Blog Post 6

I have sampled twelve replicates. There have been a few issues with collecting data, such as implementing the sampling strategy, systematic sampling. When sampling, there was two instances in which I had to turn around and find another spot to continue, unless I wanted to fall down a cliff. Another issue I have run into is that the past two months, there has been quite a bit of precipitation. This has made it difficult to obtain soil samples that are not uncharacteristically wet.

While collecting my data, I noted that the distribution of sagebrush on hill tops is approximately what I expected. However, there was one quadrant in the valleys where there were more sagebrush than expected.

Blog 6

Materials used in data collection include, 300m measuring tape for transect line and quadrant marking; as well as measuring distance from center of quadrant to species and DBH. Field journal and pencil ( not pen because ink has begun to freeze while writing due to cold temperatures). A compass to ensure my transect line ran from North to South. Activities have included me walking the randomly generated step to transect point in each substrate area. I then will walk the randomly generated steps between quadrants marking the area with bright green tennis balls ( they stand out well against the small amount of snow) Species distances and DBH are measured and recorded in field journal.

So far I have collected 10 replicates on bedrock, and 10 replicates amongst soil substrate. I have found my experimental design and methods easy to carry out without too many problems. The only difficulty I have found is trying to walk through thick brush with measuring tape , trying to keep line as straight as possible.  I have noticed that along with jack pine frequency being more common on bedrock, the species also appears to be distributed heavily in higher elevations then the rest of the forest canopy. It seems as though jack pines have adapted away from the boreal canopy, thus away from species competition. I still expect to see relative frequency and distribution higher amongst bedrock though the variable of elevation may be contributing to this bedrock preference. That or the high drainage of bedrock with low soil and water content may have determining factors for Jack pine abundance.

Blog Post 6: Data Collection

I went out and sampled 5 plots of 1m x 1m each at my site.  I did not have any problems implementing my sample design.  I did notice that the less grass there was the more thistle there was.  The taller the grasses were the less there was of thistle.  And in plots that did not have a lot of grasses there appeared to be significantly more amounts of thistle present.  This goes well with my hypothesis.

Post 6: Data Collection

Since originally making my hypothesis and making my data collections, I have decided to revise my sampling method slightly: Since I am measuring fallen leaves, there is no way to guarantee the leaves beneath a given tree were grown on that particular plant. Giving more observation to the distribution of leaves on the ground, I shouldn’t be able to make the claim of tree origin with any confidence, so I am going to instead group sampled leaves to a “habitat area.” The aggregation of the data means that I would not be able to look for associations in the data between leaf length and individual tree. However, the integrity of the data is preserved for the purpose of comparing variance within and between and groups (ANOVA), except that there is an increased risk of a Type II error. (Which is better than a Type I error, in my opinion).

I have thus sampled trees within each of two different habitat areas (one near the construction site and roadway; the other farther away) on three separate occasions. In total, 80 leaf length samples were taken from each habitat area over the data collection period.

Blog Post 6: Data Collection

Throughout this module I needed to get 3 replicate samples completed. I’m collecting a total of 15 replicates (5 from initial data) and either 3 or 4 replicates per module. I haven’t had any problems with implementing my sampling design so far… I will continue to go to my point count stations in the morning when it is nice and cool and I will record the amount of times I see a bird using the area. This no longer takes into account any birds that fly by or and bird calls since they are not technically using the area. I think this will give me more accurate data. So, because of this decision, only part of my data from the first 5 initial observations I recorded is valid and, therefore, I will only be being using half of the data. I will return to all my 5 point count stations in the same order that I did the first time and I’ll continue the process of returning to these stations one at a time over multiple days… This also gives me extra time to complete other parts of this module. So, on Aug 20th I returned to my first point count station. This station is the station with no shelter, this is the lawn area station. It was 15 degrees Celsius, however, there was a layer of smoke blanketing the area. I only saw 1 bird using the area during the whole 10 minutes… I have a feeling this is due to the smoke. I don’t know how long the smoke will stick around and I’m curious if the smoke might skew my observations; however, I can’t wait forever for it to go away and I will just have to take this into account when I am analysing the data. I then returned to my second station a couple days later on Aug 22nd . It was 16 degrees and the thick layer of smoke was still glomming above. The second count station is the intermediate station with half shelter and multiple bird feeders within the area.  Even with the thick smoke I saw 3 birds use the area. The next day, Aug 23rd  ,  I went to visit the third count station. There was no smoke!!! I was a nice morning with clear skies and it was 15 degrees Celsius.  This station is the one right in the middle of the forest with lots of shelter. Here I recorded 3 birds using this station. I will visit the rest of the stations sometime throughout the next couple of days and be finished up by module 8. From the data, I have recorded I am starting to see more of what I was expecting. I did in fact more birds in areas with more shelter than in areas of low to intermediate shelter. I will be very interested when analysing my final data to see if the smoke did in fact have any real affect, but hopefully it will be gone for good now.

Data Collection

I completed my field data collection over the span of two days from 12:00-14:00 at Creekside Park. Throughout the past month, I have been visiting the site and thinking about my research project, notably the hypothesis and study design. My original hypothesis, “the abundance of bees increase around vibrant colourful flowers and decrease surrounding pale white flowers”,  had some subjective terminology that needed clarification. The words ‘vibrant’, ’abundance’ and ‘pale had to either be removed or changed into an objective form. I switched ‘abundance’ with ‘number’, and removed ‘pale’ and ‘vibrant’. I ended up changing my hypothesis to “the number of bees increase around colourful flowers (purple, red, and yellow), and decrease around white flowers”.

I used a random sampling technique to look at  bees around 10 flower samples in the park. I have not experienced many problems with the implementation of my study. The accuracy of my study has improved by implementing my sampling on weekdays, a time frame where their are less people to disturb the bees and flowers.

Blog Post 6: Data Collection

Data Collection Date: 07.08.18

Using the Alfred Howe Greenway trail as a marker, soil samples were collected from the east and west divisions of the forested land spanning away from the trail, with soil samples taken throughout the entire length of the trail, while allowing them to be subdivided into two general areas: (1) Historically Forested Area (South part of trail) and (2) Historically Landfill Area (North part of trail).

 Photo 1: L2S3 (Location 2, Sample 2) collected soil sample (left). Soil sample collection in progress, ruler measuring depth of dug hole (4.0 inches) and soil collected (3 shovel scoops) at hole depth (right).

The exact location of where the former landfill ends was unclear. However, buried tarp was found at the mid-point of the trail, buried in the direction of the former landfill area. Reading through government archives, there was mention of eliminating water pollution through having the area covered in a landfill cover, preventing rainfall from dislodging any buried landfill materials, limiting pollution entering nearby bodies of water in the form of runoff.

Photo 2: Observations made while sampling, would be interesting to follow the visible tarp to see if it encloses the landfill area.

A total of twenty soil samples were collected; ten for each designated area. A modified random sampling strategy was used from the one implemented in Blog Post 5. This was primarily done to ensure samples were taken in their desired transect, which was one of the problems faced when using the previous sampling strategy.

The new sampling design consists of generating: (1) a random number of paces along the trail (0 to location end), (2) generating a random East or West side of trail designation (0 to 1) and (3) generating a random number of paces 90º from the trail (0 to 50).

Once three random numbers were generated for each sample, samples were numbered in order of the number of paces taken along the trail, in order to allow samples to be taken while proceeding from the north point of the trail to the south point, avoiding going back to the start of the trail for each sample to count the number of required paces along the trail for that sample.

Photo 3: Scanned field journal entry of randomly generated location of each sample. L2S1 – L2S10 correspond to samples taken off the north end of the trail (former landfill), L1S1 – L1S10 correspond to samples taken off the south end of the trail (historically forested).

There were less problems encountered in implementing this experimental design. If a randomly generated location was unaccessible (ex. extremely dense in vegetation or a very steep slope), the nearest accessible location was used to collect the soil sample.

Photo 4: Collected soil samples from both locations.

When collecting the soil samples, there was a very noticeable difference in soil colour and texture between samples collected from the former landfill area and samples collected from the historically forested area, as well as between samples collected from the East and West side of the trail.

It is interesting to be able to visually observe the soil differences in each area, making it appear that former landfill activities could have a long lasting impact on the surrounding area. However, these samples must undergo soil testing to formally analyse any soil discrepancies.

Photo 5: Visual difference in soil colour and texture between soil sample collected at the historically forested area of the trail (left), and soil sample collected at the former landfill area (right).

Enough soil (three shovel scoops) was collected for each sample in order to ensure there was enough soil to undergo pH, nitrogen, phosphorus, and potash testing using the Rapitest 1601 Soil Test Kit.


Please note: A portion of the collected soil sample testing results (including recorded topsoil nitrogen levels and soil type classification) are presented in Blog Post 8: Tables and Graphs.

 

Blog Post 6: Data Collection

Hi Class & Professor Elliot,

This past long weekend I finished my field data collection at Coldham Regional Park. I set out early in the morning to beat the summer heat and it took me around 3.5 hours to finish collecting samples.

Coldham Regional Park

Over the past two months I have been regularly thinking about my study design and hypothesis, which I have had to revise several times. From the start, my sample design seemed sound and I did not run into any problems implementing the sampling design on the ground (other than trying to cross the creek!). I took 40 replicate samples over an area of 60m by 50m, divided into four transects, to accurately capture the riparian area either side of Jack Creek.

View of Study Area – Looking East

My prediction was that there would be a greater abundance of large woody vegetation on the eastern side of the creek that has a westerly facing slope. It was interesting during field data collection, I noticed more of a pattern that in the flatter areas on the west side of the creek there was indeed greater abundance of large woody vegetation, however, as the hillside became steeper there was typically less vegetation overall.

View of Jack Creek – Facing South

Another interesting pattern that I wasn’t expecting was the number of spruce trees. I had originally thought there would be greater diversity in the species of trees (e.g. pine, spruce, maple). But during data collection, spruce trees were clearly the most abundant species. Another note was that there were several standing dead spruce trees on the western side of the creek (that gets more sunlight), and healthy, taller spruce trees on the eastern side of the creek.

Spruce Stand – Eastern Side of Jack Creek

Reflecting on my hypothesis, I am interested to see what sort of correlations I can find and other explanations during theoretical research.

Thanks for reading.

-Brittany Lange

Blog Post 6 for Katarina Duke

On average 20-25 flow measurements were taken within each creek to determine the flow discharge with 5 discharge measurements obtained per creek for a total of 25 discharge measurements. No issues occurred in implementing the sample design due to the resources available; the SonoTek Flow Tracker 2 helps eliminates sampling issues by providing quality control errors for flow measurements taken within the creek to help prevent flow measurement errors form compounding onto the discharge measurement.

Preparation for data collection was minimal as the only supplies needed in the field was a journal, SonoTek Flow Tracker 2, and spare batteries. I was not required to make tables prior to arriving in the field as the SonoTek Flow Tracker 2 stores all data that can then be downloaded onto a computer.

It has been observed that despite all the creeks being hydraulically connected to the Miracle Valley aquifer the drops in flow rate into low season of each of the creeks did not happen at the same rate. This allows me to infer that the creeks are hydraulically connected to the aquifer to varying degrees.
I also observed the presence of a fish farm in the area, west of Belcharton Creek before its confluence with Lagace Creek This did raise concerns that the algal growth observed within the creeks could be a result of excess nutrients from the farms; however, algal growth was more prominent in Seux Brook that is not within proximity of potential discharge from the fish farm. Also, since no algal growth was observed in Lagace Creek my concerns were absolved since Belcharton is a tributary of Lagace Creek.

Blog Post 6

My field data collection was ultimately collected as a “snapshot” of the site on one day.  I had been planning to collect data on multiple days over a period of weeks, however, it should be unnecessary to collect repeat information in such a short time span.  Increased sampling could also introduce confounding factors, such as counting invertebrates more than once and skewing the data to show greater abundance and diversity when there is none.

I sampled two sites, with each site consisting of three transects.  Because the study area was small, it was possible to sample the entire site with 100% coverage.  Introducing randomization for the sake of randomization in this case would have introduced unnecessary rates of error into my study.  This type of sample design was relatively easy to implement.  My only concern was in counting mobile species more than once.  Luckily, when I did encounter highly mobile species, I was able to keep an eye on them to reduce the error of counting species twice.  In a larger site, it could be beneficial to introduce smaller plot sizes and randomization to avoid counting highly mobile species more than once.

I have noticed a greater diversity of invertebrates in the native plant garden setting, which I expected, but I did not notice a greater abundance of invertebrates, which is something I had expected to observe.  Finding a small colony of ants in the turf lawn setting could account for this discrepancy as their numbers could artificially skew the data.