WAC 173-351-490
The hydrogeologic report contents. (1)
The hydrogeologic report shall meet all of the following
performance standards as follows:
(a) Examine existing site conditions for compliance with
groundwater and surface water location restrictions under WAC 173-351-130 and 173-351-140;
(b) Determine existing or background groundwater quality
conditions, including any groundwater contamination; and
(c) Define a detection groundwater monitoring program
capable of immediate and early warning detection for potential
contamination as required in WAC 173-351-400 and the
information required in subsection (2) of this section.
(2) The hydrogeologic report contents shall include the
following information:
(a) A summary of local and regional geology and
hydrology, including faults, zones of joint concentrations,
unstable slopes and subsidence areas on site; areas of
groundwater recharge and discharge; stratigraphy; erosional
and depositional environments and facies interpretation(s);
(b) A borehole program which identifies all performance
criteria of WAC 173-351-405 including lithology, soil/bedrock
types and properties, preferential groundwater flow paths or
zones of higher hydraulic conductivity, the presence of
confining unit(s) and geologic features such as fault zones,
cross-cutting structures etc., and the target
hydrostratigraphic unit(s) to be monitored.
(i) A minimum of twenty subsurface borings is required
for MSWLF sites which are 50 acres or less in aerial extent. For sites greater than fifty acres, twenty borings, plus three
borings for each additional ten acres thereafter, is required.
Soil borings shall be established in a grid pattern with a
boring in each major geomorphic feature such as topographic
divides and lowlands;
(ii) Each boring will be of sufficient depth below the
proposed grade of the bottom liner as to identify soil,
bedrock and hydrostratigraphic unit(s) conditions as required
in WAC 173-351-405.
(iii) The jurisdictional health department and the
department may approve alternate methods including geophysical
techniques, either surface or downhole including electric
logging, some sonic logging, nuclear logging, seismic
profiling, electromagnetic profiling and resistivity profiling
in lieu of some of the number of borings required in the
subsurface borehole program of (b)(i) of this subsection,
provided sufficient hydrogeological site characterization can
be accomplished and prior approval is obtained.
(iv) At each boring samples shall be collected from each
lithologic unit and tested for all of the following:
(A) Particle size distribution by both sieve and
hydrometer analyses in accordance with approved ASTM methods
(D422 and D1120);
(B) Atterburg limits following approved ASTM methods
(D4318); and
(C) Classification under the unified soil classification
system, following ASTM standard D2487-85.
(iv) Each lithologic unit on site will be analyzed for:
(A) Moisture content, following approved ASTM methods
(D2216); and
(B) Hydraulic conductivity by an in-situ field method or
laboratory method approved by the jurisdictional health
department and the department. All samples collected for the
determination of permeability shall be collected by standard
ASTM procedures.
(v) All boring logs shall be submitted with the following
information:
(A) Soil and rock descriptions and classifications;
(B) Method of sampling;
(C) Sample depth;
(D) Date of boring;
(E) Water level measurements;
(F) Soil test data;
(G) Boring location; and
(H) Standard penetration number of ASTM standard
D1586-67.
(vi) All borings not converted to monitoring wells or
piezometers shall be carefully backfilled, plugged and
recorded in accordance with WAC 173-160-420.
(vii) During the borehole drilling program, any on-site
drilling and lithologic unit identification must be performed
by a hydrogeologist, geologist or other qualified groundwater
scientist who is trained to sample and identify soils and
bedrock lithology.
(c) Depths to groundwater and hydrostratigraphic unit(s)
including transmissive and confining units;
(d) Potentiometric surface elevations and contour maps;
direction and rate of horizontal and vertical groundwater
flow;
(e) A description of regional groundwater trends
including vertical and horizontal flow directions and rates;
(f) All elevations and top of well casings shall be
related to the national geodetic vertical datum of 1929 (NGVD
29) and the horizontal datum shall be in accordance with
chapter 58.20 RCW, Washington Coordinate System and as amended
per chapter 332-130 WAC.
(g) Quantity, location, and construction (where
available) of private and public wells within a two thousand
foot (six hundred ten meter) radius of site;
(h) Tabulation of all water rights for groundwater and
surface water within a two thousand foot (six hundred ten
meter) radius of the site;
(i) Identification and description of all surface waters
within a one-mile (1.6 kilometer) radius of the site;
(j) A summary of all previously collected groundwater and
surface water analytical data, and for expanded facilities,
identification of impacts of existing facility of the
applicant to date upon ground and surface waters from landfill
leachate discharges;
(k) Calculation of a site water balance;
(l) Conceptual design of a groundwater and surface water
monitoring system, including proposed installation methods for
these devices and where applicable a vadose zone monitoring
plan, including well construction diagrams;
(m) Land use in the area, including nearby residences;
and
(n) A topographic map of the site and drainage patterns;
an outline of the waste management area and MSWLF units,
property boundary, the proposed location of groundwater
monitoring wells;
(o) Geologic cross-sections.
(3) Groundwater flow path analysis. The hydrogeologic
report shall include a summary groundwater flow path analysis
which includes all supportive documentation, and calculations
of the performance criteria of WAC 173-351-405.
[Statutory Authority: Chapter 70.95 RCW and 40 CFR 258. 93-22-016, § 173-351-490, filed 10/26/93, effective 11/26/93.]