Imperial Beach, California
Alternative Formulation
Briefing Guidance Memorandum
1. BACKGROUND:
a. Study Area. The Silver
Strand is a relatively narrow sand spit that extends northward from the Tijuana
River inlet to the entrance of the San Diego Bay, in San Diego County,
California. It separates San Diego Bay
from the Pacific Ocean, and includes the shorelines of the North Island Naval
Air Station, City of Coronado, the Navy Amphibious Base, Silver Strand State
Beach, the Naval Radio Station, and Imperial Beach. The Silver Strand shoreline is located within the jurisdictions
of both the City of Coronado and the City of Imperial Beach.
The
study area is located along the southernmost stretch of the Silver Strand
shoreline that corresponds with the corporate boundary of the City of Imperial
Beach southward to the U.S./Mexico international border.
b. Study Authority.
The study is a reevaluation of the Federal project authorized by Section 101, Public Law 85-500, River
and Harbor Act of 1958, approved July 3, 1958.
“SEC. 101. That the following works of improvement of
rivers and harbors and other waterways for navigation, flood control, and other
purposes are hereby adopted and authorized to be prosecuted under the direction
of the Secretary of the Army and supervision of the Chief of Engineers, in
accordance with the plans and subject to the conditions recommended by the
Chief of Engineers in the respective reports hereinafter designated: ...San
Diego County: House Document Number 399, Eighty-fourth Congress...”
c. Project History.
The River and Harbor Act of 1958 authorized construction of a system of
five stone groins along the beachfront of the City of Imperial Beach. The plan called for the northernmost groin
to be located at the north end of the existing U. S. Naval Radio Station
seawall. The other four seawalls were
to be constructed southward at intervals of about 305 meters (1,000 feet). The southernmost groin was to be 122 meters
(400 feet) south of Coronado Avenue (now Imperial Beach Boulevard). Construction was to start with the
northernmost groin and proceed as the down-coast side of each groin filled with
sand. Groin Number 1 (northernmost) was
completed in September 1959. Groin
Number 2 was completed in January 1961.
Groin Number 1 was subsequently extended in 1963. The two groins were not effective and
construction of the remaining project was deferred.
The City
requested that the Corps re-activate the project and investigate alternative
means to stabilize and restore the beach.
In 1979 the Chief of Engineers approved a Post Authorization Change
Report that proposed constructing a submerged offshore breakwater in lieu of a
groin system. After award of a
construction contract in 1985, a Federal District Court enjoined the project on
the basis that significant changes had occurred since the preparation of the
Environmental Impact Statement in 1978.
The construction was terminated.
The authorized project for Imperial Beach was re-classified to deferred
category in 1993-94.
d. Problem.
The Silver strand shoreline was initially a natural sand spit supplied
with sediment primarily by the Tijuana River.
Since the construction of dams and reservoirs on the river, the ocean
side of the Silver Strand has had to be artificially renourished to combat
beach erosion. Currently, erosion is
occurring at the Imperial Beach study area, while up-coast locations are
accreting.
The City of
Imperial Beach shoreline is severely impacted by coastal storms. The report
defines two study area reaches--Imperial South reach and the Imperial North
reach—based on the existence of coastal protection structures and expected
effects of long-term erosion. Local and
private interests have installed revetment across the beach face of the
majority of the beachfront buildings in the Imperial-South reach. Winter beach erosion leaves the beach
depleted of sand with cobbles and boulders exposed. Condominiums located immediately behind the revetment are subject
to damages caused by overtopping waves during significant winter storms. Where the revetment ends just south of the
development, high tides and winter storms wash debris and sand around the
revetment and cause flooding. In the
south reach, structures are susceptible to inundation and wave attack
only. The study assumes that long term
erosion would be arrested at the existing south reach revetment in about year
2007.
Structures in
the Imperial-North reach are susceptible to inundation, wave damage, and long
term erosion. Generally, revetment or
seawalls do not protect older buildings on the shoreline of the Imperial-North
reach. Net shoreline retreat along this
reach is estimated as 2 meters (6.6 feet) per year. The report indicates that at current rates, the total volume of
available sand may be exhausted by 2007, leaving a natural armoring of cobbles
and boulders at the shoreline. At that
point, the shoreline will be approximately at the first row of coastal
development. Shoreline retreat would be
expected to slow to about one meter per year at that time. The report indicates that about 30
structures could be lost to long-term erosion by the end of the 50-year period
of economic evaluation.
There are 102
residential structures, four commercial structures, and 19 vacant lots along
the beachfront of the Imperial—North and Imperial—South reaches. The report cites total equivalent annual
damages as $2,054,400 in the absence of the proposed Federal project. This amount includes $867,100 in storm
damages to structures and contents, $445,600 attributed to land loss, $391,600
equivalent annual costs for utility relocations, and $350,100 in equivalent
annual recreation losses.
e. Report Recommendation.
The report indicates that the apparent NED plan consists of constructing
a sand-filled beach berm along 2,165 metes (7,100 feet) of shoreline at the
City of Imperial Beach. The initial construction would consist of placing
850,000 cubic meters (1,110,000 cubic yards) of sand at elevation +4 meters
(13.1 feet) referenced to mean lower low water (MLLW). The beach fill at elevation +4 meters MLLW
would be about 23 meters (75 feet) wide.
The foreshore would slope from elevation +4 meters MLLW 1-meter
vertically for 15 meters horizontally to mean sea level at 0.95 meters
MLLW. Based on an estimated long-term
erosion rate of 2 meters (6.6 feet) per year, the berm would be expected to
erode away in about 11 years. The beach
berm would be replaced at that time.
Based on this 11-year cycle it is expected that beach berm would be
replaced four times during the 50-year period of anticipated Federal
participation in the project. Sand
would be dredged from offshore borrow areas.
A total of 3,400,000 million cubic meters (4,420,000 cubic yards) would
be required for the initial construction and four beach berm replacements. The report indicates that the proposed
project would reduce storm damages by about 89 percent.
f. Project Economics. The initial construction cost is stated as $5,986,500 at October
2001 prices. Continuing construction
costs are shown as $23,946,000. Based
on a 50-year period of evaluation and a 6.375 percent discount rate, this plan
has equivalent annual costs cited as $789,600.
The report indicates that equivalent annual benefits associated with the
plan are $1,799,100. Equivalent annual
net benefits are cited as $1,009,500 and the indicated ratio of
benefits-to-costs is 2.3 to 1.0.
g. Cost-Sharing.
The City of Imperial Beach is the prospective non-Federal sponsor of the
project. Cost sharing for initial
construction of the beach nourishment project would generally be 65 percent
Federal and 35 percent non-Federal in accordance with Section 103 of WRDA 1986,
as amended. Cost sharing for continuing
construction would generally be 50-percent Federal and 50-percent non-Federal.
2. POLICY
ISSUES IDENTIFIED BY CESPL FOR DISCUSSION AT THE AFB:
a. District Issue 1 (Authorization):
The existing project authorizes the Corps of Engineers to provide shore
protection along Silver Strand-Imperial Beach by constructing coastal and
nearshore structures for the purpose of shoreline stabilization. The authorized project for Federal
improvements is cost shared at a ratio of 57% Federal and 43% non-Federal. The cost sharing for the originally
authorized project was 40% Federal and 60% non-Federal. The originally authorized project has been
partially implemented, but completion was terminated based on project
ineffectiveness. The authorized Federal
project was not constructed due to opposition from local environmental
interests. The NED plan under the
existing GRR effort involves providing shore protection for Silver
Strand-Imperial Beach by constructing an initial beach fill project, with
periodic nourishment over a 50 year project life. In addition, the currently authorized project’s cost sharing
ratio of 57/43 is inconsistent with WRDA 1986, which established a cost sharing
ratio of 65% Federal and 35% non-Federal for shoreline protection
projects. Since the current GRR study
recommends a plan to provide shore protection to Imperial Beach through beach
fill with periodic nourishment versus structural solutions as presently
authorized, and since the currently authorized project cost sharing ratio is
inconsistent with WRDA 1986, SPL recommends the NED plan identified under the
current GRR study be implemented under a new authority granted by WRDA
legislation.
HQUSACE
Review Team Assessment and Recommendation: The policy
compliance review team concurs that additional congressional authorization
would be required to implement any project proposal that is significantly
different from the authorized project.
The apparent NED plan presented in the report is completely different
from that currently authorized; therefore, implementation would require new congressional
authority. However, note that based on
the plan formulation presented in the report, the policy compliance review team
questions whether the NED plan has properly identified (refer to comments in
paragraph 4 of the following). Cost
sharing for initial construction of the NED plan would be consistent with that
specified in Section 103(c)(5) of WRDA 86 (generally 65 percent Federal and 35
percent non-Federal). Cost sharing for
periodic nourishment (continuing construction) would be consistent with Section
215 of WRDA 99, which requires that such costs be shared 50 percent Federal and
50 percent non-Federal. While this
represents cost sharing in general, specific project cost sharing may differ
based on ownership and use of the shores.
The general cost shares apply for developed public or private shores
where there is adequate public access and use.
For public non-Federal shores, such as a park, the cost sharing is 50/50
and for private non-developed shores the cost sharing is 100 percent non-Federal. Federal shores are cost shared 100 percent
Federal (reference ER 1165-2-130 and Appendix E of ER 1105-2-100 http://www.usace.army.mil/inet/usace-docs/eng-regs/cecw.htm ).
District Response: District
concurs with HQUSACE Review team’s comments.
Implementation of the NED Plan will require congressional
authorization. The study area shoreline
is 100% Public, non-Federal. Project
costs will be shared 65% Federal and 35% non-Federal. Periodic nourishment would be consistent with Section 215 of WRDA
99, which requires such costs to be shared 50% Federal and 50% non-Federal.
Discussion:
All agreed
that the proposed plan would require new authorization for reasons stated in HQUSACE
recommendations.
Action: The GRR will be processed to
the Congress for new authorization in a Water Resources Development Act. Project
cost sharing is to be based on shoreline ownership, use, and type and incidence
of benefits. The project benefits are
reduced hurricane and storm damage to public and private property and
incidental recreation, see Table 2, page 11, ER 1165-2-130. For those project segments that provide
hurricane and storm damage reduction to publicly owned and privately owned
structures, 65 percent Federal/35 percent non-Federal cost sharing would be
applicable. However, for those segments
where the project will protect lands dedicated to park or conservation uses,
applicable cost sharing is 50 percent Federal / 50 percent non-Federal. Costs to protect privately owned vacant land
would be apportioned 100 percent non-Federal.
Composite cost sharing that appropriately considers the type of facilities
that would be protected by the project will be shown in the draft report, see
Appendix C, page C-1, ER 1165-2-130.
b. District Issue 2 (Ned Plan): The
NED plan (Alternative 1A) identified in the study proposes an initial beach
fill at Imperial Beach of 850,000 cubic meters, with a resultant beach width of
23 meters. Under this plan, the
shoreline would be nourished at a frequency of once every 11 years. Annual net benefits derived from this plan
are $1,009,543 at a BC ratio of 2.28.
Based on the CCSTWS, San Diego County analysis, the NED plan presupposes
a steady shoreline erosion rate.
Following initial construction (initial beach fill), at Year 11, the
shoreline is predicted to recede to baseline conditions resulting in higher
residual damages from wave attack and flooding. Alternative 1B involves an initial beach placement of 2,000,000
cubic meters, providing an initial beach width of 54 meters, with a nourishment
frequency of once every 15 years. At
Year 15, following initial construction, the protective beach is predicted to
erode to 23 meters from the baseline shoreline, thus providing a beach buffer
zone of 31 meters between nourishment cycles.
The annual net benefits derived from Alternative 1B are $946,247 at a BC
ratio of 1.86. Since Alternative 1B
results in lower residual damages than Alternative 1A, and embeds a factor of
safety by establishing a beach buffer zone between nourishment cycles, and
since the annual net benefits difference between the two alternatives is
$63,116, SPL recommends the adoption of Alternative 1B as the Federally
preferred plan for implementation.
HQUSACE
Review Team Assessment and Recommendation: The district recommends adoption of a more expensive plan
with lower net benefits than the tentatively identified NED plan. The district notes that the more expensive
plan would have a factor of safety by establishing a beach buffer zone. Note that based on the plan formulation
presented in the report, the policy compliance review team questions whether
the NED plan has been properly identified (refer to comments in paragraph 4 of
the following). In general, ER
1105-2-100 requires that the NED plan be identified and recommended for
implementation, unless the ASA(CW) grants an exemption to this
requirement. A plan that is smaller
than the NED plan may be granted a “categorical exemption” and cost shared in
accordance with the NED plan if requested by the non-Federal sponsor. A plan that is larger than the NED plan may
be recommended as a locally preferred plan (LPP). Paragraphs 4-3b(2)(a) and (b)
of ER 1105-2-100 describe the documentation required to support recommendation
of a LPP. However, typically the
incremental cost of the LPP above the cost of the NED plan would be 100 percent
non-Federal. Table 9.2 of the report
shows that equivalent costs increase by 40 percent when moving from Alternative
1A to 1B, while storm damage reduction benefits increase by only 12
percent. Table 7.2 shows that all of
the increase in storm damage reduction benefits would accrue to the
Imperial--North reach of the proposed project (Note comment 4.d below). The table shows that recreation benefits
increase by 24 percent. Thus, making
the case that the increase in storm damage reduction is “justified” by the
increased costs may be difficult.
District Response: The District concurs with HQUSACE Review Team’s
interpretation of the policy regarding recommending a project larger than the
NED Plan. Responses to comments
regarding identification of the NED Plan are addressed in the District’s
responses to Paragraph 4 of the following.
Discussion:
Corps
precedent for shore protection studies traditionally involves maintaining a
design beach section with a specific level of protection. Periodic nourishment is sacrificial material
to assure that the design beach will be available and integrity of the project
is maintained over the period of Federal participation in the authorized
project. Accordingly, Plan 1A is not a
complete plan and should be eliminated as an alternative plan.
Action: The draft report will be
revised to eliminate Alternative 1A as an alternative plan. An
appropriate array of alternative plans will be formulated and displayed in the
report to demonstrate that the NED plan is properly identified.
3. PLAN
FORMULATION AND EVALUATION:
a. Formulation
of Hurricane & Storm Damage Reduction Alternatives: The method
used to formulate alternatives may not be conducive to proper identification of
the NED plan. All alternatives shown in
the report include a design section that provides for a 23-meter (75-foot) wide
beach berm at elevation +4 meters referenced to mean lower low water. Plan 1A allows the design beach berm to
erode away (no advance maintenance), while other alternatives vary the initial
fill by including progressively larger quantities of advance maintenance. Typically, hurricane and storm damage
reduction plans that employ sand fill are formulated by first determining the
economically optimal design section.
Normally, this is accomplished by evaluating design sections that vary
the width and elevation of the design berm.
Also, such evaluations typically consider whether including a dune is
appropriate, and if so, what dune crest elevation is optimal. Once the optimum design profile is
established, analyses are done to determine the optimum advance nourishment and
periodic nourishment schedule. The NED
plan is that which optimizes both the design profile and nourishment
schedule. Advance maintenance material
is considered sacrificial. Its purpose
is to help maintain the integrity of the design section over the period of
Federal participation in the project.
If the design profile is not maintained for the 50-year period of
recommended Federal participation, as for alternative 1A, expected damages
should vary each year during the period of evaluation. Typically the NED plan design section is
identified and maintained for the period of Federal participation rather than
allowing different levels of protection for each year of the evaluation. The report must display an array of
alternatives that bracket the optimal design section. Consequently, plans that are both smaller and larger than the
optimal plan should be developed, evaluated and displayed in the report. Note that shore protection and beach
erosion control are not project purposes identified in WRDA 86. Consequently, the project must be formulated
to address the hurricane and storm damage reduction project
purpose. Thus, the plan formulation
should also evaluate viable structural solutions, such as revetments, that may
reduce hurricane and storm damages.
District Response:
The study’s coastal engineer and economist determined jointly that a
23-meter beach width was the minimum beach width required to protect
residential and commercial properties against a 100-year storm event. Following receipt of HQUSACE comments, additional
beach widths were analyzed to identify the optimized design section. Design beach widths of 12-meters, 23-meters,
25-meters, 34-meters, and 54-meters were analyzed. The 25-meter beach width, the initial width at which zero damages
related to wave attack and inundation from run up will occur, resulted in the
maximum net benefits. Varying the berm
height to optimize the design beach section was not evaluated, as it is the
position of the District that the current design height of +4-meters MLLW mimics
the natural summertime beach configuration within the study area and thus will
maximize the functionality of the beach fill project. Additional details regarding beach width and height optimization
will be covered in responses to comments regarding “Dune and Beach Width
Alternatives” and “Predicted Project Performance”.
Alternative 1A
consists of maintaining the baseline shoreline by initially providing a
23-meter wide beach. The 23-meter wide
beach would erode to the baseline conditions in 11 years. Therefore, this plan calls for periodic
nourishment every 11 years. The
disadvantage of this plan is that it provides varying levels of protection. The initial placement provides 100 year
level of protection; however, expected damages increase each year prior to
renourishment as the beach width erodes.
Plans 1B, 1C,
and 1D maintain the shoreline at the baseline + 23-meters. All of these plans provide 100 year level of
protection throughout the project life.
These plans differ only in the amount of advance nourishment to be
placed. Plan 1B provides for 15 years
of advance nourishment; Plan 1C provides for 22 years of advance nourishment
and plan 1D provides 50 years of advance nourishment.
Section 4.5 of
the Main Report addresses viable structural solutions including groins,
revetments and detached breakwaters.
These alternatives were studied in depth and documented in a
reconnaissance report dated December 1995.
That report indicated that these structural solutions were not justified
economically. In addition, there was no public support for these types of
solutions. Therefore, these
alternatives were screened out during the preliminary plan formulation (F-3)
phase of this GRR. The draft report
will include a more detailed discussion of the investigations conducted during
the reconnaissance phase study.
Discussion:
HQUSACE
representatives explained that Principles and Guidelines requires the Corps to
consider a full range of alternatives to support the identification of the NED
Plan and that the Plans 1B thru 1D were the same plan with different periods of
periodic nourishment. Also see issues
1b. above and 2b below. The District
explained the rationale with respect to not looking at alternative beach
elevations. A beach lower than natural
section will cause depressions and ponding in backshore section of berm, higher
berm elevations will result in erosion scarp which is unacceptable. The district pointed out that the current
coastal engineering manual recommends building to the natural berm elevation
since the beach will seek its long term equilibrium. HQUSACE staff is satisfied with explanation regarding berm height
being a single elevation and that the beach design is associated with varying
beach widths. However, HQUSACE staff
stressed that not evaluating alternative berm elevations is a departure from
basic plan formulation principles. It
was agreed that the district would revise the draft report to clearly explain
and provide the supporting rationale for the basis for alternative protective
beach designs including the berm elevation, berm widths and slopes. Also, the district will explain why
providing protection to storms greater than a 100-year storm return frequency
was not included as part of the formulation and analysis.
Action: The draft report will be
revised to clearly explain and provide the supporting rationale for the basis
for alternative protective beach designs including the berm elevation, berm
widths and slopes. The report text should note that Corps
projects are NOT formulated to satisfy an arbitrary level of protection. Basic planning practice requires that
arbitrary constraints to plan formulation be avoided. Contrary to the district response, there is no minimum level of
protection that must be addressed. Instead,
a comprehensive array of alternative designs must be formulated such that the
plan that maximizes net benefits (the NED plan) can be identified regardless of
the level of protection that it may provide.
b. Dune
and Beach Width Alternative: The report does not address alternatives for dune
development or optimization of the beach width, which would remain throughout
the period of analysis in between nourishment cycles. Therefore, it is not clear that the formulation has identified
the NED plan. The draft report should
address varying designs for beach width and the feasibility of dune
alternatives to assure that the NED plan has been identified.
Beach Width: Through analysis of inundation and wave
forces within the study area, it was predicted that a 23-meter wide beach,
added to an existing varying base year beach width of 10 to 25-meters, would
provide the minimum base width necessary to protect against almost all storm
damages. The analysis revealed a
23-meter wide beach fill project would result in minor inundation damages and
zero damages from wave forces for up to the 100-year storm event. Table 5 in the Coastal Engineering Appendix
(Appendix B) displays the expected extreme value for shoreline retreat for
storm return periods ranging from 1 to 100 years. For the 100-year storm event, Table 5 (land loss damage category)
predicts a 31-meter shoreline retreat.
It was calculated based on this retreat analysis that a minimum 23-meter
wide beach fill project (on top of a base year beach of 10-meters) will be
adequate to protect against damages associated with storm induced erosion and
simultaneous wave attack from a 100-year event. Based on HQUSACE comments, an optimization analysis of
protective design beach widths of 12-meters, 23-meters, 25-meters, 34-meters
and 54-meters was accomplished. The
optimization analysis revealed maximum net benefits are derived under the
25-meter beach width plan. The
accompanying table displays the cost and benefit relationship of the five (5)
analyzed plans.
Dune
Elevation: Naturally
formed dunes exist in very few beaches in California. In the case of Imperial Beach, no natural dune exists. Dunes
provide protection against hurricanes and high storm surge that is typical on
the east coast. This is not the case
for the west coast at Imperial Beach.
Imperial Beach is not susceptible to hurricane storms and high storm
surge; therefore, the District concluded that dunes would not be considered as
part of the design cross section. However, a berm elevation of +4-meters MLLW
was selected for the design section, as this elevation closely corresponds to
the natural berm elevations found within the study area. Elevations greater than +4-meters MLLW would
result in berm instability and berm scarping, which may adversely impact
recreational opportunities and potentially negatively impact the spawning
cycles for grunion. Additionally,
higher and steeper berms may result in cost inefficiencies associated with
accelerated erosion. Berm elevations less
than +4-meters MLLW will result in large beach areas inundated to the
combination higher tidal cycles and the higher frequency storm events (MHW for
this area is 1.52-meters and Hs for a return period of 2-years is
4.2-meters), and possible ponding as a result of overtopping waves and runup, and again with potentially adverse impacts to spawning grunion. In addition, the berm elevation of +4-meters
MLLW for the design beach fill cross-section is consistent with EM-1110-2-1100
(Part V), which states “design berms should generally correspond to the natural
berm crest elevation”.

Discussion:
The draft
report will need to be revised to present the results of the district’s
optimization of the design beach. In
addition, to demonstrate that a full array of alternative measures considered,
the district will revised the report to include information from the
reconnaissance study on other alternatives considered and explain why they were
screened from further analysis. The
district also explained the difference in design storm water levels and how
they differ from differ between the East, West and Gulf coasts. In the draft report the district will
include discussion of the design storm levels and levels how they differ from
the East, West and Gulf coast areas. Also see discussion for issue 2b and 3 a.
Action: The draft report will be
revised to include information from the
reconnaissance study on other alternative plans considered and provide reasons
why other alternative plans are not viable and were not considered for further
study during the feasibility phase. The
draft report will also address the design storm water levels and explain how
they differ between the East, West and Gulf coast areas.
District
Response: Concur. The
District has accomplished an analysis to optimize the cost effectiveness of the
advance nourishment cycles and to optimize the benefits for the total project
(protective base beach plus the advance nourishment cycles). The analysis concluded that the most cost
effective renourishment frequency is once every 10 years, and involves
placement of 760,000 cubic meters of sand to create a 20-meter wide advance nourishment
beach. The benefit analysis of the
total project plans concluded that the plan for a protective base beach width
of 25-meters with an advance nourishment cycle of once every 10 years is the
optimal total project. The following
tables display the annualized cost comparison for various renourishment
frequencies and the annual net benefits for the total project plans.

ANNUALIZED COST FOR
RENOURISHMENT FREQUENCIES:

ANNUAL NET BENEFITS FOR
THE TOTAL PROJECT PLANS (Base Beach Widths vs. Renourishment Frequencies):
Discussion:
The draft
report will be revised to include the information in the district response to
support the recommended periodic nourishment period.
Action: The draft report will
incorporate the development of the periodic nourishment frequencies including
rationale for volumes of nourishment.
The district will ensure that sufficient data is presented in the draft
report to support the conclusions.
d. Incremental Evaluation: The plan formulation should include an
incremental evaluation of the feasibility of protecting the Imperial--north and
Imperial--south reaches individually.
While the report indicates that the minimum project length that is
economical to construct covers both the north and south reaches, analyses should
be provided to support this assumption.
Tables 3.3 and 3.7 indicate that all erosion damages (structures, land
loss, and utility relocations) are attributed to the Imperial—North reach. However, table 3.8 shows utility relocation
damages equally distributed between the Imperial--North and Imperial--South
reaches. This apparent error should be
corrected in the draft report.
Information shown in table 3.8, when corrected, indicates that only 9.6
percent ($164,000) of the total equivalent annual hurricane and storm damages
($1,704,300) is attributed to the Imperial--South reach, while 90.4 percent
($1,540,300) is attributed to the Imperial-North reach. This suggests that a plan that would provide
an equal level of protection to both reaches is not optimal. This should be addressed in the draft
report.
District Response: The
entire project area from the northern limit to the southern limit totals
approximately 1.5 miles. The study area
was split into 2 reaches to account for the difference in beach profiles. A
rubblemound revetment fronts the south reach while the north reach is a planar
beach. It is not engineeringly feasible to build a protective
berm in the North reach without having it tail off significantly in the south
reach.
In response to HQUSACE
“Incremental Evaluation” comment that the analysis should include an
incremental evaluation of the feasibility of protecting the Imperial-North and
the Imperial-South reaches individually, the District computed the volume
needed to build a project that only protects the Imperial-North reach and
compared it to a project that would protect both the Imperial-North and
Imperial-South reaches. The District
took a conservative approach in analyzing the incremental benefits for
inclusion of the south reach. The
District only included the major damage categories of inundation, wave attack
and erosion. The benefits, shown in the
following table, exclude recreation, clean up and utilities relocation. The analysis concluded that the incremental
cost for Imperial-South is justified.

Discussion: The response to this comment does not display the data
to support the results as presented in the table. However, the methodology and results appear to be reasonable.
Action: The draft report will present
the results of the incremental analysis.
The draft report will be revised to include appropriate supporting data
to demonstrate the incremental area for the south reach beach is incrementally
justified.
e.
Predicted Project Performance:
The report
indicates that each of the alternatives eliminates all inundation or wave
attack damages in the Imperial--south reach.
This does not seem reasonable, particularly for alternative 1A since
damage potential should increase each year after the initial sand placement. For this alternative, damages should
approach without project conditions immediately prior to renourishment. Also, the assumption that all inundation or
wave attack damages would be eliminated raises the question of whether a
smaller berm width would reduce project costs without significantly impacting
benefits. This issue should be
addressed in the draft report by formulating and evaluating an array of
alternatives, with different berm widths / elevations, for each project reach.
District Response: The
district concurs that damage potential in the south reach for Plan 1A should
increase each year between sand placement.
Our without project conditions model for the south reach accounts for
damages as the beach in front of the revetment erodes. By 2007, our analysis shows that no beach exists
in the south reach. At that point, wave
attack and inundation damages start to occur.
Since Plan 1A fixes the beach at the base shoreline, this assumes there
is some beach in front of the revetment.
Therefore, no wave attack or inundation damages occur.

Discussion:
The State
of California expressed concern that south beach revetment is not engineeringly
designed and in the long term could fail.
The district agreed it would address the State’s concern by considering
that under without project conditions maintenance of the revetment will be
required to assure that the revetment is effective. As discussed in earlier comments Alternative 1A has been
eliminated from further consideration.
In addition the district explained that for beach widths larger than 25
meters there is zero residual damages as a result of limitation of maximum
design storm due to depth limited wave and tide elevations, as well as runup
dissipation.
Action: The
draft report will explain why the district does not expect any residual damages
to occur for design beach widths of 25 meters and larger. This should include information to also
address the south beach experiencing wave attack and inundation. The cost of maintenance of sections that are
revetted will be developed and presented in draft report. The district will determine the benefits
associated with avoidance of these maintenance costs and include them in the
evaluation of alternative plans. In
addition, Table
5, Appendix B, page B-11, indicates that the storm with a 1-year return period
would be expected to produce 8 meters of storm induced erosion. Similarly, about 31 meters of storm induced
erosion would be expected to occur given the 100-year event. Based on the data in Table 5, the expected
(probability-weighted) annual storm induced erosion is 16.8 meters. Typically, not all of the material removed
from a beach during a storm is lost from the system. Material displaced immediately offshore may be re-deposited on
the beach during a post storm period.
Nonetheless, the report should address the apparent disparity between
the assumed 2 meter per year average long-term erosion rate and the suggested 8
meter erosion rate associated with the 1-year return period storm. Given the data of Table 5, the report should
explain why the evaluation predicts zero residual damages for the with-project
condition.
f.
Significant Wave Height: Table 2.2 on page 2-10 shows that the
significant wave height is expected to be nearly identical for the 25-year through
100-year events. It is not clear why
this would be the case given the change in tidal conditions, wind severity, and
wave propagation that would be expected for the more severe events. An under estimate of wave heights for
significant events could lead to inaccurate estimates regarding the physical
and economic performance of the alternatives and has potential to impact the
NED plan selection. The district should
review the significant wave height analysis to verify that the appropriate
values are being used.
District Response:
The wave climatology for the extreme wave analysis was developed based
on hindcasts of 34 severe storm events during the period 1904-1988. The hindcast data set was transformed to the
project location accounting for island sheltering, refraction, shoaling, and
depth limitations. Wind driven water
level superelevation (set-up) tends to be small in Pacific Ocean wave analyses
and thus is not a governing factor. In
the Los Angeles District, extreme value wave analysis typically assumes a mean
higher high water tide elevation. Wind
severity is also not a critical factor as severe waves are generated by distant
storms and propagate as swell, compared to wind severity considerations in a hurricane-based
extreme wave analysis. The shallow
water extreme value statistical analysis results in a set of waves
representative of various recurrence intervals. The significant wave height values are nearly identical for the
25-100 year recurrence intervals which is a direct result of the fact that wave
heights in excess of 6.2 m were depth limited due to wave breaking
considerations.
Discussion:
Clarification
was provided by the District regarding the depth limited aspects of the waves
generated between 25 to 100 year storm events. The district will provide information in the draft report to
explain the depth limited aspects of the waves generated 25 to 100 year storm
events.
Action: The draft report will include
information and discussion to support the depth limited aspects of the waves
generated between the 25 to 100 year storm events.
g.
Sand Borrow Sources: Paragraph 4.7 discusses two offshore borrow
sites considered as potential sources of sand fill. However, previous text discussions on page 2-5 indicate that
while the Imperial Beach section is experiencing significant erosion, the
Coronado reach to the north is experiencing significant accretion. Since the material accreting in the Coronado
reach is being carried by littoral forces from the Silver Strand and Imperial
reaches to the south, it may be economical to consider back passing sandy
material from the Coronado area as a borrow source. The district should expand the formulation analysis to address
the potential to back pass material in order to assure that the most economical
borrow source has been identified.
District Response:
The shoaled area near Coronado beach and near Zuniga Jetty was looked at
by the Geotech Branch initially during the early phases of the study as a
possible source of sand for the project.
After some rough calculations into the cost of dredging the area and
cursory analysis of sediment sizes at this borrow area, it was not further
considered during the study. There are
two main reasons why:
1.
This area is more than 3 miles away from the beach site. During the study it was recognize that 3
miles or so seemed to be the cut-off for consideration of borrow areas, since
the cost for dredging goes up as at a greater distance from Imperial Beach,
especially at a distance of greater than 3 miles.
2.
The composite grain sizes for the Coronado/Zuniga Jetty borrow area did
not fit the grain size composite envelope for the Imperial Beach site. In other words, the grain sizes for sediment
in this borrow area were too small when compared to the sizes needed to
maintain the beach, i.e. they were not compatible with the Imperial Beach
site. The sediment is also of too low a
density to maintain the profile at Imperial Beach, i.e. it would wash away
faster than a borrow site with larger grain sizes.
Discussion:
The
district response resolves the concern.
Action: The draft report will include the information contained in the district response.
h.
Independent Technical Review: The certification of independent
technical review notes that an independent District team completed technical
review for the project proposal. The
geo-technical report suggests that the Los Angeles District has a “limited
history” with hurricane and storm damage reduction projects. Consequently, we recommend that the District
seek advice of the Philadelphia, Wilmington, or Jacksonville District in regard
to state-of-the-art plan formulation and design of hurricane and storm damage
reduction projects. The report makes
reference to the Corps’ Shore Protection Manual (SPM). Current coastal engineering practice has
gravitated toward equilibrium profile analysis in order to determine the volume
placed, and the benefits realized. This
is a more conservative design than the use of overfill factors advocated in the
SPM. The new Coastal Engineering Manual
(CEM) (Draft EM 1110-2-1100) being developed by the Waterways Experiment
Station uses this new technique. Refer
to the WEB site for the CEM: http://bigfoot.wes.army.mil/cem026.html for additional details.
District
Response: This analysis consulted extensively with the
Philadelphia District, New York District, San Francisco District, FEMA, and
North Carolina Sea Grant. In fact, the
main technical criteria for determination of wave force damages was obtained
from a study conducted by the Philadelphia District (see Appendix A, reference
USACE-PD 1992). This study used many
technical references including the Shore Protection Manual and the draft
Coastal Engineering Manual. However,
this study relied primarily on the Coast of California Storm and Tidal Wave
Study (CCSTWS). The CCSTWS was
conducted by the Los Angeles District and evaluated decades of measured data to
quantify historic shoreline and profile change. These analyses are considered more accurate and representative
than any generalized calculations for long-term shoreline change.
Discussion:
HQUSACE
strongly recommends the Los Angeles District coordinate plan formulation and
design efforts with other districts, i.e. CESAJ, that have been successful in
implementation of shore protection/beach fill projects. These
Corps districts have developed computer models (i.e. COSTDAM, GRANDUC), while
not perfected, that successfully integrate the engineering and economic aspects
of hurricane and storm damage reduction projects. Information on COSTDAM is provided as an attachment to this
guidance memorandum.
Action: The study team will continue
to coordinate and get information from other districts as needed.
4. HURRICANE AND STORM DAMAGES:
a. Long-term Erosion Damages: In Table 3.3, projected erosion damages in the north reach are almost $600,000 per structure in year 10 and over $2.1 million per structure in year 15. More specific discussions should be included in the report to support these significant levels of impact. The value of contents within a structure would be expected to be minimal when structural failure due to long-term erosion is eminent. Consequently, support should be provided for why significant content damages have been included for the long-term erosion damage estimates. Further, it may be more reasonable to assume that structures that can be moved from the shoreline would be, rather than be lost to long-term erosion. The evaluation should document that structures assumed to be lost to long-term erosion could not be moved from the shore or protected in place.
District
Response:
Data in the Table 3.3 was verified with the erosion damage model. In
year 15 the total number of structures destroyed should be 6 and in year 20, 7
structures (corrections will be made to the appendix after the AFB). These
changes reduce the average damages per structure in year 15 to a little over $1
million per year, and almost $240,000 per structure in year 20. The significant
level of impacts in years 10 and 15 are due to large structures being
destroyed. For example in year 10 a beach-front motel is anticipated to be
destroyed along with 2 apartment buildings. In year 15, three condominium
complexes are destroyed (including a major 50 unit complex).
The District concurs that some small percentage of
contents may be moved prior the structure being lost to long-term erosion. However, the District has observed that
along other erodible stretches of the southern California shoreline, residents
continue to inhabit structures that are at risk to imminent collapse. These residents have made no attempt to
safely secure valuable contents from the risk of catastrophic structural failure. Per HQUSACE recommendation, the District
will re-evaluate the use of 50% content to structure ratio for erosion
damages. The draft report will be
updated to include either additional support for the ratio that was used, or a
description of the rationale used to apply a different ratio.
Discussion:
HQUSACE
expressed concerned with the reasonableness of the assumption that no action
would be taken by property owners to reduce damage with some kind of
improvement. HQUSACE staff asserts that a reasonable economic assumption would
be that some improvement would be made especially for the high value
complexes. District countered that
there are no definite programs for the City or State that guarantees protective
improvements will be implemented.
HQUSACE indicated obvious work had been done in the past by individuals
and collective property owners to protect their assets with revetments and
bulkheads, as well as with beach nourishment.
District noted that past beach fills were opportunistic and related to
Federal activities (such as the Navy’s home porting project). The district does not believe any new
features will be implemented within the foreseeable future, nor does the
district believe that opportunistic beach fill projects can be predicted and
counted upon under future without project conditions. The State declared that
they would implement protective beach fill projects only if they could leverage
Federal funds to assist in constructing such projects. The City declared that reach wide beach fill
projects could not be implemented by the city or private parties because of the
construction costs, and thus this kind of protective project would require
state and/or Federal participation to construct. Additionally, State and City officials indicated that the
California Coastal Commission policy is against placement of protective
structures seaward of existing tide lines, and that any emergency actions or
permitting to protect an individual’s property will require an “after-the-fact”
regular permit, to include open ended mitigation of the installed
structure. Because of the potential
costs, such open-end commitments are generally avoided by individual property
owners, and may be sufficient cause for an owner or development to not take
action to protect his structure against potential storm induced damages. This comment was confirmed as valid by the
staff of the California Coastal Commission following the AFB conference. Based on this additional information/clarification
from the State, City and district representatives, it was agreed that it would
be reasonable to expect that non-Federal interest would take no action under
without project conditions. It was
recognized, however, that the district would need to revise the draft report to
provide complete support for this without project condition. This will include
State laws, policies, regulations, precedents, and/or examples to support no
action, other than soft measures.
Action: The draft report will be
revised to include appropriate documentation to provide complete support for
selection of the without project condition. This will include State laws,
policies, regulations, precedents, and/or examples of other limiting factors to
support no action, other than soft measures.
b.
Derivation of Storm Damages: It is not clear how
inundation and wave attack damages were derived or how such damages are
expected to vary for each year of the economic evaluation. The economics appendix should include
detailed explanations and examples of the derivation of the damages cited. This information should include a schedule
(listing) of expected damages by damage category for each year of the economic
evaluation. Damages should be shown
individually for the Imperial—North and Imperial—South reaches.
District
Response:
For inundation damages, coastal engineering supplied inundation depths
for the related to various storm events and beach configurations for the
selected years throughout the study period. FEMA depth damage curves were used
to estimate the dollar value of damages to structures and contents. It was
assumed that until the structure was destroyed by either erosion or wave
attack, it would be susceptible to inundation damages through the study period.
Coastal Engineering determined, based on the critical force of the waves, when
structures would be 100% destroyed by wave attack. Our analysis of wave attack assumed no damages until the wave
force reached a critical force that would destroy a structure.
The economic appendix will be updated to include detailed explanation and tables showing damages by reach and category. Provided as an attachment is a flow chart sketch displaying the logic of the economic damage model.
Discussion: A flow
chart outlining the districts rationale in deriving storm damages was presented
and the district provided a detailed description of each step of the derivation
process. It was agreed this information
should be included in the draft report’s supporting appendices.
Action: The draft report will provide a better description of the model and the supporting appendices will provide an example on how the model works on several sample structures, including the north and south reach.
c.
Double Counting: It is not clear in the report how double
counting of damages is avoided for the inundation and wave attack
categories. Further explanation should
be provided.
District
Response:
Wave attack damages were based on the probability of a storm event
occurring in any given year that would destroy a structure. Therefore, in any given year there is a certain
probability that the structure would be destroyed by wave attack. Conversely, in any given year there is a
certain probability that the structure still exists. That “probability of existence factor” from the wave attack
analysis was imported into the inundation damage model to calculate future
inundation damages. Thus avoiding
double counting.
Further, if erosion undermined the structure in any
given year, that structure would be removed from the inventory. For example, if wave attack was expected to
destroy a structure in year 10, but, if erosion destroys the structure in year
5, wave attack damages were only claimed for the first 4-years. A more detail
explanation of damage determination will be added to the draft report.
Discussion:
The district response resolves the concern.
Action: The draft report will include
further explanation and clarification to explain how damages were determined
and why there is no double counting of damages.
d.
Utility Relocation Damages: The report indicates
that as land is lost through erosion, underground utilities in the
Imperial--north reach will be vulnerable to damage or destruction. To avoid this damage, the city will move all
the utilities inland to a less vulnerable and more secure location under the
without project condition. The first
cost of these relocations is $16.7 million.
The relocations are to be completed in stages over a 5-year period
starting 15 years into the study evaluation period. The economic rationality of these expenditures should be
discussed to include why the city would not try to protect rather than relocate
the utilities. The total investment
cost for the apparent NED plan, which includes the present value of periodic
nourishment for the protection of both the north and south reaches, is
only $11.8 million. Clearly, the city
could protect only the Imperial—North reach at considerably less cost to avoid
the assumed $16.7 million in relocations.
The avoided relocation costs should not exceed the cost of protecting
the north reach only. Verify that this
is the case. Further discussion should
be provided to support the economic rationality of the without project
expenditures of the magnitude assumed in the north reach.
District
Response:
District contacted City officials after receiving this review
comment. City officials stated that the
utilities are owned by several different entities: SDG&E, Cox Cable, Pac
Bell and Cal AM Water. Costs shown to
relocate these utilities will thus be shared.
Therefore, the $16.7 million total relocation responsibility and cost to
move all of the utilities will be assumed by multiple entities, other than the
City.
Discussion:
The report
will need to include more information regarding the relationship of utilities
to the shoreline and assumptions related to when the utilities would be
relocated. In addition, the district
will include documentation regarding the assumption that the local utility
companies will be responsible for relocating their utility lines.
Action: The draft report will include
information regarding the relationship of
utilities to the shoreline and assumptions related to when the utilities would
need to be relocated. Documentation
supporting the assumption that the local utility companies will be responsible
for relocating their utility lines should also be included.
e.
Land Loss: The report includes a $445,600 benefit for
land losses avoided in the north reach.
The report does not provide any specifics on the quantity or value of
the land lost. Further information and discussion is needed to support land
loss benefits claimed.
District Response: Concur. Details will be
added to the post AFB draft. In summary, the Real Estate sections provided land
values for non-ocean view property ($75.00 per sq. ft) this was multiplied by
the square footage (approximately 274,000 square feet) of the parcel expected
to be impacted by erosion. Starting in
year-ten of the study period through year-fifty.
Discussion:
Concern is
resolved.
Action: The draft report will include
information in the district response in further support of land loss benefits
claimed. The report will document that a, non-ocean view, 5,000 square-foot (50 by
100) lot would be valued at $375,000 ($75 x 5,000).
f.
Storm Damage History: Based on the information in the report,
there have been two significant storms over the last 40 years. The 1952-1953 storm resulted in shoreline
recession and $25,000 in damages in 1953 dollars. The 1988 storm resulted in $165,000 in damages and $100,000 in
clean-up costs in 1988 dollars. It
would be helpful to know the approximate return period for these storms. Given the limited storm and erosion damages
actually documented in the past, the estimated without project damages appear
excessive and should be further discussed and supported.
District Response: During each major storm event
that has occurred at Imperial Beach, 1953, 1983 and 1988, there has been some
width of dry beach, as a result of natural conditions and limited beach
nourishment activities, that has provided protection against storm damage. However, our without project condition
assumes no new nourishment over the period of analysis. As the shoreline erodes, the damage
potential will increase. The draft
report will include a more detailed discussion.
Discussion:
As discussed in comment 3e there appears to be an inconsistency between historic beach
loss and shoreline retreat data presented in the Coastal Engineering Appendix,
Appendix B Table 5, page B-11. The
district should review the data to ensure to there are no inconsistencies
between historic beach loss and shoreline retreat data for various return
periods.
Action: The draft report will include documentation supporting that the
beach is retreating. The district will
also review the data to ensure to there are no inconsistencies between historic
beach loss and projected shoreline retreat data for various return periods.
District
Response:
Concur. The data contained in Chapter 6 is in
error. Cost sharing discussion in
Chapter 8 supercedes the information contained in Chapter 6. The report will be revised to include the
correct cost sharing apportionment.
Discussion:
The
district will review ER 1165-2-130 to delineate cost sharing apportionment for
various land uses. Chapter 6 in its
current form should be removed.
Action: The district will review ER
1165-2-130 to delineate cost sharing apportionment to account for shoreline access, ownership, and
use. Also see action item for comment
5c. Chapter 6 in its current form will be
removed and revised accordingly to address this and subsequent comments.
b.
Cost Apportionment: Paragraph 6.4 shows the net present value of
the estimated first cost and four future berm replacements ($11,821673)
apportioned 35 percent Federal ($4,137,586) and 65 percent non-Federal
($7,684,087). This is in error. See the preceding comment.
District
Response:
Concur. The data contained in Chapter 6 is in
error. Cost sharing discussion in
Chapter 8 supercedes the information contained in Chapter 6. The report will be revised to include the
correct cost sharing apportionment.
Discussion:
See
comment 5a above.
Action: See comment 5a above.
c.
Cost Sharing Percentages Must Be Adjusted To Account for Ownership
and Use: For the previously authorized submerged
breakwater project cost sharing was determined based on the shoreline ownership. At that time, 700 feet of shoreline was
owned by Federal agencies, and 4,300 feet was owned by non-Federal public
agencies. Further, the current report
indicates that there are 19 vacant lots along the beachfront. The draft report must clearly delineate
current shoreline ownership and use for purposes of determining the appropriate
cost sharing for the project. Refer to
ER 1165-2-130.
District
Response:
The draft
report will clearly delineate the current ownership of the shoreline. The study
area shoreline is currently 100% Public, non-Federally owned.
Discussion:
See
comment 5a above.
Action: Note that project cost sharing is to be based on shoreline ownership, use, and type
and incidence of benefits. The project
benefits are reduced hurricane and storm damage to public and private property
and incidental recreation. For those
project segments that provide hurricane and storm damage reduction to publicly
owned and privately owned structures, 65 percent Federal/35 percent non-Federal
would be applicable. However, for those
segments where the project will protect lands dedicated to park or conservation
uses, applicable cost sharing is 50 percent Federal / 50 percent non-Federal. Costs to protect privately owned vacant land
would be apportioned 100 percent non-Federal.
Composite cost sharing that appropriately considers the type of
facilities that would be protected by the project should be shown in the draft
report. Also see comment 5a.
d. Sunk PED Expenditures: Prior (sunk) PED costs, including costs of
past and current studies that have not been subject to cost-sharing, should be
included in total cost of the recommended project proposal. Including sunk PED expenditures in the total
cost of the recommended plan would not effect economic justification. However, sunk PED costs must be included in
the estimated of total cost for purposes of cost apportionment.
District
Response:
Concur. Sunk PED costs will be included in the
tables and discussion regarding cost apportionment in the draft report.
Discussion:
The district noted that there have been prior PED costs associated with
the currently authorized study, in which the local sponsor has met the
obligations for their share of these costs.
However, as of this date, the cost for the GRR has been completely borne
by the Federal government. The district
and the non-Federal sponsor believe there is justification to consider these
sunk PED costs a Federal responsibility and consequently, the district has
requested it be allowed the opportunity to prepare an issue paper presenting
their case regarding whether or not the GRR cost should be considered sunk
costs at 100% Federal responsibility for the proposed project under new
authority.
Action:
The district will include sunk PED expenditures in the total cost of the
recommended plan. Even though sunk PED
expenditures would not effect economic justification, these costs must be
included in the estimated of total cost for purposes of cost apportionment. The district will prepare and submit an
issue paper to HQUSACE regarding whether or not sunk PED costs should be cost
shared. The issue paper will be used as
a basis for HQUSACE reconsideration of guidance related to treatment of sunk
costs.
6. ECONOMIC
EVALUATION:
a.
Current Federal Discount Rate: The text on page
3-11 indicates that the economic analyses were conducted using a discount rate
of 6.375 percent. The appropriate
discount rate for FY02 is 6.125 percent in accordance with the Economic
Guidance Manual published annually by HQUSACE.
The district should update the economic analyses to show the appropriate
discount rate in the draft report.
District
Response:
Concur, post AFB draft will include updated numbers based on current
discount rate.
Discussion:
Concern is
resolved.
Action: The draft report will include
updated numbers based on the current discount rate.
b. Interest During Construction: Table 5.1
on page 5-1 shows that interest during construction is being computed for the
future nourishment cycles in years 12 through 45. Although periodic nourishment is considered continuing
construction, interest during construction is only calculated on PED
expenditures through the time that a project element starts to function. Therefore, there would be no IDC for the
nourishment cycles. The district should
revise the analysis of IDC in the draft report to show IDC for initial
construction only.
District
Response:
Concur, this will be re-evaluated and updated in the draft report.
Discussion: Concern is resolved.
Action: The draft report will include
the revised analysis of interest during construction.
c.
Clean Up Costs: Table 5.2 indicates that public cleanup
costs would be completely eliminated by the recommended plan despite the fact
that there are residual damages from wave attack and inundation. This seems counterintuitive since clean up
costs are generally experienced throughout the range of storm events. The district should review the assumptions
for the estimates of cleanup costs to assure that the appropriate level of
benefits and residual damages are being used to identify the NED plan.
District
Response:
Concur, this will be re-evaluated and updated in the draft report
Discussion:
The
district will also review to ensure consistency with earlier concern on
residual damages.
Action: The district will review and
update the numbers in the report as appropriate.
d.
OMRR&R Cost: The AFB document does not address
non-Federal OMRR&R costs.
Typically, activities such as maintenance of dune vegetation and
walkover structures, and emergency shaping of the beach to correct localized
accumulation or depletion of sand after storms are considered non-Federal
O&M responsibilities. Non-Federal
OMRR&R requirement should be identified in the draft report and included in
the economic evaluation of project alternatives.
District
Response:
The
project area does not consist of dunes or walkover structures. No emergency shaping of the beach is
required for the NED plan. There are no
O&M requirements associated with the NED plan.
Discussion:
Monitoring
and clean up costs are minimum activities for project maintenance. In the case for monitoring for
renourishment, this activity is cost-shared between Federal and non-Federal
interests. Monitoring for other
purposes is financed completely by the non-Federal sponsor. The draft report should discuss OMRR&R
requirements of the project.
Action: The district will identify any potential operation and
maintenance cost associated with constructed project. The report should note
that Corps hurricane and storm damage reduction projects require, as an item of
local cooperation, that non-Federal sponsors maintain the design profile. Typically, this is accomplished by moving
sand displaced by storms from one segment of the project and deposited in
another project segment. The report
should address whether this requirement can be satisfied given California
Coastal Commission regulations. Note
that if this requirement cannot be satisfied, there may be implications as to
the validity of the assumption that the design profile will be available to
prevent damages for the full period of economic evaluation.
7. :
a.
Draft EIS: The draft EIS is still incomplete, awaiting
more information, either from the Corps study team or from other agencies. This missing information should be provided
to HQUSACE for review prior to finalization of the draft EIS.
District
Response:
Concur. The document contained in this AFB Report is a preliminary draft. Missing information shall be provided in the
Draft EIS and submitted to HQUSACE for review prior to public distribution.
Discussion:
Concern is
resolved.
Action: The Draft EIS will be submitted to HQUSACE for review
prior to public distribution.
b.
Draft EIS-NEPA Requirements: Paragraphs 11 and
12 of the draft EIS (Relationship between short-term Uses of the Environment
and Maintenance and Enhancement of long-term Productivity; Irreversible and
Irretrievable Commitment of Resources) are, as presently written, merely
discussions of what the State and Federal laws require. They do not discuss specifics of the
proposed alternatives and how they relate to the required analyses. At present, these paragraphs are totally
inadequate.
District
Response:
Concur. Since this report is the
preliminary alternatives analysis, a discussion of specifics of the proposed
alternatives and how they relate to the required analysis was postponed since
the alternatives and recommended alternative changed several times, including
after the F4 document was submitted.
The required discussion will be included in the Final Draft EIS and
submitted to HQUSACE for review prior to public distribution.
Discussion:
Concern is
resolved.
Action: As indicated in the response.
c.
Endangered Species: There may be an opportunity to provide
least tern nesting areas in conjunction with the project that are separated
from public intrusion and other forms of nest destruction or harassment of
young birds while still on the nest.
The district should examine all potential for restoration of such uses
of the restored beach by species of special concern.
District
Response:
The proposed project is sited adjacent to an existing U.S. Fish &
Wildlife Service designated “Least Tern Nesting Area”. The project, as proposed will provide
protection to the existing nesting area by placing a sand berm barrier in close
proximity to this site, thereby separating the existing nesting area from
public intrusion and other forms of nest destruction or harassment. However, additional opportunities to provide
nesting areas for species of special concern may be investigated.
Discussion:
Concern is
resolved.
Action: The draft EIS will include
information in the response. The
district will not investigate additional environmental opportunities.
d.
Required Mitigation Measures: The Environmental
Appendix indicates that a number of mitigation measures are proposed for the
recommended plan. No significant
adverse impacts are identified and attributed to construction of the
recommended plan. Consequently, there appears to be no mitigation
requirement. The measures discussed in
the Environmental Appendix are ways of avoiding impacts through sound planning
of the project--not mitigation. This should
be clarified in the report.
District
Response: Concur. No significant adverse
impacts are attributed to construction of the recommended plan as
described. The final Draft EIS will
clarify that any environmental commitments to minimize short-term construction-related
impacts are not considered to be mitigation measures and no mitigation is
required.
Discussion:
Concern is
resolved.
Action: As indicated in the response.
8. LOCAL
COOPERATION: Page 6-2 contains a list of non-Federal
responsibilities, which is abbreviated and omits several items of local
cooperation typically required for shore protection projects. A complete and accurate list is required by ER 1105-2-100 app. G-9.g.(1)(d). Office of Chief
Counsel, HQUSACE, offers the following draft list for hurricane and storm
damage reduction projects. The District
should review the list carefully, with the assistance of its Office of Counsel,
and revise it further as needed to address the needs of the current project.
District Response:
Concur. The data contained in Chapter 6 is in error. The report will be revised to
include the correct cost sharing apportionment. The District will review the following draft
list provided by the HQUSACE Review Team with Office of Counsel and revise
as needed to address the needs of the current project.
Discussion:
As
indicated in the response. Also see
comment
Action: As indicated in the response.
9. REAL
ESTATE: The AFB document does not contain any
real estate information for policy review.
The draft report should include a real estate plan that satisfies the
requirements of ER 405-1-12. The real
estate appendix should also address public access and other requirements that
are unique to hurricane and storm damage reduction projects.
District
Response:
Concur. Real estate appendix will be included in the
draft report. In general, the mining,
transport and placement of beach nourishment material will take place entirely
on public lands or in public waters.
Local and state ordinances will ensure public accessibility to the
constructed project site. Beach nourishment material will be mined from
offshore sources within the jurisdictional waters of the State of
California. Typically fees are not
assessed on the excavation of offshore sediments for the purpose of providing
beach fill on public lands.
Discussion:
The
information contained in the response will be included the draft real estate
plan included in the draft report.
Action: The draft real estate plan
will be included in the draft report.
District
Response:
Concur. The data contained in Chapter 6 is in error. The report will be revised to
include the current review and approval process.
Discussion:
Concern is
resolved.
Action: The district will remove
Chapter 6 in its current form and replace it with updated requirements.
b. Imprecise Text:
The report indicates that the Federal Government and the non-Federal
sponsor are responsible for implementing and maintaining the project. Actually, the Federal Government and
non-Federal sponsor are responsible for initial construction and periodic
nourishment of the project. The
non-Federal sponsor is responsible for operation and maintenance of the project
to include maintaining the design profile.
District
Response:
Concur. The draft report will be
revised to correct this imprecise text.
Discussion:
Concern is
resolved.
Action: The district will revise the
text in the draft report.
c. Misleading Text:
The report indicates that typically property owners do not heed warnings
nor properly prepare prior to storm events and as a result sustain damage to
structure contents as well as loss of actual structures. This implies that property owners could have
avoided content damages with proper preparation. This appears to be misleading statement, as evacuation does not
typically include removing all contents from structures. Suggest more appropriate wording be used.
District
Response:
Concur. The district will revise misleading
text. This section will be re-visited
along with the content to structure ratios discussed in paragraph 4.
Discussion:
Concern is
resolved.
Action: The district will revise the
text in the draft report.
d.
Typographical Error: The summary of without project damages
(Table 3.8) has total without project damages to include recreation transfer
costs of $2,309,000. This amount should
be $2,054,000.
District
Response:
Concur. The draft report will be corrected to
include the correct recreation transfer costs.
Discussion:
Concern is
resolved.
Action: Text will be corrected in the
draft report.
After
extensive research into the availability of numerical programs to assist in the
evaluation of coastal projects, the Coastal Storm Damage Assessment Model
(COSTDAM) was selected as the most appropriate computer model to estimate
damages resulting from coastal storm processes impacting the study area.
COSTDAM is a Fortran program originally developed by Wilmington District and
later updated for use in Philadelphia District. The program initially examines
a structure for damages caused by wave attack based on the relationship between
the structure's first floor elevation and the total water elevation that
sustains a wave. It then determines if the structure has sustained any erosion
damage. If the water elevation is higher than the first floor elevation, the
program calculates damage caused by inundation based on Federal Insurance
Administration (FIA) depth-damage curves adjusted to account for increased
damage caused by salt water. COSTDAM applies standard Corps evaluation
procedures during this process. Each structure is evaluated using appropriate
inundation stage frequency, wave damage elevation frequency, and storm erosion
(based on distance from established baseline) frequency profiles. Each profile
is integrated with each structures stage damage profile to establish a damage
frequency profile. To avoid double counting, if damage occurs to the structure
by more than one damage category (i.e., wave attack, erosion, and inundation),
COSTDAM takes only the damage category with the greatest damages and eliminates
the damages from the others. Average annual damages are then calculated and
aggregated for the study area by appropriate reaches. The assumptions and input
data are outlined below.
ASSUMPTIONS
Pertinent
assumptions applicable to the COSTDAM analyses include the following:
• Structures
will be rebuilt if completely lost in a storm event;
• The
few vacant lots located along the beach front will be developed prior to the
base year;
• The
associated content value of each structure is estimated to be 50 percent of the
structure value; and
• Based on sample comparisons, depreciated replacement
costs calculated by the Marshall Swith Residential and Commercial Software
Estimator result in values ranging from 6 percent greater to 4.5 percent less
than currently assessed values estimated by the city of Hampton.
There are two basic input files used in the
COSTDAM analysis: the "structure" file, which contains the database
information for each structure inventoried, and the "control" file,
which contains the frequency parameters for the representative hydraulic
profiles used to characterize the erosion, wave, and inundation mechanisms.
The "structure" file contains the
following pertinent inputs:
• Name
of reach
• Structure
identification
• Distance
of structure from baseline
• Distance
to midpoint of structure
• Ground
elevation at structure
• Ground
clearance at structure (distance between ground and first floor)
• Value
of structure
• Value
of structure contents
• Class
of structure (determines applicable depth-damage curve)
• Class
of contents (determines applicable depth-damage curve)
• Category
code to designate foundation type
• Category
code to designate whether the structure is residential or commercial
The "control" file contains the
following pertinent inputs:
• Number
of structures
• Economic
period of analysis
• Interest
rate
• Event
probabilities used in the analysis
• Wave
damage criteria
• Reach
data
• Storm
erosion, wave impact, and wave damage elevation data
• Inundation profiles for event probabilities