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 3: Ongoing Field Observations

I have decided to observe the three sites described in blog post 1 on Thompson Rivers University (TRU) campus. I plan to study how bird species differ across the different sites on TRU campus depending on the topography and vegetation of each site. I will be observing the three different sites and recording the bird species that are present. It can then be determined how the bird species distribute and their approximate abundance throughout the TRU campus.

Here is a copy of the sample data retrieved on March 21. It outlines the various bird species observed at each site

I predict that bird species will distribute differently throughout the TRU campus. Based on this prediction I then hypothesize that each site of study on TRU campus will have a different dominant bird species that is associated with that area. The species abundance at each site can then be utilized to determine the dominant species.

In this study, the bird species will be the response variable and the site of study will then be the explanatory variable. The response variable (particular bird species) will then be a result of the area of observation (explanatory variable). This data is considered to be categorical or discrete.

 

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

 

Blog 5: Design Reflections

Initial date collected went over all as predicted. On average the partly sheltered trees had amount a 50 50 ratio of living and dead moss growing on the tree trunks. The 5 trees observed were selected by simple random technique and locations were easy to find. In total took about 30 minutes. Will continue to use the simple random technique when observing 10 trees each from the 3 categories (sheltered, partially sheltered, and exposed).

(Exposed trees are trees that have very littler branches covering the trunk of the tree to the weather at the park)

Post 9: Field Research Reflections

I had a limited amount of time to carry out my field research project as I travelled a long way to the beach for only a day. There were of course various other reasons, one of them being that I’m starting a full time job thus I would like to finish my studies as soon as possible with concentration before starting work and I’m recently married. Marriage comes with a lot of responsibilities. I had done my fair bit of research before I even went to the beach to do any measurements and I had been thinking about a research topic for a very long time. I recently went to Morocco for my honeymoon and collected some sea shells as a souvenir. I was looking at the various sea shell sizes at home and was questioning the reason behind the varying sizes, so I thought I’d do a sea shell size related topic. I then went online and did some research as to what is involved in measurements at the beach.

In my opinion the most challenging part of this research project was figuring out a topic to base my research on. Once I had a topic in mind the rest was straightforward. Although I found similar research studies to mine online, I have gained a lot of appreciation for how ecological theory is developed. It is only after completing my own research project that I understood the amount of effort that goes into developing the theory and experimental design. It is also very necessary to have the right equipment for the research project. Sometimes what seems like a very simple study comes with a lot of complications.

Post 8: Tables and Graphs

I found it quite simple to organize and summarize my data as the results of my field data were not so complicated. I resorted to a table to display the length and aperture measurements on both Castle beach and Jetty beach. I also made a separate column for the length to aperture ratio for both beaches. Upon calculating all the ratios, I totalled the ratios for the exposed and sheltered shores and took a mean. One of my results at Castle beach was anomalous (n=8) since it had a large variance from the mean value of 1.58. Therefore, it does not fit the remaining values and I did not use it in my calculation. The lengths of the dog whelks are generally smaller and the aperture is larger at Castle beach, giving a smaller ratio. For instance, the highest value for the length to aperture ratio at Castle beach was 1.74 while the highest value at Jetty beach was 2.04. Similarly, the lowest value for the length to aperture ratio at Castle beach was 1.37, whereas the lowest value at Jetty beach was 1.42.

An interesting investigation involving dog whelks may be comparing the genetics of dog whelks on exposed and sheltered shores and trying to explain what differences in the genetic makeup cause the variation in shell size on the shores. This study can involve more shores and replicates. However, varying abiotic and biotic factors such as weather and predators may cause discrepancies in the results.

Post 7: Theoretical Perspectives

The theoretical basis of my research project examines how rocky shore exposure to wave action at Jetty beach and Castle beach, Pembrokeshire, affects the length to aperture ratio of dog whelks at 4 metres above chart datum. The factors affecting the desiccation of dog whelks are temperature, relative humidity, wind speed and light intensity. These abiotic factors may cause the dog whelks to migrate up or down the shore depending on the varying conditions. Predation and feeding are definitely biotic factors affecting dog whelks. Crabs and birds are common predators and thicker and longer shells provide protection against crabs on sheltered shores. The reason dog whelks stay on the lower shore relative to the upper shore may be for protection against birds so they may not be seen.

Apart from the environmental factors affecting the dog whelks’ shells, genetic factors may also affect the shape of their shells. Human activity may also disrupt the species habitat. Crothers explains that dog whelks spend hours on top of their feed in order to digest it, therefore I returned them to their original spot to minimize disruption to their feeding cycle when I was measuring their shells.

Keywords: Dog-whelks, shell size, exposure

Post 6: Data Collection

I have recorded 30 replicates on each beach for a total of 60 replicates. I measured the length and aperture of the dog whelks and calculated a ratio to help me compare the results for both beaches. I took each measurement with a Vernier caliper and measured the height of the shore above chart datum using a clinometer and a meter ruler. I took each measurement at random along a 20 m transect and recorded the results.

I had to finish taking my measurements before the tide rose up too high. I didn’t have a hard time implementing the sample design. Plus I gave myself plenty of time to record my results from Jetty beach to Castle beach.

I noticed an ancillary pattern that the length to aperture ratio of the dog whelks at Castle beach is generally smaller compared to Jetty beach. The pattern supports my hypothesis and prediction which stated that the exposure to wave action influences the length to aperture ratio of dog whelks thus the length to aperture ratio will be smaller in the exposed beach.

 

Post 5: Design Reflections

For my preliminary investigations I surveyed both Castle beach and Jetty beach to see at which height dog whelks were most abundant. At Jetty beach I noticed that the dog whelks were mainly present on the middle shore. From my research I knew that the tide at 11:30 AM was 2.07 m above chart datum. Therefore, I measured the height to the middle shore at 4 m above chart datum by using a clinometer and a meter ruler. I stood at 2.07 m above chart datum and held the clinometer perpendicular to the meter ruler and measured 1 m above chart datum. With the help of my husband I marked the point at 3.07 m above chart datum and then I measured 0.93 m the same way as mentioned up to the area where there was an abundance of dog whelks. I initially planned to lay out a 15 m transect line, however I changed this to 20 m instead so the results are more representative of the shore. At 4 m above chart datum I laid out a 20 m transect line and took my measurements. I repeated the process at Castle beach. In order to measure the length and aperture of the dog whelks I did try to use a 30 cm ruler at first but I found that the Vernier caliper provided more precision and accuracy.

The data that I collected suggests that the length to aperture ratio of the dog whelks at Castle beach is generally smaller compared to Jetty beach. This so far supports my hypothesis. I plan to continue collecting data using the same technique and I will definitely use a Vernier caliper instead of a 30 cm ruler for more precision and accuracy of the measurements.

Post 4: Sampling Strategies

In the virtual forest tutorial I used the area based sampling method for all three sampling strategies. The technique from the fastest estimated sampling time to the slowest estimated sampling time was systematic sampling technique at 12 hours and 7 minutes, haphazard at 12 hours and 27 minutes and random sampling at 12 hours and 47 minutes. The 2 most common species in the Snyder-Middleswarth Natural Area were Eastern Hemlock and Red Maple. The 2 rarest species were Striped Maple and White Pine. The percentage error for Eastern Hemlock for systematic, random and haphazard sampling were respectively: 3.34%, 4.23%, and 8.17%. The percentage error for Red Maple for systematic, random and haphazard sampling were respectively: 5.38%, 40.45%, and 19.42%. The percentage error for Striped Maple for systematic, random and haphazard sampling were respectively: 90.29%, 18.86%, and 28.57%. The percentage error for White Pine for systematic, random and haphazard sampling were respectively: 100%, 50% and 296.42%. The accuracy changed with species abundance. For the two most common species the sampling strategy that was more accurate was systematic. For the two rarest species the sampling strategy that was more accurate was random sampling. The accuracy declined for rare species. The large percentage error may be because 24 was not a sufficient number of sample points to capture the number of species in this community or to accurately estimate the abundance of these species.