1.1 Enhancement of the Peel Waterways
The initiative to start exploring how the
Peel Region’s man-made waterways could be enhanced should be thought of a
‘pilot study’. This investigation and
report is one of the starting points of a program that will grow and evolve as
experience is gained on how the area reacts to enhancement. This will provide valuable understanding of
the how different species are using or not using added structures, and it will
inevitably give birth to ideas and
other programs as depicted in Figure 1. Progress
can be reviewed and existing programs adjusted if necessary, and new ideas
explored and developed.
At this stage of the program, there is no
objective to target the enhancement of a specific species. However as experience is gained, it may then
be appropriate to explore specific enhancement activities that target certain
species, as well as how natural areas may be enhanced/restored or protected from
wave erosion.
Figure 1. Pictorial
representation of the enhancement program and its review and expansion.
1.2 Ranking of Sites for Enhancement
§
Objective is
general enhancement of biodiversity with no specific species targeted
during the first stage of the program.
In order to help
prioritise where efforts and resources should first be directed, each site was
judged on its merits for its potential to benefit from enhancement and/or its
ability to respond to enhancement and provide a return value, eg species
diversity or abundance, or community benefits.
This was done using the criteria outlined in Table
1.
Enhancement programs should have clear objectives, and the objectives
for the first stage of this pilot study into enhancing the man-made waterways
is to increase biodiversity in general and gain a better understanding of how
local species are interacting with materials added.
Assessment of such criteria is subjective or
based on data where available, and has been used as a guide to help the
Steering Group understand the logic behind the selection of the most suitable
sites. The criteria were not ‘weighted’
for this study, however the PHCC could
easily add their own weighting to the criteria as part of their internal
assessment of options and how to proceed.
Table 1. Criteria used
to assess and rank each site for enhancement potential.
|
Feature / Attribute |
Description |
Rating |
|
1.
Water Quality |
Clarity/turbidity,
salinity fluctuations, residence time of water (flushing rate), potential for
serious contamination, stratification. NB: quality rating is
relative to the existing system and between sites, and not pristine ocean or
estuary waters. |
ê = very poor êê=
poor êêê
= average êêêê
= good êêêêê
= excellent |
|
2.
Existing Substrate Material |
Sediments and ability
to support concrete modules |
ê = very poor êêêêê
= excellent |
|
3.
Bottom Profile |
Slope profile, space
available for modules. |
ê = very poor êêêêê
= excellent |
|
4.
Neighbouring Habitats |
Habitats considered
productive and/or essential contributors of food or shelter such as wetlands,
saltmarshes, seagrass meadows. |
ê = very poor êêêêê
= excellent |
|
5.
Existing Biota |
Diversity/abundance of
fish, crustaceans and fouling organisms as an indicative potential of what
could be present. |
ê = very poor êêêêê
= excellent |
|
6.
Potential Diversity/Abundance |
Estimated potential of
the site to attract a range of species and/or increase abundance, as well as
attract new species, relative to existing species at the site. |
ê = very poor êêêêê
= very high |
|
7.
Permit Requirements |
Complexity of permit
process to carry out enhancement options. |
ê = very
complex/costly êêêêê
= none required |
|
8.
Access and Ease of Deployment |
Availability of
suitable access points and travel distance from module construction area (by
land and water). |
ê = very limited
access êêêêê
= excellent access |
|
9.
Educational Value |
Ability for the site to
be used for community, school, or university studies, or education. |
ê = very poor êêêêê
= excellent |
|
10. Value
Adding Potential |
Ability for enhancement
to contribute significantly to the ‘value’ of the area, or incorporate other
value adding options such as underwater live video, educational trails. |
ê = very poor êêêêê
= excellent |
|
11. Sponsorship
Potential |
Attractiveness of the
site and its enhancement for sponsors, ie exposure, feel good factor,
potential return on investment. |
ê = very poor êêêêê
= excellent |
|
12. Cost
– reported in Table
3 |
Estimated level of cost
to implement a suitable enhancement program for the site, including
transport, permits, number of modules, deployment, monitoring, and other
ongoing costs. |
ê = very low êêêêê
= very high |
Table 2. Ranking of each
site for enhancement potential.
ê =
very poor, êê=
poor, êêê =
average, êêêê =
good, êêêêê =
excellent
|
Site |
Water
Quality |
Existing
Substrate Material |
Bottom
Profile + space |
Neighbouring
Habitats |
Existing
Biota |
Potential Diversity/ Abundance |
Permit
Requirements |
Access
and Ease of Deployment |
Educational
Value |
Value
Adding Potential |
Sponsorship
Potential |
TOTAL SCORE |
RANKING |
|
Ocean Marina (incl Dolphin Quay) |
êêêê (potential
for oil/heavy metals) |
êêêê |
êêêêê |
êêê |
êêêê |
êêêêê |
êêêê |
êêêêê |
êêêêê |
êêêê |
êêêêê (high
public profile) |
48 |
1 |
|
Hall
Park Public Swim area |
êêêêê |
êêêêê (currents
could be an issue) |
êêêê |
êêêê |
êêêê |
êêêêê |
êêê? |
êêêê |
êêêêê |
êêêê |
êêêêê (high
public profile) |
48 |
1 |
|
Northport
– Village Beach and Bouvard Village |
êêêêê |
êêêê |
êêê |
êêê |
êêêê |
êêêêê |
êêêê |
êêê |
êêêêê (snorkelling
beach for school projects) |
êêêêê (options
such as u/w webcam) |
êêêêê (high
public profile) |
46 |
2 |
|
Mariners
Cove (Sales Office + marina area) |
êêê |
êêêêê |
êêêê |
êêêêê (Creery
Wetlands Nature Reserve) |
êêêê |
êêêê |
êêêê |
êêê |
êêêêê |
êêêê |
êêêêê (high
public profile) |
46 |
2 |
|
Leeward
Canals |
êêê |
êêêêê (good
mix of rock sizes) |
êêêêê (incl
ledge at foot of canal wall) |
êêêêê (Nature
Reserve) |
êêêê |
êêêê |
êêêê |
êêê |
êêêê |
êêêê (tie-in
with Nature Reserve) |
êêêê (mainly
residents) |
45 |
3 |
|
Eastport
Marina |
êêêê (potential
for oil/heavy metals) |
êêêê |
êêê |
êêêê (diverse
channel plus Nature Reserve) |
êêê |
êêêêê |
êêêê |
êêêê |
êêêê |
êêêê |
êêêêê (high
public profile) |
44 |
4 |
|
Eastport
– Foreshore Reserve Canal |
êêêê |
êêêê |
êêê (mattress
revetment) |
êêêêê (Adjacent
to Nature Reserve)) |
êêê (not
established yet) |
êêêêê |
êêêê |
êêê |
êêêê |
êêêê |
êêêê |
43 |
5 |
|
Soldiers
Cove |
êêêê |
êêêêê |
êêêê |
êêêêê (small
barrier saltmarsh island) |
êêê? |
êêêê |
êêê? |
êêêê |
êêê |
êêê |
êêê (mainly
residents) |
41 |
6 |
|
Performing
Arts Complex boardwalk |
êê |
êêê |
êêêê |
êêê |
êêê |
êêê |
êêê |
êêêê |
êêêêê |
êêêê |
êêêêê (high
public profile) |
39 |
7 |
|
Mandurah
Quays |
êêêê |
êêêê? (excellent
varying rock sizes) |
êêê? |
êêêê (nearby
saltmarsh islands) |
êêêê (ample
abundance already) |
êêêê |
êêê? |
êêê |
êêê |
êêê |
êêê (mainly
residents) |
38 |
8 |
|
Santavea
Rd Canals |
êêê |
êêê (good
variable rock rip rap, 30cm soft mud) |
êêê? |
êê (potential
for seagrass?) |
êêê |
êêêê |
êêêê |
êêê |
êêê |
êêê |
êêê (mainly
residents) |
35 |
9 |
|
Cambria
Is Canals |
êêê |
êêê |
êêê? |
êê |
êê |
êêê |
êêêê |
êêê |
êêê |
êêê |
êêê (mainly
residents) |
32 |
10 |
|
Waterside Canals |
êêê |
êêê |
êêê? |
êê |
êê |
êêê |
êêêê |
êêê |
êêê |
êêê |
êêê (mainly
residents) |
32 |
10 |
|
Yanderup
Canals |
êê (estuarine,
tannin rich, turbid) |
êêê |
êêê? |
êê |
êêê |
êêê |
êêêê |
êêê |
êêê |
êêê |
êêê (mainly
residents) |
32 |
10 |
From this ranking, the sites that fall within the top three are:
1. Mandurah Ocean Marina and Hall Park Public Swim area.
2. Port Bouvard – Northport, and Port Mandurah – Mariners Cove.
3. Port Mandurah – Leeward.
This system of ranking the sites has limitations just as any system does. It is however a useful starting point and encourages discussion and analysis of the sites. It is also provides a useful summary of the merits of each site, which the Steering Committee or other groups can take into consideration and perhaps narrow down. For example, a group or Council could choose to select the sites only on their ability to attract maximum diversity, or closeness to natural wetland areas.
The following points should be considered regarding the ranking of sites.
§ Assessing the sites required a level of judgement based on experience of similar areas, and the information gained during the short time available for the site visit. Therefore the rankings are a starting point and a guide only, and should not be considered to be absolute and final, or a mandate that the PHCC can not choose to prioritise other sites. Comments from the PHCC are welcome.
§ At the end of the day, it will be the decision of the groups involved as to which areas are enhanced first.
§ Available funding and its source, eg sponsorship, will also play a role in dictating where efforts are directed.
§ The rankings should NOT be taken to mean that the lower ranked areas are not worth attention. It is likely that residents or other groups could have different objectives than those represented by the attributes used in this ranking system, therefore lower ranked areas could become higher priorities.
§ The rankings have no weightings attached to the different attributes, therefore all attributes are considered to be of equal importance. The PHCC may wish to add weightings if necessary to help internal decision making.
§ The success of each program at each site, and the ability for each site to achieve the ranking it has been given is very much dependent upon the effort put into it. For example, one of the reasons the No. 1 ranked site the Ocean Marina (and proposed Dolphin Quay) is a leading site is because of its close vicinity to Mandurah, its public access and significant potential to use the enhancement for public display/education. However, if this aspect is not utilised or utilised fully, then the value of the site is decreased.
§ The rankings can be extrapolated to cover the other canals within the same development as the site surveyed, ie the rankings for Santavea Rd canal could be used for other canals nearby. However, prior to deployment some investigations of factors such as canal floor should be made.
1.2.1 Ranking by Cost
Cost was separated from the main ranking table because it is highly variable. For example one site may only require a few modules, however a canal estate could utilise hundreds. Cost was included however to provide an indication of the relative approximate cost of initiating a reasonable level of enhancement at each site. The costs are relative to the specific area, therefore the lowest and simplest enhancement option is used as a benchmark for the others. Costs also take into account expenses such as transport of modules to site, deployment, promotion, permits, signage, and additional design studies. Details of enhancement strategies for the top sites are provided in Section Error! Reference source not found..
Table 3 Approximate
enhancement cost to initiate enhancement.
ê = very low, êê= low, êêê = medium, êêêê = high, êêêêê = very high cost
|
Site |
Cost |
|
Ocean
Marina (incl proposed Dolphin Quay) |
êêê |
|
Cambria
Is |
êê |
|
Santavea
Rd |
êê |
|
Mariners
Cove (Sales Office + marina) |
êê |
|
Leeward |
êê |
|
Waterside Canals |
êê |
|
Performing
Arts Complex boardwalk (u/w lighting could add an ongoing cost) |
êê |
|
Hall
Park Public Swim area |
ê |
|
Soldiers
Cove |
êê |
|
Mandurah
Quays |
êê |
|
Yanderup
Canals |
êê |
|
Northport |
êêê |
|
Eastport |
êê |
|
Eastport
Marina |
êêê |
The least expensive option is the Hall Park Public Swim area. This site only requires several modules and has minimal transport and deployment difficulties. This is discussed further in Section Error! Reference source not found..
The most expensive sites are the Ocean Marina, Northport, and Eastport. This relates to the number of modules that would be used, time to position and deploy them, signage for public education, school programs that may participate, monitoring costs, and distance of transport of modules to actual deployment location.
Obviously some expenses are not actual costs as some resources will be donated.