Blogpost 3: Ongoing field observations

The organism which I plan to study is the distribution of Spotted Knapweed, Centaurea biebersteinii.

The Knapweed plants have light purple flowers with thin and extending petals. The stalk is light-green, thin, and does not cover a lot of horizontal space. Each plant may have multiple flowers and stands 1 to 2 feet tall, generally speaking. The Knapweed plants seem to grow both in patches and also individually.

In each of the three stratum types, forested, forested with minimal/no cover, and open grassland, the physical features of each plant appeared similar. The distribution between areas is different, however. The Knapweed is virtually non-existent in the forested area; however, in areas of forest with no cover, Knapweed seems to grow in large patches as well as regularly by themselves. In the open grassland, Knapweed does not grow in patches, rather, it grows individually and often.

Processes that may play a part in this observed pattern could be access to sunlight, or competition with other species. Soil type is fairly uniform throughout this entire mountainside region, and precipitation is fairly rare in arid Kamloops this time of year.

Because of these observations, I hypothesize that Knapweed will grow more frequently in areas with more access to sunlight; if a stratum has more access to sunlight, then Knapweed will grow in greater frequency than in other stratums.

A response variable could be Knapweed frequency (continuous), or perhaps Knapweed density (continuous), and a explanatory variable could be access to sunlight (can be set up categorically or continuously).

Knapweed.

Blog Post 3: Ongoing Field Observations

The organism that I plan to study is the bullfrog (Lithobates catesbeianus) present at the Champlain Lake south wetland/swamp site chosen for observation. I had taken note that the stationary presence of a Lithobates catesbeianus in stagnant water appeared to be dependent on its location featuring sub-merged aquatic vegetation. None of the seven total observed Lithobates catesbeianus were present in an area of water that had no aquatic vegetation beneath the organism.

The three locations I have chosen to observe the organism of interest is the interior small channel flowing south, the main open body, and the lake mouth channel running into the wetland body (see photo for location references).

  1. Location 1: Interior small channel (south flowing)
    The water in the wetland had dropped approximately 1 foot, leaving the channel to be very shallow and featured minimal room for aquatic vegetation. The channel was very stagnant and I did not observe any bullfrogs (Lithobates catebeianus) present in this area. I assume their absence in this channel was due to low water levels causing restriction for travel along the channel.
  2. Location 2: Main Open Body
    The main open body of the wetland also had signs of lower water levels along the shoreline, exposing previously submerged rocks and some dried up aquatic vegetation. This location had the majority of Lithobates catebeianus present and featured ample aquatic vegetation beneath each organism. I noted in my field journal the surrounding areas lacking visible aquatic vegetation, also lacked the presence of a Lithobates catebeianus. The water was very stagnant in this location as well.
  3. Location 3: Lake Mouth Channel (running southbound into wetland body)
    The lake mouth channel had a few sections of submerged aquatic vegetation and featured one smaller Lithobates catebeianus on the interior side of the channel. This channel had slight/low flow entering southbound into the wetland body and I predict the lack of Lithobates catebeianus presence throughout the lake mouth channel location is due to minimal aquatic vegetation coverage and difference in water velocity.

I postulate that the presence of a stationary Lithobates catebeianus is dependent on ample (>50%) coverage of submerged aquatic vegetation beneath the organism. Based on the postulate hypothesis, one potential response variable could be the Lithobates catesbeianus and one potential explanatory variable being the percentage of submerged aquatic vegetation coverage. The response variable would be categorical in this case, being the presence/absence of the Lithobates catesbeianus, and the predictor variable would be continuous, being the percentage of aquatic vegetation coverage. I expect the Lithobates catebeianus is stationary in water with ample aquatic vegetation beneath the organism to evade other predators present in the wetland.

I had a few images to accompany this post, however, are too large to include.

Overview of the Locations discussed
The bullfrog present next to the dock. Only present in areas that featured submerged aquatic vegetation

 

Blog Post 3!

I plan to study the tidal pools at McNeil Bay in Victoria BC. The organisms that live in these pools are both biotic and abiotic. Examples are barnacles, fish, brown and green algae. The abundance of these organisms varies depending on the zones of the pool from high tide to low tide. The three locations I chose to observe the changes in were low tide, intermediate tide and high tide. Below is some notes that I recorded on the locations:

  1. Low tide: Greater biodiversity, the organisms here do not need to be well adapted to drying out and extreme temperatures. Organisms such as anemones, brown seaweed crabs and fish live here.
  2. Intermediate tide: At this point there is a mixture of both species in the low and high tide but mostly it looks like there are a few invertebrates (chiton) but lots of seaweed.
  3. High tide: Organism here have to survive drying out, currents and wave action. A larger abundance of barnacles, seaweed with only a few invertebrates can be observed.

These patterns could be due to the very different environments that they live in varying with elevation. I hypothesize that low tide zones will have greater abundance than high tide for (species) due to the less harsh conditions for it to live in. I predict larger biotic organisms are only in low tidal zones. Based on my hypothesis one potential response variable would be the total number of each species in the tidal pools which is categorical. A continuous variable would be the percentage of cover of each pool with seaweed. One explanatory (predictor) variable would be the unique environment the tide pool provides for the species. This variable would be categorical since there are 3 distinct locations of the pools.

I am not very good at drawing so I only sketched a few things but mostly I have chosen to take pictures and document my field observations all electronically.

Image from the CRD showing the intertidal zones.

 

3 intertidal zone sketches. Note Mid-High and Low Tide order.

Blog Post 3: Ongoing Field Observations

Between March 17 and June 2, 2019, I made 9 visits to my study area, totaling 14.75 hours of field observation and 188 data points with associated covariates; 159 of which were indicative of terrestrial vertebrates.  Where possible, photographs of wildlife or indicators of their presence were taken and stamped with UTM locations, or identified visually or by song.  I was using a cell phone camera and am a poor photographer so frequently I was unable to capture images of animals I observed.  I decided to end my investigations on June 2, given that a significant increase in observed industrial (e.g., water withdrawal and nearby industrial noise, scheduled changes to river flow regime), recreational (e.g., human presence and deposition of wildlife attractants) and transit activity (e.g., off-road vehicles, boating) which had the potential to affect wildlife activity in the direct vicinity of my study area.  This seemed a reasonable if not necessary place to end my field observations.

As I collected data over time (e.g., prior do, during and after spring freshet), the edges of the floodplain and riparian areas became clearly defined and the terrestrial vertebrate community structure within each emerged as evidenced by sightings, audible calls, observations of tracks, animal sign as well as active nests, dams and dens.  Despite the changing seasonal conditions, habitat use by certain species and classes of vertebrates remained relatively consistent in the riparian area and floodplain as well as in and above the open water.  For example, Tundra Swans were only observed in open-water on the Halfway River while Geese were observed everywhere but open-water on the Halfway river (i.e., floodplain, riparian area and open-water on the Peace River); dabbling ducks were only observed on open-water in the Peace River.   Western Toad tadpoles were only observed in pools on the floodplain while both grouse species I observed were in the riparian area.  All of the carnivorous species I observed were on the floodplain.

Given that my study location is at the confluence of a regulated and a non-regulated river, the Peace River and Halfway Rivers respectively, I was presented with a unique opportunity to examine how regulation of river level and discharge could be related to vertebrate habitat use and community structure.  Both rivers are influenced similarly at the confluence by local snow and ice melt, but only the Peace River is regulated by upstream hydroelectric infrastructure.  The area most affected by rising water level and flow rate or discharge is the floodplain, given large areas of it are inundated daily due to fluctuating river level.

Thus, the biological attribute I am interested in examining is vertebrate community structure in discrete areas (i.e., riparian, floodplain, and open-water areas) at the confluence of the Peace and Halfway Rivers.

My hypothesis is that short-term fluctuations in river level and/or discharge affect terrestrial vertebrate habitat use, and thus the community structure of riparian, floodplain and open-water areas of the Peace and Halfway Rivers deferentially.

If the community structure of terrestrial vertebrates is affected by short term fluctuations in river level and discharge, I predict that the species richness and diversity of the floodplain will fluctuate to a greater degree than the riparian and open-water areas relative to hydro metric conditions.

Response Variable: Species diversity; continuous

Explanatory Variable I: River level; continuous

Explanatory Variable II: Area; categorical

 

Note: UTM extraction is proving to take much longer than I had anticipated and will be included at a later time for anyone interested!

 

Date Time Time Spent Area UTM Temperature Precipitation Wind Species Observation Approximate Halfway  Level Approximate Halfway Discharge Approximate  Peace Level Approximate Peace Discharge
03/17/09 12:00-15:30 3.5 h Riparian 6C None Light; west Bald Eagle Nest 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Riparian 6C None Light; west Bank Swallow Nest 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Canada Goose Scat 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Canada Goose Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Peace 6C None Light; west Canada Goose Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Overhead 6C None Light; west Common Raven Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Coyote Tracks 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Moose Scat 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Riparian 6C None Light; west Mule Deer Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Mule Deer Scat 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Riparian 6C None Light; west Sharp-tail Grouse Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/17/09 12:00-15:30 3.5 h Floodplain 6C None Light; west Unknown Dabbling Duck Breeding Pair Visual 0.760 m 19.0 m3/s 2.56 m 860 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Canada Goose Scat 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Canada Goose Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Overhead 11C None Light; west Canada Goose Visual 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Peace 11C None Light; west Canada Goose Visual 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Common Raven Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Overhead 11C None Light; west Common Raven Visual 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Coyote Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Riparian 11C None Light; west Elk Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Mouse Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Mule Deer Scat 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Mule Deer Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Riparian 11C None Light; west Mule Deer Scat 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Peace 11C None Light; west Tundra Swans Visual 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/24/19 13:00-4:30 1.5 h Floodplain 11C None Light; west Wolf Tracks 0.795 m 21.0 m3/s 2.49 m 800 m3/s
03/31/19 12:30-14:30 2.0 h Floodplain 5C Light; rain Light; west Bald Eagle Visual 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Peace 5C Light; rain Light; west Canada Goose Visual 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Overhead 5C Light; rain Light; west Common Raven Visual 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Floodplain 5C Light; rain Light; west Coyote Tracks 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Floodplain 5C Light; rain Light; west Mule Deer Scat 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Riparian 5C Light; rain Light; west Mule Deer Scat 0.900 m 100.0 m3/s 2.49 m 890 m3/s
03/31/19 12:30-14:30 2.0 h Riparian 5C Light; rain Light; west Rabbit Visual 0.900 m 100.0 m3/s 2.49 m 890 m3/s
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Beaver Chewed trees 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Beaver Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Canada Goose Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Peace 8C Light; rain – Clearing Light; west Canada Goose Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Overhead 8C Light; rain – Clearing Light; west Canada Goose Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Riparian 8C Light; rain – Clearing Light; west Chickadee Singing 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Overhead 8C Light; rain – Clearing Light; west Common Raven Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Coyote Scat 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Coyote Tracks 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Floodplain 8C Light; rain – Clearing Light; west Muskrat Visual 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Riparian 8C Light; rain – Clearing Light; west Ruffed Grouse Drumming 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Riparian 8C Light; rain – Clearing Light; west Unknown Mammal Den 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/15/19 13:00-14:30 1.5 h Riparian 8C Light; rain – Clearing Light; west Unknown Wood Pecker Drumming 0.87 m 90.0 m3/s 2.37 m 650 m3/3
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Canada Goose Tracks 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Peace 11.5 None Moderate; West Canada Goose Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Overhead 11.5 None Moderate; West Common Raven Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Coyote Scat 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Coyote Tracks 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Peace 11.5 None Moderate; West Mallard (breeding pair) Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Moose Tracks 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Mule Deer Tracks 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Mule Deer Tracks 1.19 m 140 m3/s 2.33 m 625 m3/s
04/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Unknown Carnivore Scat 1.19 m 140 m3/s 2.33 m 625 m3/s
4/21/19 13:45-15:15 1.5 h Riparian 11.5 None Moderate; West Bald Eagle Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
4/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Squirrel Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
4/21/19 13:45-15:15 1.5 h Floodplain 11.5 None Moderate; West Unknown Sparrow Visual 1.19 m 140 m3/s 2.33 m 625 m3/s
4/21/19 13:45-15:15 1.5 h Riparian 11.5 None Moderate; West Unknown Sparrow Nest 1.19 m 140 m3/s 2.33 m 625 m3/s
4/29/19 15:48-17:45 2.0 h Riparian 8.5 rain; clear; snow Light; west Blue Jay Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Canada Goose Scat 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Canada Goose Tracks 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Canada Goose Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Peace 8.5 rain; clear; snow Light; west Canada Goose Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Riparian 8.5 rain; clear; snow Light; west Common Raven Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Coyote Tracks 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Killdeer Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Rabbit Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west River otter Tracks 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Riparian 8.5 rain; clear; snow Light; west Ruffed Grouse Drumming 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Riparian 8.5 rain; clear; snow Light; west Snipe Winnowing 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Riparian 8.5 rain; clear; snow Light; west Unknown Sparrow Visual 1.01 m 110 m3/s 2.26 600 m3/s
4/29/19 15:48-17:45 2.0 h Floodplain 8.5 rain; clear; snow Light; west Western Flicker Visual 1.01 m 110 m3/s 2.26 600 m3/s
5/13/19 10:45 – 12:15 1.5 h Halfway 13.5 None Light; west Bank Swallows Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Black Bear tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Canada Goose tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Canada Goose tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Peace 13.5 None Light; west Canada Goose tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Canada Goose Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Canada Goose visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Chickadee visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Common Raven Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Killdeer visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Moose tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Mule Deer tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Mule Deer visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west River otter tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Robins Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Squirrel visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Tundra Swans tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Halfway 13.5 None Light; west Tundra Swans Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Feline Retractable Tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Mammal tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Mammal tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Songbird tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Songbird Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Songbird Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Songbird Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Floodplain 13.5 None Light; west Unknown Songbird Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Unknown Songbird Tracks 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Unknown Songbird Visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/13/19 10:45 – 12:15 1.5 h Riparian 13.5 None Light; west Unknown Sparrow visual 1.39 m 175 m3/s 2.97 1340 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none American Robin visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Bank swallows visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Bank Swallows Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Beaver dam 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Beaver Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Black Bear Tracks 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Canada Goose scat 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Canada Goose Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Canada Goose visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Canada Goose Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Riparian 10.5 None none Chickadee song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Killdeer Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Mule Deer tracks 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Mule Deer Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Red-winged black bird Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Riparian 10.5 None none Robins song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Snipe song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Squirrel Visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Halfway 10.5 None none Tundra Swans visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Mammal Tracks 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Mammal Tracks 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Mammal Tracks 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Sandpiper visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Peace 10.5 None none Unknown Sandpiper visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Songbird song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Songbird song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Songbird song 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Floodplain 10.5 None none Unknown Songbird visual 1.49 m 195 m3/s 2.97 1400 m3/s
5/26/19 08:00-09:15 1.25 h Riparian 10.5 None none Yellow Headed Blackbird song 1.49 m 195 m3/s 2.97 1400 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Bank Swallows Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Beaver Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Beaver Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Canada Goose tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Canada Goose Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 peace 16 none Light; west Canada Goose tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 peace 16 none Light; west Canada Goose visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Chickadee Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Common Raven Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Common Raven Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Coyote tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Coyote tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Elk tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Magpie Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Mule Deer Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Mule Deer tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Mule Deer tracks 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Unknown Raptor Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 peace 16 none Light; west Unknown Sandpiper Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 peace 16 none Light; west Unknown Shorebird Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Unknown Songbird song 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Halfway 16 none Light; west Unknown Songbird visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Unknown Songbird Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Unknown Songbird Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Unknown Songbird visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Riparian 16 none Light; west Unknown Sparrow Visual 1.53 m 200 m3/s 3.04 1424 m3/s
6/2/2019 10:23-11:36 1.16 Floodplain 16 none Light; west Western Toad Tadpole Visual 1.53 m 200 m3/s 3.04 1424 m3/s

 

 

BLOG POST 3

I visited the study site which was the area located near my house. Due to high industrial activity and its proximity to my house, I decided to evaluate the type and abundance of plant species in this area. One of the most notable species which I identified was the nodding onion (Allium cernuum). My field study was to evaluate the growth pattern of this plant. I will be determining the abundance of the plant at different locations, plant integrity and the proportion of land that is covered with this plant relative to its proximity to the industrial site. I have observed that the distribution of the plant differs with regards to the proximity of the area to the industrial sites.   Upon inspection, the nodding onion plant was most abundantly located at locations distal to the industrial sites. One possible explanation was an increase in the concentration of heavy metals in the surrounding soil located at proximity to the industrial site. Heavy metal concentration in the soil can be facilitated by the transport of heavy metal particles by the rain and the wind.  Increased heavy metals can impact soil integrity by affecting key microbial processes leading to a decrease in soil microorganisms. Heavy metals can also inhibit plant metabolism leading to stunted plant growth.  Given the fact that this plant is found most abundantly in areas distal to the industrial sites, I hypothesize that heavy metal concentration in the soil will be higher in areas at close proximity to the industrial site which will, in turn, lead to less abundance of the nodding onion plant in this site. The response variable in this study will be the abundance of nodding onions relative to the proximity of the site to the areas of high industrial activity. This variable can thus be classed as categorical. One potential explanatory variable will be the rain while the wind can be classified as another explanatory variable. These two variables are thus classified as continuous variables.

Blog Post 3: Ongoing Field Observations

My second visit to my study site took place on July 17th, 2019. It had rained in the area about an hour and a half prior, leaving the ground quite moist. The sky was grey, and the temperature was 14 degrees Celsius. I have chosen to base my Field Study project off of the moss present in the dead patches of grass in shaded areas of my backyard. I am observing what I identified to be Common Fern moss (Thuidium delicatulum) across the gradient from healthy grass to dead patches of grass or areas of strictly soil. I will be looking specifically at the percent cover of species, structural integrity and abundance at different locations along this gradient. The response variable of my Field Study project is the percent cover of Fern moss. Due to the fact that this moss is only found in the shaded areas of my yard and strictly in the dead patches of grass where my dog urinates, one possible explanatory variable of this occurrence may be the lower pH soil composition in these areas causing low soil fertility and optimal growth conditions for this type of moss. These variables would be considered continuous data (measured on pH scale, percent coverage of moss at certain locations in the yard) as well as categorical data (presence or absence of species).

I chose the Southwest corner of my backyard for my first location. This area receives plenty of shade under the columnar aspen tree. The moss is thicker, and it seems to be growing along the transition between grass to no grass. It is very abundant in this location.

For the second location, I chose an area in between the Japanese lilac tree and the columnar aspen by the South fence. This area receives relatively the same amount of shade as location 1. The grass is lacking in this area and there are mainly patches of soil. I see rotten moss in this area, and there is a very small amount of healthy moss.

Location 3 is to the right of the Japanese lilac tree where the grass meets the border of the garden. There is barely any Fern moss in this area, however Pincushion moss (Leucobryum glaucum) is growing in the garden.

These observations have led me to the hypothesis that moss grows in specific levels of moisture, sunlight and acidity. When these factors exceed or fall short of the desired conditions, moss may react to these changes by rotting, stunting its growth or not growing altogether. A change in percent cover of Fern moss between three different locations in my yard may be a result of nonoptimal levels of these factors.

I predict that if my backyard lacked trees, a two-meter-high fence, and did not have burnt spots from my dog’s urine, the Fern moss would be less abundant, would have a low percent cover or be completely absent.

Blog Post 3: Ongoing Field Observations

Blog Post 3: Ongoing Field Observations

 

I returned to my study site for the second time on July 12, 2019 at 19:00 h. The weather was overcast but not raining or windy. For my subject I have chosen to study a biological attribute of the area. I am interested in the change in species composition and species diversity along the elevation gradient of the slope. The response variable is the species diversity. One possible explanatory variable is the amount of sunlight which changes with rising elevation due to cedar hedges across the field from the slope causing shade. This data would be considered both categorical (presence or absence of certain species at specific elevations) and continuous (percent coverage of species at distinct elevations).

Location 1: The first location was at the base of the slope, 0 metres above the flat field. Ferns (Athyrium filix-femina), were the dominant species with approximately 80% coverage. These ferns were similar height, standing at 1 metre tall. These ferns were directly across the field from cedar hedges (Thuja occidentalis) that were around 5 metres tall. Other vegetation includes corn sow thistle, clover, and tall grasses. The clover looked desiccated despite frequent rainfall in the area.

Location 2: The second location was approximately 3 metres up the slope from the base. This area was dominated by Saskatoon berry bushes (Amelanchier alnifolia).  There were also 2-3 developing birch (Betula) and maple (Acer). This was the only location where I noticed there was a species of bird present. The height of these plants was approximately the same as the opposing hedges.

Location 3: The final location 10 metres from the base of the slope. Fully developed pine and birch trees were the dominant species. There was a minimal number of ferns but they were shorter than the ferns found at the base of the slope.

In an area with no blockage by the cedar hedges, there were several fully developed pine trees at base level.

 

My hypothesis is as follows: Plants need sufficient access to resources including nutrients, water, and sunlight. In the absence of any of these resources, plants may not develop into complex organisms. Therefore, the change in species composition and diversity may be attributed to the lack of sunlight to base level plants due to the taller cedar hedge rows.

 

My prediction is as follows: If the cedar hedges are taller than the developing plants across the field, then they will not have sufficient access to sunlight and will not be as complex or tall as the plants found at higher elevations with greater access to the sunlight.

Blog Post #3 – Ongoing Field Observations

  1. Identify the organism or biological attribute that you plan to study.

After visiting my study site several times over the last week, I am eager to focus my research project on bird species in some way.  Over the last couple days, my ideas for study subjects have been wide ranging. Amongst some of my ideas:

  • attempting to sample the abundance of all individual bird species I encounter  at various points in the park (an unrealistic idea for someone with little to no working knowledge of bird identification, especially by song)
  • Measuring the abundance of bird species at different times of day, to see when activity is highest. (an appealing idea, but again with little knowledge of various bird species this study would likely have a large bias due to my own inaccuracies)
  • I then thought about grouping birds into groups (ie: songbirds, water birds, birds of prey) and sampling throughout the park at various times of day.  (Better, as I’m confident I can accurately tell the difference between these 3 groups, however the studies I looked at still put considerable emphasis on using bird songs to count species that have low visibility.)

 

I finally decided that water bird observations would be the direction I took as there are fewer species and each is fairly easy to accurately identify, even for an inexperienced bird watcher like myself.  They are also highly visible given their propensity for water and shore-based activities, so the need to identify based on song is eliminated. I will focus my observations on the 2 ponds in the park as I have not observed water birds outside of the immediate area of the ponds.

I knew I wanted to look at behavior patterns throughout the course of the day to see if I could discern any differences.  Once I thought more about bird behavior, I realized I would need to find a way to quantify these activities in a way that I could then interpret as data.  My admittedly limited experience in ecology prior to this course led me on a clumsy search through the library resources where I eventually stumbled upon the term “Time-activity budgets”.  This describes perfectly what I was hoping to sample and I’ve found several good papers describing techniques that would be feasible for the scope of this project.

I finally settled on measuring the time-activity budgets of 4 common waterfowl species at 3 different times of day (dawn, midday, dusk)

      • Mallard
      • Canada Goose
      • Franklins Gull
      • Spotted Sandpiper

Note: This species list is still subject to change as I had not taken note of specific species abundance of waterfowl during my previous visits. I plan to use the 4 most common species present in the park and will finalize my list during a trial data collection period this weekend!

  1. Use your field journal to document observations of your organism or biological attribute along an environmental gradient. Choose at least three locations along the gradient and observe and record any changes in the distribution, abundance, or character of your object of study.
    • I’ve noticed that some species (ie: the Gulls) spend a lot of time on the shore while others (ie: Mallards and Canadian Geese) are often found swimming in the open water. Therefore, the gradient I am using in my observations:  Shoreline (land) → shallows (estimated < 5 m from shore or visible foliage above waterline) →  open water
    • Sample Times: Dawn/midday/Dusk
    • Using the “Rule of 10” suggestion from the tutorials, I plan to collect data at my site on 10 different days (10 replicates).
      • 10 days x 3 times of day = 30 total sample periods
    • I plan to sample 3 individuals from each species at each visit
      • 4 bird species x 3 individuals/species = 12 individual birds/period x 30 sample periods = 360 individual birds analyzed.
    • I will be recording bird activities in a categorical nature (ie: Feeding, Resting, Comfort care, Locomotion, etc) every 15 seconds for 5 minutes, for each subject analyzed.
      • 5 minutes/bird, recording behavior every 15 seconds = 20 data points/bird
      • Each sample period: record data for 1-3 members (depending on abundance, goal=3) of each target species = 4-12 birds x 5 minutes each = 20-60 minutes= 80-240 data points/sample period
      • 10 days of sampling at 3 periods/day = 30 total sample periods = 2400-7200 data points collected
  2. Think about the underlying processes that may cause any patterns that you have observed. Postulate one hypothesis and make one formal prediction based on that hypothesis. Your hypothesis may include the environmental gradient; however, if you come up with a hypothesis that you want to pursue within one part of the gradient or one site, that is acceptable as well.

I predict that the water bird species studied will display increased levels of higher-energy activities (flight, feeding, etc) in dusk/dawn periods due to cooler temperatures, and increased display of lower energy activities (comfort, resting) mid-day when temperatures are higher.

The null hypothesis would be that time of day has no effect on the time-activity budgets of water bird species.

In studying 4 different species, I also hope to detect differences in activity patterns between them. I predict that the larger species (ie: Canada Geese) will spend more time feeding than their smaller comparators due to the increased energy demands required by larger organisms.

The null hypothesis here would be that the size of bird has no effect on behavior patterns throughout the day.

 

  1. Based on your hypothesis and prediction, list one potential response variable and one potential explanatory variable and whether they would be categorical or continuous. Use the experimental design tutorial to help you with this.
    • Response variable: behavior patterns (categorical)
    • Explanatory variable: time of day (categorical)

Based on the tutorial on experimental design, my study would be classified as a tabular design.

 

 

Sample data collection table that I have designed and will test this weekend:

L=land S=Shallows O= Open water

 

Blog Post 3: Ongoing Field Observations

  1. The organism that I plan to study is the white spruce (Picea glauca).
  2. The gradient that I will be analysing is the amount of space between trees from very crowded to 3m apart. This distance is an average of the distance between tree trunks at ground level. The most crowded location (location 1, annotated in red, Figure 1) is the forest stand at the north end of my study site; the mid-level spacing (location 2) is a cluster of trees near the house (annotated in blue, Figure 1); the location with the furthest distance between trees (location 3) is at the north west corner of the study site (annotated in black, Figure 1). Figure 1.

These trees were all planted by my family about 10 years ago. I am planning to study and compare various patterns within the white spruces. These patterns consist of tree height, new growth/bud abundance, and DBH (diameter at breast height). I plan to use tree height and DBH to calculate biomass, which can be used to determine productivity through a regression model based on the relationship between DBH (cm) and biomass (kg). There are many opportunities for comparison.

3. The most obvious underlying process that may cause observed patterns is the amount of direct sunlight received by an individual. Another might be any limiting of a resource due to a higher density of individuals in the area. It is hypothesized that overcrowding of white spruce (Picea glauca) decreases overall productivity and ability for seasonal growth (budding). If trees have more space between each other, they will be more productive due to more available sunlight and resources. Trees that are subject to crowding will be less productive than those that have ample space to themselves. For example, I predict that location 1, the most crowded, will have higher competition for soil resources, which may restrict growth. In contrast, trees in location 3 may have more room to spread their roots and absorb sufficient resources.

4. One potential response variable is whether the white spruce (sample unit) is crowded or spaced. A potential response variable is the abundance of new buds or tree height. These variables will both be continuous, as they will both be measured on a numeric scale (centimetres or metres for distance between trees and height; number of buds).

Blog Post 3: Ongoing Field Observations

I plan on studying the amount of paper birch in the area surrounding disturbance in my site. Disturbed areas consists of two large areas in which trees were removed in order to accommodate for housing to be developed. I plan on surveying along the edge of the disturbed area in 5m,10m and 20m intervals( this variable is classified as continuous )  . I predict that due to paper birch being a shade intolerant species it will only be found on the edge of the disturbed area due to the fact that without adequate sunlight it does not thrive. One potential explanatory variable that could affect the growth of paper birch in this area could be percipitation.