landfill
Page 21 of 24
A September 16, 1998, Regional Board comments on the August 12, 1998 Trench
Water Management Plan which disagreed with the County’s statement that, ". . some
of the steps necessary to implement the Proposed Trench System Plan are beyond
the control of the County." The Board also stated that the County’s Plan lacked
information regarding expected flow rates from the system during wet weather.
Specifically, the Board pointed out that their interim plan for spray application of the
collected liquid directly to an area on the western ridge line failed." Using direct
application to land as a primary means of for applying thousands of gallons of water
to already wet slopes may present stability problems, that concentrations of metals
may accumulate in the area of the spray field, that soil samples should be collected
and analyzed, that the proposed monitoring of runoff from the area did not specify
what was going to be monitored, that no criteria had been proposed as to how data
collected would be evaluated, and that no contingency plan had been made to
establish thir course of action if impacts from the spray field are detected.
(98 Correspondence.tif, Images 122 and 123)
An August 27, 1999 Regional Board letter to Santa Barbara County Public Works
stated that control of storm water discharge as required in the Board’s Notice of
Violation issued on June 19, 1998 had still not been completed after more than one
year and that the Board may implement formal enforcement actions. The Board
further stated that the County do not have adequate ability to control sediment-laden
runoff or other unforeseen releases of waste from the landfill.
(99 Correspondence.tif, Image 77 thru 79)
R
ECOMMENDATIONS
The following measures are necessary to ascertain the potential for impacts to
water quality and to determine the need for additional feasible corrective actions and
mitigation measures to reduce such impacts.
1) Define the contacts between the existing landfill mass and all man-made
conduits, all discernable artificial fill, disturbed soils, and formations through field
subsurface investigation. This will reveal conduits for the migration of landfill
contaminants to surface water and groundwater. All subsurface investigation
should be conducted through a conductor casing. A structure contor map of the
bottom of the landfill relative to GW table contout map should be produced to
provide crossesction of the bottom of the landfill relative to the water table.
Enegeneering designs must be developed and implemented for the purpose of