WAC 173-304-490
Groundwater monitoring requirements. (1) Applicability. These requirements apply to owners and
operators of landfills, piles, landspreading disposal
facilities, and surface impoundments that are required to
perform groundwater monitoring under WAC 173-304-400.
(2) Groundwater monitoring requirements.
(a) The groundwater monitoring system must consist of at
least one background or upgradient well and three down
gradient wells, installed at appropriate locations and depths
to yield groundwater samples from the upper most aquifer and
all hydraulically connected aquifers below the active portion
of the facility.
(i) Represent the quality of background water that has
not been affected by leakage from the active area; and
(ii) Represent the quality of groundwater passing the
point of compliance. Additional wells may be required by the
jurisdictional health department in complicated
hydrogeological settings or to define the extent of
contamination detected.
(b) All monitoring wells must be cased in a manner that
maintains the integrity of the monitoring well bore hole. This casing must allow collection of representative
groundwater samples. Wells must be constructed in such a
manner as to prevent contamination of the samples, the sampled
strata, and between aquifers and water bearing strata and in
accordance with chapter 173-160 WAC, Minimum standards for
construction and maintenance of water wells.
(c) The groundwater monitoring program must include at a
minimum, procedures and techniques for:
(i) Decontamination of drilling and sampling equipment;
(ii) Sample collection;
(iii) Sample preservation and shipment;
(iv) Analytical procedures and quality assurance;
(v) Chain of custody control; and
(vi) Procedures to ensure employee health and safety
during well installation and monitoring.
(d) Sample constituents.
(i) All facilities shall test for the following
parameters:
(A) Temperature;
(B) Conductivity;
(C) pH;
(D) Chloride;
(E) Nitrate, nitrite, and ammonia as nitrogen;
(F) Sulfate;
(G) Dissolved iron;
(H) Dissolved zinc and manganese;
(I) Chemical oxygen demand;
(J) Total organic carbon; and
(K) Total coliform.
(ii) The jurisdictional health department in consultation
with the department may specify additional or fewer
constituents depending upon the nature of the waste; and
(iii) Test methods used to detect the parameters of
(d)(i) of this subsection shall be EPA Publication Number
SW-846, Test Methods for Evaluating Solid Waste - Physical/Chemical Methods except for total coliform which
shall use the latest edition of Standard Methods for the
Examination of Water and Wastewater.
(e) The groundwater monitoring program must include a
determination of the groundwater surface elevation each time
groundwater is sampled.
(f) The owner or operator shall use a statistical
procedure for determining whether a significant change over
background has occurred. The jurisdictional health department
will approve such a procedure with the guidance of the
department.
(g) The owner or operator must determine groundwater
quality at each monitoring well at the compliance point at
least quarterly during the life of an active area (including
the closure period) and the post-closure care period. The
owner or operator must express the groundwater quality at each
monitoring well in a form necessary for the determination of
statistically significant increases.
(h) The owner or operator must determine and report the
groundwater flow rate and direction in the uppermost aquifer
at least annually.
(i) If the owner or operator determines that there is a
statistically significant increase for parameters or
constituents at any monitoring well at the compliance point,
the owner or operator must:
(i) Notify the jurisdictional health department of this
finding in writing within seven days of receipt of the
sampling data. The notification must indicate what parameters
or constituents have shown statistically significant
increases;
(ii) Immediately resample the groundwater in all
monitoring wells and determine the concentration of all
constituents listed in the definition of contamination in WAC 173-304-100 including additional constituents identified in
the permit and whether there is a statistically significant
increase such that the groundwater performance standard has
been exceeded, and notify the jurisdictional health department
within fourteen days of receipt of the sampling data.
(j) The jurisdictional health department may require
corrective action programs including facility closure if the
performance standard of WAC 173-304-460 (2)(a) is exceeded
and, in addition, may revoke any permit and require
reapplication under WAC 173-304-600.
(3) Corrective action program. An owner or operator
required to establish a corrective action program under this
section must, at a minimum with the approval of the
jurisdictional health officer:
(a) Implement a corrective action program that reduces
contamination and if possible prevents constituents from
exceeding their respective concentration limits at the
compliance point by removing the constituents, treating them
in place, or other remedial measures;
(b) Begin corrective action according to a written
schedule after the groundwater performance standard is
exceeded;
(c) Terminate corrective action measures once the
concentrations of constituents are reduced to levels below the
limits under WAC 173-304-460 (2)(a).
[Statutory Authority: Chapter 43.21A RCW. 85-22-013 (Order
85-18), § 173-304-490, filed 10/28/85.]