HomeMy WebLinkAboutBLD2021-00082-09A-Geotech ReportStratum Group File: 10.29.19B
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PO Box 2546, Bellingham, Washington 98227
May 3, 2021
Lisa Volkert
Re: Geologic Hazard Assessment
142 North Maple Street, Irondale, WA
Jefferson County Parcel 961804001
Dear Ms. Volkert:
This geologic hazard assessment was conducted to assess the risk of landslides and erosion on
the subject property. It is our understanding that you are planning to construct a new home,
driveway, and septic drainfield on the site. The property includes a shoreline bluff on the west
shore of Port Townsend Bay in Irondale.
Based on our geologic hazard assessment, it is our opinion that the proposed development on the
site will not be at risk of landslides or erosion for at least 100 years as long as it is located at least
35 feet from the top edge of the bluff. This setback distance will provide adequate protection
from potential future incremental bluff retreat and will also provide space behind the home to
prevent concentration of stormwater near the shoreline bluff. The site plan provided for the
development of the site indicates the home and septic will be located much more than 35 feet
from the top edge of the slope.
This geologic hazard assessment included a field inspection of the subject property and vicinity
including the upland area, shoreline bluff, and shoreline reach. Our evaluation also included
review of historic aerial photographs and maps, available geologic mapping, lidar (light detecting
and ranging) imagery, the proposed site plans, and our own notes and observations we have
made in the vicinity of the site and at locations with similar geologic conditions.
GENERAL GEOLOGY
The Geologic Map of the Port Townsend South and Part of the Port Townsend North 7.5-minute
Quadrangles, Jefferson County, Washington (Schasse and Slaughter, 2005) indicates that the
upland portion of the property is underlain by Vashon recessional delta deposits (Figure 1). The
shoreline bluff is mapped as mass wasting deposits (Figure 1). A level area at the base of the
bluff in the northeast corner of property is mapped as modified land.
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Figure 1. Clipped and annotated geologic map showing the subject property location. Qgod = Vashon recessional
delta deposits, Qmw = mass wasting deposits, Qml = modified land, Qga = Vashon advance outwash, Qgome =
Everson glaciomarine drift, Qf = fill material.
Our observations are generally consistent with the above described mapping. Machine dug test
pits on the upland portion of the property reveal moderately dense low cohesion medium sand
with gravel with scattered small cobbles consistent with Vashon recessional outwash (Figure 2).
Hand dug test pits on the slope revealed loose sand and gravel overlying moderately dense sand
and gravel of similar composition. Based on these observations, it is our opinion that the bluff is
underlain by a thin mantle of colluvium overlying Vashon recessional outwash deposits. This is
consistent with observations made along a steeper bluff face to the south of the subject property
where similar recessional deposits are found overlying Vashon till and Vashon advance
glaciolacustrine or glaciomarine deposits. The till and glaciolacustrine units are not indicated on
the map, but this is likely primarily due to the scale of the map.
Figure 2. Vashon recessional deposits on the subject property.
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Lidar imagery of the site (Figure 3) and vicinity shows a level area at the base of the bluff in the
northeast corner of the property. This level area is at least in part the result of filling and grading
that took place for historical iron works that included numerous iron kilns along waterfront. The
waterfront in this area was also modified by adding dredged material from the bay just to the
north as part of fill used for a log yard associated with a saw mill that was formerly located
further to the north. The historical use of this area is consistent with the mapping of the level
area at the base of the bluff as modified land.
While the area designated as mass wasting on the map on the steep shoreline bluff slopes is
consistent with our observations, we note that the wider mass wasting area designated to the
north of the subject property is actually a large area of modified land associated with the former
steel mill.
Figure 3. Lidar hillshade image showing modified land at the northeast corner of the property from historical iron
works and saw mill along the shoreline to the north.
SITE SPECIFIC OBSERVATIONS
The 1.26-acre subject property is located on a shoreline bluff on the western shore of Port
Townsend Bay in Irondale. An easement across the adjacent property to the southwest (parcel
961804003) will be used to access the site from North Maple Street.
Modified
land area
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The property is currently undeveloped. The upland portion of the property slopes gently to the
northeast (Figure 4). Measured slope angles in this area range from 0 to 11 degrees. The upland
portion of the property is predominantly covered in brush including Scotch broom, Nootka rose,
ocean spray and Himalayan blackberry. Trees on the perimeter of the previously cleared upland
area include western red cedar, red alder, and big leaf maple.
Figure 4. The gently sloping upland portion of the property.
The shoreline bluff on the property (Figure 5) is between 65 and 80 feet high. Measured slope
angles on the bluff ranged from 34 to 38 degrees. The bluff is essentially a planar angle of repose
slope. Vegetation on the bluff consists of mixed forest stands that include big leaf maple, western
red cedar, Douglas fir, and red alder with an understory including sword fern, snowberry, ocean
spray, thimbleberry, stinging nettle, and other brush. During our site investigation, we observed
evidence of minor soil creep and raveling on the bluff.
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Figure 5. The shoreline bluff on the subject property.
The northeast corner of the property below the bluff there is an elevated platform between the
base of the bluff and the shoreline (Figure 3). This platform is associated with the former iron
works and later saw mill that were formerly located at the base of the bluff along the shoreline at
and to the north of the property. Visible remnants of the ironworks on and near the subject
property include remnants of brick walls and scattered loose bricks from iron kilns along the
beach (Figure 6).
The shoreline reach fronting the subject property is characterized by a sand and gravel beach
with scattered cobbles (Figure 6). The lower beach face includes an abundance of small rocks
likely associated with the former iron works. There is also some slag material present. The beach
also contains abundant shell fragments. The beach has been altered significantly by past fill.
Much of the elevated platform consists of sand and shells from dredged material placed on the
shoreline to create a broad area for log storage to the north (Shipman, Gravel Beach Blog). Some
of this sand and shell material has eroded and makes up a significant portion of the current beach
(Figure 6). The beach to the north was again modified immediately to the north of the subject
property during a cleanup of the former iron works site and included the addition of additional
beach material, placement of logs and site grading post cleanup work (GeoEngineers, 2014).
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Figure 6. The shoreline reach at the subject property. View is to the north. Note kiln bricks and rocks as well as
significant shell material derived from the dredge fill material to the north.
Maximum fetch at the site is approximately 9 miles northeast across Port Townsend Bay and
across Admiralty Inlet to Whidbey Island. Despite this relatively large fetch in one direction, the
site is relatively protected in all other directions due to its position in Port Townsend Bay.
SHORELINE PROCESSES
Shoreline landform and drift mapping completed by Coastal Geologic Services (2013) for the
Washington State Department of Ecology mapped the subject property shoreline as a transport
zone (Figure 7). Transport zones are areas where sediment is transported by wave and current
movement along the beach, but little to no sediment is being added to the beach by erosion of the
bluff area above the beach. The shoreline just south of the property is mapped as a feeder bluff.
The shoreline drift or sediment transport direction along the shoreline has been mapped as
towards the north at the subject property. The transport direction shifts to the south a few
hundred feet south of the property.
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Figure 7. Annotated Washington Coastal Atlas coastal landforms map showing the subject property location.
Our site observations and interpretations are consistent with the above described shoreline
mapping. We did not observe any evidence of wave erosion at the base of the bluff on the subject
property. However, we did observe evidence of wave erosion at the base of the bluff and shallow
landsliding approximately 300 to 600 feet south of the subject property. We have observed some
minor erosion of the elevated area of the beach fill material to the north, but no significant
erosion was noted at the subject property itself. It appears that there is a small area of accretion at
the south end of the dredge platform at the subject property as the dredge platform protrudes out
from the base of the bluff and has modified the shoreline transport at the subject property
creating an area where the beach has moderately been filled in and widened south of the dredge
fill area Figure 8.
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Figure 8. Shoreline at the subject property.
GEOLOGIC HAZARD ASSESSMENT
During our site investigation, we did not observe any evidence of previous, ongoing, or incipient
landsliding on the subject property. We also did not observe any groundwater perching, seepage,
or springs. There are no conditions on the bluff slope that portend future landslides. Observed
shallow landsliding on the steep bluff approximately 300 to 600 feet south of the subject
property is caused by groundwater perching within recessional sand and gravel overlying
compact glaciolacustrine or glaciomarine silts and clays as well as till. However, these perching
layers are not present on the subject property.
The bluff on the site is essentially an angle of repose plainer slope. Therefore, top of bluff retreat
will be minor as long as no erosion takes place at the base of the base of the bluff.
The shoreline waterfront at much of the property and to the north has been significantly altered
dating back to the waterfront kilns associated with the iron works, the later dredge material fill
placed on the shore associated with the saw mill that used the fill area as a log storage yard and
the most recent addition of beach material and fill associated with the environmental remediation
at the former iron and steel works. The cleanup as built drawings (GeoEngineers, 2014) indicates
that the kiln foundations were left in place (we observed some of the kiln foundations) and the
shoreline beach was built up including gravel beach nourishment to the north of the site.
The result of the fill material and kiln foundation locations is such that we do not anticipate base
of bluff erosion will take place for many decades into the future. The fill platform, kiln
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foundations and beach nourishment are effectively precluding erosion of the base of the bluff at
the subject property.
Keuler (1988) mapped the shoreline at the subject property as an approximately neutral coastal
segment of little erosion or deposition. We concur with Kueler (1988) that this shore reach is
subject to little erosion. The lack of erosion is primarily due to the placement of fill immediately
to the north that has pushed the beach outward well away for the base of the bluff.
For determining the appropriate home location setback from the top edge of the bluff, we used an
average rate of bluff retreat of 2 inches per year at the subject property. Given the lack of erosion
and shoreline processes described above, 2 inches per year is a very conservatively high rate.
Using this conservatively high bluff retreat rate, the bluff should be expected to retreat
approximately 17 feet over the next 100 years.
We do note that the underling soils on the bluff slope consist of sand that may be susceptible to
erosion. We recommend an additional 15 feet be added in order to create ample space to allow
for infiltration of stormwater.
Yhe site plan for the home and septic have the home set approximately 80 feet back from the top
edge of the bluff and the septic drainfield located approximately 65 feet back from the top edge
of the bluff at its closest point.
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CONCLUSIONS AND RECOMMENDATIONS
Based on our geologic hazard assessment, it is our opinion that a proposed home on the site will
not be at risk of landslides or erosion for at least 100 years as long as it is located at least 35 feet
from the top edge of the bluff. This distance will provide adequate protection from potential
incremental bluff retreat and will also provide space behind the home to for stormwater
infiltration without impacts to the bluff slope. Based on site plans the home will be located
approximately 80 feet back from the top edge of the bluff slope and the septic drainfield will be
approximately 65 feet back from the top edge of the bluff at its closest location.
Stormwater management: Stormwater from the home should be dispersed or infiltrated on site in
the vicinity of the home consistent with the Stormwater Management Manual for Western
Washington. Stormwater should not be concentrated within 15 feet of the top of the bluff. The
site plan indicates stormwater will be dispersed approximately 70 feet back from the top edge of
the slope.
Vegetation management: Tree removal on the bluff should be limited to hazard tree removal.
Clearing on the bluff will lead to an increase in raveling and bluff retreat due to reduced soil root
strength. Limbing of trees for view corridors is acceptable and topping of big leaf maple trees is
acceptable.
Yard Waste and Debris: No yard waste or dead vegetation should be disposed of on or near the
top of the bluff. Yard waste and debris may become a wet unstable mat that can slide down and
damage the slope and increase the frequency of slope failure and raveling. The waste also kills
vegetation and damages root structures that support slopes.
Stratum Group appreciates the opportunity to be of service to you. Should you have any
questions regarding this assessment please contact our office at (360) 714-9409.
Sincerely yours,
Stratum Group
Dan McShane, L.E.G., M.Sc. Geoff Malick, L.G., M.Sc.
Licensed Engineering Geologist Licensed Geologist
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References:
GeoEngineers, 2014. As-Built Report Shoreline Habitat Restoration Irondale Iron and Steel
Plant.
Keuler, R.F., 1988. Map showing coatsal erosion, sediment supply, and longshore transport in
the Port Townsend 30- by 60-Minute Quadrangle, Puget Sound Region, Washington.
USGS Map I-1198-E.
MacLennan, A.J., J.W. Johannessen, S.A. Williams, W. J. Gerstel, J.F. Waggoner, and A.
Bailey, 2013. Feeder Bluff Mapping of Puget Sound. Prepared by Coastal Geologic
Services, for the Washington Department of Ecology and the Washington Department of
Fish and Wildlife. Bellingham, Washington. 118p. 42 Maps.
Schasse, H.W. and Slaughter, S.L., 2005. Geologic Map of the Port Townsend South and Part of
the Port Townsend North 7.5-minute Quadrangles, Jefferson County, Washington.
Washington Division of Geology and Earth Resources, Geologic Map GM-7.
Shipman, H, Gravel Beach Blog multiple posts under Irondale.
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