Attachment 7 - Wildlife Technical Memorandum(o2)Wetland & Aquatic Sciences
Wildlife Ecology
Landscape Architecture
TECHNICAL MEMORANDUM
June 16, 2021
To: Ms. Bel' Johnson
Landscape Manager
Point Edwards HOA
93 Pine Street
Edmonds, WA 98020
From: Andrew J. Rossi, B.S.
Wildlife Biologist
Raedeke Associates, Inc.
Richard W. Lundquist, M.S.
President / Wildlife Biologist
Raedeke Associates, Inc.
RE: Point Edwards HOA Edmonds —
Great Blue Heron Assessment
(RAI Project No. 2021-010-001)
This report documents the results of our field investigation at the Point Edwards
Condominium Complex in Edmonds, WA. The purpose of this investigation is to
evaluate current wildlife use and habitat conditions within the study area, as well as
evaluate the historical mapped sites of the great blue heron (Ardea herodias) colony and
any other regulated species such as bald eagles (Haliaeetus leucocephalus) in the vicinity
of the project site.
This Technical Memorandum is intended for submittal to the City of Edmonds as part of
an application by Point Edwards HOA for a Type III -A Permit seeking authorization
from the City to (1) remove, coppice, or trim existing trees including a number of red
alder (Alnus rubra) trees and (2) revegetate the slope with other native plant varieties, as
well as some non-native cultivars. See the Combined Map Set (Exhibit 2) of revegetation
plans for specific tree locations and treatments (Thomas Rengstorf and Associates.
2015), which is attached as Appendix A to this technical memorandum.
Raedeke Associates, Inc. staff visited the study area on February 16, 2021, and on March
11, 2021. During these field investigations, we documented wildlife presence, sign, and
habitat, and we also described plant communities. We recorded information regarding
2111 N. Northgate Ave, Ste. 219 Seattle, WA 98103 206-525-8122 www.raedeke.com
Attachment 7
2
reproduction, habitat use, and activities of all wildlife species observed. In addition, we
noted special habitat features such as large and/or hollow trees, snags [standing dead or
partly dead trees at least four inches in diameter at breast height (dbh) and at least six feet
tall], and large downed logs.
STUDY AREA LOCATION
The project site consists of a 21-acre property, containing 261 Snohomish County Tax
Parcels, at 93 Pine Street in Edmonds, Washington (Figure 1). This places the property
within the northwest quarter of Section 26, Township 27 North, Range 3 East, W.M. Site
details received from Bel Johnson on January 20, 2021 determined the property
boundaries.
The project site is immediately adjacent and southwest of a parcel owned by The
Chevron Corporation (Figure 2). This Chevron Site is not currently being utilized for any
commercial uses.
PROJECT DESCRIPTION
The Type III -A Permit application submitted to the City of Edmonds by Justina Kraus
and Bel Johnson (2020) outlines the complete summary of proposed actions at the project
site. The project will be completed in three phases. Phases I and II involve the removal,
coppicing, and pruning of trees. In total, the project proposes to remove 35 trees, coppice
(cut but leave stump for resprouting) 22 trees, prune 82 trees, create 31 snags, and leave
87 trees unchanged. All tree modifications will be completed using small handheld tools
such as chainsaws and/or trimmers. A wood -chipper may potentially be used to create
mulch, but would only be positioned on the existing access road above the slope to the
south of where tree modifications will take place.
Phase III involves the replanting of the slope. Similar to Phases I and II, the revegetation
in Phase III will be completed using only hand tools such as shovels and wheelbarrows.
In total, the project proposes to install 45 trees, 48 large shrubs, 61 medium shrubs, 92
low shrubs, 90 ferns and 126 ground cover plants. See Appendix A for figures outlining
revegetation plans (Thomas Rengstorf and Associates 2015).
These modifications will take place on the northern and northeastern edges of the project
site (Appendix A). The northwestern slope will be unaltered.
Point Edwards HOA Edmonds Raedeke Associates, Inc.
Great Blue Heron Assessment June 16, 2021
Attachment 7
REVIEW OF BACKGROUND INFORMATION
WDFW PHS Database
The current Washington Department of Fish and Wildlife (WDFW 2021) online Priority
Habitats and Species (PHS) database map depicts two areas at or in the vicinity of the
project site (Figure 3) with records of use by great blue herons. The first area is located
at the southwestern corner of the stormwater pond in the northern portion of the project
site and extends towards the nearest condominium building to the south. The second area
is located within the Chevron Parcel to the northeast of the project site and it is
approximately 135 to 250 feet northeast of the project site. Both entries in the PHS
database are listed under March 25, 2002. They also both indicate the presence of three
unoccupied nests and up to 17 herons in previous years. There are no entries on the PHS
database that indicate these nests have been active since before 2002.
The PHS map also indicates the presence of wetland, resident coastal cutthroat trout
(Oncorhyncus clarki), and Coho salmon (Oncorhynchus kisutch) habitat within the
northeast portion of the Chevron parcel and extending towards the northeast into
Edmonds Marsh. Finally, estuarine wetland and Dungeness crab (Cancer magister)
habitat are indicated on the PHS map west of the project site within the Puget Sound. No
other priority or otherwise regulated species or habitats are indicated as occurring within
1,000 feet of the project site on the PHS database.
Great Blue Heron Colony History
WDFW no longer conducts annual monitoring of heron colonies (Gary Bell, WDFW,
personal communication 2021), and information that WDFW does provide is second-
hand. The last known successful nesting period was before the PHS entry in March
2002, when there were reportedly up to 17 herons. It is possible that eagle predation
greatly reduced the number of nesting pairs and fledglings. WDFW (Gary Bell, Gretchen
Blatz, WDFW, personal communication, 2021) confirmed that they had no further
information regarding this potential rookery area. They also indicated the nearest
documented activity was approximately 1 mile from the site and this information had not
been updated since 2002.
EXISTING CONDITIONS
Vegetation and Habitat Description
The majority of the project site consists of the "formal grounds" surrounding the
condominium buildings. Plant communities in these areas are characterized by small
ornamental trees and ornamental shrubs with some areas (particularly around the
perimeter of the formal grounds) characterized by more native plant species such as salal
(Gaultheria shallon), red -twig dogwood (Corpus sericea), Oregon grape (Mahonia
aquifolium), and sword fern (Polystichum munitum).
Point Edwards HOA Edmonds Raedeke Associates, Inc.
Great Blue Heron Assessment June 16, 2021
Attachment 7
El
The proposed revegetation area in the north section of the project site is characterized by
a low diversity stand of red alder (Alnus rubra) with very few shore pine (Pinus contorta)
and western red cedar (Thuja plicata), where an understory of invasive species such as
holly (Ilex aquifolium), English ivy (Hedera helix), and Himalayan blackberry (Rubus
armeniacus) are beginning to become more established. The proposed revegetation area
along the northeastern edge of the project site is characterized by dense growth of shore
pine with some bigleaf maple (Acer macrophyllum), vine maple (Acer circinatum), and
red -twig dogwoods (Cornus sericea) interspersed between them.
These vegetation communities extend off -site slightly to the north and east onto the
Chevron property, but then end where an empty gravel pad exists on most of the Chevron
site. The proposed revegetation areas are bordered to the south by a publicly accessible
walking path that extends just northwest of the stormwater pond, where it ends.
Current Status of the Heron Colony and Other Significant Habitat Features
During our field investigations we observed a single nest structure within the boundaries
of the project site in the northern portion (Figure 4) of the site. This nest was
approximately 2 feet wide and 1.5 feet deep, and was constructed out of approximately
1/4 — inch sticks, but we did not observe any activity by herons or raptors at this tree
during our site visits. Also, we did not observe any individual herons or signs thereof at
the project site during our two field visits. We did, however, observe 3 stick nest
structures off -site to the northeast from a vantage point to the north of Edmonds Marsh.
These nests appeared to have the size and structure to support great blue herons, but also
did not show any signs of heron activity during our site visits. The nests were located
approximately 250 feet from the northeast edge of the project site.
Based on our observations at the Edmonds Point property during our two visits to the
study area, it appears that the herons have abandoned the former colony site, with (1)
only one remaining potential 2-foot diameter nest (that is not confirmed as having ever
been utilized by herons) still present, (2) no herons present during site visits, and (3) no
evidence of current heron nesting activity such as whitewash or feathers beneath nest tree
areas. We do not have any evidence to suggest that herons have nested at this site since
before the WDFW PHS entries dated March 2002. Thus, based on our observations and
information available, we believe the Point Edwards heron colony is no longer active and
has likely been inactive for over 18 years.
There is, however, anecdotal evidence to suggest herons utilize the area for other non -
nesting purposes. Local residents have reportedly observed a single heron in the vicinity
of the stormwater pond on the ground (Bel Johnson. Personal communication. Feb 16,
2021). It appears the stormwater pond with its cattails (Typha latifolia) functions as
foraging habitat for at least one heron on an irregular basis. Further, Edmonds marsh
serves as foraging and potential nesting habitat for herons.
Point Edwards HOA Edmonds Raedeke Associates, Inc.
Great Blue Heron Assessment June 16, 2021
Attachment 7
5
Regarding other regulated species, we saw no evidence of nesting activity by bald eagles
in the vicinity of the Point Edwards project site during our field investigations. During
our field investigation Bel Johnson indicated two trees located south of the project site
that were common perching locations for bald eagles (Figure 4), but no bald eagles were
observed on or over the project site during our field visit.
We did not observe any priority logs or snags during our visit to the project site, nor any
other priority habitats or otherwise regulated wildlife species.
Other Wildlife Observations
During our field investigations, we observed 17 bird species, spotted towhee, red -
breasted nuthatch, song sparrow, Anna's hummingbird, American crow, dark -eyed junco,
golden -crowned sparrow, golden -crowned kinglet, Canada goose, red -winged blackbird,
black -capped chickadee, pine siskin, American robin, Cooper's hawk, red-tailed hawk,
varied thrush, and killdeer. The Cooper's hawk and red-tailed hawk were observed
soaring over the site. We did not observe any other wildlife species or their sign during
our field investigations.
CURRENT HERON PROTECTION RECOMMENDATIONS
The WDFW (Azerrad 2012) revised its Priority Habitat and Species (PHS)
recommendations for great blue heron protection in 2012. These management
recommendations state "...recommendations applying to an active colony should remain
in effect for at least 10 years after nesting has ceased at the site of any former colony".
Because there is no evidence to indicate neither the nest in the northern portion of the
project site, nor the three observed nests to the northeast of the project site have been
active for over 18 years, according to the great blue heron guidance, the management
recommendations do not necessarily apply to these habitat features.
WDFW's current recommendations categorize colonies (which are defined in the
recommendations as Heron Management Areas — HMAs) as "rural," "suburban/rural,"
and "urban." These new recommendations provide separate buffer and protection
guidelines for each such category. Had the colony been active, it would fall into the
"suburban/rural" category due to (1) the amount of development around the colony site,
(2) the herons' historic habituation to human activity within a short distance to the colony
site (e.g., the use of the public trail with colony viewing sites located within 250 feet of
the colony site), (3) construction and commercial activities in the adjacent roadways, and
historic gas station, and (4) the overall developed nature of the surrounding habitat within
a commercial/industrial area of the City of Edmonds. For active "suburban/rural" HMAs,
the PHS recommendations are for a 200-meter (656-foot) year-round vegetated buffer
and a seasonal (nestingibreeding) no -activity buffer of 200 meters (656 feet), extending
out from the year-round buffer.
Point Edwards HOA Edmonds Raedeke Associates, Inc.
Great Blue Heron Assessment June 16, 2021
Attachment 7
0
The WDFW PHS guidelines recognize that new activities in proximity to an HMA are a
concern mainly when they exceed the type and intensity of historic activities in the area
(Azerrad 2012). Therefore, any project disturbances must be considered in the context of
the existing land use. Neither great blue herons nor bald eagles are listed on the
Washington State endangered, threatened, sensitive, or candidate species lists (WDFW
2019).
EVALUATION OF IMPACTS OF THE PROPOSED PROJECT
Impacts to the former Great Blue Heron Colony
As noted above, the WDFW (2021) PHS entries and correspondence with WDFW (Gary
Bell, Gretchen Blatz, WDFW, personal communication, 2021) indicate that no heron
nesting activity has been documented at the project site nor at the site to the northeast
since before March 2002. This is further confirmed by our field observations.
Accordingly, there are no great blue herons nesting at the project site that could be
impacted by the proposed vegetation management project. Any revegetation occurring
outside of a nesting season, while increasing overall species diversity and leading to the
development of high -quality large native trees (through planting and maintenance) would
enhance the overall habitat quality at the project site.
Impacts to Bald Eagles and Other Wildlife Habitat
The currently proposed vegetation management would occur entirely within the north and
northeastern edges of the project site. Those do not appear to have any habitat features
utilized by bald eagles. The two eagle perching trees (as well as other large potential
perching trees nearby to these two documented trees) located to the south of the project
site (Figure 4) will have significant visual screening from any vegetation management
activity due to existing vegetation, buildings, and a topographic break between them and
the vegetation management areas. The US Fish and Wildlife Service (2007) Bald Eagle
Management Guidelines encourage preserving large roost trees, preventing disturbances
to flight paths accessing foraging sites, and using pesticides, herbicides and other
chemicals in accordance with local, state, and federal guidelines. These
recommendations are all consistent with the proposed vegetation management plan.
Removal of many of the red alder trees as part of the proposed vegetation management
plan would cause the temporary displacement of some individuals of common species,
such as those documented in the "Other Wildlife Observations" section. However, we
expect these losses of individuals to be replaced over time with the establishment of the
variety of native plant species proposed. Thus, we anticipate relatively little adverse
impact over the long term to existing wildlife habitat or special habitat features on the
project site as a result of the vegetation management proposed. The proposed increase in
plant diversity, coupled with the ability to properly manage the health of the trees in these
areas over time will likely enhance the habitat within these vegetation management areas.
Point Edwards HOA Edmonds Raedeke Associates, Inc.
Great Blue Heron Assessment June 16, 2021
Attachment 7
Summary of Impacts on Wildlife and Wildlife Habitat
The proposed project would have no adverse impacts on the former heron colony within
the site boundaries and to the northeast, or either of the known eagle perching trees
located to the south of the project site. The heron sites have not been occupied for over
18 years and the eagle perching sites would have sufficient screening to avoid adverse
impacts. Further, we have not observed any evidence of nesting by bald eagles on or near
the project site.
We would expect an increase in overall wildlife species diversity utilizing the project site
as a result of an increased plant community diversity and increased overall tree health
from maintenance. Replacing the relatively sparsely vegetated understory that includes
invasive species with a variety of native shrubs and ground covers will increase plant
species richness and structural diversity, which should benefit wildlife habitat over time.
Additionally, the creation of snags through the management of the red alder trees will
promote further species diversity by encouraging use of the project site by cavity -nesting
species such as pileated woodpeckers.
RECOMMENDED MITIGATION MEASURES
Mitigation includes measures to avoid or minimize potential impacts to any great blue
herons that may utilize the project site or habitats in the vicinity of the project site. As
stated in the permit application (Kraus and Johnson 2020) arborists will perform or
supervise tree and plant modifications using known industry standards and protocols,
including the American National Standards Institute ANSI-A300 standards, which apply
to the tree care industry. For the proposed revegetation project, measures to avoid or
minimize the potential impacts to herons and other wildlife species include the following:
• To the extent feasible, schedule all revegetation to take place outside of the
nesting season, or late August through February (Azerrad 2012).
• Retain some of the healthiest red alder trees, including the individual with the
existing potential remnant nesting structure, to promote overall plant species
diversity and retain soil stability and habitat functionality.
• Most of the trees listed on the planting plan actually grow as tall shrubs (e.g., vine
maple, serviceberry). Thus, we recommend including the installation of native
tree species such as western hemlock (Tsuga heterophylla), western red cedar
(Thuja plicata), and shore pine (Pinus contorta) that can continue to grow under
the partial shade of existing vegetation and enhance the habitat quality in the
future as the plant community matures.
Point Edwards HOA Edmonds
Great Blue Heron Assessment
Raedeke Associates, Inc.
June 16, 2021
Attachment 7
• Focus on planting Pacific Northwest native plant varieties on the slopes and
reserve non-native cultivars to the periphery of slopes nearest the formal grounds
as much as possible.
• Any removal of invasive plants that must take place in the spring before fruiting
or seeding should be conducted without the use of power tools or heavy
equipment wherever possible to avoid any disturbance to potential nesting species
on our near the project site.
LIMITATIONS
We have prepared this report for the exclusive use of Bel' Johnson / Point Edwards HOA
and their consultants. No other person or agency may rely on the information, analysis,
or conclusions contained herein without permission from Bel' Johnson / Point Edwards
HOA.
We warrant that the work performed conforms to standards generally accepted in our
field, and has been prepared substantially in accordance with then -current technical
guidelines and criteria. The conclusions of this report represent the results of our analysis
of the information provided by Permit III -A proponent Bel' Johnson / Point Edwards
HOA and their consultants, together with information gathered in the course of this study.
No other warranty, expressed or implied, is made.
Thank you for the opportunity to prepare this information. If you have any questions,
comments, or need additional information, we are available at 206-525-8122 or via email
at rwlundquistgraedeke.com.
LITERATURE CITED
Azerrad, J. M. 2012. Management recommendations for Washington's priority species:
Great Blue Heron. Washington Department of Fish and Wildlife, Olympia,
Washington. March 2012.
Kraus, J. Johnson, B. 2020. Point Edwards Homeowners' Association Board Presents
City of Edmonds Type III -A Permit Application: Design Review for Vegetation
Modifications on a Geologically Sensitive Critical Slope. December 16, 2020.
Thomas Rengstorf and Associates. 2015. Existing Tree Survey and Revegetation Plans.
Exhibit 2. 29 July, 2015 plan set for Point Edwards HOA Edmonds, Washington.
Point Edwards HOA Edmonds
Great Blue Heron Assessment
Raedeke Associates, Inc.
June 16, 2021
Attachment 7
0
U.S. Fish and Wildlife Service. 2007. National bald eagle management guidelines. May
2007.
Washington Department of Fish and Wildlife. 2021. PHS on the web. Available
at: https://geodataservices.wdfw.wa.gov/hp/phs/. Last accessed February
19, 2021.
Washington Department of Fish and Wildlife. 2019. State Listed Species & State
Candidate Species. Revised June 2019. Available at:
https://wdfw.wa.gov/sites/default/files/2019-
06/threatened%20and%20endangered%20species%201ist.pdf. Last
Accessed March 12, 2021
Point Edwards HOA Edmonds
Great Blue Heron Assessment
Raedeke Associates, Inc.
June 16, 2021
Attachment 7
Additional Figures
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SOURCE INFORMATION: Washington Fish and Associates, Inc.
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Attachment 7
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IIFAM P U
THOMAS RENOSTORE
AND ASSOCIATES
a..,,., POINT
EMARDS
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NORTH SLOPF-
I.ASTSF.eT1ON-
EXIST ING TREE
SURVEY
Exhibit 2
L104
Revegetation Plan