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Council Meeting/Documents/Piling Installation Proposal - 333A Stewart Ave., View Royal, BC - Subtidal Habitat assessment
Appendix

Piling Installation Proposal - 333A Stewart Ave., View Royal, BC - Subtidal Habitat assessment

November 2, 2021Pages 100–1047 sections

Technical assessment of the subtidal environment and biophysical description of the project site at 333A Stewart Avenue.

1 CALL TO ORDER
Mar. 31, 2021Joachim Carolsfeld & Lee CritchleyNo eelgrass was observed in the project area

Piling Installation Proposal

333A Stewart Ave., View Royal, BC Subtidal Habitat assessment

Joachim Carolsfeld & Lee Critchley Mar. 31, 2021

Page 100–104

Overview:

It is proposed to add pilings to the existing legal dock associated with 333 Stewart Ave., View Royal (Fig. 1), to provide it greater stability – especially during storms. The work will take place approximately 15 m from the shore (fig. 2).

Localization of work site in Esquimalt Harbour (Google maps)
Localization of work site in Esquimalt Harbour (Google maps)
Figure 1. Localization of work site in Esquimalt Harbour (Google maps)
Localization of work site relative to shoreline (Google Maps)
Localization of work site relative to shoreline (Google Maps)
Figure 2. Localization of work site relative to shoreline (Google Maps)

The current report is a description of the subtidal environment of the immediate area, to inform assessment of environmental risk associated with the project.

Page 100–104

Methodology:

The area was filmed by Lee Critchley in a zig-zag matrix from 2-4.2 m depth. This footage was examined for biophysical description.

Page 100–104

Location description

The location is at the mouth of Limekiln Bay, part of the Esquimalt Harbour, an area characterized in the CRD Harbours Atlas (Fig. 3). In general, this is a bedrock and boulder shoreline, with pocket beaches, leading to a shallow soft bottom.

Substrate type map of Limekiln Bay
Substrate type map of Limekiln Bay

Figure 3. Substrate type of Limekiln Bay (AMR, 2004)

The site evaluation confirmed this general character – a bedrock and boulder-rich steep shoreline drops to a sandy mud bottom at a depth of about 2 m. The soft bottom extends at a low slope into the harbor, with scattered debris and rocks.

Page 100–104

Biological assessment:

At the time of the survey (January, 2021), the mud bottom in the area of the proposed pilings was devoid of large algae or eelgrass, with some wireweed Sargassum and bladed kelp Laminaria on larger rocks. More algae are present on the rock shore, including a variety of bladed red algae, and may be more prevalent later in the year. Otherwise, the sandy mud bottom has a thick diatom biofilm, pock-marked by active clam and worm burrows (Fig. 4), with numerous plumose anenomes (Metridium spp.) attached to debris. The pink starfish Pisaster brevispinus was observed, likely responsible for numerous clam excavation pits. Red rock crabs were also seen (Fig. 6).

Clam mounds and diatom film on mud/shell substrate
Clam mounds and diatom film on mud/shell substrate
Figure 4. Clam mounds and diatom film on mud/shell substrate
Plumose anenomes on debris
Plumose anenomes on debris
Figure 5. Plumose anenomes on debris

Figure 6. Rock crab on mud substrate

Page 100–104

Summary:

No eelgrass was observed in the project area. The sandy mud bottom, with rich clam resources and Laminaria kelp bed, are typical of this region and widespread. Piling placement should not affect any sensitive habitats.

Page 100–104

Reference:

Archipelago Marine Research (AMR). 2004. Subtidal Survey of Physical and Biological Features of Esquimalt Harbour. Report and Map Folio. Report to Victoria and Esquimalt Harbours Environmental Program, Transport Canada and Formation Environment Risk Management, CFB Esquimalt, Department of National Defence. 76 pp.

Page 100–104
Extracted from: 2021 11 02 Council Agenda - Agenda - Pdf