HomeMy WebLinkAbout3307; CARLSBAD BLVD SHORE PROTECTION; FEASIBILITY STUDY; 1984-11-01FEASIBILITY STUDY
CARLSBAD BOULEVARD
SHORE PROTECTION
CARLSBAD BEACH STATE PARK
FOR THE
City of Carlsbad
by
Woodward-Clyde Consultants
November 1984
Project No. 54268E-0002 Woodward-Clyde Consultants
TABLE OF CONTENTS
Page
INTRODUCTION
GENERAL SITE CONDITIONS 3
Surface Conditions 3 Bluff and Beach Conditions 4 Geologic and Groundwater Conditions 5 Bluff Erosion 6 Tide, Wind and Wave Climate 8
STATEMENT OF PROBLEM 10
PRELIMINARY ENGINEERING DESIGN CRITERIA 15
PROPOSED PRELIMINARY DESIGN 16
ECONOMIC CONSIDERATION 18
Construction Cost Estimate 18 Maintenance Cost Estimate 19 Benefit Estimate 20 Benefit Cost Ratio 21
REFERENCES 22
FIGURES
Location Map
Site Plan and Location
Pictures at Hemlock and Tamarack Avenues
Pictures at Ocean Street and Juniper Avenue
Bluff Profiles - Tamarack and Hemlock Avenues
Bluff Profiles - Acacia and Chestnut Avenues
Profiles - Walnut Avenue and Ocean Street
Conceptual Design Section - Riprap Revetment
Conceptual Design Section - Reinforced Earth
Concrete Seawall
Conceptual Design Section - Cribwall
APPENDIXES:
A. GEOLOGIC INVESTIGATION
Field and Office Investigation A-i
Geologic Setting A-i
Geologic Units and Erosion Characteristics A-2
Geologic Structure A-3
Woodward-Clyde Consultants
TABLE OF CONTENTS (CONT.)
Page
APPENDIXES (CONT.)':
GEOLOGIC INVESTIGATION (CONT.)
Ground Water Conditions A-3 Seismicity and Faulting A-4 Bluff Erosion and Slope Stability A-4
COASTAL DATA AND ENGINEERING DESIGN CALCULATIONS
Evaluate Deepwater Wave B-i Check Largest Wave That Will Break on Seawall B-3 Design of Stone B-4 Wave Run-up B-4
BENEFIT CALCULATIONS
Loss of Property C-i Loss of Beach User Benefits C-i Loss of Bicycle Lane Use C-i Traffic Reduction Costs C-2 Facility Replacement Costs C-2
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Woodward. Clyde Consultants
FEASIBILITY STUDY
CARLSBAD BOULEVARD SHORE PROTECTION
CARLSBAD BEACH STATE PARK
CARLSBAD, CALIFORNIA
INTRODUCTION
The subject portion of Carlsbad Beach State Park is approximately 4500 feet
long and generally located along the coast between Oak Street and the
entrance to Agua Hedionda Lagoon in the City of Carlsbad, California (See
Figure No. 1). It is bounded by Carlsbad Boulevard and Ocean Street on
the east and the Pacific Ocean on the west. A 20 to 40 foot high bluff is
situated between Carlsbad Boulevard and the beach .Carlsbad Boulevard is a
main thoroughfare along the Pacific Coast in the City of Carlsbad (See Figure
No. 2). For a couple of miles, Carlsbad Boulevard runs parallel with and
adjacent to Carlsbad State Beach and is the primary access to the beach in
this area. Carlsbad Boulevard is also the only roadway west of Interstate
Highway 5 to cross Agua Hedionda Lagoon. Therefore, it not only carries a
large amount of north-south traffic, but also has all the area's major utilities
buried beneath the roadway. In the subject area, approximately 3,500 feet
of roadway with the included utilities is constructed on a 30 to 40 foot high
bluff of relatively easily eroded sandy terrace deposit which backs the beach
from Pine Avenue to Sequoia Avenue (See Pictures - Figures Nos. 3 and 4).
At the south end, the Boulevard drops down in a length of about 500 feet to
an elevation of approximately +20 feet at the bridge across the inlet to Agua
Hedionda Lagoon. At the north end of the project Ocean Street extends
along the bluff top for about 500 feet between Pine and Oak Avenues.
The beach here is historically thin and narrow. Almost every year the winter
storms strip away the thin layer of sand, leaving a discontinuous layer of
cobbles over the wave cut bedrock platform. Then the spring and summer
swells rebuild the beach with another thin layer of new sand. During the
more severe winter storms, the large waves rush across the cobble beach and
attack and undercut the upper portion of the bluff.
Project No. 54268E-0002 Woodward-Clyde Consultants
During the storms of 1983, a few areas of the bluff eroded back to the edge
of the roadway requiring the City of Carlsbad to make emergency repairs in
the most critical areas. Due to the exposure to storm waves along this
stretch of shoreline, •and the easily erodible characteristic of the bluff,
continuing erosion is inevitable without construction of some type of shoreline
protection.
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Project No. 54268E-0002 Woodward-Clyde Consultants
GENERAL SITE CONDITIONS
Surface Conditions
North of Agua Hedionda Lagoon, Carlsbad Boulevard extends generally
parallel to and along the top of the bluff above Carlsbad Beach State Park.
The boulevard is generally set back from the bluff edge distances varying
between as little as 2 feet to as much as 50 feet. Public parking is available
along the west side of Carlsbad Avenue between Tamarack and Cherry
Avenue. At the intersection of Pine Avenue, Carlsbad Boulevard turns
inland away from the coastal bluffs. At this point, Ocean Street continues
northerly adjacent to the bluff top. Parking is also available along Ocean
Street. Private homes have been built- along the top of the bluff north of
Oak Avenue.
At the south end of the study area, two parallel rock jetties extend seaward
about 200 feet from the mouth of Agua Hedionda Lagoon. A paved public
parking area is located north of the jetties and generally south of Tamarack
Avenue. The parking area includes approximately 2 acres and is located
generally west of and below Carlsbad Boulevard along the toe of the bluff.
Grading for the parking area apparently consisted of placing fill from the
back beach area, adjacent to the toe of the bluff, out to near the end of the
jetties. This resulted in a relatively level pad several feet above the
elevation of the beach. Some rock riprap has been placed along the seaward
limits of the northern portion of the parking area as a means of temporary
slope protection. The riprap generally consists of a single layer of 2 to 4
ton stone placed upon a cobble berm.
A local park area, which extends along a portion of the top of the bluffs,
consists of a landscaped picnic area with a concrete walkway leading generally
through the picnic area and along the top of the bluff. This park extends
from south of Tamarack Avenue north to approximately Cherry Avenue. The
landscaping includes trees, grassy areas, picnic tables and a low wooden
railing along the top of the bluff. A public restroom is located near the top
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of the bluff near Tamarack Avenue. Public beach access stairways, which
lead down from the top of the bluff, are located at the restroom facility
(Tamarack Avenue) and across from Cherry Avenue. A vehicular beach
access ramp is also located near the north end of the park at Ocean Street.
Beach access is also available at the parking lot at the south end of the
park. The public access at Cherry Avenue consists of a concrete stairway
elevated several feet above the bluff by columns and pier foundations. The
stairway was originally located adjacent to a second public restroom located at
beach level. During the winter storms of 1983, this restroom, and the lower
stairway landing were heavily damaged by storm waves and were subsequently
demolished and removed. Portions of the concrete-slab foundations below the
old restroom area remain in place on the beach. The stairway landing has
been repaired and replaced with a wooden structure. A portion of the
natural slope below the upper landing has been rebuilt with stacked
sand-filled sacks.
Drain pipes are located upon the bluff at many locations. Several of the
pipes lead down from storm drains and man-holes located along Carlsbad
Boulevard to concrete box culverts built at the toe of the bluff. Other pipes
collect surface water run off from along Carlsbad Boulevard and adjacent
areas. It is our understanding that these pipes are to be relocated and
surface water runoff diverted away from the bluffs , as part of a future
improvement project.
Bluff and Beach Conditions
The coastal bluffs along Carlsbad Beach generally rise between 30 to 40 feet
above the beach. Elevations along the top of the bluff range from about 40
to 50 feet above sea level (Mean Sea Level Datum). Gullies and deep ravines
are developed nearly continuously along the face of the bluff. Many of the
wider, more extensively gullied areas extend -from the beach level up to the
top of the bluff. The upper portions of many of the deeper gullies and
ravines have been partially filled with material dumped from the top of the
bluff. The materials used for the dumped fill include concrete and asphalt
p rubble.
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As part of this study, topographic profiles of the coastal bluffs were
surveyed at the six locations, shown on Figure 2. The results of the
topographic profiles are shown as Figures 5, 6 and 7. Typical bluff
inclinations range from about 1:1 to 2:1 (horizontal to vertical) with localized
steeper and flatter areas. In general, the steepest portion of the bluffs lies
along the toe of the bluff at the back edge of the beach. Along much of the
area, a relatively flat sandstone ledge which is typically 15 to 20 feet wide is
exposed along the base of the bluff.
Much of the bluff face is barren; vegetation along the bluff consists of
scattered patches of iceplant and native grasses with locally dense stands of
bamboo.
The beach along the base of the bluffs is typically about 100 to 150 feet
wide. Abundant cobbles form a low berm several tens of feet wide along the
back edge of the beach. Seasonal variations in longshore drift, wave height
and wave frequency result in varying beach levels and volumes of sand. The
slope of the beach generally ranges from approximately 12:1 to 10:1 where
sand is predominant and 6:1 to 5:1 where cobbles are predominant. Recent
profile measurements by Scripps Institution of Oceanography indicate that the
bottom slope starting at approximately 100 to 150 feet offshore is about 40:1
or flatter.
Geologic and Groundwater Conditions
The upper portion of the coastal bluffs along Carlsbad Beach State Park are
composed of Late Pleistocene marine deposits. These sediments generally
consist of soft, friable fine-to coarse-grained sand. The Pleistocene
sediments were deposited upon a wave-cut platform (marine terrace) that was
cut during a high stand of sea level estimated at about 85,000 to 120,000
years ago. The Pleistocene deposits are underlain by Eocene marine
sandstone of the Santiago Formation. The sediments comprising this formation
are indurated and generally well-cemented. The sandstone is exposed as a
resistant ledge along the toe of the coastal bluffs. The contact between the
Eocene sandstone and the overlying Pleistocene sand generally lies at
elevations ranging from about +6 to +11 along the toe of the bluffs and dips
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down to as low as -3 feet at the south end of the study area (near Tamarack
Avenue). Bedding within both geologic units is essentially horizontal. The
slope of the sandstone under the beach is estimated to be on the order of
10:1 to 7:1.
A perched ground water table typically occurs at the •contact between the
Pleistocene deposits and the Santiago Formation. This conditions is common
along the north San Diego County coastline. Abundant ground water seepage
was noted at many locations along the toe of the bluff within the study area.
The source of the ground water is thought to be primarily surface water
introduced locally as rainfall and irrigation that percolates into the permeable
terrace sands. When the ground water reaches the relatively impermeable
Santiago Formation, it flows laterally along the seaward-sloping contact until
it reaches the bluff face. A line of vegetation commonly grows at this point
on the bluff.
A more detailed Geologic report is presented in Appendix A.
Bluff Erosion
The coastal bluffs along Carlsbad Beach State Park appear to be actively
eroding at variable rates as a result of several erosional processes. Active
erosion is indicated by such features as steep near vertical slopes at the toe
of the bluffs, lack of vegetation in areas along the bluff face, lack of talus
and material eroded from the bluff face, and the presence of erosion gullies
along the bluff face.
It appears that the most significant erosion of the bluffs occurs chiefly by
wave action during high tides and storms. The Pleistocene sand exposed in
the upper portions of the coastal bluffs is friable and weakly cemented and is
subsequently easily eroded by high wave action. Undercutting along the toe
of the bluffs results in near vertical exposures of the sand. These steep
faces are only marginally stable and quickly slough back to a less steep slope
inclination. Comparison of old topographic maps with current profiles
indicates that up to 10 to 15 feet of erosion has taken place along portions of
the bluff during the past ten years.
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Perhaps the most dramatic recent bluff erosion occurred during the winter
storms of 1983 (see cover photograph). During this period, very rapid
coastal erosion coincided with spring tide conditions and a ten- to twelve-foot
swell coupled with extremely strong winds. At Carlsbad State Beach, two
bathhouses were undermined and submerged, the lower foundation of a main
stairway was lost and the •parking lot south of Tamarack Avenue was
undermined. Portions of Carlsbad Boulevard, both adjacent to Carlsbad
Beach State Park and the Encino Power Plant were severely damaged and
collapsed in places during this storm. Carlsbad Boulevard was closed due to
flooding. To the south, at South Carlsbad State Beach, the coastal bluffs
were reported to have retreated by as much as 15 to 20 feet in a single storm
(Kuhn and Shepard, 1984).
Locally, two areas of the upper bluff adjacent to Carlsbad . Avenue have
required fairly extensive temporary slope repair. This slope rebuilding was
required in 1983 along two approximately 50 foot wide stretches of the bluffs
west of Walnut Avenue and Acacia Avenue. This temporary slope repair
generally consisted of rebuilding the slope by placing a fill slope down to the
level of the beach, and using riprap to protect the toe of the fill slope. Jute
netting was laid upon the slope to retard surface water erosion. It is
estimated that the cost of this and other associated temporary remedial work
along this stretch of beach was in excess of $100,000.
Surface water runoff also contributes to erosion of the upper bluffs. Much of
the upper bluff is extensively gullied and rilled. Several drain, pipes from
storm drain inlets located along. Carlsbad Boulevard empty surface water onto
the bluffs. Some of the storm drains supports also appear to be partially
undermined. At South Carlsbad Beach State Park, severe erosion of the
bluff face, on the order of several tens of feet back from the bluff edge,
resulted following the collapse of a similar drain pipe.
Pedestrian traffic also appears be contributing to the erosion of the upper
bluff areas as many foot paths are present across the bluffs. Localized areas
of the upper bluff are also affected by animal burrowing.
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Tide, Wind and Wave Climate
Tides in the study area vary over a maximum 9 to 10 foot range; the highest
astronomical tide for the vicinity being approximately 4.9 feet (MSL Datum).
There are two high and two low tides each day with approximately 6 hours
between each high and low tide. The mean tide range is 3.8 feet and the
diurinal range is 5.3 feet.
Winds are predominantly from the northwest throughout the year, with wind
velocities averaging from 5 to 10 miles per hour. Storms moving in from the
Pacific Ocean occasionally bring somewhat stronger winds but the duration is
relatively short. Tropical cyclones from the south reach the area on rare
occasions. Extreme sustained wind speeds approaching 50 knots are expected
off the southern California coast below 35 degrees latitude statistically once in
a 100 years (NOAA, 1980).
Waves reach the study area from both the southern and northern
hemispheres. Waves from the south are low, typically less than 3 feet, and
occur quite frequently during the summer months. The primary source of
waves is from the northern swell, with periods of 6 to 12 seconds and
onshore directions of northwest to west. Large waves can be expected to
arrive at any time during the year and to continue for three to four days at
a time. These high wave episodes are often not associated with local storms.
Waves 12 to 15 feet in height have been observed on occasion and breakers
with estimated heights of 15 to 20 feet have been observed off the coastline.
Maximum wave heights observed along the San Diego County coast during the
storms in January and February of 1983 were on the order of 6 to 12 feet
with wave periods of 5 to 9 seconds.
Carlsbad Beach is exposed to wave action from the south through northwest.
The outer islands, as well as the Cortez and Tanner Banks tend to shelter
the coastline from long period waves. Deepwater waves unaffected by island
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interference, only arrive from the southwest between Cortez Banks and the
Los Coronados Islands.
A study of tsunamis in San Diego County, conducted for the Office of Civil
Defense in 1968, indicated that the relatively wide continental shelf and
borderland has acted as an effective diffuser and reflector of energy that
arrives from remotely generated tsunamis. Only two or three locally
generated tsumanis, none of which reached the San Diego County Area, are
known to have occurred off southern California since 1800.
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STATEMENT OF PROBLEM
The western edge of Carlsbad Boulevard, between Cherry Avenue and Pine
Avenue, is generally located within several feet of the top of the coastal
bluffs. Several stretches of this portion of the bluff have recently required
fairly extensive slope repair in order to prevent the roadway from becoming
undermined. In the event of severe storm conditions and accompanying high
waves, it is apparent that the existing roadway and utilities along this
stretch of the park are in danger of being undermined. The toe of the bluff
slope along this stretch of Carlsbad Boulevard is completely exposed to winter
storm waves when the narrow beach is eroded. Progressive undercutting of
the bluff by waves and slope sloughing will continue and increase in
magnitude until the coastal bluff, which forms a buffer zone between the
beach and Carlsbad Boulevard, has been eroded away and the roadway has
started to collapse. If this bluff retreat is allowed to continue, heavy losses
to public property may result along with loss of utility services to a large
area and loss of vehicular access to a considerable length of beach.
North-south through traffic would also be completely disrupted causing
distress to many businesses located along Carlsbad Boulevard.
The portion of Carlsbad Boulevard south of Cherry Avenue and north of
Tamarack Avenue appears to be in a relatively more favorable location with
respect to potential distress resulting from bluff erosion or collapse, as the
roadway in this area is generally set back several tens of feet from the top of
the bluff. It is anticipated that the public parking area, and possibly the
paved access road below Tamarack Avenue, will require a more substantial
means of shore protection than is currently in place.
The western edge of Ocean Street at the north end of the project between
Pine Avenue and Oak Avenue is also relatively close to the top of the bluff
and may be subject to undermining due to erosion.
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Project No. 54268E-0002 Woodward-Clyde Consultants
CONSIDERATIONS OF POSSIBLE SOLUTIONS
Several alternatives to constructing shore protection structures are possible.
One alternative would be to do nothing, in which case, continued bluff
erosion would be expected to occur. The rate and degree of such erosion
would be dependent upon the severity of future storms. At the present, it
is estimated that the average rate of erosion is on the order of 1 to 1.5 feet
per year with local variations. It is estimated that possibly within several
years, portions of Carlsbad Boulevard may be unuseable and the utilities
would have to be relocated. Another alternative would be to relocate
Carlsbad Boulevard and all utilities further east or to make Garfield Street
the main street and to relocate utilities along Garfield Street. This solution
would require the City of Carlsbad to obtain ownership of portions of land
east of Carlsbad Boulevard. Neither of these options are consistent with the
general plan for this area and complete relocation of street and utilities is not
considered economically feasible.
Beach nourishment or offshore protection are also possible alternate
considerations. The Army Corps of Engineers suggested several alternatives
for stabilizing and maintaining sand as a protective buffering beach at
Oceanside. These measures included rock revetments, groin systems, sand
fills, breakwaters, and a permanent sand by-pass system. Only the sand fill
program has been attempted to date and was only temporarily successful.
However, a sand by-pass is currently being designed for Oceanside harbor
entrance to provide a continuous sand replenishment system. It is possible
that the sand replenishment program may also provide an additional source of
sand along Carlsbad's beaches. This in turn may provide some protection for
the bluffs. It will be several years before the results of this program can be
evaluated. Based on historic records of beach levels along Carlsbad, it does
not appear that beach replenishment would be feasible for Carlsbad Beach
State Park. It also appears that any offshore structure in this area would
not be economically feasible.
At the present time ,the most appropriate solution for protection of the subject
bluffs appears to be some type of seawall or rock revetment. For such
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construction it is important to address encroachment on the beach; the visual
aesthetics; the current use of the area, the hazards associated with
potentially unstable, oversteepened slopes; the potential for future erosion;
the potential for damage and loss of benefits; the engineering design criteria;
and the cost. We have identified and reviewed advantages and disadvantages
of several structural alternatives. The structures evaluated included the
following:
° Rock Revetment
° Vertical Seawall
0 A Combination Vertical Seawall - Rock Revetment
In order to enhance the visual appearance of the project, and to provide
additional benefits, other features should also be considered. These may
include the effective use of walls to reclaim eroded land to provide new park
areas or overlook areas above the beach; the use of different types of
structures along the alignment; the use of a curved alignment; and the
improvement of drainage.
As a part of the proposed shore protection construction, beach access should
also be taken into consideration. Currently, beach access is provided along
public access stairways located at Tamarack Avenue and Cherry Avenue and
an access ramp at Ocean Street. Also, many unimproved foot trails lead down
to the beaches from the top of the bluff. Emergency vehicle access is
possible at the south end of the public parking area at beach level and along
an unimproved dirt road leading down to the beach at Ocean Street near Pine
Avenue. It is apparent that the existing accessways within the subject study
area need to be improved and that additional beach access is needed along a
this stretch of shoreline. Improvement of lateral access along the top of the
bluff should also be considered.
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A general summary of the selection considerations and the relative ratings for
various types of construction are presented on Table 1 below.
Table 1
Shore Protection Selection Considerations
Anticipated Relative Type of Beach Ease of Level of Visual Cost Per Protection Encroachment Construction Maintenance Appearance Lineal Ft
Stone revetment Highest Easiest Low Satisfactory Lowest
Reinforced concrete
vertical seawall Lowest Hardest Lowest Good Highest
Reinforced earth
wall with toe stone Medium Medium Low Good Medium
Cribwall with toe
stone Medium Medium Medium Satisfactory Medium
Fabriform (concrete
filled bags) Medium Medium Low Poor Low
H-pile with wood Medium or concrete lagging to and toe stone Medium Medium Highest Satisfactory High
Currently there is a rock ledge exposed along much of the bluff. For
preliminary design, it is anticipated that the proposed structures would be
located on or landward of this ledge and that the encroachment onto the
usable beach area would be limited. The structures would be curved to
match the existing topography and vertical walls would be used to reclaim
land and provide a more pleasing - visual appearance. Both Reinforced Earth
Walls (which can be colored and textured) and crib walls (which can be
planted) have been used in this regard. It is anticipated that the structures
would be designed for a 30 to 50 year life with relatively low maintenance.
The current accessways should be improved and one or two accessways
added.
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Based on our preliminary review of the various alternative methods of shore
protection, it appears that the most suitable structural method of bluff
protection consists of a stone revetment incorporated with vertical seawalls in
some areas and no protection in others. Some typical cross sections of
alternative methods are presented on Figures 8, 9 and 10. It appears that two
additional accessways would be adequate; typical details are shown on Sheet
Nos. 1 thru 4.
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PRELIMINARY ENGINEERING DESIGN CRITERIA
The design of a seawall or a stone revetment, which are considered in this
report, is in general accordance with the information and procedures
contained in the U .S. Army Corps of Engineers' Shore Protection Manual,
Volumes I, II and III, 1975 and information contained in the List of
References attached to this report. The following coastal engineering criteria
were selected for use in the preliminary design:
1. Tidal Range
MLLW datum
Highest estimated water level +7.79 feet Mean higher high water +5.61 " Mean high water +4.89 Mean Sea Level (NGVD datum) +2.88 " Mean Lower Low Water +0.00 " Lowest estimated water level -2.18 "
*NGVD datum
+4.91 feet
+2.73 "
+2.01 "
+0.00 "
-2.88 ".
-5.06 "
Estimated storm surge and wave set-up,, 2.1 feet
Highest estimated still water level (SWL): +9.9 feet (MLLW datum)
Deep water wave period: 16 seconds
Elevation at toe of revetment: +3 feet (MLLW datum)
Assumed worst condition: sand scoured down to toe of revetment
so water depth (ds) = 6.9 feet
Average inshore slope: 1 to 25 (m=0.04)
Maximum wave height of wave breaking on revetment: Hb=8. 6 feet
Stability coefficient for two layers of armor stone: X = 2.0
Specific gravity of armor stone: S r = 2.64
*NGVD - National Geodetic Vertical Datum (formerly called Sea Level Datum of
1929)
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PROPOSED PRELIMINARY DESIGN
The subject 4500 foot long portion of the coastal bluffs is characterized by
dramatic changes in topography; variations in bedrock exposures, vegetation
and extent of erosion; and variations in current use. It therefore appears
that a variation in the type of remedial treatment or shore protection used
might also be appropriate.
For preliminary design, a stone revetment type of seawall with a curved
alignment is proposed to be the basic type of shore protection along the base
of the bluff within the Carlsbad Beach State Park study area. A typical
design would place the top of the revetment at a maximum elevation of +22
feet (NGVD), the toe at elevation +3 feet, the slope inclination at 2 to 1
(horizontal to vertical) and the armor stone would consist of 4 ton stone.
The revetment -would generally follow the toe of the bluff at approximate
elevation +6 feet and would be located approximately 100 to 150 feet west of
the west edge of Carlsbad Boulevard. In areas where the bedrock is higher
than +6 feet the top of the revetment could be lowered. Engineering design
calculations are presented in Appendix B.
In those areas where significant erosion has occurred into the bluff, a
vertical reinforced earth wall or a sloped crib wall (both with toe stone)
would be utilized. to provide a better visual appearance, to reclaim land and
to provide overlook areas. It is anticipated that areas which might be
considered for such treatment include, the bluff in the vicinity of Walnut
Avenue, Maple Avenue, Acacia Avenue and Cherry Avenue. It is estimated
that approximately 500 lineal feet of seawall would be constructed.
In some areas where existing heavy vegetation is present or where Carlsbad
Boulevard is set further back from the top of the bluff, such as between
Tamarack and Juniper Avenues, providing a wider buffer zone, no treatment
may be a consideration. It is estimated that up to 400 to 500 feet of the
project could be left in its current state.
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At the south end of the project at the parking lot, the existing stone
revetment would be improved to provide better protection for this area.
The existing accessways would be repaired and improved and two new
accessways would be constructed. It is proposed that one of the new
accessways be designed to accommodate handicapped persons or that the
existing accessways at the north and south ends of the project be improved
to provide better handicapped access.
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ECONOMIC CONSIDERATIONS
Construction Cost Estimate
The subject project extends along approximately 4500 feet of shoreline. For
preliminary planning, it is estimated that approximately 3500 feet will be
protected by a stone revetment that approximately 500 feet will be protected
by a vertical seawall with toe stone protection, and that approximately 500
feet will be left in its existing state. For purposes of estimating costs, it is
also assumed that the construction will include a new beach access stairway, a
new handicapped beach access ramp and repair of the three existing beach
accessways. The estimated cost of construction Is as follows:
Quantity Unit Cost Amount
Mobilization and Demobilization 1 L. S. $25,000 $25,000
Site Preparation 1 L. S. 10,000 10,000
Excavation•
Terrace and Beach Deposits 10,000 cu.yds. 3.00 30,000
Bedrock 5,000 cu.yds. 25.00 125,000
Backfill, compacted 15,000 cu.yds. 2.00 30,000
Armor stone 85,000 tons 20.00 1,7001000
Underlayer stone 22,500 tons 20.00 450,000
Quarry run 14,000 tons 10.00 140,000
Filter cloth 37,500 sq.yd 2.00 75,000
Reinforced Earth/crib wall 8,500 sq.ft 25.00 21,250
Reinforced concrete foundation 500 L.F. 170.00 85,000
Reinforced concrete wave
deflector 500 L.F. 55.00 27,500
Modifications repair/existing
ramps and stairway 1 L.S. 85,000 85,000
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Quantity Unit Cost Amount
New concrete stairway 1 L. S. 25,000 25,000
New handicapped ramp 1 L. S. 85,000 85,000
Subtotal $2,913,750
Contingency (25%) 728,000
Total, Estimated Construction Contract Cost $3,641,750
Engineering and Design (0) 145,500
Supervision and Administration (4%) 145,500
Total Project Cost $3,932,750
Maintenance Cost Estimate
The preliminary design criteria are considered relatively conservative and
fairly large armor stone (4 ton) are proposed for the revetment and toe
stone. It is therefore anticipated that the damages to the revement and
seawall should be small during most of the design life. It is correspondingly
assumed that the annual maintenance costs would also be relatively small.
Annual maintenance costs are assumed to be I percent of the estimated
contract cost.
Annual Maintenance = 0.005 x 3,641,750 = $18,000 per year
-19-
Project No. 54268E-0002 Woodward-Clyde Consultants
Benefit Estimate
Benefits are calculated comparing the existing facilities and area use to
probable conditions assuming no protection is provided and that erosion
continues. The lost benefits include value of eroded property, lost user
benefits, costs of vehicle travel due to detour and cost of facility
replacement. For our estimation process, the following assumptions were
made: a rate of erosion of 1.5 feet per year, a 50 year useful life for the
project, a conservative $400,000/acre value for property, an interest rate of
12 percent, an average beach use of 2640 persons per day, an estimated
future average daily traffic on Carlsbad Boulevard of 27,000/day, an average
daily bicycle traffic on the bicycle lane of 200/day and the presence of gas,
electric, telephone, water and sewer facilities and future storm drain and
reclaimed water lines along Carlsbad Boulevard. Computations are presented
in Appendix C.
Average Annual Benefits Lost Per Year
Value of eroded property - $62,000
Beach user benefits lost - $337,500
Bicycle lane use lost - $109,500
Vehicle operating cost on detour - $2,250,000
Lost time value on detour - $1,928,500
Facility replacement costs - $77,000
Total Annual Benefits Lost = $4,764,500
-20-
Project No. 54268E-0002 Woodward-Clyde Consultants
Benefit Cost Ratio
Construction costs are spread over the estimated 50-year useful life of the
project and added to the annual estimated maintenance cost to give a total
annual cost of:
Annualized construction cost - 3,900,000 x 0.12042 = $470,000
Annual maintenance cost - 0.01 x 469,638 = 18,000
Total Annual Cost - $488,000
When compared to the estimated total annual benefits lost of $4,764,500 this
gives a ratio of benefits to cost equal to approximately 10.
It is apparent that the loss of Carlsbad Boulevard as a north-south travel
way is the most dominant factor in the Benefit Cost Ratio. Excluding the
vehicle and lost time costs for the detour, the remaining benefits have an
annual cost of $586,000 which gives a ratio of benefits to costs equal to
approximately 1.20.
-21-
Project No. 54268E-0002 Woodward-Clyde Consultants
REFERENCES
Fischer, Michael L., 1983. "Preliminary Report on January, 1983 Coastal
Storm Damage as prepared by Mary Lou Swisher, Geologist, Energy,
Technical Services Division" preliminary report to California Coastal
Commission.
Howe, Steve, 1978, "Wave Damage along the California Coast, Winter, 1977-78
"prepared for California Coastal Commission.
Inman, Douglas L., 1976, "Man's Impact on the California Coast Zone"
prepared for State of California Department of Navigation and Ocean
Development.
Kuhn, G.G.., and Shepard F.P., 1984, "Sea Cliffs, Beaches and Coastal
Valleys of San Diego County: Some Amazing Histories and Some Horrifying
Implications" University of California Press.
Kuhn, G.G. and Shepard, F.P. 1979, "Accelerated Beach
- Cliff Erosion Related to Unusual Storms in Southern California," California Geology No.
32.
Personal Communication, G .G. Kuhn, October, 1984.
Marine Advisors, 1960, "Design Waves for Proposed Small Craft Harbor at
Oceanside, California" prepared for U.S. Army Corps of Engineers, Los
Angeles District.
Meteorology International Incorporated, 1977, "Deep Water Wave Statistics for
the California Coast, Station 611 , Department of Navigation and Ocean
Development.
National Oceanic and Atomospheric Agency, 1980 ,11A Climatology and Oceanographic Analysis of the California Pacific and Outer Continental Shelf
Region."
Scripps Institute of Oceanography, 1984, "Coast of California Storm and Tidal
Wave Study," prepared for U .S. Army Corps of Engineers, Los Angeles
District, Planning Division.
State of California, 1977, "California Coastal Engineering Data Network,
Second Annual Report, January 1977 through December 1977" Department of
Navigation and Ocean Development.
State of California, 1977, "Assessment and Atlas of Shoreline Erosion along
the California Coast," Department of Navigation and Ocean Development.
U. S. Army Corps of Engineers, 1980, "San Diego County, Vicinity of
Oceanside, California - Survey Report for Beach Erosion Control" Main
report including Draft Environmental Impact Statement.
-22-
Project No. 54268E-0002 Woodward-Clyde Consultants
U. S. Army Corps of Engineers, 1975,
Army Coastal Engineering Research Center.
"Shore Protection Manual," U. S.
Waldorf, B. Walton, Flick, Reinhard E. and Hicks, D. Murray, 1983. "Beach
Sand Level Measurements - Oceanside and Carlsbad, California - December
1981 to February 1983 Data Report." S10-Reference No. 83-6.
-23-
I
Scale : III
LOCATION MAP
CARLSBAD BOULEVARD SEAWALL
PROJECTNO: 54268E-0002 ~, DATE: 10-11-84
W000WARD-CLYDE CONSULTANTS
-
OCEAN STRE / WALNUT PROFILE:..
/. PROFILE
' . -
- Project Area
'Js-%r4L .IJIN I tUL I IUIN UI- , I AL L I-'AKK
Lu
IR IR
0
1 to T 09 LJ
El Iq 09
Og
9 1 s 0/ AvA1HIH A CARLSBAD B6ULEV ARD
- -- nvo
co
7
77
413
ov
_
I
CHESTNUT -- - -
/
:.
CIA
ffILE:. 7 jA
•
- T
TTTt .
; V 330 PROFILE
I3vd
•S - roject
-
S TOPOGRAPHIC BASE MAPS FOR CITY OF CARLSBAD, 0 200 40Q - - SITE PLAN AND LOCATION
MAP SHEETS i-i AND K-i L OF
- - MAP PREPARED PRIOR TO CARLSBAD BOULEVARD..BLUFF PROFILES
M1 ti1kP A p. •,. ,•i --GRAPHIC SCALE (Feet r A DI CD A r ri ii mi A t r.. r- A ill Al v s lI I'd
FACILIT1S.
-- - -
- / - -
W000WARD-CLYDE CONSULTANTS
BACK BEACH AND BLUFF AT LOCATION OF HEMLOCK PROFILE.
ERODING BLUFF IS COMPOSED OF PLEISTOCENE TERRACE DEP-
OSITS CONSISTING LARGELY OF FRIABLE SAND. THE UNDER-
LYING SANTIAGO FORMATION IS EXPOSED AS A RESISTANT
LEDGE AT THE BASE OF BLUFF. NOTE GRCUND WATER SEEP-
AGE AT THE CONTACT OF THE TWO GEOLOGIC UNITS.
II
-. p.
'
VIEW NORTH FROM AGUA HEDIONDA JETTY AT PARKING LOT
AND TAMARACK AVENUE. RESTROOM FACILITY IN BACK-
GROUND. NOTE LOCALLY SPARSE RIPRAP COVERAGE.
CARLSBAD BOULEVARD SEAWALL
DRAWN BY: ch CHECKED BY:7'i,LI PROJECT NO: 542 68E-00011 I DATE: 101184 FIGURE NO: 3
WOODWARD-CLYDE CONSULTANTS
II - ..-
/
.--c
- •- -- '-
i _r,
- ..--
- - - • ,-.. 'S -- — -
_c
-S. . . S • -
i-
---•---..-------- _,±._.__i 'C
-
i
.• -
--------------5— .5,.
I- ' '' '
•-
-? .-
- . — - -
S -
4 , • - A ç .. • '' .__5 .As. •• . -. - ,, - - - '5 - - -
-.- ": -. .:- •A ___. - - sT - •,• - — -.
5.... .--. - -,. _'___5__•
k '' ".•. '-.
- - •• .-.• :-- - -.:-.. - -- - ---c—
.-- ..
- - — --
FIGURE NO: 4
est West
60- .• ACACIA PROFILE
.• Carlsbad Avenue
40-
- FILL
-
PLEISTOCENE TERRACE DEPOSITS .
- Bedrock Ledge
eu-
• - *
- FILL
7 _____ •• - - ____ I Beach Sand
SANTIAGO FORMATION 0-
__ ..• .....
CHESTNUT PROFILE
z. 0
I-
40
20-
Carlsbad Avenue
ro
. I *
0 • PLEISTOCENE TERRACE DEPOSITS. .
-. Exposed Bedrock
ca t - -
Ledge
i Beach Sand
SANTIAGO FORMATION
0 20 40
I _]
GRAPHIC SCALE (Feet)
W000WARD-CLYDE CONSULTANTS
East
601
WALNUT PROFILE West
Carlsbad Avenue a..J ,Guard Rail
-. .
FILL
a.
4-a
PLEISTOCENE TERRACE DEPOSITS
I— Bedrock Ledge
. .....
.Beach Sand
T
SANTIAGO FORMATION
2C
0
I-' E
4J
-J u) —10
5
Ocean Street
I Pirkinn
OCEAN STREET PROFILE
NZ FILL.
co Bedrock Ledge
PLEISTOCENE TERRACE DEPOSITS
Cobble Berm
40 0 Beach Sand
SANTIAGO FORMATION
0 20 40 BLUFF PROFILES
-I CARLSBAD BOULEVARD
GRAPHIC SCALE (Feet) DRAWN BY: ch I CHECKED BY:
DATE: 10-11-84 PROJECT NO:
W000WARO-CLYDE CONSULTANTS
20
[Ij
ME
60-,
WESTERLY EDGE
50 •.. / CARLSBAD BOULEVARD
40
PLEISTOCENE TERRACE DEPOSITS
U-
S z 0 I- 20-
>
-J w
GENERALIZED NATURAL SLOPE
S
FILTER FABRIC LINING
1 /2-TON STONE
-_EL. 22'
2
IIJ
I 3 TO 4-TON ARMOR STONE
CONSTRUCTION
END OF FILTER FABRIC LAPPED BACK
k\
BEACH LEVEL VARIES
BEACH SAND
EXCAVATION
10. _____ —
EL. 61
0-
_—
SANTIAGO FORMATION
QUARRY WASTE
0 10 20
GRAPHIC SCALE (Feet)
ME
W000WARD-CLYDE CONSULTANTS
60-
WESTERLY EDGE
CARLSBAD BOULEVARD
50-
GENERALIZED NATURAL SLOPE
* 40
D
30 PLEISTOCENE TERRACE DEPOSITS
uj
10-
SANTIAGO FORMATION
COMPACTED EARTH BACKFILL
WITH SELECT MATERIAL
RECOMPACTED SLOPE
REINFORCING STRIPS
CONCRETE WAVE DEFLECTOR
EL. 221
'I
N
,- PRECAST CONCRETE WALL FACING
......... ....
EL. 141
3-TON STONE TOE PROTECTION
BEACH LEVEL VARIES
I 7\c
EL 61
/ CUT OFF BEACH SAND
WALL FOOTING CONSTRUCTION
I A S A T I#I. I C.A'.iMVMuIjI GRAVEL DRAIN
0 10 20
GRAPHIC SCALE (Feet)
8E-0002 I
WUUUWMflU-LYU UIIUIMI
W000WARD-CLYDE CONSULTANTS
Project No. 54268E-0002 Woodward-Clyde Consultants
APPENDIX A
GEOLOGIC INVESTIGATION
Project No. 54268E-0002 Woodward-Clyde Consultants
APPENDIX A
GEOLOGIC INVESTIGATION
for
CARLSBAD BOULEVARD SHORE PROTECTION
Field and Office Investigation
The geologic conditions at Carlsbad State Beach Park were mapped during
October of 1984. The geologic mapping was completed on San Diego County
orthophotos of the coastline flown at a scale of 1" -2001. Topographic profiles
of the coastal bluffs were surveyed at the locations shown on Figure 2 of the
Feasibility report; the profiles were made using a level and leveling rod. At
each of the profile locations, shallow test pits were dug down through the
beach to measure the bedrock elevation.
During the geologic reconnaissance, field observations were made of the
erosional conditions and characteristics of the coastal bluffs. In order to
make a more thorough evaluation of the erosional processes and erosion rates
along the study area, current observations of the bluff conditions were
compared with historic photographs and maps that date back about 30 years.
Photographs taken several years before, during and immediately after the
winter storms of 1983 were particularly useful in evaluating the rate and
nature of bluff retreat.
Geologic Setting
The shoreline along Carlsbad Beach State Park, like much of the coastline
along San Diego County, is backed by low coastal bluffs. The bluffs are
backed by a broad, low relief coastal plain that generally extends several
tens of miles inland. Agua Hedionda Lagoon and Buena Vista Lagoon are two
lagoons located immediately south and about I mile north, respectively, of the
state park. The lagoons generally act as "sediment traps", as sand and
sediment are largely discharged from the lagoons only during periods of
A-i
Project No. 54268E-0002 Woodward-Clyde Consultants
sustained, high runoff. Longshore transport of sand in the littoral zone
along this stretch of coastline is predominantly to the south. In order to
maintain circulation and tidal action within Agua Hedionda Lagoon, the
entrance to the lagoon is periodically dredged. The sediment dredged from
the lagoon is distributed hydraulically along the beach area south of the
lagoon inlet.
Geologic Units and Erosion Characteristics
The coastal bluffs backing the state beach area are underlain by Eocene
sandstone of the Santiago Formation; the sandstone is typically exposed as a
low ledge along portions of the toe of the coastal bluff. The Santiago
Formation Is overlain by Pleistocene terrace deposits which are exposed along
the face of the bluffs. The Pleistocene sediments were deposited upon a
wave-cut platform (marine terrace) that was cut during a high stand of sea
level estimated at about 85,000 to 120,000 years ago. The contact between
the two geologic units generally varies in elevation along the toe of the bluff
from +6 to +11 feet and dips down to as low as -3 feet at the south end of
the study area.
The Santiago Formation consists of greenish grey clayey sandstone; the
sediment comprising this formation is indurated and is generally much more
resistant to erosion than the Pleistocene sand. The upper bluffs are
comprised of soft, friable, fine- to coarse-grained sand. These deposits are
typically weakly cemented, and are not capable of standing for long periods
as vertical exposures over several feet in height. Steep faces eroded into
the Pleistocene deposits are only marginally stable, and quickly slough back
to a less steep slope inclination. The Pleistocene deposits are also relatively
easily eroded by surface water runoff. -Many relatively deep gullies and small
ravines have been partially filled with material dumped from the bluff top.
A-2
Project No. 54268E-0002 Woodward-Clyde Consultants
Geologic Structure
Local bedding attitudes within the Santiago Formation could not be determined
from the current exposures. The regional dip of the Santiago Formation is
generally to the northeast at inclinations typically less than 10 degrees.
Bedding within the Pleistocene deposits is nearly horizontal; the lower sandy
portion is highly cross-bedded. The contact between the two geologic units
slopes seaward at several degrees.
The presence of fractures, joints or faults may greatly accelerate the wave
erosion process in the coastal environment. The Pleistocene terrace deposits
are generally not a highly fractured or jointed unit; no faults were observed,
nor have any faults been mapped that displace the marine terrace. The
Santiago Formation, however, is typically jointed and fractured to varying
degrees; many northeast-trending fractures and small faults commonly cut the
Eocene bedrock. At other nearby locations along the coast, such features as
surge channels and sea caves are commonly formed by wave action scouring
the sedimentary rock adjacent to faults or fractures. Along the study area,
bluff erosion does not appear to be greatly influenced by these features.
Ground Water Conditions
A perched ground water table typically occurs at the contact between the
Santiago Formation and the Pleistocene deposits. This condition is common
along the North County coastline and has been recognized as a contributing
factor to bluff erosion.
The source of the groundwater is thought. to be primarily surface water
introduced locally as rainfall and irrigation that percolates into the permeable
terrace sands. When the ground water reaches the relatively impermeable
Santiago Formation, it flows laterally along the seaward-sloping contact until
it reaches the bluff face. A line of vegetation commonly grows at this point
on the bluff. Prominent ground water seepage was observed along the toe of
the bluffs at many locations within the study area.
A-3
Project No. 54268E-0002 Woodward-Clyde Consultants
Seismicity and Faulting
The faults within the study area do not displace the wave-cut terrace and are
overlain by Pleistocene deposits, indicating that movement has not occurred
during the past at least 85,000 and possibly 120,000 years.
The nearest potential earthquake sources include the offshore continuation of
the Rose Canyon Fault zone, mapped about 3 miles west of the study area.
More distant earthquake sources include the Elsinore Fault zone, mapped
about 25 miles to the northeast. Many historic moderate earthquakes have
occurred on the Elsinore Fault, whereas no earthquakes of magnitude 4.0 or
greater have been recorded on the Rose Canyon. In general, although the
historic seismicity record of Southern California is relatively short, the San
Diego area has historically been recognized as an area of relatively low
seismic activity. Although no specific seismic evaluation was performed for
this study it appears to be reasonable to estimate that the largest
earthquake-induced ground acceleration at the site with an average
recurrence of 100 years is about 0.15 to .20g.
Bluff Erosion and Slope Stability
The bluff areas along the state park are subject to wave run up and impact
during periods of high waves accompanied by high tides. During these
periods, much of the lower portions of the bluff slope are subject to
undercutting by wave action. During the winter storms of 1983, significant
erosion occurred along much of the state beach area. Localized areas of the
bluffs apparently experienced much more severe erosion. In particular,
several stretches of the bluffs generally west of Walnut Avenue and Acacia
Avenue were undercut to the extent that subsequent, slope sloughing partially
undermined portions of Carlsbad Avenue. These areas of slope failure were
rebuilt with compacted fill slopes and a protective layer of riprap placed along
the toe of the rebuilt slopes.
A-4
Project No. 54268E-0002 Woodward-Clyde Consultants
In general, the natural slopes comprising the coastal bluffs appear to be
grossly stable in their present condition.. However, the sandy, friable
terrace deposits, when undercut and oversteepened by wave action, are only
marginally stable at relatively steep slope inclinations. Experience with this
geologic unit in the subject area and at other locations along the coast has
shown that once slopes are oversteepened, additional surface sloughing and/or
relatively shallow slope failures are likely to continue to occur within and
adjacent to the undercut area until more stable slope inclinations are reached.
Factors that could influence slope failures within such potentially unstable
areas include heavy rainfall, ground water seepage, earthquakes, and
additional erosion by high wave action. Relatively minor slope failures or
blockfalls could represent a potential hazard to beach users.
A-5
Project No. 54268E-0002 Woodward-Clyde Consultants
APPENDIX B
COASTAL DATA AND ENGINEERING
DESIGN CALCULATIONS
Project No. 54268E-0002 Woodward-Clyde Consultants
APPENDIX B
ENGINEERING DESIGN CALCULATIONS
for
CARLSBAD BOULEVARD SHORE PROTECTION
Evaluate Deepwater Wave -
Based on the "San Diego County, Vicinity of Oceanside, California
- Survey
Report for Beach Erosion Control" prepared by the U .S. Army Corps of
Engineers, Los Angeles Disrict and dated September 1980, there is an 80
percent chance that the highest significant wave height would range from 11.7
to 14.2 feet at a minus 32.5 foot depth. From these analyses, we selected a
maximum non-breaking wave of 14.2 feet and a wave period of 12 seconds for
preliminary evaluation. Observations of . the nearshore profiles show an
average slope of the ocean floor on the order of 1-foot vertical to 25 feet
horizontal.
H0=14.2 feet
T =12 seconds
m =0.040
d =32.5 feet
L0=5.12T 2=737 feet (Deepwater Wave Length)
for d = 32.5 = 0.0441 ; d = 0.0877 Table C-i from
Lo 737 L Vol. III - SPM
h = 1.046
H 0
= H = 14.2 = 13.6' (equiv. deepwater wave height)
1.046 1.046
B-i
Project No. 54268E-0002 Woodward-Clyde Consultants
Determine type of wave hitting the structure for breaking wave conditions
using Figures 7-2 and 7-3 from Vol. II - SPM
H'0/Lo = 13.6/737 = 0.0185
H' /crT 2 = 13.6/32.2(12)2 = 0.0029
Hb/H'o = 1.35 ; so H = 1.35 x 13.6 = 18.4 feet Fig. 7.3
From Fig. 772, 0 = 1.025 , a = 1.520
HIgT 2 = 18.4/32.2 x 144 = 0.004
min d = 1.025 x 18.4 = 18.9 feet
max d = 1.520 x 18.4 = 28.0 feet
Assume a toe elevation at the seawall as 4-3 (MLLW), an extreme tide of
7.8 feet, a storm surge and wave set-up of 2.1 feet. Then design still water
level = +9.9 feet and d5 = 6.9 feet.
Comparing d5 to db: 6.9 <18.9 ft. (mm.) indicates that the maximum . design
wave will start breaking before it reaches the seawall. Using a slope of
m=0.04 and a breaking depth of 18.9 ft. (mm.) indicates that the maximum
design wave will start breaking a distance of a = 18.9-6.9 = 300 feet from the
seawall. .04
Breaker travel distance a = (4.0-9.25m)Hb Eq. 7-3 Vol. II SPM
= (4.0-9.25 x 0.04) 18.4 = 66.8 feet ; this indicates that the wave
will have finished breaking before it gets to the seawall,
Project No. 54268E-0002 Woodward-Clyde Consultants
Check largest wave that will break on seawall
for d = 6.9 ft. - (use Fig. 7-4 and 7-2) S
.T L0(ft) d8/gT2 Hb/ds Hb(ft) H/gT2 B = dblHb
6 184 0.0060 1.07 7.4 0.0064 1.16
12 .737 0.0015 1.21 8.3 0.0018 0.95
15 1152 0.0010 1.23 8.5 0.0012 0.93
17 1480 0.0007 1.24 8.6 0.0009 0.91
20 2048 0.0005 1.25 8.6 0.0007 0.90
T16 sec , Hb=8.6ft.
(mm) db = 0.92 x 8.6 = 7 9 feet
c*7.9-6.9=25ft. and a =(4.0-9.25x0..04) 8.631ft.
0.04
Design wave H = 8.6 ft. .
B-3
Project No. 54268E-0002 Woodward-Clyde Consultants
Design of Stone
W = 165 lbs (unit of weight of armor stone)
H = 8.6 ft. (design wave height = Hb)
Sr = 2.64 (specific gravity)
cot e = 2/1 (slope of seawall)
= 2.0 (stability coef. of armor units)
165 (8.6) 104.949
W = 2 x (2.64 -1P x 2 = 17.64 = 5950 lbs
= 3.0 tons
Use four ton (4) average stone for armor for three layer section:
Underlayer stone, W10 = 600; use I to I ton stone
Bedding Material, W200 to W4000 = 30 to 1J lbs.; use quarry waste
with 50 lbs. size
maximum
Wave Run-up
d6.9ft. , T16sec., Hb=S.6ft. and m=0.040
H/gT2 = 0.0010 , from Fig. 7-5 Hb /HI o=2.32
H' = 8.6 = 3.71 and H' IgT 2 = 0.005 ° 2.32
d/H?0 = 6.9/3.71 = 1.86 and cote = 2
Fig. 7-10 and 7-11 Vol. II SPM R/H'0 = 5.3 for d5/H'0 = 0.8
R/H'0 = 4,1 for d5/H'0 = 2.0
Design R/H'0 = 4.24
R S = 4.24 x 3.71 = 15.7 ft. for smooth surface
tane=0.5 , Hb=8.Gft.
K = 1.19 from Fig. 7-13 Vol.IlSPM
B-4
Project No. 54268E-0002 Woodward-Clyde Consultants
R = 1.19 x 15.7 = 18.7 ft. (corrected run-up)
= 18.7/3.71 = 4.23 (for smooth)
= 3.0 (for riprap) Fig. 7-15
riprap = 3.0 = 0.71
smooth 4.23
Rriprap = 0.71 x 18.7 = 13.3 feet (run-up onriprap surface)
Height of wall to prevent overtopping = 9.9 + 13.3 = + 23.2 ft.
= + 23 ft. MLLW
= + 20 ft. NGVD
Use wall high of +22 ft.*NGVD
* NGVD - National Geodetric Vertical Datum (formerly call Sea Level
datum of 1929).
B-5
I.'
CALIFORNIA
i'(A •
ENGINEERING
DATA
NETWORK
SECOND ANNUAL REPORT
JANUARY 1977 THROUGH DECEMBER 1977
IN COOPERATION WITH
SCRIPPS INSTITUTION OF OCEANOGRAPHY
UNIVERSITY OF CALIFORNIA
DATA ANALYSIS AND UTILIZATION (CONTINUED).
In CD In CD In Cu C-U
LU) tR]IH IAVM iNV]LdIN9IS
FIGURE 7
-12-
STATION JO. 4 OCEANSIDE 1977
TABLE
CUMULATIVE HEIGHT P0BARILITIES
HEIGHT PROBABILITY
295 0.0000
295 0.0000
275 0.0000
265 000000
255 0.0000
245 0.0000
235 0.0023
225 0.0034
215 0.0046
205 0.0046
195 0.0057
185 0.0057
175 0.0057
165 0.0057
155 0.0057
145 0.0069
135 0.0080
125 0.0103
115 o.oiso
105 0.0219
95 0.0311
85. 0.0519
75 0.0727
65 0.1200
55 0.1905
45 0.2806
35 0.4295
25 0.7170
15 0.9757
5 1.00.00
CUMULATIVE PEAK PFPIOD PROBABILITIES
PERIOD PROBABILITY
(SEC)
22+ 0.0000
20 0.0496
17 0.1558
15 0.3960
13 0.6004
11 O.6893
9 0.7875
7 0.9526
5 100000-
-22-
jo
300
290
9 280
270
EGO
ao
240
230
220
210
200
G 190
ieo
170
io
140
130
120
Ho•LJJ > 10O
90
H LL 70
GO
.c.fl Lr 50
40
30
20
10
:i 1jJ :1!I
A
_
1 41 101 31 11 1 1
TOTAL OF BGG OBSERVATIONS
ii
28+ 20 17 15 13 ii 9 7 5
PEAK PL1 IOO (SEC)
.JOINT DISTRIBUTION TABLE
IEANIDE 1977 FIGURE 17
-27-
OCEANSIDE
JAN. 1977
P E R S ISTENCE
(CONSECUTIVE DAYS (3 OR MORE) SIGNIFICANT
WAVE HEIGHT IS 'H' FEET OR LESS)
FEET DAYS
I 0,
2 5,
3 60
4 8 5,
5 81 5
b 81 5,
8 81 5
10 8, 5,
12 81 5
MAXIMUM DAILY SIGNIFICANT WAVE HEIGHT FOR JAN. 1977
DATE (JAN.) 1 2 3 4 5 6 ----------------------------------------------------------
SIG.HT (FT.) . 3 3 4 4 3.
DATE (JAN.) 8 9 . 10 11 12 13 --------------------------------------------------
SIG.HT (FT.)
DATE (JAN.) 15 16 17 18 19 20
SIG.HT (FT.)
DATE (JAN.) 22 23 24 25 26 27
-.
SIC.HT (FT.) 2 2 1 2
DATE (JAN.) 29 30 31
SIG.HT (FT.) 3- 4 3
-44-
OCEANS IDE
FEB. 197?
P E R S I S T E N C E
(CONSECUTIVE DAYS (3 OR MORE) SIGNIFICANT
WAVE HEIGHT IS 'N' FEET OR LESS)
FEET DAYS
I 8.
2 4,
3 10, 5, 4.
A 1 11 81 sli
5 20. 6,
6 28.
8 28,
10 28.
12 28.
MAXIMUM DAILY SIGNIFICANT WAVE HEIGHT FOR FEB. 1977
DATE (FEB.) 1 2 3 4 5 6 7
SIC.HT (FT.) 4 2
------------------------------------------------------------
2 3 3 4 3
DATE (FEB.) 8 9 10 11 12 13 14 ------------------------------------------------------------
SIG.HT(FT.) 3 5 4 2 2 2 2
DATE (FEB.) 15 16 17 18 19 20 21
SIG.HT (FT.) 3 3 3 3 3 2 6
DATE (FEB.) 22 23 24 25 26 27 28
SIG.HT (FT.) 6 5
------------------------------------------------------------
3 3. 3 2 3
OCEANSIDE
MAR. 19??
P E R S I S T E N C E
(CONSECUTIVE DAYS (3 -OR MORE) SIGNIFICANT
RAVE HEIGHT IS 'N' FEET OR LESS)
FEET DAYS
I
2 6 4,
3 7, 6 5, 3,
4 311,
5 38,
6 31,
8 31
18 31
12 :31,
MAXIMUM DAILY SIGNIFICANT WAVE HEIGHT FOR MAR. 1977
DATE (MAR.) 1 2 3 4 5 6 7
SIC.HT (FT.) 6 4 4 . 3 2 22
DATE (MAR.) 8 9 10 11 12 13 14
SIG.HT (FT.) 2 4
------------------------------------------------------------
4 2 2 3 4
DATE (MAR.) 15 16 17 18 19 20 21
SIG.HT (FT.) 3 3 4 3 2. 2 2
DATE (MAR.) 2.2 23 24 25 26 27 28
SIG.HT (FT.) 2 2 2 4 3 2 3
DATE (MAR.) 29 311 31
---------------. ---------------------------------
SIGHT (FT.) 3 - 3 2
-
OCEANSIDE
P E R S I S T E N C E
(CONSECUTIVE DAYS (3 OR MORE) SIGNIFICANT
WAVE HEIGHT IS 'N' FEET OR LESS)
30 DAYS OF OBSERVATION
APR. 1-309 1977
FEET DAYS
1 0,
2 49 39 39 39
3 159 89 49.
4 30.
5 30,
6 30,
8 30,
10 30,
12 30,
MAXIMUM DAILY SIGNIFICANT WAVE HEIGHT FOR APR. 1977
DATE (APR.) 1 2 ------------------------------------------------------------
3 4 5 6 7
STG.HT (FT.) 3 4 3 2 2 3 2
DATF (APR.) A 9 10 11 12 13 14
SIG.HT (FT.) 2 2 4 3 2 2 3
DATE (APR.) .15 16 ------------------------------------------------------------
17 18 19 20 21
SIG.HT (FT.) 2 2 2 3 3 2 2
r)ATF (APR.) 22 23 24 ------------------------------------------------------------
25 26 27 28
SIG.HT (FT.) 2 2 3 3 . 4 3 2
DATF (APR.) 79 30 ----------------------------------------------------------
SIC.HT (FT.) 2 2
•
a.
•
. —. — - - —
-
. — ---- —-- --
—
_____ - -
a — —
z I I
I - —
.1
-
..a ........ ..- ......
-
a . .
5 a . _ . — . . : - . - • :
.
—
-
__....._ .....•t ........._a a
a• - _.._.._I
• .:.
-::
11IIIIUIIlII1lIItI!IIIIIlIlJ IJIIIllIIfIJllIIIII!flhllll!I.l ItIIIIIfII!IIIIII!tlll
JflIsi FFR MAR '
i Wave Height Legend 11— > 8 METERS
- '-1-6 TO 8 METERS
100,
.
fl-4 TO 6 METERS
—3 TO 4 METERS
loll 2 TO 3 METERS
—1 TO 2 METERS
.15 10
-05 <1
ale METER
'I \
360
340
300
250
IVA
- — -- L Kuh
_L.----•.. .....
260- -• -..--.
.
\ -c• /'i" -...
I -S.
240 \ "1 /1'\ \ ,' '•120
/ •5__ '-.-. \ 220 /---H---_\, 140
200 160 I80
All Years
Figure III. I
FREQUENCY DISTRIBUTION ROSE
1951 -1974
STATION 6
(31.5N 118.4W)
COMBINED SEA/SWELL
Iyu
360
340
.1.11
300
260 .
September
360 340
320
300
250
60
--
October
360 340
320
300
10
260.j
I-47)
260--'r / IT
240' • / / 140
220
200
ISO
November
360 340
320
— — \,/• \ I
300
.' ••\ hi 5 ._•• I
I,••.- ."5' • I
.49
260 -
-
'5 / I 140
,•"•- I
220
200 I 160 180
December
360 \34
.
0
300
\ i
280
— —
I.t.t.
.18 1
260.---k
-.--
-- 240
220 - -.-------------- — -
280 -- — —
2
LESS 11.1
.05
260 ......
6-111-2
360 340
320 \_----- rc
300
280
I —
—t-
260 - .•-fT\ ' /
240 / 140 /
22$ i--- --H------
200 160
180
January
360 340
320 .I?0
\ \ I 300
Ito
280
38
/\L
LL
a 'CUR
260 •-4\ .---2• '5-'120
'/—_i--- 240
140 >( / I
/
22$
\t
200 1 16$ 180
February
360 340
be
300
Ito
280
LESS Tw-\
.22 26O---'
ol
240
220'
200
March April
340 •. 360
- .- —-
'il -it
260-- 07
'S
-
'S
5'
5-
.5- -
360 340
— I
>c\j111
360 \34
I
30$ K\,
•iI
-.:.s..\\
I1
'0 280
I OVER
.22
260
May June July August
6-111-4
STATION 6
WAVE HEIGHT DURATION GRAPH
1946-1974
COMBINED SEA/SWELL HEIGHT'
1946-47
1947-48
1948-49
1949-50
1952-53
1953-54
1955-56
1956-57
1959-60
1960-6!
1961-62
1962-63
1963-64
1964-65
1965-66
1966-67
1967-68
1968-69
1969-70
1-72
1972-73
1973-74
1974-75
__________ • _.. ._ - _________
_ : :L....... LL• -- ____
!- - : . . _i - - .. - . - - - - - -
--- - _-• - -, - .•. - -.....- !-. -
_ETETEEL
T.-
c
- -. -- - - - . - .•... - -
-_-
- -
:-=--
- - - - .... - - •- ••-J -
___ - - -
. .. - - - ..
_______
- - -=.- _ :_=- • _ _... __. _,...
.............................
-:•__-_- ___ -- - - -_- .. •. - -fl-- H- - - -•; -_•.....- - - . - - . - - I.
______ it
--
_.
=.. ___. • .
----•- - a-. - • - • -- - - r - --
=• - -=• •-.- - - I - - .. - -I -. - - I - - ............
JUL AUG SEP OCT NOV DEC JAN
+ DATA NOT AVAILABLE
TIME INTERVAL = 24 HAS
Figure III. 2
FEB MAR APR MAY JUN.
- 4511
- 3-I II
- 23 fl
3-I II
-
IAflLE 111.5 .
• STATION 6
(31.5N 116.4W)
EXTREME WAVE EVENT LISTING
COMBINED SEA/SWELL •' 5 METERS
• COMPILED FROM ONCE-DAILY WAVE COMPUTATIONS
1951-1974
CHRONOLOGICAL ORDERING WAVE HEIGHT ORDERING : PERIOD ORDERING
DATA HEIGHT PERIOD DIRECTION : DATA HEIGHT PERIOD DIRECTION : DATA HEIGHT PERIOD DIRECTION
29 MAR 53 5.7 10 310 06 MAP 56 6.7 11 344 • 24 DEC 64 5.8 11 311 06 MAR 56 6.7 11 344 29 FEB 72 6.6 11 321 • 06 MAR 56 6.7 11 344 20 APR 62 5.4 10 327 24 DEC 64 5.8 11 -311 • 29 FEB 72 6.6 11 321 08 JUN 64 5.6 10 298 29 MAR 53 5.7 10 310 • 29 MAR 53 5.7 10 310 24 DEC 64 5.8 11 311 08 JUN 64 5.6 10 298 • 20 APR 62 5.4 10 327 26 MAY 67 5.3 10 299 20 APR 62 5.4 10 327 • 08 JUN 64 5.6 10 298 05 MAY 68 5.0 10 298 26 MAY 67 5.3 10 299 • 05 MAY 68 5.0 10 298 04 MAY 69 5.1 9 273 07 MAY 70 5.1 9 320 • 26 MAY 67 5.3 10 299 07 MAY 70 5.1 9 320 04 MAY 69 5.1 9 273 • 07 MAY 70 5.1 9 320 29 FEB 72 6.6 11 - 321 05 MAY 68 5.0 10 298 04 MAY 69 5.1 9 273
6.11182 TABLEIII.5
Project No. 54268E-0002 Woodward-Clyde Consultants
APPENDIX C
BENEFIT CALCULATIONS
Project No. 54268E-0002 Woodward. Clyde Consultants
APPENDIX C
USER BENEFIT CALCULATIONS
for
CARLSBAD BOULEVARD SHORE PROTECTION
Loss of Property
It is estimated that the average rate of erosion is approximately 1.5 feet per
year along the 4500 feet length of the subject study area. It is assumed that
the value of the property is $400,000 per acre.
1.5 x 4500
Annual value of eroded property = 43,560 x $400,000 = $61,980
Loss of Beach User Benefits
It is generally considered that the beach season in Carlsbad is year around.
Maximum use will be in the summer, weekends and holidays. Minimum use will
be weekdays during the winter. Based on City of Carlsbad data the average
daily use for the 4500 feet of beach is 2640 persons which gives an annual
use of approximately 963,600 persons.
Using the Corps of Engineers' criteria of 100 square feet of beach required
for each user and an average beach width of 100 feet gives a beach capacity
of:
4500 x 100
100 = 4500 persons for peak periods
This appears to be consistent with the estimated average daily use of 2640
persons. It is therefore estimated that the average user days per year with
good access is 900,000.
It is estimated restricted access and parking will reduce the average use by
25 percent. Thus, the total user days lost per year is 225,000.
If the value of each recreation day benefit is assumed to be $1.50, and if
good access and parking is not maintained, the annual beach user benefit loss
will be:
Annual Beach User Benefit Loss = 1.5 x $225,000 = $337,500
Loss of Bicycle Lane Use
Carlsbad Boulevard has a dedicated bicycle lane along its full length 'in the
study area. This is considered a main recreational bicycle travel lane in the
C-'
Project No. 54268E-0002 Woodward-Clyde Consultants
area and Is conservatively estimated to have an average daily traffic of 200
and an annual traffic of 73,000. Each trip is considered equivalent to a
recreation-day benefit at a value of $1.50 per trip. Thus, the annual bicycle
user benefit loss will be:
Annual Bicycle user Benefit Loss = 1.5 x $73,000 = $109,500
Traffic Reduction Costs
Carlsbad Boulevard is a main north-south travel way which has an estimated
future average daily traffic volume (ADT) of 27,000 vehicles. This traffic
level is anticipated to be reached and exceeded within the next approximate
20 to 25 years. This gives an average yearly traffic of 9,855,000. For this
analysis an annual vehicle traffic of 9,000,000 is used. Loss of Carlsbad
Boulevard would require this traffic to go east on Tamarack Avenue
approximately 0.6 miles to Interstate Highway 5, south on Interstate 5 to
Cannon Road and then east on Cannon Road approximately 0.4 miles to the
coast. Using a vehicle operating cost of $0.25 per mile would produce a total
annual vehicle operating cost for using the detour of:
Annual Vehicle Operating Cost = 0.25 x (0.6 + 0.4) x 9,000,000 = $2,250,000
This detour. would also result in lost time for the occupants of the vehicles.
Assuming the average occupancy rate is 1.5 persons per vehicle, the average
speed is 35 miles per hour, and the value of a person's time is $5.00 per
hour, it will give an annual time cost for use of the detour of:
Annual Lost Time Cost = 5.00 x (0.6 + 0.4) x 1.5 x 9,000,000/35 = $1,928,600
Facility Replacement Costs
It is assumed that each existing utility would have to be replaced over a
length of 4000 feet once during the design life of 50 years. The estimated
cost for the replacement of each facility is as follows:
4" high pressure gas main - $240,000
12" water main - 200,000
12"-16" sewer main - 160,000
Electrical lines - 20,000
Telephone lines - 20,000
Total Cost $640,000
For a design life of 50 years and an interest rate of 12 percent, the
annualized cost is determined by multiplying the total cost by 0.12042.
Annualized facility replacement cost = $640,000 x 0.12042 = $77,000
Some additional costs may also be attributed to the proposed future storm
drain and reclaimed water line.
C-2