ABSTRACT: The Draft Environmental Impact Report CALAM MONTEREY PENINSULA WATER SUPPLY PROJECT, April 2015, prepared for California Public Utilities Commission and prepared by Environmental Science Associates (ESA) (1789 pages) document copy is embedded; 7.12 Environmentally Superior Alternative is reproduced and the Appendices for the Draft Environmental Impact Report (EIR) documents copies (1971 pages) are embedded in the following Posts.
7.12
Environmentally Superior Alternative
The analysis of alternatives presented in Section 7.11, taken together with the analysis of the proposed MPWSP and the MPWSP Variant in Chapters 4 and 6, respectively, provide a basis to identify the environmentally superior alternative, pursuant to CEQA Guidelines Section 15126.6, among the alternatives to the proposed project and those to the MPWSP Variant. The environmentally superior alternative is the alternative identified as meeting most of the basic project objectives and resulting in the fewest significant environmental impacts. CEQA Guidelines Section 15126.6 provides that if the No Project Alternative would be the environmentally superior alternative, the EIR shall also identify an environmentally superior alternative among the other alternatives. Here, No Project Alternative 1 may technically qualify as the environmentally superior alternative because it would involve the least amount of change to the existing physical environment. However, No Project Alternative 1 would not meet most of the basic project objectives, is not feasible for reasons indicated previously, and could result in different impacts than the proposed project or other options given the failure of No Project Alternative 1 to supply sufficient water for customers within the CalAm service territory. For this reason, the discussion below focuses on selecting another environmentally superior alternative from among the myriad options presented in this EIR.
It is important
to recognize that the selection of the environmentally superior alternative is
not always a
straight-forward and formulaic exercise. In some cases, including here, no
alternative stands out from
others as eliminating significant and unavoidable, long-term environmental effects. As
such, considerable weighing among gradations of impacts and judgments as to the relative
importance of topical impact areas in the context of the proposed project come
into play. Such judgments,
while based upon reasoning grounded in the scientific study that comprises the EIR, are
inherently subjective. This means that, though this EIR identifies an
environmentally superior
alternative, the CPUC decision-makers could ultimately come to a different
conclusion as to which
option is the environmentally superior alternative based upon applying
different weights to
various impact areas.
The following
discussion of the environmentally superior alternative assumes that the
Alternative Pipeline Configuration 2, as described previously in Section 7.9.3
and as used for all of the alternatives analyzed above, would be used for
either the proposed project or the MPWSP Variant.
Because the
proposed project would result in the least amount of construction and operation impacts compared
with either Alternative 1 or Alternative 2, it is the environmentally superior alternative of
the proposed project alternatives (as opposed to Variant options). While Alternatives 1
and 2 would not result in impacts to the Salinas Valley Groundwater Basin, the effects of the
project in this regard would be less than significant, except as to one impact concerning
remediation that would be less than significant with mitigation. On the other
hand, Alternatives 1
and 2 would cause numerous construction effects that are significant and would require
mitigation to attain a level of less than significant. Furthermore, Alternative
1 may prove infeasible due
to failure to meet the basic objective of the project to supply sufficient
replacement water to CalAm customers and the lack of site control for the slant
wells. Alternative 2 may prove infeasible due to regulatory and permitting
hurdles, and also would cause significant impacts above and beyond those
identified for the project without corresponding offset to project significant
effects. For these reasons, the proposed MPWSP project is the environmentally superior
alternative among those options that do not include the GWR facilities.
Similarly,
because the MPWSP Variant results in the least amount of construction and operation impacts compared with either Alternative 3 or Alternative 4, it is the
environmentally superior alternative of
the MPWSP Variant alternatives. The explanation provided in the paragraph above with respect to
environmental impacts and project feasibility applies equally to the choice among the MPWSP Variant and Alternatives 3 and 4.
When combined with other CalAm facilities (e.g. pipelines and ASR facilities) the project variant would have impacts similar to the proposed project for most of the topical areas evaluated. However, there are several impacts of the project variant that are unique, or are more or less severe than the proposed project. These factor heavily into the selection of the environmentally superior alternative and are thus listed below.
When combined with other CalAm facilities (e.g. pipelines and ASR facilities) the project variant would have impacts similar to the proposed project for most of the topical areas evaluated. However, there are several impacts of the project variant that are unique, or are more or less severe than the proposed project. These factor heavily into the selection of the environmentally superior alternative and are thus listed below.
The following
impacts are unique to the GWR facilities of the project variant, and would not
be
associated with
the proposed project:
- The soils that underlie the proposed
location for the Injection Well Facilities in the Seaside Groundwater
Basin could be susceptible to hydro-collapse if large quantities of water
were
injected into the ground. The risk would
be less than significant.
- Construction of the proposed Reclamation
Ditch and Tembladero Slough diversions could indirectly result in habitat modifications for endangered or
threatened fish species as a result
of construction activities and dewatering the construction sites. This
impact would be
less than significant with
implementation of mitigation.
- Operation of the project variant would
result in changes in stream flows that may interfere with fish migration in the Salinas River and Reclamation Ditch.
This impact would be less than
significant with implementation of mitigation.
The following impacts would be more severe with the project variant
than with the proposed project:
- Construction of the project variant
would result in an overall increase in the amount of soil that would be
disturbed, and therefore, would increase the potential to result in soil
erosion and loss of topsoil. The combined impact would be mitigated to a
less-than-significant level.
- Rapid water fluctuations may induce
erosion and sedimentation within the downstream affected reach of the
Reclamation Ditch and Tembladero Slough components of the project variant
that would not occur under the proposed project. This significant impact
of the project variant would be reduced to less-than-significant with the
implementation of mitigation.
- The addition of the GWR Facilities would
result in an overall increase in temporary, construction-related trips on
local roadways compared to the proposed project, and construction of the
GWR facilities would overlap with construction of the CalAm facilities for
almost two years. The combined significant impact would be mitigated to a
less-than significant level.
- The proposed project would be able to
mitigate the generation of noise levels to meet the applicable standards
during construction. However, impacts associated with construction at the
Tembladero Slough Diversion site would conflict with County Code Section
10.60.030, resulting in a significant and unavoidable impact of the
project variant, even with mitigation.
- While the emissions of PM10 associated
with the proposed project could be mitigated to a less-than-significant
level, the total combined maximum day construction emissions of the MPWSP
Variant would result in a significant unavoidable impact even with
mitigation.
- Discharges of the proposed project
through the existing outfall would result in exceedences in Ocean Plan
water quality objectives for PCBs and ammonia. Discharges associated with the
project variant would, in addition, exceed Ocean Plan water quality
objectives for chlordane, toxaphene, DDT and TCDD Equivalents. All exceedences,
for both projects, could be reduced to less than significant with the
implementation of the same mitigation measure.
The following impacts would be less severe with the project variant
than with the proposed project:
- The response of the SVGB to the
operations of the project variant in the Dune Sands Aquifer and 180-Foot
Equivalent Aquifer would be much less pronounced than under the proposed
project because less water would be extracted from the slant wells and
more water would be provided to CSIP for agricultural users, and Salinas
Valley return water would be injected into the 180-Foot Equivalent
Aquifer.
- Interference with the remediation of a
contaminated groundwater plume at Fort Ord can be mitigated under the
proposed project; it would be avoided with operation of the project variant
as a result of the dampened groundwater elevation response in the SVGB.
- The combined components of the project
variant would use 4,700 MWh/year less energy than the proposed project.
The impact would be less than significant for both the proposed project
and the project Variant since the energy would not be used in a wasteful
and inefficient manner.
The project variant would generate 253 metric tons CO2e (GHG) per
year less than the MPWSP. The impact would remain significant and unavoidable for both the
proposed project and the project variant. The MPWSP Variant would generate certain significant
environmental effects that would not occur with the project, but for the most part, such
effects would be less than significant with implementation of mitigation measures.
There are two significant unavoidable impacts that would occur with the
MPWSP Variant and not with the proposed project – construction PM10 emissions
and noise – but these impacts would be temporary in nature and thus may be accorded
a lesser weight than impacts of a more permanent and on-going nature. The MPWSP
Variant would result in an increase in other construction related impacts
(cultural resources, traffic and biological resources) due to the construction
of the GWR Project elements. Each of these temporary impacts would be less than
significant with mitigation. Although the MPWSP Variant and the proposed
project would each result in a significant environmental impact associated with
greenhouse gas emissions, the Variant would use less energy than the project
and thus would have somewhat lower greenhouse gas emissions than the project.
Compared to the proposed project, the MPWSP Variant would provide a diversified
portfolio of water supplies, reduce pumping from the SVGB, increase Seaside
Basin groundwater supplies, and improve groundwater levels and quality in the
SVGB. While both the proposed project and the MPWSP Variant would have less
than significant effects on the SVGB levels from pumping at the slant wells,
the effects would be minimized with the MPWSP Variant. As noted, reasonable
minds could differ as to the selection of the environmentally superior alternative.
Nonetheless, weighing the short term unavoidable construction impacts of the
Variant against the longer-term, more severe impacts of the project in the key
areas of groundwater and greenhouse gas emissions, between the two options, the
MPWSP Variant is deemed to be the environmentally superior alternative.
Public
Meetings
The
CPUC will be holding four public meeting/open house presentations to facilitate
your review of the Draft EIR:
Tuesday
May 26, 2015, 1:00 pm: Marina Public Library, 188 Seaside Ave Marina
Wednesday
May 27, 2015, 1:30 pm: Oldemeyer Center, Seaside Room, 986 Hilby Ave.
Seaside
Wednesday
May 27, 2015, 6:30 pm: Oldemeyer Center, Laguna Grande Hall, 986 Hilby
Ave. Seaside
Thursday
May 28, 2015, 1:30 pm: Sunset Center, Carpenter Hall, San Carlos Street,
Carmel
Public Comment
on the Draft EIR:
As of April 30,
2015, this begins a 60-day public review period; your written comments are due
no later than July 1, 2015 and should be sent to:
Andrew
Barnsdale
California Public Utilities Commission
c/o Environmental Science Associates
550 Kearny Street, Suite 800
San Francisco, CA 94108
California Public Utilities Commission
c/o Environmental Science Associates
550 Kearny Street, Suite 800
San Francisco, CA 94108
Comments can
also be sent by fax to (415) 896-0332, or by email to mpwsp-eir@esassoc.com
CEQA
Process Schedule
|
|
Public Release of Notice of Preparation
|
October 10, 2012
|
EIR Scoping Period (30 days)
|
October 10, 2012 -
November 9, 2012
|
Public Scoping Meetings
|
October 24, 2012
and October 25, 2012
|
Draft EIR Publication
|
April 30, 2015
|
Public and agency comment period
|
Comments are due by
July 1, 2015
|
Public hearings on Draft EIR
|
May 2015
|
All-party Meeting in Monterey
|
July 30, 2015
|
Publication of Final EIR
|
October 2015
|
CPUC Proposed Decision Issued
|
December 2015
|
All-party Meeting
|
January 2016
|
Proposed Decision on Commission Agenda
|
February 2016
|
Draft Environmental Impact Report CALAM
MONTEREY PENINSULA WATER SUPPLY PROJECT, April 2015, prepared for California
Public Utilities Commission
And prepared by Environmental Science Associates (ESA) (1789
pages)
(Application
A.12-04-019, filed April 23, 2012)
Draft
Environmental Impact Report
To
view the complete Draft EIR without appendicies, click here [pdf 57.7mb].
To
view the Appendices for the Draft EIR, click here [pdf 281mb].
Executive
Summary
[pdf]
1. Introduction [pdf]
2. Water
Demand, Supplies, and Water Rights [pdf]
3. Project
Description
[pdf 6.67mb]
4. Environmental
Setting, Impacts, and Mitigation Measures
4.1 Overview [pdf]
4.2 Geology, Soils, and Seismicity [pdf 4.08mb]
4.3 Surface Water Hydrology and Water Quality [pdf 5.06mb]
4.4 Groundwater Resources [pdf 16.1mb]
4.5 Marine Resources [pdf]
4.6 Terrestrial Biological Resources [pdf 3.98mb]
4.7 Hazards and Hazardous Materials [pdf]
4.8 Land Use, Land Use Planning, and Recreation [pdf]
4.9 Traffic and Transportation [pdf]
4.10 Air Quality [pdf]
4.11 Greenhouse Gas Emissions [pdf]
4.12 Noise and Vibration [pdf]
4.13 Public Services and Utilities [pdf]
4.14 Aesthetic Resources [pdf]
4.15 Cultural and Paleontological Resources [pdf]
4.16 Agriculture and Forestry Resources [pdf]
4.17 Mineral Resources [pdf]
4.18 Energy Conservation [pdf]
4.19 Population and Housing [pdf]
4.1 Overview [pdf]
4.2 Geology, Soils, and Seismicity [pdf 4.08mb]
4.3 Surface Water Hydrology and Water Quality [pdf 5.06mb]
4.4 Groundwater Resources [pdf 16.1mb]
4.5 Marine Resources [pdf]
4.6 Terrestrial Biological Resources [pdf 3.98mb]
4.7 Hazards and Hazardous Materials [pdf]
4.8 Land Use, Land Use Planning, and Recreation [pdf]
4.9 Traffic and Transportation [pdf]
4.10 Air Quality [pdf]
4.11 Greenhouse Gas Emissions [pdf]
4.12 Noise and Vibration [pdf]
4.13 Public Services and Utilities [pdf]
4.14 Aesthetic Resources [pdf]
4.15 Cultural and Paleontological Resources [pdf]
4.16 Agriculture and Forestry Resources [pdf]
4.17 Mineral Resources [pdf]
4.18 Energy Conservation [pdf]
4.19 Population and Housing [pdf]
5. Cumulative
Impacts
[pdf]
6. MPWSP
Variant
[pdf 3.15mb]
7. Alternatives [pdf 10.3mb]
8. Growth-Inducement
Potential and Secondary Effects of Growth [pdf]
9. CEQA
Statutory Sections
[pdf]
10. Report
Preparers
[pdf]
Appendices
A. NOP
and NOP Scoping Report [pdf 3.6mb]
B1. MPWSP
Plant Sizing Data: Various Five- and Ten-Year Normal, Dry, and Maximum Month
Demand Scenarios
[pdf]
B2. State
Water Board Final Analysis of the Monterey Peninsula Water Supply Project [pdf 22.4mb]
C1. Analysis
of Historic and Future Coastal Erosion with Sea Level Rise [pdf 7.0mb]
C2. Coastal
Water Elevations and Sea Level Rise Scenarios [pdf]
C3. Exploratory
Borehole Results
[pdf 69.2mb]
D1. Far-Field
Analysis of Brine Discharge [pdf 10.6mb]
D2. Brine
Discharge Diffuser Analysis [pdf]
D3. Water
Quality Analysis of the Discharges [pdf]
D4. Ocean
Plan Compliance Assessment [pdf 4.05mb]
E1. Test
Slant Well Groundwater Modeling and Analysis - CEMEX Active Mining Area [pdf 9.82mb]
E2. Monterey
Peninsula Water Supply Project Groundwater Modeling and Analysis [pdf 127mb]
F. Special-status
Plant and Wildlife Species Considered [pdf]
G. Air
Quality and Greenhouse Gas Emissions Calculations [pdf]
H. Pure
Water Monterey Groundwater Replenishment Project, Project Description [pdf 24.4mb]
I. Component
Screening Results
[pdf]
J1. Coastal
Water Project EIR Analysis: MPWMD 2006 Estimate of Long-Term Water Needs
Compared with Growth Anticipated in Jurisdictions General Plans [pdf]
J2. Secondary
Effects of Growth
[pdf]
By
Jim Johnson, Monterey Herald
Posted:
04/30/15, 7:50 PM PDT
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