Wash. Admin. Code § 173-351-405 - Performance standards for groundwater monitoring system designs
Groundwater monitoring well placement.
The groundwater monitoring system design must meet the following performance criteria:
(1) A
sufficient number of wells must be installed at appropriate locations and
depths to yield representative groundwater samples from those
hydrostratigraphic units which have been identified as the earliest target
hydraulic pathways and conduits of flow for groundwater and contaminant
movement, and storage.
(2) The
number, spacing, and depths of monitoring wells must be based on the site
characteristics including the area of the MSWLF unit and the hydrogeological
characterization of WAC
173-351-490, and requires a
demonstration based on all of the following information:
(a) A groundwater flow path analysis which
supports why the chosen hydrostratigraphic unit best serves the installation of
a detection or assessment groundwater monitoring well system capable of
providing early warning detection of any groundwater contamination.
(b) Documentation and calculations of all of
the following information:
(i)
Hydrostratigraphic unit thicknesses including confining units and transmissive
units;
(ii) Vertical and horizontal
groundwater flow directions including seasonal, man-made, or other short term
fluctuations in groundwater flow;
(iii) Stratigraphy and lithology;
(iv) Hydraulic conductivity; and
(v) Porosity and effective
porosity.
(3)
Hydraulically placed upgradient wells (background wells) must meet the
following performance criteria:
(a) Must be
installed in groundwater that has not been affected by leakage from a MSWLF
unit; or
(b) If hydrogeologic
conditions do not allow for the determination of a hydraulically placed
upgradient well then sampling at other monitoring wells which provide
representative background groundwater quality may be allowed.
(4) Hydraulically placed
down-gradient wells (compliance wells) must meet the following performance
criteria:
(a) Represent the quality of
groundwater passing the relevant point of compliance specified by the
jurisdictional health department. The downgradient monitoring system must be
installed at the relevant point of compliance specified by the jurisdictional
health department during the permitting process of WAC
173-351-700 or through the permit
modification process of WAC
173-351-720(6).
Additional wells may be required by the jurisdictional health department based
upon areal extent of the MSWLF unit, complex hydrogeologic settings or to
define the extent of contamination under WAC
173-351-440 and
173-351-450.
(b) When physical obstacles preclude
installation of groundwater monitoring wells at the relevant point of
compliance at existing units, the downgradient monitoring system may be
installed at the closest practicable distance hydraulically down gradient from
the relevant point of compliance that ensures detection of groundwater
contamination in the chosen hydrostratigraphic unit.
(5) All monitoring wells must be cased in a
manner that maintains the integrity of the bore hole. This casing must be
screened or perforated and packed with gravel or sand, where necessary, to
enable collection of samples. The annular space between the bore hole and well
casing above the sampling depth must be sealed to prevent corruption of samples
and contamination of groundwater. All wells must be constructed in accordance
with chapter 173-160 WAC, Minimum standards for construction and maintenance of
water wells and chapter 173-162 WAC, Regulation and licensing of well
contractors and operators. All wells must be clearly labeled, capped, and
locked.
(6) The owner or operator
must apply for a permit modification under WAC
173-351-720(6)
or must apply during the renewal process of WAC
173-351-720(5),
for any proposed changes to the design, installation, development, and
decommission of any monitoring wells, piezometers, and other measurement,
sampling, and analytical devices. Upon completing changes, all documentation,
including date of change, new well location maps, boring logs, and well
diagrams must be submitted to the jurisdictional health department and must be
placed in the operating record of WAC
173-351-200(10).
(7) All monitoring wells, piezometers, and
other measurement, sampling, and analytical devices must be operated and
maintained so that they perform to design specifications throughout the life of
the monitoring program.
(8) The
groundwater monitoring system and hydrogeologic report including any changes to
the groundwater monitoring system must be prepared by a geologist or other
licensed professional in accordance with the requirements of chapter 18.220
RCW, Geologists.
(9) The
groundwater monitoring system design and hydrogeologic report must be made a
part of the permit application in accordance with WAC
173-351-730(1)(b)(iii).
Notes
Statutory Authority: RCW 70.95.020(3), 70.95.060(1), and 70.95.260(1), (6). 12-23-009 (Order 07-15), § 173-351-405, filed 11/8/12, effective 12/9/12. Statutory Authority: Chapter 70.95 RCW and 40 CFR 258 . 93-22-016, § 173-351-405, filed 10/26/93, effective 11/26/93.
State regulations are updated quarterly; we currently have two versions available. Below is a comparison between our most recent version and the prior quarterly release. More comparison features will be added as we have more versions to compare.
No prior version found.