Stream
Maintenance Program
Program
Environmental
Impact Report
Summary
A. THE SANTA CLARA VALLEY WATER DISTRICT
The Santa Clara Valley Water District ("District") is a special purpose
governmental agency responsible for providing water supply and flood
protection for Santa Clara County, California in an environmentally
responsible manner. For flood protection, all creeks in Santa Clara
County with a watershed greater than 320 acres are in the District's
jurisdiction.
B. PROPOSED PROJECT: THE STREAM MAINTENANCE PROGRAM
1. The Scope of the Stream Maintenance Program
The Stream Maintenance Program (SMP) describes a proposed program
for conducting routine stream and canal maintenance. The program is
intended to be ongoing and can be modified as conditions change. The
program is intended to apply to three major activities, sediment removal,
vegetation management, and bank protection, and a group of minor activities.
The program is intended to cover these activities wherever they may
occur in the District's jurisdiction, subject to several specific limitations.
The SMP incorporates several explicit steps for evaluating and reporting
the effectiveness of the mitigation in the Program ( see SMP Figure
3-1, SMP Resource Protection Protocol). This cycle of annual evaluation
and improvement makes the SMP capable of adapting to new information
and changing conditions to improve Best Management Practices (BMPs)
effectiveness. It is expected that the full suite of resource protection
incorporated in the SMP will allow the District to minimize environmental
effects under a wide range of actual work needs.
2. Sediment Removal
Sediment removal occurs when an accumulation of sediment (1) reduces
flood water conveyance capacity, (2) prevents facilities or appurtenant
structures from functioning as intended, or (3) impedes fish passage
and access to fish ladders. Thus the overall purpose is to ensure the
proper function of District facilities.
The District estimates that it removes an average of 80,000 cubic
yards of sediment on about 16 miles of channel per year in Santa Clara
County. The actual quantity and location varies from year-to-year depending,
in part, on rainfall of the past season. Cumulatively, sediment removal
is projected for approximately 60 miles of streams. Sediment removal
from canals is estimated to be less than 1000 cubic yards per year.
Sediment removal generally occurs between July 1 and October 15. A
variety of heavy equipment is used. The average duration of a sediment
removal project is 10 days. Appropriate temporary dams and pipes are
used if water must be bypassed around the site during work. Excavated
sediment is disposed at a landfill or other suitable site.
3. Vegetation Management
Vegetation management removes plant growth which blocks channels or
which reduces flood flow. Vegetation management helps maintain the ability
of channels to function as flood protection channels and also provides
control of invasive, non-native plants and control of weeds at revegetation
sites. The District also manages vegetation to protect levees, and concrete
linings from plant roots; to meet local fire codes, to provide visual
clearance of a facility; and to provide access along maintenance roads.
Depending on the original design and the characteristics of the channel,
the frequency of vegetation management varies from annually to every
few years.
In many creek sections, both sediment removal and aquatic herbicide
application are done in different years within the maintenance cycle.
For example, in the year following sediment removal, herbaceous wetland
vegetation may become established, and in the third year, may pose a
potential flood hazard. Herbicide is applied to kill the vegetation,
and herbicide application may continue in subsequent years before sediment
accumulates until it eventually reaches a point where flood capacity
is significantly reduced and sediment removal is again required.
Herbicides are used extensively and are preferred by reason of lower
cost over mechanical and hand control methods. Currently, the District
does not use herbicides in the Pajaro River Basin ("South County"),
but would do so under the proposed SMP. The herbicide use in the Pajaro
River Basin would be on approximately 56 miles of channel, 11 miles
of which would be done in conjunction with sediment removal. Vegetation
in these areas of the Pajaro River Basin is currently controlled by
hand or mechanical methods.
Currently, the District uses glyphosate (Monsanto's Roundup® Pro
and Aquamaster®, an aquatic formulation formerly marketed as Rodeo®)
to control in-channel vegetation . Upland herbicide spraying applies
to levees, unpaved maintenance roads, District right-of-way, and along
some property lines. Pre-emergent herbicides control vegetation on levees
and access roads by preventing the germination of weed seeds. The District
uses a range of pre-emergent herbicides, including pendimethalin and
chlorsulfuron. This particular application may change to reflect new
restrictions under consideration by the California Department of Pesticide
Regulation.
4. Bank Protection
Bank protection involves an action by the District to repair stream
banks that are eroding or are in need of preventative erosion protection.
The District may implement bank protection when the problem (1) causes
or could cause significant damage to a property or adjacent property,
(2) is a public safety concern, (3) adversely affects transportation
or recreational use, (4) adversely affects water quality or beneficial
uses, or (5) adversely affects riparian habitat. Based on past experience,
the District estimates that an average of one linear mile of stream
banks may be repaired each year spread over some 30 to 50 individual
work sites. Work is usually done between July 1 and October 15.
Bank repairs may take several forms from installing "hard" structures
(e.g., rock, concrete, sack concrete, gabions) to "soft" structures
(e.g., willow brush mattresses, log crib walls, pole plantings) or a
combination of hard and soft structures. An important feature of the
SMP is a programmatic approach to impact assessment and mitigation at
bank protection sites that takes into account fisheries and riparian
resources values (SMP Appendix E). The District will install no more
than 50% of future bank protection projects under the SMP as hardscape.
5. Minor Activities
Minor maintenance activities include trash removal, installation of
fences and gates; repairs to restore access roads and levees; grading
small areas to improve drainage and reduce erosion; repair to existing
structures (e.g. replacement of concrete linings and culverts);
sediment removal at stream gages, outfalls, culverts, flap gates, tide
gates, inlets, grade control structures, fish ladders, fish screens;
graffiti removal; tree pruning along maintenance roads; irrigation,
weeding, replanting and other maintenance at mitigation sites; removal
of obstructions to flow at bridges, streamflow measuring stations, box
culverts, storm drain outfalls and drop structures; removal of trees
in danger of falling, fallen trees, and associated debris to maintain
channel design capacity; and ground squirrel and rodent control with
traps, smoke bombs, and pesticides.
6. Mitigation Incorporated in the Project
Chapter 4 of the SMP presents policies to protect resources during
the implementation of routine stream maintenance activities. These policies
provide guidance to District managers and staff in the environmental
review, design, and implementation of individual stream maintenance
projects. BMPs have been developed to implement each of these policies
and to mitigate environmental impacts identified in the EIR.
a. Best Management Practices (BMPs)
The SMP has specifically developed BMPs applicable to routine stream
maintenance, and these are incorporated into the SMP (SMP Appendix
G). The BMPs provide mitigation for potential Water Quality, Vegetation,
Wildlife and Fisheries, Land Use and Cultural Resources impacts.
b. Wetland and Riparian Compensation
Over the long-term, the SMP has the potential to significantly affect
the ecological and biological environment of Santa Clara County by
cumulatively affecting wetland habitats, including tidal and freshwater
wetlands and riparian habitats. Though measures in this EIR will avoid
or reduce these impact, the District acknowledges that it would not
be to a less-than-significant level if compensatory mitigation were
not provided.
The SMP includes a compensatory mitigation package to compensate
for the significant residual impacts of sediment removal and vegetation
management on in-stream wetlands and riparian vegetation. The compensatory
mitigation package includes the following components: (1) tidal wetland
restoration; (2) freshwater wetland creation; (3) stream and watershed
protection; and (4) control of giant reed. This mitigation is described
in detail in Chapter 5 of the SMP.
Bank protection is addressed by the Programmatic Impact and Mitigation
for Bank Protection protocol (SMP Appendix E) which compares the intensity
of the work method and amount of hardscape against the environmental
sensitivity of the work location. Impact and mitigation are balanced
between individual projects.
c. Special Status Species
The avoidance and minimization measures incorporated in the project,
described in SMP Chapter 4, are considered sufficient to reduce
most, but not necessarily all, potential impacts of the SMP on special-status
species to a less-than-significant level. Residual impacts are reduced
to less than significant by specific provisions in the compensatory
mitigation program described above.
7. SMP Exclusions
a. Activities Outside of Routine Maintenance are Excluded
In the course of CEQA review, the District determined that there
were possible channel maintenance activities that may not be accommodated
by the BMPs and other programmatic mitigation proposed as part of
the SMP. The following maintenance activities are excluded from the
SMP: sediment removal and vegetation management on stream reaches
above the 1,000-foot elevation contour which is above the reservoirs;
hardscape bank protection projects which occur in high quality fisheries
habitat or existing high quality riparian habitat, and initial removal
of in-channel trees in Llagas Creek downstream of Luchessa Avenue
to the confluence with the Pajaro River.
b. Other Activities are Excluded
Routine maintenance restores flood conveyance capacity to design
levels, but does not increase design capacity. The District also plans
and carries out flood protection projects as Capital Improvement Projects
(CIP). The CIP are subject to separate engineering and environmental
review which will take into account project specific impact and mitigation.
Once the CIP is completed, maintenance at the project site will be
incorporated into the SMP.
The SMP does not include certain other District maintenance activities
such as percolation ponds, in-stream water infiltration barriers (summer
dams), or dam and reservoir maintenance.
C. REGULATORY SETTING
1. CEQA
The District acts as the lead agency in fulfilling the requirements
of the California Environmental Quality Act (CEQA).
The District has conducted routine maintenance of canals and channels
used for water supply and stormwater conveyance in the past. Previously,
routine activities have been subject to a case-by-case determination
of potential for environmental impact followed by appropriate CEQA review.
The District is preparing this Program Environmental Impact Report
(EIR) because: 1) The District is seeking new long-term regulatory permits
for some routine maintenance activities from other agencies which require
the District to prepare a CEQA review; 2) the District is proposing
the use of herbicides for stream maintenance in the Pajaro Basin, an
area where they are not currently used; and 3) the District can minimize
future case-by-case review by considering the cumulative effects of
all potential SMP activities in a single Program EIR.
A Program EIR, defined in CEQA Guidelines Section 15168, is used for
a series of individual actions that are related "geographically, as
logical parts in a chain of contemplated actions in connection with
... a continuing program, or as individual actions carried out under
the same statutory or regulatory authority having generally the same
environmental effects that can be mitigated in similar ways." Thus the
SMP and this EIR emphasize the role that formally established programmatic
mitigation will play in the District's future maintenance work.
The maintenance activities described in this program EIR are ongoing
and will remain effective for an indefinite period of time as long as
the nature of the work or environmental conditions do not substantially
change. Because permits from other agencies will need to be renewed
in 10 years, the District will reexamine the applicability of the Program
EIR at that time and make revisions as needed.
2. Permits from Other Agencies
The District is applying for permits or other forms of regulatory approvals
for those activities included in the SMP that are under the jurisdiction
of the California Department of Fish and Game, the Regional Water Quality
Control Board and the U.S. Army Corps of Engineers. It is the District's
intent that the program and mitigation defined by the SMP would serve
as the basis for state and federal permits and permit conditions. The
program EIR will help state and federal agencies comply with their environmental
review requirements.
D. ENVIRONMENTAL EFFECTS
The proposed program is the continuation of routine sediment removal,
vegetation management and bank protection activities that have been
carried out by the District for many years. Work is done on modified
and unmodified channels. The need for ongoing maintenance has resulted
from land use change in the watershed and from past modifications to
once natural channels, first done to support agriculture, and later
to provide flood protection and to accommodate transportation corridors
for urban developments on the valley floor and low foothill areas of
Santa Clara County. The maintenance program did not create the conditions
that led to the need for maintenance, but routine maintenance is now
needed to protect surrounding properties from flood and bank failure
damage.
The environmental setting of the project - the environmental baseline
from which project impacts are measured - is the present-day disturbed
creek condition. In this context, most of the effects of maintenance
are either insignificant or can be mitigated to less than significant
by application of the BMPs included in the SMP.
The Draft Program EIR identifies several impacts on biological resources
as significant and unavoidable.
A) Sediment removal and vegetation management remove wetland and riparian
(streamside) vegetation which provides habitat for fish and wildlife,
including some special status species. Mitigation through the BMPs and
the compensatory mitigation program appreciably reduce the magnitude
of the wetland and riparian impact, but local effects near work sites
may not be completely offset by mitigation away from the affected reach
or in a different watershed. The local effect is fragmentation of wildlife
habitat, with loss of habitat area, quality, and connectivity. The residual,
unmitigated effect is considered adverse, significant, and unavoidable
(Impact Bio-4).
B) Hardscape installation for bank protection has the potential to
reduce riparian vegetation functions and values and associated wildlife
and fisheries habitat. Placement of hardscape is a permanent change
that can contribute to the increasing fragmentation of the natural bank
landscape, which can affect wildlife that depend on stream corridors.
Although implementation of the BMPs and programmatic mitigation (SMP
Appendix E) would reduce the magnitude of impacts, there would likely
be residual unmitigated impacts is some watersheds. The cumulative impacts
from bank protection would thus remain significant and unavoidable (Impact
Bio-5).
C) Repeated herbicide vegetation control has the effect of holding
channel vegetation to a lower successional stage and changes the vegetation
community (the plant and animal species present). Because the District
has been using herbicides in North County for many years, the environmental
baseline already shows this effect and further work under the SMP will
not have a significant incremental impact. Resuming herbicide use in
the Pajaro River Basin, however, will produce changes and a concomitant
loss of stream vegetation functions and values, which would cause a
significant cumulative adverse impact on wildlife habitat. (Impact Bio-6).
The impacts on wetland and riparian vegetation (Bio-4) and impacts
of herbicide use on the vegetation community (Bio-6) would gradually
abate if the practices were discontinued. The cumulative effects of
hardscape bank protection, however, are deemed irreversible.
The potentially significant effects found in the Draft Program EIR
are listed in the Summary Table S-1, along with the BMP identification
code number and the short title of the BMP. The full list of BMP's is
attached as SMP Appendix G.
There are environmental effects that do not exceed the threshold of
CEQA significance found in Chapters IV-C Land Use and IV-D Hazards,
Public Health and Public Safety. While many of these effects will be
further reduced or avoided by the implementation of the BMPs these less
than significant effects are not listed in Table S-1 or otherwise discussed
in the Summary.
E. CUMULATIVE EFFECTS
Most sediment removal and vegetation management activities repeatedly
take place on the same reaches of channels, in places most affected
by past urbanization and channel alteration. As described above, the
removal of wetland or riparian vegetation associated with the SMP is
considered cumulatively significant. The placement of additional hardscape
within stretches of vegetated channel may also contribute to significant
cumulative impacts in some watersheds over the years.
The District is currently planning and designing several flood protection
projects. These Capital Improvement Projects are not part of the proposed
SMP. In each case, these Capital Improvement Projects are subject to
an environmental review and will as necessary mitigate incremental impacts
on the channels to levels of environmental insignificance. There are
potential cumulative environmental impacts associated with the compensatory
mitigation projects for the SMP. Project specific environmental impacts
of the mitigation projects will be addressed as part of the specific
CEQA documents that will be prepared for all mitigation projects.
F. ALTERNATIVES TO THE PROPOSED PROJECT
The alternatives analysis focuses on the ways that the long-term,
cumulative impact of routine maintenance could be reduced. The proposed
project is adoption of the SMP and implementation of its work performance
protocol and programmatic mitigation. The proposed SMP is characterized
as the "Multi-Year Program Alternative" and is the District's preferred
alternative. The "No Project" Alternative represents the District not
adopting the SMP and continuing the current practice of routine maintenance.
The "No Work" Alternative projects conditions with no maintenance work
conducted. All of the other alternatives evaluated in this Chapter focus
on different ways to operate under an SMP. The main differences between
the alternatives are 1) the amount of flood protection provided; 2)
the amount of herbicide used; and 3) the amount of stream vegetation
affected.
1. Alternatives Evaluated in EIR
1. Multi-Year Program Alternative The
Multi-Year Program Alternative, which is described in detail in the
SMP and is the Preferred Alternative, includes sediment removal, vegetation
management, bank protection and minor associated work. Projected levels
of work are based on historical levels with minor adjustments made
for foreseeable future changes. The program includes BMPs and a compensatory
mitigation package. This programmatic EIR would serve as the major
vehicle for evaluating future work under CEQA, and projects are expected
to be covered by 10-year permits.
2. Existing Program Alternative [No Project] continues
current maintenance criteria and practices without establishment of
programmatic assessment and mitigation; continuation of case-by-case
regulatory review.
3. No Work Alternative discontinues
maintenance of streams, canals and other associated District facilities.
Allows channels to form by themselves. Over time, these facilities
could fill in with more sediment and vegetation and could reduce flood
protection.
4. No Herbicides Alternative assumes no use of
herbicides in routine stream or canal maintenance. Instead, vegetation
will be managed by mechanical and hand methods in those areas in which
herbicides are currently used in the Santa Clara Basin, and no herbicides
will be used in the Pajaro River Basin.
5. Modified Pajaro River Basin Alternative is similar
to the proposed Multi-Year Program Preferred Alternative except that
it will not include the use of herbicides in stream channels of the
Pajaro River Basin unless they are for the control of non-native,
invasive plants. Instead, hand and mechanical methods will be used
to control vegetation in the Pajaro River Basin stream channels. Herbicides
would be used in adjacent upland areas in the Pajaro River Basin,
and in channels associated upland areas in the Santa Clara Basin and
in canals.
6. Reduced Work Alternative reduces the overall
amount of routine stream maintenance work. Sediment removal and vegetation
management would no longer take place in unmodified channels except
100 feet upstream and downstream of bridges or road crossings as needed
and at stream gages, outfalls, trash racks and other in-stream structures.
Herbicide use will resume in the Pajaro River Basin. Maintenance activities
in canals would be the same as under the Multi-Year Program Alternative.
Hardscape structures would not be included in the SMP with this alternative.
2. Environmental Comparison of Alternatives
The primary environmental difference among alternatives is in the
magnitude of significant biological effects. Most other areas of potential
impact are not significant for the proposed project, or can be reduced
to insignificance by mitigation incorporated in the project, and do
not vary appreciably among alternatives.
The No Work Alternative would eliminate all maintenance and would
have significant public safety and economic impacts due to increased
risk of flooding. Overall, there would be more vegetation in the stream
channels.
The Existing Program Alternative would have less opportunity for regional
compensation for cumulative maintenance impact. Although some mitigation
could be imposed during individual project review, the SMP represents
a significant opportunity to accomplish a regional aquatic, wetland,
and riparian enhancement program.
Alternatives with reduced herbicide use (Existing Program, No Herbicides,
Modified Pajaro River Basin, and Reduced Work) have the benefit of less
long term vegetation change, but would result in a greater annual removal
of vegetation. Because mechanical methods are less efficient than herbicides,
regrowth between treatment is greater in areas treated only with mechanical
methods so there is usually more vegetation present when the work is
done.
The "Reduced Work" Alternative would reduce impacts to stream vegetation
by one-fifth and would not have cumulative impacts from hardscape structures,
however, it may reduce the amount of flood protection.
3. Alternative to Maintenance is Beyond Scope of SMP
Maintenance does not include activities such as raising levees to
increase design flood capacity, reconfiguring stream channels, or limiting
or modifying upstream land uses. While the need for maintenance and
hence the impact of maintenance in some streams could be reduced by
changing the channel condition, the necessary design and construction
work is beyond the scope of routine maintenance and the proposed SMP.
Table S-1
Summary of Potentially Significant Impacts and Mitigation Incorporated
into the Proposed SMP
Key to Table S-1:
| Impact: |
The impact number and short description
from EIR Chapter IV. |
| BMP Code |
The code number cross referencing
BMPs in EIR Chapter IV and SMP Appendix G, Best Management Practices
listing. |
| Short Title |
Short title of the BMP |
| Activity |
Category of maintenance activity
most affected: SR = Sediment Removal; VM = Vegetation Management;
BP = Bank protection; MM = Minor Maintenance. |
| Impacts |
BMP
Code |
Short
Title |
Activity |
| Unavoidable Adverse
Impacts that would Remain after Mitigation |
|
| IV-B. Biology |
| Impact
Bio-4: The cumulative impact of sediment removal and vegetation
management would fragment wildlife habitat |
1.13 |
Prevent Scour Downstream
of Sediment Removal |
SR |
| 2.1 |
Minimize vegetation removal |
All |
| 3.6 |
Remove Sediment from
One Side of Large Channels in Alternate Years at Selected Sites |
SR |
|
Off-site Compensatory
Mitigation
|
| Impact
Bio-5: Bank protection would cause a loss of riparian vegetation
functions and values, which would cause a significant cumulative
adverse impact on wildlife and fisheries habitat |
2.1 |
Minimize vegetation removal |
All |
| 2.3 |
Minimize Hardscape in
Bank Protection Design |
BP |
| 3.5 |
Minimize Loss of Aquatic
Habitat from Bank Protection work |
BP |
| 3.14 |
Maintain or Provide Escape
Cover |
BP |
| Impact
Bio-6: The cumulative effects of resuming herbicide use
in the Pajaro River Basin would substantially reduce the value of
the habitat for wildlife |
2.1 |
Minimize vegetation removal |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
All |
| 3.18 |
Herbicide use in aquatic
areas |
VM |
| 3.19 |
Develop a biodiversity
monitoring program |
All |
|
Off-site Compensatory
Mitigation
|
| Impacts That
Would Be Mitigated to less than Significant |
| IV-A. Geomorphology |
| Impact Geo-1.
Sediment removal in certain locations may increase erosion downstream
of the removal site. |
1.13 |
Prevent Scour Downstream
of Sediment Removal |
SR |
| Impact Geo-2.
Elimination of in-channel vegetation may increase sediment
accumulation downstream. |
1.14 |
Minimize Sediment Transport
Downstream from In-channel Herbicide Sites |
VM |
| Impact Geo-3.
Removal of vegetation may increase local erosion. |
1.16 |
Minimize Local Erosion
increase from In-channel Vegetation Removal |
VM |
| Impact Geo-4.
Bank protection measures can direct flows downstream, resulting
in new erosion and bank instability problems. |
1.15 |
Prevent Erosion Downstream
of Bank Protection Sites |
BP |
| Impact Geo-5.
Removal of woody debris may reduce channel bed diversity.
|
3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| IV-B. Biology |
| Impact
Bio 1: Sediment removal and vegetation management would
impact in-stream wetland and riparian vegetation |
1.13 |
Prevent Scour Downstream
of Sediment Removal |
SR |
| 2.1 |
Minimize vegetation removal |
All |
| 3.6 |
Remove Sediment from
One Side of Large Channels in Alternate Years |
SR |
| Off-site
Compensatory Mitigation |
| Impact
Bio-2: The project could result in removal of heritage-sized
trees |
2.1 |
Minimize vegetation removal |
All |
| 2.2 |
Minimize Stream Access
Impacts |
SR, BP |
| 2.8 |
Replace heritage trees |
BP |
| 3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| Impact
Bio-3: Program implementation could introduce invasive
plant species into native, riparian, or wetland habitat areas |
2.1 |
Minimize vegetation removal |
All |
| 2.5 |
Planting |
BP |
| 2.6 |
Mulching |
BP |
| 2.7 |
Seeding |
BP |
| Impact
Bio-7: Chemical use by the District, especially for rodent
control, could adversely affect non-target species |
2.1 |
Minimize vegetation removal |
All |
| 3.1 |
Minimize Impacts to Special-status
Animals Via Site Assessments and Avoidance Measures |
All |
| 3.18 |
Herbicide Use in Aquatic
Areas |
VM |
| 3.2 |
Minimize Herbicide Impacts
on Non-target species |
VM |
| 3.21 |
Minimize Rodent Control
Impacts on Non-target Species |
MM |
| 4.7 |
Herbicide Use Requirements |
VM |
| Impact Bio-8:
Maintenance activities could introduce invasive wildlife
species |
3.4
|
Mitten Crab Control Measures |
SR |
| Impact
Bio-9: Maintenance activities could directly harm nesting
species protected under the Migratory Bird Treaty Act and other
statutes |
2.1 |
Minimize vegetation removal |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
All |
| 3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| 3.19 |
Develop a Biodiversity
Monitoring Program |
All |
| Impact
Bio-10: Maintenance work conducted in channels could substantially
interfere with migration, spawning, incubating, or rearing habitat
for native aquatic species |
2.2 |
Minimize Stream Access
Impacts |
SR, BP |
| 3.7 |
Salvage Native Aquatic
Vertebrates from Dewatered Channels |
SR, BP |
| 3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| 3.11 |
Avoid Dewatering an Entire
Isolated Stream Reach |
SR, BP |
| 3.12 |
Maintain Low-flow Fish
Passage |
SR, BP |
| 3.13 |
Remove Temporary Fills
as Appropriate |
SR, BP |
| 3.14 |
Maintain or Provide Escape
Cover |
SR, BP |
| 3.15 |
Restore Riffle and Pool
Configuration of Channel Bottom |
SR, BP |
| 3.16 |
Restore Spawning Gravels
in Work Site Areas |
SR, BP |
| 3.17 |
Reuse Sediments and Gravels
As Appropriate |
SR |
| Impact
Bio-11: Temporarily suspended sediment can adversely affect
aquatic or semi-aquatic species |
1.1 |
Conduct Work During Low
Flow Periods |
All |
| 1.2 |
Tidal Work Areas |
SR |
| 1.3 |
Dewater/ Bypass Water
at Non-tidal Sites |
SR, BP |
| 1.4 |
Avoid Erosion When Restoring
Flows |
SR, BP |
| 1.5 |
Erosion and Sediment
Control Measures |
BP |
| 1.6 |
Use of Wheel and Track
Mounted Vehicles in Stream Bottoms |
SR, BP |
| 1.7 |
Pump/
Generator Set Operations and Maintenance
|
SR, BP |
| 1.8 |
Handle Sediments So As
to Minimize Water Quality Impacts |
SR |
| 1.9 |
Soil Stockpiles |
SR |
| 1.12 |
Groundwater Management |
SR, BP |
| 1.14 |
Minimize Sediment Transport
Downstream from In-channel Herbicide Sites |
VM |
| 1.15 |
Prevent Erosion Downstream
of Bank Protection Sites |
BP |
| 2.2 |
Minimize Stream Access
Impacts |
SR, BP |
| 3.1 |
Conduct In-Channel Work
During the Dry Season |
SR, BP |
| Impact
Bio-12: Sediment Removal would adversely affect special-status
species |
1.3 |
Dewater/ Bypass Water
at Non-tidal Sites |
SR, BP |
| 1.4 |
Avoid Erosion When Restoring
Flows |
SR, BP |
| 2.4 |
Minimize Impacts to Special-status
Plants by Avoidance Based on Site Assessments |
All |
| 3.1 |
Minimize Impacts to Special-status
Animals Via Site Assessments and Avoidance Measures |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
All |
| 3.3 |
Avoid serpentine habitat
|
All |
| 3.6 |
Remove Sediment from
One Side of Large Channels in Alternate Years |
SR |
| 3.7 |
Salvage Native Aquatic
Vertebrates from Dewatered Channels |
SR, BP |
| 3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| 3.1 |
Conduct In-Channel Work
During the Dry Season |
SR, BP |
| 3.11 |
Avoid Dewatering an Entire
Isolated Stream Reach |
SR, BP |
| 3.12 |
Maintain Low-flow Fish
Passage |
SR, BP |
| 3.15 |
Restore Riffle and Pool
Configuration of Channel Bottom |
SR, BP |
| 3.16 |
Restore Spawning Gravels
in Work Site Areas |
SR, BP |
| 4.5 |
Vehicle and Equipment
Cleaning |
All |
| 6.1 |
Spill Prevention |
All |
| 6.4 |
Vehicle and Equipment
Fueling |
All |
| 6.5 |
Vehicle and Equipment
Maintenance |
All |
| Impact
Bio-13. Vegetation Management would adversely affect special-status
species. |
1.14 |
Minimize Sediment Transport
Downstream from In-channel Herbicide Sites |
VM |
| 2.1 |
Minimize vegetation removal |
All |
| 2.2 |
Minimize Stream Access
Impacts |
SR, BP |
| 2.4 |
Minimize Impacts to Special-status
Plants by Avoidance Based on Site Assessments |
All |
| 3.1 |
Minimize Impacts to Special-status
Animals Via Site Assessments and Avoidance Measures |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
SR, BP |
| 3.3 |
Avoid serpentine habitat
|
All |
| 3.7 |
Salvage Native Aquatic
Vertebrates from Dewatered Channels |
SR, BP |
| 3.1 |
Conduct In-Channel Work
During the Dry Season |
SR, BP |
| 3.18 |
Herbicide Use in Aquatic
Areas |
VM |
| 3.2 |
Minimize Herbicide Impacts
on Non-target species |
VM |
| 4.7 |
Herbicide Use Requirements |
VM |
| Impact
Bio-14. Bank Protection would adversely affect special-status
species. |
1.5 |
Erosion and Sediment
Control Measures |
BP |
| 2.3 |
Minimize Hardscape in
Bank Protection Design |
BP |
| 2.4 |
Minimize Impacts to Special-status
Plants by Avoidance Based on Site Assessments |
All |
| 2.5
2.6
2.7
|
Planting, Mulching, Seeding |
BP |
| 3.1 |
Minimize Impacts to Special-status
Animals Via Site Assessments and Avoidance Measures |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
All |
| 3.3 |
Avoid serpentine habitat
|
All |
| 3.7 |
Salvage Native Aquatic
Vertebrates from Dewatered Channels |
SR, BP |
| 3.14 |
Maintain or Provide Escape
Cover |
BP |
| 3.19 |
Develop a Biodiversity
Monitoring Program |
All |
| Impact
Bio-15: Minor Stream Maintenance Activities would adversely
affect special-status species. |
2.4 |
Minimize Impacts to Special-status
Plants by Avoidance Based on Site Assessments |
All |
| 3.1 |
Minimize Impacts to Special-status
Animals Via Site Assessments and Avoidance Measures |
All |
| 3.2 |
Minimize Impacts to Breeding
Birds Via Site Assessments and Avoidance Measures |
All |
| 3.3 |
Avoid serpentine habitat
|
SR, BP |
| 3.7 |
Salvage Native Aquatic
Vertebrates from Dewatered Channels |
SR, BP |
| 3.9 |
Retain Woody Materials
and Vegetation |
BP, MM |
| 3.1 |
Conduct In-Channel Work
During the Dry Season |
SR, BP |
| 3.21 |
Minimize Rodent Control
Impacts on Non-target Species |
MM |
| IV-. D Public
Safety |
| Impact WQ-1.
Erosion of mercury containing sediment. |
1.1
|
Avoid Exposing Soils
with High Mercury Levels |
BP |
| IV-E. Cultural |
| Impact Cul-1:
Disruption of Cultural Resources |
7.1
|
Discovery of Cultural
Remains or Historic Artifacts |
All |
| Impact Cul-2:
Disruption of Native American Burials |
7.1
|
Discovery of Cultural
Remains or Historic Artifacts |
All |
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