Blog Post 1 Observations – 777 Oliver St. Oak Bay, B.C.

Location:

The area chosen for study is located at 777 Oliver St. in Oak Bay, British Columbia. The area contains 3 closely linked micro ecosystems that are situated in an urban residential environment.
Oak Bay is in the Coastal Douglas fir biogeoclimatic zone. This zone is the most at risk zone in BC and it has the highest concentration of rare and endangered species in Canada (District of Oak Bay, 2014).
The first site visit occurred on the first day of spring (March 20, 2018) at approximately 1:00 pm. It was mostly sunny with a temperature of 10 degrees and light wind.

 

Site Details:

Two study area ecosystems are located in the front of the property. The rear study area is separated by the two in the front by a residential home. 
The study areas at the front of the property are West facing and end at the city street, which has a low volume of traffic. The total area of both is approximately 7 metres long by 11 metres wide, with each being about equal in size. 
This area is roughly split in half by a pathway that separates a predominately native plant garden from a typical grass lawn. The garden contains approximately 38 native and 9 non native plants, trees, and shrubs. Additional plants are assumed to be present below ground in a dormant stage. Both sides are contained by asphalt driveways.

Front yard – Both sites March 20

 

Front yard native plants March 20

 

Front non-native grass March 20

The rear of the property is East facing and is approximately 14 metres wide by 24 metres long. It is primarily moss covered, with some remnant occurrences of non-native grass in the central location. One large Garry Oak tree is present, which dominates the area by crown cover. The moss/grass is contained by a small buffer on 3 sides consisting of spruce, birch, cedar, plum, ash (sapling to immature size) and low shrubs of wild rose, snowberry and others that appear to be non-native. The remaining side is contained by the rear of the house and a cement pad.

Back yard entire site March 20

 

Back yard North facing hedge March 20

 

Back yard South facing hedge March 20

The overall topography of the entire site is flat, with a gentle slope of < 1 metre from the front of the property to the back. Early signs of leaf development on some trees and shrubs was present, while the remainder of species appeared to be dormant.

 

Field notes March 20 (rough guide for location and tally of species)

Purpose:

I am interested to see if there is any advantage to wildlife in an urban garden setting that is dominated with native plants. Two possible controls exist, with one being adjacent to the primarily native garden, which is a typical lawn ecosystem that is typical in the neighbourhood. A further control exists in the back yard, which is also fairly typical for the neighbourhood except that it is bordered on 3 sides by a large number of native plants and trees.
One concern is that the ecosystem in the back yard (containing roughly 20% native plant/tree cover compared to roughly 85% native plant cover in the front yard) will be over-represented with visits from wildlife or insects because it is not influenced by the pedestrian or vehicle traffic that the front yard receives.

A possible question to consider is the scale of the primarily native plant garden, which is quite small in comparison to the total property size. It is possible that it is too small and sub-optimally located for any measurable effect on wildlife or insects.

Aside from wildlife, including birds, it may be more suitable to focus the study on the activity of insects alone, which may be less affected by the location of the native plant garden. However, there have been previous wildlife observations that suggest it may be possible to observe wildlife visiting various parts of the property.

A possible complication is the seasonality. With the start of spring, it could be that more wildlife or insects appear throughout the study area and duration due to the changing season alone. It is my hope that the control of a non native grass lawn area adjacent to the primary interest of study -the native plant garden- will be sufficient to determine if the native plants are attracting more wildlife or insects.

I am also interested to see if the native plants self-reproduce and increase in abundance or if the non-native species reproduce and encroach on the native plant garden.

Reason for interest in the study / Possible outcome

When I bought my house, I dug up the front lawn and planted mostly native plants, except where a couple of existing ornamental plants/trees were established because it was my intention to increase habitat for local wildlife.

My current intention is to do the same to the remaining land on the property.  The removal of non-native species is a future consideration.

I am interested to know if there is any measurable effect on having a native plant garden at this current size and condition, which is less than 2 years old. A previous study that is related showed that insect activity was not increased by small scale additions of native plants and that they in fact preferred non-native plants (Matteson, K. C., 2011).

Having a similar study area, I am curious to see if there is a similar effect in the region where I am located, which is different from the study area that Matteson looked at.  If there are significant observations that wildlife or insects prefer the non-native species which are present, I would consider keeping them for that value and re-cosnider an all native plant garden for the rest of the property.

References:

District of Oak Bay, 2014. District of Oak Bay Official Community Plan. Retrieved from: [https://www.oakbay.ca/sites/default/files/ocp/2014/OakBay-OCP-Final-Website-dec0414.pdf]on March 21, 2018.

MATTESON, K. C., & LANGELLOTTO, G. A. (2011). Small scale additions of native plants fail to increase beneficial insect richness in urban gardens. Insect Conservation and Diversity, 4(2), 89-98. 10.1111/j.1752-4598.2010.00103.x

Blog Post 1: Observations Revised

I have decided to revise my original Observations Blog Post as my final project has changed. After much thought of the different ecological areas in Kamloops, I decided to observe three distinct areas on the Thompson Rivers University (TRU) campus. Each of these areas are slightly different with the first one being a small wooded area, the second being an open grassland with a few ornamental trees lining the area and the last being a garden with high densities of various flowers, trees, shrubs and wildlife. I visited each site on March 21, 2018 at 10:30am in which the weather was slightly overcast with a breeze. I spent thirty minutes at each site observing their various attributes. Each site visited on the TRU campus had different organisms that gravitated to that specific site. This had me wondering why are the specific organisms, especially birds, attracted to particular sites? I also noticed that the weather was slightly different at each site. It’s important to understand that the weather changes were rather minimal, however, one site was more windy than the other two or one site would receive more sunshine than the other two sites. This had me wondering if the minor weather changes played a role in determining which species preferred which site? Lastly, even though all of the sites were on the TRU campus I noticed how they significantly differed in their landscape. This had me wondering how does this occur? Each site I looked at were all within a 5 minute walk of each other so how does the landscape vary to such a degree within a confined space. Furthermore, due to each site having its own distinct features does that determine which organisms are able to thrive better in one area compared to another?

Below are visual representations of each sited observed within the TRU campus:

Site 1
Site 2
Site 3

 

Post 1: Observations

The study sites that I have chosen for this research project are two rocky shores in Pembrokeshire, United Kingdom: Castle beach and Jetty beach. The beaches are in close proximity to one another and they are roughly a ten-minute walk apart. Each study area is approximately 0.6 metres by 15 metres. Castle beach is an exposed shore whereas Jetty beach is a sheltered shore. Castle beach consists of lower biodiversity compared to Jetty beach. It is Jetty beach has an abundance of animal and plant species. The vegetation at Jetty beach is composed of mainly seaweeds and lichens. Both beaches consist of a fair number of dog whelks. Dog whelks are also known as rock snails. The weather at the beaches in winter was sunny but cold. The temperature was about 10 °C. The beaches were visited on February 17, 2018 at 10:30 AM.

Three questions that are interesting or striking and could form the subject of my research project are:

  • How do edaphic characteristics affect the dog whelks’ abundance on Castle beach and Jetty beach?
  • How does rocky shore exposure to the tide at Castle beach and Jetty beach affect the size of dog whelks?
  • Does the sheltered shore consist of more soil nutrients than the exposed shore thereby supporting more biodiversity?

Castle beach

Jetty beach

Cultus Lake – Initial Observations

January 26, 2018
12:30 – 13:15
Weather: 5°C and overcast; rain earlier in the day

I have chosen Cultus Lake as my research site. It is 6.3 km2 with a maximum depth of 44 m. The lake basin is bound by International Ridge to the east, Vedder Mountain to the west, the agricultural lands of the Columbia Valley to the south, and a heavily used recreational beach to the north. The mountains around Cultus Lake are forested with mostly coniferous trees and patches of regenerating deciduous trees. The vegetation at the north end of the lake is maintained with almost no understory and only select mature coniferous trees remaining. Portions of Cultus Lake are within a Provincial Park. The park areas are largely occupied by campgrounds.  The lake attracts between 1 and 3 million tourist visits per year. The lake is subject to anthropogenic nutrient loading from agricultural activities and septic leaching.  It is home to two species at risk, the Cultus Pygmy Sculpin (Cottus aleuticus, Cultus population) and the Cultus population of sockeye salmon (Oncorhynchus nerka). The littoral areas of the lake have been invaded by invasive Eurasian milfoil (an aquatic plant). My questions are as follows:

  1. Is eutrophication of the lake leading to deep water oxygen depletion?
  2. Do fish, specifically the Cultus Pygmy Sculpin, favour portions of the lake that have higher concentrations of dissolved oxygen?
  3. If oxygen depletion does occur, does the lake fully recover during winter overturn?

 

Blog Post 1: Observations

Blog Post #1: Initial Observations of Study Area

Cameron Purdy – T00028679

January 31, 2018


Address:  33844 King Rd, Abbotsford, BC, V2S7M7

Coordinates: 49.0291° N, 122.2854° W. ~40m above sea level

Weather: Light rain showers, ~ 4ºC.

Seasonality: Winter

Time: 3:20PM


Description of Study Area:

The area(s) I have decided to observe are two separate ecological islands on the University of the Fraser Valley campus. Prior to UFV being built, the location was comprised of mainly farmland. Historically, the Fraser River had a much larger footprint and had floodplains that covered much of Abbotsford including areas surrounding UFV. 

Location A is a temperate deciduous forest with area (A=440m²). It is bordered to the north by the Abbotsford Entertainment and Sports Center, and surrounded by parking lots to the east, west, and south. The general topography of the forest is flat, however there is a slight slope coming down from the parking lot on the east most side. The most prevalent vegetation found includes Convallaria majalis, Oemleria cerasiformis, Maianthemum racemosum, and Trientalis borealis. Additionally, tree canopy cover in this forest is quite dense and filters out much of the sunlight. Few species of birds could be seen flying amongst the trees. 

From left to right:

  1. Forest A looking north from the south. Parking lot can be seen to east with the slight slope leading down into the forest.
  2. Forest A looking north from south. Parking lot can be seen to west, Abbotsford Entertainment Center can be seen at the north end of forest.
  3. Forest A looking north from south. Proposed transect line through middle of forest.

 

Location B is also a temperate deciduous forest with area (A=540m²). It is bordered by buildings and a walkway to the west and south, and grass fields to the north and east. Centrally located in the forest is a small pond (A~200m²) that is surrounded by marshy wetlands. The general topography is relatively flat, with a slight slope on the east most side of the forest. The pond situated within the forest collects water that runs off the slope, and has a small stream that exits the forest to the south. The most prevalent vegetation found includes Rubus spectabilis, Rubus idaeus, Oemleria cerasiformis. The tree canopy cover in this forest is less dense than that of location A. While no wildlife was seen, frogs could be heard from the pond. 

From left to right:

  1. Forest B looking north from south. Open grass field can be seen to east, ground slopes downward towards the west.
  2. Forest B looking north-east from south-west. Pond and marshy surrounding areas seen.
  3. Forest B looking south-west from north-east. Proposed transect line through middle of forest.

Follow up Questions: 

1) What leads to the difference in vegetation among the two forests. How could they have a significantly different prevalence of plant species when they are located so close to each other?

2) While we know the vegetation differs between the two sample forests. How does the fauna differ between the two. Is there a higher prevalence of specific invertebrates in one forest over the other?

3) What are the differences in soil composition? If there are differences, could these in fact be linked to the the prevalence of specific flora and fauna in their respective forests.

Blog post 1

I am choosing to do my field study in Mount Douglas Park, located in Victoria, B.C. I visited the park on February 6th, 2018, at around 12:30 pm. It was overcast, lightly raining at times, with a temperature of 8C. Mount Douglas Park is quite a large park, with an area of 188 hectares, and the summit reaches an elevation of 225 m (District of Saanich, 2018). From what I observed, the lower areas of the park are lightly rolling hills, with flat areas, and are covered in forest. The forest is predominantly douglas fir (Pseudotsuga menziesii) and there are a few big leaf maples (Acer macrophyllum). The understory is dominated by Oregon grape (Mahonia aquifolium), sword fern (Polystichum munitum), snowberry (Symphoricarpos albus), and Indian plum (Oemleria cerasiformis) which I identified when I got home. The top of Mount Douglas Park transitions into a more open, rocky ecosystem with garry oak (Quercus garryana) and arbutus (Arbutus menziesii) trees, with scotch broom (Cytisus scoparius) becoming prominent. Lichens tended to favour one side of the tree, which usually faced more open areas, but could be a NSEW preference. The Oregon grape leaves seemed to be smaller at the summit, and had a reddish hue.

The park is disturbed with a high presence of invasive species such as English holly (Ilex aquifolium) and English ivy (Hedera helix).

There are an infinite amount of possibilities here, but three areas that seem most feasible to explore are:

  1. The size of the Oregon grape leaves/plant is smaller in the open areas at the top of Mount Douglas, compared to the lower, closed forest.
  2. The green dust/or crust lichen prefers certain sides of trees, however the sides that the lichen prefers seems to vary in the park, therefore, is it a NSEW preference, or a light availability preference?
  3. Do the areas surrounding the heavily used trails have less species diversity (or more invasive species) than the less frequently used trails?

 

District of Saanich. (2018). Mount Douglas Park. Retrieved February 6, 2018 from: http://www.saanich.ca/EN/main/parks-recreation-culture/parks/parks-trails-amenities/signature-parks/mount-douglas-park.html

Post 1 – Initial Observations

The area that I have chosen to study is a field that runs along the Bow River in the South of Calgary, Alberta. The Pine Creek Wastewater Treatment Plant is located here. The green space next to it, and which runs a long ways along the Bow River, is used by dog walkers (of which I am one) and some owners as an offleash area for dogs to run in. It is not designated as an offleash area by the City of Calgary. The region of the pathway that I walk runs approximately 6 km total, and is on a ridge slightly above the Bow River. A more accurate distance measurement must be made. The Northern stretch of path is more heavily wooded, with many plants growing around the path and on the hills that border the West side of the path. There is a smaller, secondary path that wanders down towards the river and then back up to the meet the main pathway. Walking South from the parking lots, the path is at a higher elevation from the river, and a steep rocky embankment makes it harder to access the river. Northeast of the parking lots there is a main access point to the river.

 

I go to this area at least once a day during the week with my dogs, but it wasn’t until the end of January that I brought my journal along with me. There are still many natural elements in the park, and more possible subjects to explore than I initially thought, as I had previously only thought about the dogs I was walking. There are many different species of plants, and I have observed ducks, hawks, deer, and coyotes in the area.

 

I brought my field journal with me on January 30, 2018 at 1030 hours. The weather was excellent that day: sunny and 7℃ with only about 1 cm of snow still on the ground. This is quite warm for the end of January, but was thanks in part to a Chinook blowing in.

 

Three questions that came to mind were:

  • Are there species of plants that are found only along the river, and not in areas that are farther removed from the river?
  • There are many wolf-willows (Elaeagnus commutate) along the pathways. The ones that are nearest the path are under 3’ tall, while the ones that are along the secondary pathway are well over 6’. Is this due to the proximity, either distance or elevation, from the river?
  • Are the plants on the islands in the middle of the river the same as those along the pathway that I walk, or are they different? Is this due to lack of human activity, or increased presence of wildlife?

Post #1: observations

Post #1: Observations at Beacon Hill Park

 

I will be conducting my field research at Beacon Hill Park, a designated city park in Victoria, BC. When Victoria was settled in 1843, Beacon Hill park was a completely natural area. Beacon Hill Park was reserved as a park by the city of Victoria in 1858. Although some of the park has experienced human alterations through the planting of flower beds, construction of a water park and petting zoo, much of the park still features its natural ecosystem.  Most notably, the park protects a native Garry Oak ecosystem. The park features several ecosystems, including grasslands, forested areas and a man-made lake.  The highest elevation of the park is approximately 40m above sea level.

Date of observations: January 4 2018

Time of day: 4:15pm

Weather: 4˚C, wind 14km/h from the northeast. Clear skies. Sun was just about to set at 4:32pm.

Area of park: ~0.62 km2

Seasonality: winter

 

For my field study, I decided to select 3 locations to make observations. Each location features a different ecosystem.

Figure 1: Aerial map of Beacon Hill Park

 

Location 1: Forest near the “world’s tallest totem pole”

 

GPS coordinates:

48.408699, -123.358520

The forested area near the “world’s tallest totem pole” features a network of human footpaths through a forest of deciduous and coniferous trees. This location had the most-dense vegetation and the most evidence of decomposition.  Many plants surrounded the trees including bushes that had lost their leaves, brown, tall grasses and short green grass. One of the bushes had white berries, leading me to believe it was a snowberry (Symphoricarpos albus).  I found evidence of herbivory in dry, brown leaves that covered the forest floor.  One small bird was spotted during my observations. Lichen was present on tree trunks. Garbage from humans was also present.

 

Figure 2: Vegetation along footpath

 

Figure 3: Snowberry bush Symphoricarpos albus

 

Figure 4. Possible evidence of herbivory

 

Location 2: Top of Beacon Hill

 

GPS coordinates: 48.410488, -123.364813

 

The top of Beacon Hill has the highest elevation at the park, at 40m above sea level. The area includes an exposed, grassy region surrounded by what appeared to be Garry Oak (Quercus garryana) trees and arbutus (arbutus unedo) trees.   The trees were bare of leaves, but the shed leaves had accumulated on the ground below. Some trees retained brown, dry leaves and these leaves showed evidence of herbivory by an insect.  I noticed a Himalayan blackberry bush (Rubus armeniacus), which is a rampant invasive species all around Victoria.  Similar “wheat” looking grasses were observed to the grasses at location 1.  As well, the bush with the white “berries” (Symphoricarpos albus) was present.

 

Figure 5: Garry Oak

 

Figure 6: Arbutus tree

Location #3: Man-made stream ecosystem

 

GPS coordinates:

48.414201, -123.365927

 

The final location I will consider is a man-made stream ecosystem on the western edge of the park.  Although most of the plants here were likely planted by humans, this area had the most biodiverse foliage.  I observed the following vegetation:

-ferns

-coniferous tree with very soft needles. This tree was the tallest of the trees I observed anywhere in the park and had the widest diameter.

-deciduous tree

-leafy ground plant

-a large shrub close to the stream’s edge

-moss on rocks

 

Ducks were heard, but not seen.  The ground was covered in a brown “mulch”.  The stream flowed at a medium rate into a relatively large man-made lake.

 

 

Figure 7: Man-made stream

 

Figure 8: soft needles

 

Potential research questions:

 

  • What impact does elevation have on number of species, growth rate of vegetation and microclimate?
  • How do bird species respond to man-made structures, such as the man-made stream ecosystem, in comparison to natural wetland ecosystems?
  • Which location experiences the most insect herbivory and why?

 

 

Blog Post 1

Blog Post 1: Observations

Initial Observations of the Study Area by Randy Nguyen

November 2, 2017

The area of study that I have chosen to investigate is Stanley Park in Vancouver, B.C.

AddressVancouver, BC V6G 1Z4

Area4.049 km²

Coordinates: 49.3017° N, 123.1417° W

Weather: Clear Skies, 130C

Time and Date Visit Site: 1:25pm on November 2, 2017

Description of the study area:

This large public park borders the downtown of Vancouver in B.C and is entirely surrounded by waters of Vancouver Harbour and English Bay.  It also a very historical park which dates back during the 1858 Fraser Canyon Gold Rush and after years of colonization by the British, the land was later turned into Vancouver’s first park in 1886. The name “Stanley Park”, came from the 16th Earl of Derby, a British Politician who later became a governor general.

In present time, the park draws thousands of resident and visitors everyday and to take part in recreational activities in the area.  To name a few popular attractions in Stanley, people take part in biking and walking along Vancouver seawall, forest trails, and go visit the Vancouver Aquarium.

Wild Life in Stanley Park

Stanley Park has a diverse habitat ranging from coniferous forests to boggy wetlands to sandy beaches and to rocky shores. At least 500 species are known to live in the park and to name a few: Bald eagles, bats, beavers, squirrels, coyotes, harbour seals and racoons. For plants, we have a few invasive species such as Himalayan blackberry (Rubus discolor) and English holly (Ilex aquifolium). For native trees, we have conifers such as the western hemlock and western red cedar, and Douglas fir.

Deciduous

  • Bigleaf maple (natural regeneration)
  • Black cottonwood (natural regeneration)
  • Wild and choke cherry (natural regeneration)
  • Red alder (natural regen and planted)

Rare

  • Pacific yew
  • Cascara
  • Pacific dogwood
  • Arbutus (planted)

In recent news, the Vancouver park board is taking first steps to examine whether it would be feasible to one day reconnect Lost Lagoon with Coal Harbour to recreate a salt marsh.

http://vancouversun.com/news/local-news/vancouver-fresh-idea-to-turn-stanley-parks-lost-lagoon-salty-again

 

With ideas from the media and my observations of the park, I can devise 3 questions to narrow down my topic for the field research project:

  • Because humans are using the park recreationally, are there any possible risks to the conservations areas and the species living there?
  • How bad has the invasive species (i.e. Himalayan Blackberry) have put other native species of plants at risk?
  • If the Vancouver park board decides for some reason to turn the Lost Lagoon to a salt marsh, what potential impact can that cause on the current wild life habiting the Lost Lagoon?

Post 1.

Blog Post 1: Observations.

The area I have chosen is a piece of municipal-owned land in Sooke, British Columbia. It is a roughly rectangular piece of forested property approximately 150 meters by 300 meters surrounded on all sides by residential areas. There is a gated road from one street through the forest to the other end for use by maintenance vehicles to access a drinking water storage and pumping station. The lot is sloped with an elevation of 60 meters above sea level at the east end and 85 meters at the west. There is swampy terrain at the east which dries out just before the land slopes up. Red alders are the dominant tree at both ends with large western red cedar, western hemlock and Douglas fir in the middle section. Many animals inhabit this area part of the time. They include birds such as hummingbirds, robins, woodpeckers and owls. Herons had a colony here a few years ago but they have since moved on. Mammals that live here include squirrel, raccoon, black tailed deer and black bear. All of these animals are not permanent residents. They tend to pass through and use the area as a sort of shelter, but for the most part they not afraid of humans and roam the nearby streets, yards and other fragmented forest properties. The area does not see a lot of human activity. Maintenance crews drive in a couple of times a week and since their access lane is gated they are the only vehicle traffic. Occasionally neighbourhood kids play in here or cut across as a shortcut between blocks. Homeowners whose backyards border the property have encroached a few meters in with sheds and compost piles. This region sees only a few days of snow a year. The micro climate is so extreme that sometimes the higher elevation gets some snow and the lower end of the property does not. The past few years has seen fire bans from about May to October; it is so dry here that a few sparks would ignite the forest.

I visit this area all the time. My backyard borders it and I am often watching the deer and birds in here. In the spring a hummingbird built her tiny nest on a branch a meter from my childrens’ treehouse. We spent many mornings sitting on the little balcony watching the progress of her babies.

Some areas of personal interest that I may study:

  1. Many animals live in both the forest and the surrounding urban area. To what extent do they rely on the forest?

  2. There is a group of red alders growing in swampy ground. In the past few years they have begun slowly tilting but remaining seemingly healthy until they completely fall over. Why are they doing this now?

  3. There are a few specimens of “nurse logs”, dead wood that new plants grow on. Why do some stumps and logs host new trees and some don’t?