The Plankton of Pedder Bay Lab

Triceratops

BACKGROUND: Microscopic plankton can be can be collected in a way that allows us to determine densities of the organisms, and therefore compare different pelagic environments. We have already seen how plankton populations can vary from part of the ocean to another. In order to quantify plankton, the following method is suggested. You are urged to come up with your own research problem concerning plankton populations and then proceed to use the following techniques to investigate. Although this lab refers to Pedder Bay on Vancouver Island,, It could be modified to suit any location.PROCEDURE:In order to determine densities of organisms, we first have to know the volume of the water from which the sample is taken.
1. Calibrating the log:

    • You will use a plankton net with a small propellor driven counting log to measure distance travelled in the water that is sampled. To calibrate the log, measure off a distance on the docks, read the dial at the beginning of the trial, drag it through the water the length of the measured section, and the difference in the reading at the end of your tow will be the length of your cylinder of water.
    • Now calculate how many counts on the dial there are per meter.
    • Divide the number of counts per meter into the number of counts through the distance you drag the net for your sample. This gives you a number of meters in length for the sample cylinder.
    • Measure the diameter of the net opening and now calculate the volume of sample taken from the open ocean. The formula for volume of a cylinder is V=(pi X radius squared) X h(meters)

3. What is in The sample?

      • Note the total volume of the sample traken. Then remove a representative subsample of 1 ml.
      • Place the 1ml sample in a slide with a measured viewing chamber. Count numbers of individual species in representative quadrats. Obtain the average, and multiply this number by the total number of quadrats available.

4. Density determination.

      • .Now calculate the density of the individual species in the sample . i.e. number per cubic cm. then per cubic meter.

5. Option :

    • Calculate the number for a larger area e.g. Pedder Bay ! Hint treat it as a segment of a cone for volume determinations, use a chart to determine the measurements of the bay..

Pedder Bay frequently has booms of Mesodinium rubrum. This organism turns the bay a deep wine color . It is not a poisonous red tide , but we have noticed that when it is pumped up into seawater tanks, it will easily smother some of the filter feeders such as sponges. Blooms often coincide with nutrient loading followed by a period of sunny weather.

 

ADAPTATION OF ORGANISMS TO BRACKISH WATER ECOSYSTEMS

FIELD LAB ON ADAPTATION OF ORGANISMS
TO BRACKISH WATER ECOSYSTEMS

Environmental System
Lester Pearson College
Garry Fletcher


BACKGROUND: A class discussion on the problems that organisms have in adapting to the habitats of Brackish water ecosystems.

PROCEDURE:

1.Reading: Biology of Marine Life by Sumich (look up and discuss the reference to Stenohaline and Euryhaline organisms)

Using the graphical information about the distribution of Amphipods, design a protocol to test the model here in the esturary of Pedder bay. Examine water samples from a number of Estuarine locations.


2. Look for invertebrates in some of the following possible locations:
Strand line of Pedder Bay at Weir Point.
Estuary of “Garry’s Creek”
Strand Line of Taylor Beach
Estuary of Witty’s Lagoon
Estuary of salmon enhancement stream in Pedder Bay

3. Document the presence of plant species in the estuarine conditions. Several methods will be suggested to quantify their distribution. Identification pictures are available to help with the species. When you have decided how to portray the distribution of Plant Species, discuss this with your teacher and then proceed.

The Fouling System– Pedder Bay-Archive

The fiollowing set of lab reports were done as an exercise by the marine environmental systems class in September 1997

ENVIRONMENTAL SYSTEM CLASS ASSIGNMENT : SEPTEMBER 1997

For the first assignment of the year, the first year environmental systems classes were given the task of working in groups to examine different one meter sections of the dock skirt at Lester Pearson College. This was their first experience in using html as a word processing and presentation media, and the following presentations represents their first draft.

A COPY OF THE FIELD-LAB WORKSHEET:

THE “FOULING SYSTEM”

PEARSON COLLEGE DOCKS IN PEDDER BAY

ENVIRONMENTAL SYSTEMS FIRST YEAR FIELD LAB

INTRODUCTION:

You will be shown a section of the protective rubber skirt hanging from the Pearson College docks. On the bullrail of the dock you will find lettered sections of 1 meter. Growing on the rubber you will find a community of organisms which lives in this unique location . On this first introductory lab, we want you to use this set of organisms to gain a better understanding of the structure and function of ecosystems.

TOOLS YOU WILL USE:

Reference: Odum- ECOLOGY and Our Endangered Life Support System page 38-58)

Identification Manuals,

Adobe PageMill Software, Power MacIntosh Computer

OBJECTIVES:

After doing this lab you will be able to:

A) Model using Odum’s Symbols the material; cycles and energy flow of the Pedder Bay fouling system represented on your section of dock skirt. (Page 40-41 Odum- ECOLOGY and Our Endangered Life Support System)

B) Define the boundary of your system.

C) Identify the Structural components of the system:

1) Biotic:

Horizontal distribution aspects- regular, clumped, random, etc.

Vertical Distribution of organisms- stratified- (depth),

Biodiversity of the organisms

2) Abiotic:

Temperature, light-Intensity and Quality, Nutrients, Wave Action, tidal height, Salinity, etc.

D) Identify the Functional Components of the system:

1) Energy Flows- Producers, Consumers, Decomposers, Trophic Levels

2) Material Cycles: ( Biogeochemical Cycles) -Nitrogen, Phosphorous, Carbon, etc.

3) Succession – Temporal and Spatial.

E) Prepare a web-ready page representing the process and findings of this study.

F) Discuss the ways that humans might have an impact on this system.

G) Quantify the populations of the community , (using density and frequency measures)

PROCEDURE:

1. You will work in four groups for this field lab. Special effort should be made to include all members of the group. Decide on a recorder for the group. The end product will be one electronic lab report for each group, made up of the contributions of all.

2. Use the references available and discussion with the teacher to establish a name for the major players in the system.

3. Examine the section of dock skirt assigned to your group. Describe the populations qualitatively and quantitatively .

4. You will be supplied with some tools to measure some of the abiotic factors in the area, Record the change of at least one of those factors over some predetermined unit of time. (a temporal aspect)

5. Produce a full page diagram model of the system being studied using the appropriate Odum symbols. Use different colors to represent energy flow and material cycles.

6. Prepare a web-ready document on the lab, link in photographs done with the video camera. Indicate to the teacher when you have decided which shots you want.

7. Open a glossary file ( Create it in the program EXCEL) on the computers to record new words encountered in this lab. Where you can translate into your own language, make that addition in a column.

OPEN ENDED SUGGESTIONS:

You may wish to work on a few more challenging ideas once you have understood the basics. The following could be done individually or by the group.

1. Is what you see happening here the same 24 hours a day? How can this be included in your model?

2. Can you devise a method to quantify wave action? How significant is it as an abiotic factor?

3. How fast does recolonization or succession take place here in the bay, and what steps does it go through in the process. Could a small scale experiment be set up to monitor this?

4. What is the diversity index of the organisms here ( use Simpson’s Diversity Index)

5. Further work will be done on the plankton of Pedder Bay later on. Is there anything you could do at this point to quantify these important organisms? Is the plankton composition constant from day to day (temporal aspects).

6. Prepare a “Case Study” of one of the organisms in this system. Life cycles- growth rates etc.

7. Design a pyramid of biomass for the system. (This would entail wet or dry weights of the organisms of each trophic level.)

September 1997, Environmental Systems

Garry .Fletcher:. Lester B. Pearson College

STUDENT PAGES

Sophie Desoulieres, Fiona Talbot-Strong, Tamas Vonyo.

Tubeworms Anonymous

The rain was dripping on us as we embarked on our most difficult task of staring at stuff on a rubber skirt attached to the dock on our beautiful campus. Being generally good-natured, we pressed on regardless.

Purpose of the field lab: To observe the unique biodiversity that can be found on a rubber skirt.

Procedure: We looked at the plant and animal life present, learning their names and functions within our system, and measured both the air and water temperatures within that system. We decided the boundaries of our system, i.e. 25 cm deep, one metre long, and one metre from the dock. This being said, we kept in mind that the surrounding area directly affects our system.

tube worms, pink sponge, yellow sponge, limpets, mussels, ulva, school of anchovies, jelly fish, obelia, phytoplankton. The amount of plankton was such that one could see 3.25 metres towards the ocean floor.

Producers: Ulva, phytoplankton, diatoms

Primary consumers: anchovies, limpets,

Secondary consumers: salmon, seagulls ( In general seagulls eat salmon, which makes them tertiary consumers too. )

Abiotic factors:
Temperature: 10.1 C ; Salinity: 27 ppt (parts per thousand)
The salinity rate of the water in Pedder Bay is lower than the one of the Pacific Ocean ( 36 ppt ) As Pedder Bay is in an estuary ( fresh and sea water ).Wave action: There were 5 waves ( about 30cm high ), when a boat passed. We noticed that there were less plankton when we made our measure with the Secchi disc.

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Forrest Pass , Eri Akamatsu, Kelly Bowen

On September 16, 1997, we went down onto the docks of Pedder Bay to study the marine ecosystem. We took note of the various species of creatures living on the rubber skirt surrounding the dock. We observed that there are many factors affecting the ecosystem, both biotic and abiotic.

Purpose of the Field Lab:

The purpose of the field lab was to formulate a model of the marine ecosystem on the rubber skirt around the college dock.

PROCEDURE:

To begin, we went to the docks and took note of the various creatures we saw on our rubber skirt. We also recorded the factors within our three cubic metre marine system.

Species List:
-Barnacles

-Mussels

-Ulva (Green Algae)

-Limpets

-Seaweeds

-Halochondria (Yellow Sponge)

-Red Filamentous Algae

-Obelia (Something Whitish)
-Isopods
-Little Fish
-Gulls
-Douglas Fir Needle
-Ocean Spray
-Leaves

-Boats (wake and oil residue)
-Guano (contains nitrogen and phosphates)

OBSERVATIONS:

During this lab, we observed the interaction of several marine species. In addition to observing organisms feeding on other organisms (ie: barnacles on plankton, harbour seals on herring or anchovies), we also observed organisms involved in symbiotic relationships. For example, we observed barnacles anchored to limpets. The relationship results in mutual benefit as (a) the barnacles are able to anchor themselves, alleviating problems that could result from “swimming free”, and (b) the barnacles help to discourage predators that could potentially prey on the limpets. There are several other biotic factors that affect the system, including “guano” produced by seagulls that, as it contains phosphates and nitrogen, helps to maintain the balance of nutrients within the system.

We also observed numerous abiotic factors that could , and in all likelihood do, affect the lives of the living organisms. These include the temperature of the water, a factor that helps to determine which organisms can survive in the system; the amount of sunlight to which the system is exposed, a factor which affects the plankton, algae, and seaweed populations; and the salinity of the seawater. Human activity also plays an important role in the system. The wake from boats, pollutants from human sources, and the number of fish caught by commercial fishing fleets and recreational anglers all affect the processes of the system.

It is unlikely that the processes within the system are constant. Seasonal disparities in sunlight, temperature, and animal and human population in and around the system indubitably affect the many of the qualities of the system. For example, a sudden rise in the seagull population could upset the delicate nutrient balance in the system. This sudden change, coupled with favourable amounts of sunlight and warm temperatures, would precipitate a large algae “bloom”. The rise in the seagull population could be a direct result of a drop in the seal population, thus eliminating competition between the two species over their common food source: fish. The decline in the seal population, in turn, could be the result of human economic factors: pollution from seaside industrial projects, or the massacre of seals resulting by fisherman angered by low salmon returns. Thus, abiotic factors that fluctuate throughout the year have a profound impact on the processes of the system and, by extension, on the organisms therein.

Visibility is an indicator of light penetration and is, therefore, an important quantifiable abiotic factor. One uses a Secchi dish to quantify visibility; on September 19, 1997, the Secchi dish was visible to a depth of 3.5 metres. However, in winter, this figure would increase because of the lack of plankton and algae in the frigid water. Human activity on the periphery of the systemwould also have an effect on the visibility; fertilizers carried in runoff from seaside farms could upset the nutrient balance of the system, perhaps creating an algae “bloom” (decreased visibility), while large falls of “acid rain” could adversely affect the pH level within the system, killing off the algae/plankton. The second scenario has occurred in parts of Ontario, creating lakes that are “crystal clear”.

The action of waves and tides have an effect on the system and its member organisms. Tides and waves “flush out” the system, thus helping to maintain the nutrient levels necessary for the survival of organisms within the system. Without tide and wave action, the water in the system would become stagnant. Nutrients, such as nitrogen, would accumulate in the stagnant water, fertilizing algae and other marine plants. While tide action is fairly easy to quantify, the quantification of wave action poses a challenge. One could determine the regularity of waves by counting the number of waves the pass a certain point in an hour (day, month, year) and divide by the number of minutes (hours, days, months) to derive an average. It could also be useful to determine the average height of waves passing a point, or the force with which these waves strike a dock. These would all aid in the quantification of wave action.

Forrest, Eri, Kelly

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Sara Pavan, Giovanni Rosso, Sebastian Ferrero:
For this lab we analysed the system contained in a section of the rubber skirt which protects our docks at Pedder Bay.

PURPOSE: To model the structure and function of the fouling system.

 

BIOTIC STRUCTURE:( Species List )

Polyorchis, Mussels,Isopod,Sea Squirt,Herring,Blue Heron,Cormorant,Harbour seal,Sea Gulls,Limpet

Materials: Thermometer, meter stick, and a spatula

Boundary: Our system included the “I” section of the dock skirt. The environment we considered was 1m deep and ran to the opposite side of the bay. We determined this to be our boundary because it would include factors which influence our small section of the rubber skirt such as mammals, birds and human factors.

Distribution aspects: The most prosperous life forms in our system were the mussels. After taking several measurments in different parts of the skirt we found out that the average density is of about 28 mussels per 25 centimeters squared. These results lead us to the conclusion that there are more or less 1800 shells in the “I” section. They were clumped towards the bottom of the skirt with very few of them near to the surface.

The sea squirts were clumped again around the bottom and were hidden between mussels. Numerous herring and even one polyorcas jellyfish migrated through our system.We sighted many birds entering our system to feed. The distribution was clumped- with a large concentration of lifeforms near the bottom of the rubber skirt, and far less organisms living at the top. Smaller organisms usually used the harder shell of the mussels as shelter and grew underneath them. The isopods in particular could usually find concealment under the cover of seaweed and mussels.

Abiotic: The temperature of the water was 12.5 degrees Celsius while the external temperature was 15 degrees. The light was brighter towards the top of the water. Nutrients in our system were provided by sun light , organic waste, and other materials brought in by the tide and other external factors. Because the tide changed often and fairly extremely, fewer organisms lived above the lowest sea level. It can be assumed that the ones which did were hardier and didn’t require an environment as stable as the ones living further under the water surface.

Docks by night: We also had a chance to observe the piece of skirt we observed during the night and we found out that several other species are apparent at that time. These were: shrimp (Two different species, which grasp on algea, shells and pieces of material also close to the sea level. We noticed that this behavior changes during windy evenings. In fact, they don’t come very near to the surface then, probably because until a certain depth the waves caused by the wind make it difficult for them to swim and grab materials.) ; clam worms (These invertebrates like to swim quite near to the surface especially around light sources); sculpins (These small fish like to search for food under the green algae beside the mussels) ; herring (These fish can also easily be seen during the day but at night they seem to be less active); small crabs (Some crabs appear near to the surface, but only small ones); fluorescent organisms (We never saw these organisms before. They look like small larvae and glow with a greenish light. They also like to swim near to light sources. The reddish brown striped shrimp seem to be slower but better protected by a larger thicker shell); seals (As almost all the organisms we listed above they are also far more daring at night when they come quite close to the docks.

Human impact: During the day the area around the docks is constantly crowded by boats which travel from the marina to the open sea and back. This causes both noise pollution and pollution of the water through oil, and waste products. Both these factors cause the animals to become more reticent during the day. Algae and shells don’t have the capability to react because they don’t have the ability to move but ” intelligent” animals such as seals, birds and fish often build a realtionship with human beings which permits them to find food easily. The best way in which people can operate in an environment is by respecting it and not trying to change the habits of the creatures that live inside it. Concluding we could say that as the number of human beings increases the density of animals who can’t move diminishes meanwhile the others can diminish , increase or remain the same as long as the new conditions are beneficial to them. Some animals might also be leaving during the day and coming back at night when the whole bay is more peaceful.

Density: We already have mentioned some of the density and distribution aspects of organisms living on the skirt before, but now we would like to spend a few words talking about animals which swim or fly around it : CORMORANTS ( These big black birds that have the habit of staying on the top branches, preferably if not covered by leaves, of high trees which grow near to the water usually gather in large groups until they haven’t covered the space they can use to sleep. In the bay they aren’t bigger of a dozen but at Race rocks, for example, the groups probably count hundreds of units.) ; SEALS ( These animals get near to the docks especially at night or during rainy days when the boat traffic is less intense and they aren’t normally more than two or three, but they don’t stay still in one place, instead they move around all over the place); KINGFISHERS ( These cute small birds are quite scared from human beings therefore they can normally be seen in the distance, mostly alone.); SEA GULLS ( Their density is usually higher on rainy days when they gather in flocks and search for food in the middle of the bay, otherwise they can be seen flying quite high in the sky but then their number isn’t very high); BIG FISH ( We suppose that during the day they stay in the middle of the bay in deep water and in repaired places away from noise and predators; we noticed although that the herring near to the bay sometimes jump scared out of the water at night, we therefore think that this is because both seals and big fish come near to the surface and the skirt; BALD EAGLES ( These huge birds seem to be quite rare around the bay but during these weeks we saw two or three circling high in the sky.)

Waves: As we mentioned before we noticed that waves have a great influence on the animal behavior around the skirt, but we think that it also interacts with animals at a certain depth because the bigger the waves are and the more intense the current is the more food and material you get carried into the bay, therefore fish become more active. The opposite end of the issue is that any pollution or negative influences will also enter the system faster.

It is quite hard to quantify waves although we could measure the highest point reached by one of them on a stick attaching it to the docks and then the lowest one when the water settles down; we could then approximate the number of waves by counting the ones which pass through a certain spot in a certain lap of time and describe then their shape . This procedure could probably give as a quite clear idea of what the sea was like on a certain day.

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Sarah McEachern, Karine Gaulin, Marieve Therriault

The Astounding Ecological System of Pedder Bay

It was the sixteenth day of September; a dark, rainy, dismal day when our brilliant Environmental Systems teacher got the ingenious idea of forcing us out into the elements. We plunged our hands into the ocean in search of life forms. We strained our eyes to catch sight of passing jelly fish and anchovies, we scraped our hands on barnacles and clams and we nearly fell into Pedder bay trying to count mussels.

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Organisms of the Fouling System

by: Michal Mlcousek, Eva Mejnertz,

t was a rainy morning when we went to Pedder Bay. We were supposed to survey many organisms, which we haven’t seen before in our countries. It was a very nice introduction to a new subject – Environmental systems, which aim is an attempt to understand and realize everything as a system, depending on many factors.
Purpose of the field lab To gain a better understanding of the structure and function of the eco system, through a practical exercise.

Procedure: We lifted the rubber skirt protecting the docks, to observe the many organisms that were part of the system, depending on each other.

Structure biotic species list:

By Michal Mlcousek,and Eva Mejnertz

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By: Merideth Shaw, Kuba Fast, Rocio Martinez, Monica Segura

Introduction

In our first environmental systems lab we went down to the college docks to examine the ecosystem of its protective rubber skirt. Pearson College is located on the northern shore of Pedder Bay, at the southern end of Vancouver Island. The bay is open to the southeast to Juan de Fuca Strait. It has a rock shoreline and is about 10 meters deep. It has tides of up to 3.3 metres, with the waves of up to 2.5 metres in extreme. The weather conditions around Pedder Bay are not at all severe – with usually wet and mild winters and cold and dry summers, with very low annual temperature amplitudes. Due to their southern exposure, the docks receive a fair amount of direct sunlight.

Purpose of this lab

The purpose of this lab is to model the structure and function of the Pearson College docks’ fouling system

Biotic structure

(i) Species list

also : – isopods,– small fish.

plantae:– ulva,– filamentous diatom.

By: Merideth Shaw, Kuba Fast, Rocio Martinez, Monica Segura

 

===============================================

By: Nick Lanham , Alex Gesheva, Andreina Torres Angarita

 

Purpose

To model the structure and function of the ecosystem of the life growing on the rubber skirt using a functional diagram with Odum symbols.

 

Biotic Structure

Species List:

 

 Mussels  Limpets
 Isopods  Barnacles
 Algae( Ulva)  Algae (Diatom)

 

Horizontal Distribution:

The organisms in our system were, for the most part, evenly distributed horizontally along our system. The exceptions were mussels, which were clumped in some areas, and very sparse in others, and the limpets, which were randomly scattered throughout.

 

Vertical Distribution:

There was a clearly defined vertical distribution in our system. The young Ulva algae grew near the top, as it needs more light and heat and as we moved deeper the mussels and older algae began to show up.

Abiotic Factors

We took 2 separate measurments of the temperature of the air and of the water in our system. The average air temp was 16.5. The water avarage was 10.5.

System Boundary:

By: Nick L. , Alexandra G., Andreina T.

Donna Gibbs: SPECIES LIST- From: William Head, Rosedale Rocks, Race Rocks

SPECIES LIST:

Compiled by:Donna Gibbs of the Vancouver Acquarium on dives made at Rosedale Rock, West Race Rocks and William Head in the summer of 1997. Groupings are made in Phylums or Divisions.

Dive 432 – Rosedale, Race Rocks – June 12, 1997

 

Epiphytic red algae (Smithora, Antithamnion, Ceramium, Polysiphonia)

Iridescent blade red algae (Iridea)

Encrusting coralline algae (Lithothamnion)

Branching coralline algae (Bossiella, Corallina, Calliarthron)

Bull kelp (Nereocystis)

Blade kelp (Costaria)

Blade kelp (Alaria)

Woody-stemmed kelp (Lessoniopsis, Eisenia, Pterygophora)

 Tar spot (Codium setchellii)
 Tan finger sponge (Isodictya quatsinoensis)

Orange-red encrusting sponge (Ophlitaspongia pennata)

Thick, dark red encrusting sponge (Plocamia karykina)

Boring sponge (Cliona celata)

Crumb-of-bread sponge (Halichondria, Haliclona spp.)

 Giant black feather-duster worm (Eudistylia vancouveri)

Sand-dwelling feather-duster worm (Sabella spp.)

Slime tubeworm (Myxicola infundibulum)

Multi-colour calcareous tubeworm (Serpula vermicularis)

Honeycomb tubeworm (Dodecaceria fewkesi)

Spaghetti or shell binder worm (Thelepus crispus)

 Plumose anemone (Metridium giganteum)

Red and green or Christmas tealia (Urticina crassicornis)

Crimson anemone (Cribrinopsis fernaldi)

Brooding or proliferating anemone (Epiactis prolifera)

Zoanthid (Epizoanthus scotinus)

Ostrich-plume hydroid (Aglaophenia struthionides)

Delicate-plumed hydroid (Plumularia spp.)

Orange hydroid (Garveia annulata)

Snail-fur hydroid (Hydractinia sp.)

Pink-mouthed solitary hydroid (Tubularia marina)

Thread-like, creeping network hydroid (Orthopyxis spp.)

Pink or violet branching hydrocoral (Stylaster venusta)

Encrusting hydrocoral (Allopora petrograpta)

Tiny star jellyfish (Phialidium gregarium)

  Other encrusting bryozoan (Schizoporella spp., Microporella spp., Eurystomella spp.)

Northern staghorn bryozoan (Heteropora pacifica)

 Gumboot chiton (Cryptochiton stelleri)

California mussel (Mytilus californianus)

Rock or purple-hinged scallop (Crassedoma giganteum)

White-cap limpet (Acmaea mitra)

Rough keyhole limpet (Diodora aspera)

Snail-dwelling slipper shell (Crepidula adunca)

Leafy hornmouth shell (Ceratostoma foliatum)

Blue top snail (Calliostoma ligatum)

Heath’s dorid (Geitodoris heathi)

Coloured dendronotid (Dendronotus diversicolor)

  Sea flea (Anisogammarus spp., Orchestia spp.)

Coon-stripe shrimp (Pandalus danae)

Candycane or candy-stripe shrimp (Lebbeus grandimanus)

Kincaid’s commensal shrimp (Heptacarpus kincaidi)

Giant or giant acorn barnacle (Balanus nubilis)

Oregon crab (Cancer oregonensis)

Masking or sharp-nose crab (Scyra acutifrons)

Hairy, flat lithode crab (Hapalogaster mertensii)

Scaled crab (Placetron wosnessenskii)

Orange hermit crab (Elassochirus gilli)

 Blood star (Henricia leviuscula)

Long-rayed or rainbow star (Orthasterias koehleri)

Six-rayed star (Leptasterias hexactis)

Sunflower star (Pycnopodia helianthoides)

Sun star (Solaster stimpsoni)

Serpent or daisy brittle star (Ophiopholis aculeata)

Giant red sea urchin (Strongylocentrotus franciscanus)

Purple sea urchin (Strongylocentrotus purpuratus)

Giant or California sea cucumber (Parastichopus californicus)

Creeping pedal or armored sea cucumber (Psolus chitonoides)

  Mosshead warbonnet (Chirolophis nugator) gorgeous – huge and red!

Copper rockfish (Sebastes caurinus)

Quillback rockfish (Sebastes maliger)

Black rockfish (Sebastes melanops)

Tiger rockfish (Sebastes nigrocinctus)

Kelp greenling (Hexagrammos decagrammus)

Ling cod (Ophiodon elongatus)

Scalyhead sculpin (Artedius harringtoni)

Red Irish lord (Hemilepidotus hemilepidotus)

 

Lobed compound tunicate (Cystodytes lobatus)

White-crust compound tunicate (Didemnum albidum)

Dive 433 – Rosedale, Race Rocks – June 13, 1997

 Epiphytic red algae (Smithora, Antithamnion, Ceramium, Polysiphonia)

Encrusting coralline algae (Lithothamnion)

Branching coralline algae (Bossiella, Corallina, Calliarthron)

 Woody-stemmed kelp (Lessoniopsis, Eisenia, Pterygophora)  Tar spot (Codium setchellii)
 Tennis ball sponge (Tetilla arb)

Smooth orange puff-ball sponge (Suberites montiniger)

 Red sand-dwelling tubeworm (not Sabella)  Coon-stripe shrimp (Pandalus danae)

Candycane or candy-stripe shrimp (Lebbeus grandimanus)

Kincaid’s commensal shrimp (Heptacarpus kincaidi)

Giant or giant acorn barnacle (Balanus nubilis)

Oregon crab (Cancer oregonensis)

Masking or sharp-nose crab (Scyra acutifrons)

Other encrusting bryozoan (Schizoporella spp., Microporella spp., Eurystomella

spp.)

 Lined chiton (Tonicella lineata)

Red chiton (Tonicella insignis)

Gumboot chiton (Cryptochiton stelleri)

Swimming or pink scallop (Chlamys sp.)

White-cap limpet (Acmaea mitra)

Rough keyhole limpet (Diodora aspera)

Leafy hornmouth shell (Ceratostoma foliatum)

Dire whelk (Searlesia dira)

Dwarf hairy triton (Trichotropsis cancellata)

Blue top snail (Calliostoma ligatum)

Cockerel’s dorid (Laila cockerelli)

Plumose anemone (Metridium giganteum)

Red and green or Christmas tealia (Urticina crassicornis)

Crimson anemone (Cribrinopsis fernaldi)

Brooding or proliferating anemone (Epiactis prolifera)

Zoanthid (Epizoanthus scotinus)

Sea fir (Abietinaria spp., Thuiaria spp., Sertularia spp.)

Ostrich-plume hydroid (Aglaophenia struthionides)

Delicate-plumed hydroid (Plumularia spp.)

Orange hydroid (Garveia annulata)

Pink or violet branching hydrocoral (Stylaster venusta)

 Blood star (Henricia leviuscula)

Long-rayed or rainbow star (Orthasterias koehleri)

Six-rayed star (Leptasterias hexactis)

Sunflower star (Pycnopodia helianthoides)

Sun star (Solaster stimpsoni)

Giant red sea urchin (Strongylocentrotus franciscanus)

Purple sea urchin (Strongylocentrotus purpuratus)

Giant or California sea cucumber (Parastichopus californicus)

Black sea cucumber (Cucumaria lubrica)

 Copper rockfish (Sebastes caurinus)

Quillback rockfish (Sebastes maliger)

Kelp greenling (Hexagrammos decagrammus)

Ling cod (Ophiodon elongatus)

Scalyhead sculpin (Artedius harringtoni)

Cabezon (Scorpaenicthys marmoratus)

Lobed compound tunicate (Cystodytes lobatus)

White-crust compound tunicate (Didemnum albidum)

Dive 434 – West Race Rocks – June 13, 1997

   

Woody-stemmed kelp (Lessoniopsis, Eisenia, Pterygophora)

 Surf grass (Phyllospadix)
 Tan finger sponge (Isodictya quatsinoensis)

Boring sponge (Cliona celata)

Pecten sponge (Mycale adhaerens)

Sulphur sponge (Myxilla lacunosa)

Smooth orange puff-ball sponge (Suberites montiniger)

 Orange ribbon worm (Tubulanus polymorphus)

Giant black feather-duster worm (Eudistylia vancouveri)

Sand-dwelling feather-duster worm (Sabella spp.)

Honeycomb tubeworm (Dodecaceria fewkesi)

Spaghetti or shell binder worm (Thelepus crispus)

 
 Kelp-encrusting bryozoan (Membranipora membranacea)

Other encrusting bryozoan (Schizoporella spp., Microporella spp., Eurystomella

spp.)

Spiral or spiral-tuft bryozoan (Bugula californica)

Fluted bryozoan (Hippodiplosia insculpta)

Northern staghorn bryozoan (Heteropora pacifica)

 Gumboot chiton (Cryptochiton stelleri)

California mussel (Mytilus californianus)

Sea bottle clam (Mytilimeria nuttallii)

Rough keyhole limpet (Diodora aspera)

Northern or pinto abalone (Haliotis kamtschatkana) 1 – 4″

Dwarf lurid triton (Ocenebra lurida)

Monterey sea lemon (Archidoris montereyensis)

White dorid (Archidoris odhneri)

Opalescent aeolid (Hermissenda crassicornis)

Three-lined aeolid (Flabellina trilineata)

Coloured dendronotid (Dendronotus diversicolor)

Giant Pacific octopus (Octopus dofleini)

White-spotted tealia (Urticina lofotensis)

Crimson anemone (Cribrinopsis fernaldi)

Brooding or proliferating anemone (Epiactis prolifera)

Zoanthid (Epizoanthus scotinus)

Soft coral (Gersemia rubiformis)

Sea fir (Abietinaria spp., Thuiaria spp., Sertularia spp.)

Ostrich-plume hydroid (Aglaophenia struthionides)

Delicate-plumed hydroid (Plumularia spp.)

Orange hydroid (Garveia annulata)

Snail-fur hydroid (Hydractinia sp.)

Pink-mouthed solitary hydroid (Tubularia marina)

Pink or violet branching hydrocoral (Stylaster venusta)

  Leather star (Dermasterias imbricata)

Blood star (Henricia leviuscula)

Long-rayed or rainbow star (Orthasterias koehleri)

Velcro or fish-eating star (Stylasterias forreri)

Six-rayed star (Leptasterias hexactis)

Sunflower star (Pycnopodia helianthoides)

Sun star (Solaster stimpsoni)

Morning sun star (Solaster dawsoni)

 Kelp greenling (Hexagrammos decagrammus)

Ling cod (Ophiodon elongatus)

Scalyhead sculpin (Artedius harringtoni)

Cabezon (Scorpaenicthys marmoratus)

Red Irish lord (Hemilepidotus hemilepidotus)

 Light-bulb tunicate (Clavelina huntsmani)

Stalked, dwarf light-bulb tunicate (Pycnoclavella stanleyi)

Stalked compound tunicate (Distaplia smithi)

Dive 431 – William Head, Vancouver Island – June 12, 1997

Epiphytic red algae (Smithora, Antithamnion, Ceramium, Polysiphonia)

Iridescent blade red algae (Iridea)

Encrusting coralline algae (Lithothamnion)

Branching coralline algae (Bossiella, Corallina, Calliarthron)

 

Bull kelp (Nereocystis)

Woody-stemmed kelp (Lessoniopsis, Eisenia, Pterygophora)

 Orange-red encrusting sponge (Ophlitaspongia pennata)

Thick, dark red encrusting sponge (Plocamia karykina)

Boring sponge (Cliona celata)

Hermit crab sponge (Suberites suberea) with Pagurus stevensae

 Agassiz’s peanut worm (Phascolosoma agassizii)

Scale worm (Halosydna brevisetosa, Harmothoe spp.)

Slime tubeworm (Myxicola infundibulum)

Multi-colour calcareous tubeworm (Serpula vermicularis)

Cement tubeworm (Sabellaria cementarium)

Spaghetti or shell binder worm (Thelepus crispus)

Plumose anemone (Metridium giganteum)

Red and green or Christmas tealia (Urticina crassicornis)

Fish-eating tealia (Urticina piscivora)

Brooding or proliferating anemone (Epiactis sp.)

Orange cup coral (Balanophyllia elegans)

Sea fir (Abietinaria spp., Thuiaria spp., Sertularia spp.)

Silver-tip hydroid (Abietinaria greeni)

Pink or violet branching hydrocoral (Stylaster venusta)

Encrusting hydrocoral (Allopora petrograpta)

Water jellyfish (Aequorea victoria)

Tiny star jellyfish (Phialidium gregarium)

Other encrusting bryozoan (Schizoporella spp., Microporella spp., Eurystomella

spp.)

Northern staghorn bryozoan (Heteropora pacifica)

Southern staghorn bryozoan (Diaperoecia californica)

 

 

 Oval brachiopod or lamp shell (Laqueus californicus) ?
 Lined chiton (Tonicella lineata)

Red chiton (Tonicella insignis)

Gumboot chiton (Cryptochiton stelleri)

Swimming or pink scallop (Chlamys sp.)

Rock or purple-hinged scallop (Crassedoma giganteum)

Jingle shell (Pododesmus cepio)

Northwest ugly clam (Entodesma saxicola)

Hooded puncturella (Puncturella cucullata)

Northern or pinto abalone (Haliotis kamtschatkana)

Leafy hornmouth shell (Ceratostoma foliatum)

Dwarf lurid triton (Ocenebra lurida)

Oregon or giant hairy triton (Fusitriton oregonensis)

Dwarf hairy triton (Trichotropsis cancellata)

Blue top snail (Calliostoma ligatum)

Ringed top snail (Calliostoma annulatum)

Variable lacuna (Lacuna variegata)

Smooth-edged wenteltrap (Opalia borealis)

White dorid (Archidoris odhneri)

Nanaimo dorid (Acanthodoris nanaimoensis)

Cockerel’s dorid (Laila cockerelli)

Opalescent aeolid (Hermissenda crassicornis)

Red-gilled aeolid (Flabellina verrucosa)

 Common gray mysid (unknown) ?

Coon-stripe shrimp (Pandalus danae)

Kincaid’s commensal shrimp (Heptacarpus kincaidi)

Giant or giant acorn barnacle (Balanus nubilis)

Oregon crab (Cancer oregonensis)

Masking or sharp-nose crab (Scyra acutifrons)

Flat porcelain crab (Petrolisthes cinctipes)

Turtle or butterfly crab (Cryptolithodes typicus)

Flat, granular-claw hermit crab (Elassochirus tenuimanus)

Sponge hermit crab (Pagurus stevensae)

Blood star (Henricia leviuscula)

Long-rayed or rainbow star (Orthasterias koehleri)

Sunflower star (Pycnopodia helianthoides)

Sun star (Solaster stimpsoni)

Serpent or daisy brittle star (Ophiopholis aculeata)

Green sea urchin (Strongylocentrotus droebachiensis)

Giant red sea urchin (Strongylocentrotus franciscanus)

Purple sea urchin (Strongylocentrotus purpuratus)

Giant or California sea cucumber (Parastichopus californicus)

Red sea cucumber (Cucumaria miniata)

Creeping pedal or armored sea cucumber (Psolus chitonoides)

  MPacific herring (Clupea harengus pallasi) school of juveniles

Blackeye goby (Coryphopterus nicholsi)

Mosshead warbonnet (Chirolophis nugator)

Longfin gunnel (Pholis clemensi)

Copper rockfish (Sebastes caurinus) one adult

Puget Sound rockfish (Sebastes emphaeus) school of 200 juveniles

Kelp greenling (Hexagrammos decagrammus)

Scalyhead sculpin (Artedius harringtoni)

Broad-base tunicate (Cnemidocarpa finmarkiensis)

Horse-shoe or disc-top tunicate (Chelyosoma productum)

Stalked, dwarf light-bulb tunicate (Pycnoclavella stanleyi)

Orange social tunicate (Metandrocarpa taylori)

White-crust compound tunicate (Didemnum albidum)

The PEDDER BAY MIDDEN Lab

PEDDER BAY MIDDEN

Just west of Pearson College in Pedder Bay is a bank along the estuary which is being eroded under the roots of a large Douglas Fir. We do a field lab there using the evidence from the First nations midden to piece together a picture of what the original system of Pedder Bay must have been like when First Nations people lived in the area, several centuries ago.

 

We are able to make observations of the exposed midden shell fragments and determine the species of shellfish harvested here. One interesting find was a shell of a native rock oyster, a species that is no longer found in Pedder Bay, but which was obviously part of the diet several hundred years ago.

The objective of this lab is to construct a systems diagram of this Bay Ecosystem which includes these early indigenous  people

Ecological Succession Lab-Part 1. BIOMASS

ECOLOGICAL SUCCESSION-PART 1. BIOMASS
Objective 2.3.6,
Background reading reference, Odum page 193-194,
PART 1: LAB ON BIOMASS ACCUMULATION ON SUCCESSION PLATES
PROCEDURE:1. You will be taken to the docks where you will retrieve a succession slide box that has been left suspended in the bay for the past year. Return to the lab and clear off all life forms, (mostly invertebrates) that have grown in that time.

2. Separate the organisms into different species groups. Identify the groups to family or genus level and put them in the small trays provided and leave for at least 24 hours in the marine dryer. You may as an option at this point take a wet biomass determination.

3. Weigh the species in order to get a dry biomass of the different life forms.

4. Calculate the surface area from which the organisms were removed .

5. Do a biomass determination on each species — grams per square cm.

6. Enter your own results in an Excel chart on the computer. Produce a pie graph of the results.7. Obtain the raw data from the other teams in the class and make another graph of the cumulative results.
Discussion:1. Referring to page 194 of Odum, explain how biomass in a community is affected by succession.

2. Design the protocol of a lab using similar materials that you could use to test this theory and that of how species diversity is affected by succession .

3. Compare your graph with the total class results. What would you consider to be the best result and why? (use the word replication in your answer)
 :
ECOLOGICAL SUCCESSION IN PEDDER BAY -PART 2
Objective: 2.3.5 ,Objective 2.3.6,
Background reading reference, Odum page 186-207
PART 2 :Succession –
PROCEDURE:1.Place 10 clean microscope slides in a cleaned succession slide box.

2.Suspend the box in 1 meter of water in the designated location on the docks.

3. After 2 weeks, remove one slide and examine 5 fields of view under 100X in the compound microscope. Use the diagrams and booklets provided to identify the species to the genus level.4. Tally the number of each species in each field of view and then make a cumulative tally. It may help to make sketches of the species in order to be able to associate a name with the appearance.

5. In EXCEL , enter your counts and make a pie chart of the results which is labelled with % as well as number for each species.

6. Repeat this procedure at two week intervals, for at least 8 weeks.

OPTION A: Compare your results with those freom previous years: Consult the teacher if you wish to do more complex statistics on the variations observed.

OPTION B: Add to the collection of photographs of diatoms .

OPTION C: Dip at least one slide in the antifouling compund ” EASY NET” and compare after 8 weeks the effectiveness of this treatment.

Discussion:1. Referring to page 193- 194 of Odum, explain how species diversity in a community changes with succession. Provide evidence from your work to support or reject this theory.

2. Examine the model provided for a similar succession sequence from Oregon waters. Using that model , make your own flow chart to compare the two locations.

EVALUATION: Include an extensive evaluation of the lab.

PEDDER BAY IB GROUP FOUR SCIENCE PROJECT IDEAS

PEDDER BAY GROUP FOUR SCIENCE PROJECT IDEAS

January 21 1997

G.Fletcher

OVERVIEW:

  • Our overall theme this year for the IB Group four project as chosen by the first year science students of Lester Pearson College is Pedder Bay. Since we have had some experience with this region for some time, it is the intention of this file to lay out some of the possible themes within this project and to point out some possibilities for collaboration of members of the different sciences in the groups for the purpose of doing these preliminary studies..
  • It is expected that research could be either of the descriptive or the experimental variety. Both approaches are valuable when atttempting to understand a system.
  • It is suggested that in order to make this research of future lasting value as well as present value, some projects could seek to set up protocols for long term research and establish sites on the already existing Pedder Bay web site which would have permanent value for baseline and and a data bank for follow up information. In order to do this it is necessary to have the reports submitted in electronic form done in html, now quite easy to do because of the presence of the Adobe GoLive software on the college computers. Also word processing done in other formats can now easily be converted to basic html by these computers.
  • Students will also prepare a poster presentation for their final report, and it is suggested that the these posters be available for viewing in the dining hall as well as on the internet for several days prior to a general session in the dining hall when each group will be given time to respond to peer questions on their presentation.
  • It also should be obvious that individuals or groups may do further follow-up in-depth depth studies that would be appropriate as extended essay topics in any of the sciences. The amount of easily obtained data that we have at our fingertips here is potentially very great.

 


Pedder Bay as a Seasonal Estuary:

The distribution of the halocline, the freshwater-saltwater interface is quite pronounced at this time of year. It is easily determined by using the salinometer directly , or from samples collected and analysis in the lab. The halocline could have great variability in different parts of the bay- from head to mouth as well as side to side , and it could change in relatively short periods of time. It could be influenced by tidal cycles and there could be correlations made with rainfall. Also the mixing of water coming out of the river could have an effect on the salmon and bird habitat of the estuary. The Chemistry of all aspects of the sea water, pH, dissolved oxygen, nutrients could be examined. How well mixed is it or is there stratification. These factors determine life zones of the bay.

Bioluminescence in the Bay :

Timing , distribution , quantification of this phenomenon may be possible depending on conditions and time of year.

The Effect of Artificial Dock Lights on Organisms:

Experimentation with screening lights shining in the water to change intensity and color on the influence of the attraction of organisms would be possible.

Light Attenuation in the Water Column:

The visibility through the water column can be roughly measured by our Secchi Disk, a 50cm white disk which eventually disappears when lowered in the bay ( can be done from the docks) . It always has different depths of visibility if measured inside the bay versus the outer part. There is probably a very defined line in the outer bay where the visibility changes suddenly. A transect of measurements through this zone could give some interesting results.

There is another effect that we always note and that is large difference in plankton in the inner and outer bay areas. This difference is in species composition as well as population density. There is probably a correlation with several physical factors, the predominant one being the distance into the bay that the currents going by the outside of the bay actually penetrate, both laterally and at depth. This could be quantified and modeled.

Current Patterns in the Bay:

We often observe while diving that there is a counter-gyre at the mouth of the bay.. On an ebb tide, the water will come in along the south side of the bay as far as Fossil Point. turn north and flow out on the north side. This rotation may be the cause of the accumulation of the tide line drift flotsam in a tongue extending into the bay on some tidal exchanges. We have 10 buoys equipped with radar reflectors that can be used to accurately plot these current patterns. With Second Nature moored near fossil point, accurate trajectories of the drifters can be measured. There may be collaboration with people measuring plankton and turbidity levels to see if there are correlations of these factors.

What effect does the shape of the bay have on current velocities? Since the bay is generally half-funnel shaped, it should be possible to produce a mathematical model to predict the effect of shape on current speeds at different parts of the bay.

Effect of Boat Speed on Shoreline Wash:

Wave height, frequency and duration of inundation by shoreline species as the result of wash from boat traffic could be a significant factor in the Pedder bay ecosystem .

Wave Energy in Pedder Bay:

The shape,depth and orientation of Pedder Bay allows wave energy to have an effect on the different ecosystems within the bay. Calculations can be made for predicting Fetch and the effect it has on the widths of the bands of intertidal zonation.

Oil Pollution and Pedder Bay:

The very real possibility of some day having to cope with an oil spill in Pedder Bay is of some concern. We have recently been in consultation with Dr. Malcolm Hepworth who visited the college and introduced us to the idea of using Peat Pellets for oil spill cleanup. There is a possibility of doing small scale experimentation on the process of oil removal. Also there is a good opportunity here for extended essay follow up, and publication of useful research.

Chronic Oil Pollution In Pedder Bay:

The small amounts of oil residues from boat traffic is significant in some harbours. This oil can be collected by skimming with a commercially available absorbent material made for soaking up oil. Calculations of surface area covered by droplets of oils of various viscosity could also be measured. A survey of boat owners and bilge-pumping habits of their boats may also be revealing, and may help inform owners of alternate strategies.

Sedimentation and Sediment Dispersion related to Water Velocity

Cores of sediments taken on a line perpendicular to the shoreline might show a decline in sediment size or mass (easily measured by our particle Sieves and scales– screen size ranges from 4 millimeters to 40 microns available. Since sediment transport varies with current velocities, models about sediment deposition could be proposed and tested.

Some of the sediment is Biogenic ( barnacle shells), Carbon from old forest fires,

Anthropogenic: wood waste from log booms, erosion materials from the influence of human activities. Probably sedimentation rates could be calculated.

Terrigenous material, sediments from erosion further out at sea or along shorelines.

Glaciation Evidence on Pedder Bay Shorelines:

What is the extent of glacial evidence around the bay? There is a large conglomerate on fossil point,

granite boulders on Weir Point, glacial striations on bedrock around the bay. Calculations could be done on the forces required to transport these, and estimates of distances traveled could be made.

Alternate Energy Potential of Pedder Bay:

What is the volume of water that could be made to generate energy from Pedder Bay if a tidal barrage was installed at various locations in the bay ? What is the fresh water runoff potential if a dam was created on the Salmon Stream .

The Salmon Stream:

Since the stream is part of the input to the Pedder Bay system, it can be iuncluded in the study of the bay. Food webs in the stream, flow volumes of the river, temperature regime of the water as we go from early to late spring, these questions and more relating to this stream could be investigated. The waterfall itself has some potential for problems to be generated.

The Sewage System:

Both Biology and Environmental Systems students have already been through the part of the system that handles our liquid waste disposal. They have been made aware of the inputs and outputs of the system and the role of microorganisms in it’s treatment process.

Other areas to be pursued: Information is available on the model for dispersion of effluent from outfalls. There is a relationship between depth of the outfall and the rate of dispersal of coliform bacteria that is a bioindicator for sewage. Essentially a plume comes out that disperses like a cone . It could be hypothesized that the dispersal of this cone varies according to whether the tide is rising or falling, with a consequent ebb and flow of current. Samples of water taken at specific times and locations around the outfall could be used to test the model of dispersion.

  • Coliform bacteria can be cultured in the lab.
  • Fluorosceine is an effective dye for measure of dispersion. It can be added at the treatment plant. Possibly it could also be added in small increments directly into the outfall stream by a diver.

The outfall can be visited by diving and visual observations and measurements can be made.

In addition two other outfalls discharge into Pedder Bay: The Helgeson Point Outsell from the DND and the Pedder Bay Marina Outfall. Monitoring of dispersion of coliform could take place around those outfalls as well. Previous coliform tests by environmental systems labs have shown a higher occurrence of coliform in the vicinity of the Pedder Bay Marina itself.

Bird Life in Pedder Bay:

The bird population changes seasonally in the bay: several species of grebes, muralist, ducks and mergansers, as well as herons, kingfishers, buffleheads, scoters, and Rhinoceros auklets are residents . If the whole bay is considered as a bird habitat, it is likely that different species have different patterns of distribution. The locations of different bird populations , the timing and population levels of these and correlation to weather patterns has not been done. There is a concern that boat traffic, may already be impacting on these birds. In the future the specter of Sea-doos in the bay would no doubt seriously impact the birdlike. Some of the birds such as the Western Grebe, are one of the few bird species that nest on the Canadian Prairies and then overwinter in small protected bays. A good baseline study of these populations could be valuable for protecting them in the future.

The Cormorant Influence:

For the past four and a half years Cormorants have taken up roosting in the trees along the south side of Pedder Bay opposite the college. Recently we have referred to the presence of these birds as a major reason for seeking protection for that part of the forested strip from the possible effects of a campground and trail system proposed by the DND. At present there are no statistics on the actual number of birds using the site, the timing of their use and the effect of their use on the vegetation ( note: some Douglas fir are showing signs of crown death. ) It is possible that there is a considerable change going on in the soils of area with nutrients and acidification from droppings. A controlled study could be set up to monitor this .

Species Diversity:

There are a number of indices of species diversity available. Shannon, Simpson etc. Several sites could be chosen for a comparison of the effectiveness of these indices. Various ecosytems can be compared,: the fouling ecosystems on the dock skirt , the life on a square half-meter under the floats, distribution of algae relative to light levels, the rocky intertidal, the estuary plants or invertebrates, the tide lines on the small beaches ( abundant with amphipods).

Invertebrate and Algal Distribution and Biomass in the Intertidal zone:

Permanent monitoring plots could be established whereby weekly cropping of Fucus , the brown algae, could lead to productivity comparisons of different regions of the bay… Correlations may be established with many other factors. north South side exposure, inner-outer bay influence, etc. Several permanent reference pegs drilled in by our students several years ago already exist along the side of Pedder Bay. At fossil point we have past records which can be contrasted with present populations.

Ecological Succession:

For many years, the students of the environmental systems classes have collected data on succession of the diatom community on glass slides suspended in Pedder Bay. The same process can be used to test the effect of different substrates and different chemicals on succession . We do have one commercial preparation , a wax called easy net which can be spread on substrates for controlling succession of fouling organisms . There has been a great deal of research by chemical companies and the military into different chemical coatings and materials that can be used to retard organism growth. Slower growth means fuel savings for ship hulls going through water.

Invertebrate Attachments :

Bay mussels are abundant on the docks, their use of the Byssal thread, an elastic-like substance could be a subject of an interesting study. Tensile strengths of these threads from mussels of different exposures could be compared.

Invertebrate Dynamics:

A number of invertebrates are easily obtainable for various studies of physiology. . A few are listed here:

Sponge: filtration rates

Mussels: cilia beating patterns

Tube worms, contraction strength, speed of withdrawal, light sensitive.

Shrimp: transparency allows internal dynamics to be observed, temperature variation can affect heart rates.

Barnacles: calculations of water volume filtering when feeding.

Anemones: these have a primitive nerve net which responds to touch- measurement of reaction times possible.

Heart Cockle: Escape response speeds

Crabs: decorator crabs have some interesting behavior related to dressing themselves for camouflagewhen exposed to different materials.

Kelp growth studies:

The growth parameters of algae transplanted onto substrates suspended from the docks can make an interesting study. Bull kelp can grow several centimeters a day. Direct measurement of migration of punched holes in the lamina is one way for this study. Also the translocation of nutrients can be studied by the transmission of weak solutions of radionuclides supplied in one area of the lamina or leaf. Marine algae are also a good source of biogas for energy, can production rates be calculated.

Measuring Abiotic Factors In Pedder Bay

 

Using the Salinometer to record a salinity in a depth profile

At Lester Pearson College in the Marine Science/Environmental Systems classes, having the Bay handy as an outdoor lab enables us to always do several labs on quantifying the Abiotic factors in Pedder bay. Two students made up this post to explain what they were doing in class. 

Interview of Gavin by Cedar, September, 1996

lowering a collection bottle for samples at depth

Cedar: Why did you choose to go out to Pedder Bay?

Gavin: We went to learn how to use different tools to measure the abiotic factors in the bay.

Cedar: What exactly are abiotic factors?

Gavin: These are the physical factors which affect the system, ecosystem. for instance, the salinity of the water at different depths.

 

Cedar: What do you use to measure the salinity of the water?

Gavin: We used a salinometer connected to a probe which we lowered into the water.

Secchi disk being lowered for water transaparenccy measurement

Cedar: How do you measure the other abiotic factors and what tools do you use?

Gavin: To measure turbidity we use the secchi disc which is basically a 50cm diameter disc with lead weights attached. We lower the disk until it was just out of sight , bring it back into view and average the distance to estimate the point where it disappears. The disk is raised and measurements taken.

To measure pH we first take a sample using a water sampler , then use a portable pH meter.

 

 

 

 

Abiotic and Biotic factors being measured using a belt transect on a mudflat in Pedder Bay

Pedder Bay, British Columbia Wave Climate Study and Wave Protection Considerations

Pedder Bay, British Columbia-Wave Climate Study and Wave Protection Considerations

Final Report
( THE FIRST FEW PAGES ONLY ARE PRINTED. The COMPLETE VERSION IS AVAILABLE FROM FISHERIES AND OCEANS )

Prepared for: Government of Canada, Fisheries and Oceans

Prepared by: W.F. Baird & Associates Coastal Engineering Ltd.

Ottawa, Ontario

March 1991

TABLE OF CONTENTS

1.0 INTRODUCTION 1
2.0 SITE BATHYMETRY 2
3.0 WATER LEVELS 3
4.0 CURRENT DATA 5
5.0 WIND DATA 6
6.0 WIND-WAVE HINDCAST 11
7.0 PACIFIC OCEAN SWELL 17
8.0 RECORDED WAVE DATA 19
9.0 WAVE CONDITIONS AT THE PROPOSED SITE 20
10.0 SAMPLE BREAKWATER CROSS-SECTIONS 22
11.0 CONCLUSIONS AND RECOMMENDATION 24
REFERENCES

APPENDIX A – WIND DATA SUMMARIES

APPENDIX B – DEEP WATER WAVE HINDCAST SCATTER DIAGRAMS

APPENDIX C – WAVE HINDCAST SCATTER DIAGRAMS FOR THE LOCAL CLIMATE AT THE SITE

APPENDIX D – WAVE DIFFRACTION DIAGRAMS

APPENDIX E – RECORDED WAVE DATA

 

1.0 INTRODUCTION

The Department of National Defence (D.N.D.) is considering the expansion of the existing facilities and the construction of a new jetty at Canadian Forces Ammunition Depot (CFAD) Rocky Point located on Pedder Bay. British Columbia. Pedder Bay is situated at the southern end of Vancouver Island and is open to the southeast to Juan de Fuca Strait, as shown in Figure 1. 1. Figure 1. 2 shows a closer view of the existing bathymetry and facilities at the site.

The site is directly exposed to waves generated locally within Juan de Fuca Strait, particularly by winds from the east and southeast directions. In addition, the site is also partially subjected to long period swells that propagate through the Juan de Fuca Strait from the Pacific Ocean and diffract around the Rocky Point headlands into Pedder Bay.

The overall objectives of this investigation were to define the wave climate at the proposed site and to complete an initial assessment of wave protection requirements. Specific tasks that were undertaken included:

Assessment of possible wave protection requirements for the proposed harbour.

The results of this investigation are presented in the following sections of this report.

2.0 SITE BATHYMETRY

The water depths within Pedder Bay and the nearby portions of Juan de Fuca Strait is described on a series of charts produced by the Canadian Hydrographic: Service , Fisheries and Oceans Canada,

The underwater topography (bathymetry) within Pedder Bay, as shown in Figure 1.2, is fairly regular with water depths in excess of 20 m at the entrance to the bay. Much of the bay. east of Watt Point, has water depths of approximately 5 to 10 m. Depths along the existing DND jetty range from 6.5 m to 9.5 m according to a 1982 survey by CHS. A small series of shoals and emergent rocks are located on the north side of Pedder Bay directly opposite the jetty. The navigable water is indicated by buoys maintained by the DND.

The bathymetry within Juan de Fuca Strait in the vicinity of Pedder Bay is relatively deep, dropping off to 80 m or greater in a distance of 1000 m from the entrance to the bay. A prominent topographic feature to the south of the bay is an extensive series of shoals called the Race Rocks. These rocks have a direct effect on waves generated from the south and on long period swells propagating down Juan de Fuca Strait.

A hydrographic survey has been carried out in the area east and north of Fossil Point by Klohn Leonoff Ltd. (1990) for DND. An initial comparison of the results of this survey with previous surveys shows little change to the bathymetry in this area.

 

3.0 WATER LEVELS

Water level recorders near Pedder Bay have been located at Victoria and at Sooke Harbors. The Victoria gauge has been operating since 1909 and the Sooke gauge has been partially operational since 1973. Tides In the waters between Vancouver Island and the mainland vary considerably due to the presence of numerous islands and the complex bathymetry of this region. The tides at Sooke are mixed. mainly semi-diurnal (two high and two low waters in one day) while at Victoria the tides are mixed, mainly diurnal (one high and one low water in a day).

The mean water level at Pedder Bay Is estimated by Fisheries and Oceans Canada at 1.8 m above Chart Datum. Table 3.1 represents the tidal heights and extremes for Pedder Bay, Sooke and Victoria.

 

Table 3.1

Tidal Heights and Extremes

Height Above Chart Datum (metres)RECORDED

HHW LLW Mean LLW Mean HHW Mean Highest Lowest
Pedder Bay 3.3 0.2 2.5 0.6 1.8 N.A. N.A.
Sooke 3.6 0.3 2.8 0.8 1.9 3.8 0.2
Victoria 3.3 0.2 2.5 0.7 1.9 3.7 -0.5

Note: HHW = Higher High Water

LLW = Lower Low Water

Based on the above values, it is recommended that a maximum water level of +3.8 m be utilized for the design of any harbour structures. The mean water level of +1.8 m was utilized for all refraction and diffraction analyses.

Conversations with representatives of CHS have indicated that Geodetic Datum has not been extended to the Pedder Bay area: however, the recent survey by Klohn Leonoff Ltd.

(1990) shows a conversion between Geodetic and Chart Datum. This conversion is given

as: Elevation (Geodetic) = Elevation (Chart Datum) -1.878 m

4.0??CURRENT DATA

The tides flowing into and out of Juan de Fuca Strait create significant currents within the Strait. The magnitude of these currents depends on the size of the tide and may be considerably altered by the meteorological conditions.

Currents were measured four miles south of the Race Rocks in the centre of Juan de Fuca Strait, as shown in Figure 1. 1. On a typical large tide. the maximum tidal currents are approximately 1.5 m/s and 2.0 m/s for the flood (rising) and ebb (falling) tides, respectively.

The peak tidal currents within Pedder Bay Itself are not expected to be large enough. to significantly affect the piloting of vessels into a new facility due to the limited tidal volume contained within the Bay. Currents will, however, have some effect on the refraction of waves into Pedder Bay at certain times, as discussed in Section 6.2.

5

The Metchosin Biodiversity Strategy

PURPOSE: This draft document was prepared in the 1990s by local resident and International authority on Biodiversity Strategies, Robert Prescot Allen. Modifications and input from the Metchosin Advisory Commission and the students of the Environmental Systems class at Lester B. Pearson College have been included.  The purpose of the strategy is to enable the Council and residents of Metchosin to fulfill the commitments to conserve biodiversity as expressed in the Official Community Plan.

We welcome any comments and seek input on how this may be improved.


RATIONALE FOR A BIODIVERSITY STRATEGY FROM THE OCP:( Official Community Plan)

2.2.2 To promote the conservation of the biodiversity of the district – the variety of natural communities, native wild species and populations, and domesticated species and populations.

2.2.3 To maintain creeks, streams and inland wetlands in their natural state, by minimizing the impact of development.

2.2.4 To maintain uplands, forested lands and areas with old growth Douglas Fir in their natural state, by minimizing the impact of development.

2.2.5 To manage marine shorelands in a manner compatible with the biological and physical processes acting on and within them.

2.2.6 To identify and preserve sensitive natural environments for future generations and to maintain sufficient lands in their natural state so that rare and diverse plant and animal life will continue to exist and flourish.

2.2.9 To promote the restoration of marginal agricultural and /or previously degraded land to wildlife habitat.

Commitments to conserve biodiversity may also be found in the OCP’s general environmental policies and policies on lakes, creeks and streams; inland wetlands; marine shorelands; wildlife habitat; unique and attractive vegetation and tree cover.

The Garry-Oak Douglas fir zone is probably the most threatened ecological region in North America. It is restricted to southeastern Vancouver Island, The Gulf and San Juan Islands, The Puget trough and Willamette valley ( the rain shadow zone East of the mountains of Vancouver Island, Olympic peninsula and Washington/ Oregon Coast) Most of this zone has already been converted to farms and residential areas or has been heavily modified. Little natural Ecosystem remains. Municipalities that still have significant tracts of this ecological zone have something very valuable and unique. It is an obligation and service to the more urbanized municipalities and to future generations to maintain this heritage.


OBJECTIVES:

The ultimate objectives of this strategy are to:

  • Maintain viable populations of every species native to Metchosin.
  • Maintain viable samples of every natural community in Metchosin.
  • Initial priority will be given to species and natural communities that are endangered, threatened or rare nationally , provincially or regionally.

The Enabling Objectives of the strategy are to:

  1. Increase the number of residents who value native species and natural communities and are committed to conserving them.
  2. Increase social and economic incentives fore maintaining native species and natural communities.
  3. Increase legal support for maintaining native species and natural communities.
  4. Improve information on native species and natural communities of Metchosin and on introduced species that threaten them.
  5. Develop the Organizational capacity to maintain native species and natural communities.
  6. Obtain the resources required to maintain native species and natural communities.

VALUES:

Objective 1: Increase the number of residents who value native species and natural communities and are committed to conserving them.

  • Action: 1.1 Produce and distribute a leaflet describing the uniqueness and heritage value of the natural communities and native species of Metchosin.
  • Action 1.2 Prepare a high quality presentation on the uniqueness and heritage value of Metchosin’s native species and natural communities and the Biodiversity Strategy for Metchosin. This should be suitable for public gatherings and a TV presentation.
  • Action 1.3 Prepare and promote a “collaborative” style Internet site on Metchosin biodiversity, and the Biodiversity Strategy.
  • Action 1.4 Contact local schools to determine the extent of curricular involvement at present with Metchosin biodiversity. Enlist the help of teachers and students to contribute to identifying and promoting conservation of biodiversity.
  • Action 1.5 Prepare a demonstration booth for Metchosin Day which is designed to heighten public awareness on biodiversity issues of the community.
  • Action 1.6 Promote artistic performances on biodiversity themes to heighten awareness in the community.

INCENTIVES

Objective 2 : Increase social and economic incentives fore maintaining native species and natural communities.

  • Action 2.1 : Develop ways of increasing people’s self esteem and social standing if they do something to conserve native species and natural communities.
  • Institute community recognition of conservation efforts.
  • Encourage cooperation between neighbors to join up areas of greenspace.
  • Set time-lines for community achievement of greenspace designation .
  • Establish a high profile “community green map”.
  • Action 2.2 : Provide financial incentives (e.g. tax breaks) for maintaining native species and natural communities. Land dedicated to conserving native species and natural communities should be taxed at a rate low enough to encourage people to do so ( just as agricultural land is taxed at a favorable rate).

Recommended Steps: Draft a proposal

Council endorses proposal

Provincial government is lobbied to support the proposal

Lobby other municipalities to obtain support.

  • Action 2.2 : Provide financial incentives for restoration of degraded habitat. This could be done where there are agricultural areas overgrown with weedy species.

LAWS

Objective 3: Increase legal support for maintaining native species and natural communities

  • Action 3.1: Develop and implement an optimal zoning strategy for maintenance of native species and natural communities. Current zoning is not the most suitable for the conserving of biodiversity. A more flexible zoning system might help property owners dedicate land for conservation while meeting their economic priorities. The ecosystem unit should be taken into account when providing for subdivision or development. Certain ecosystem components must not be compromised if we are to maintain viable populations of native species.

Recommended steps: (I) Discuss what an optimal and achievable zoning system based on an ecosystem component approach would look like.

(ii) Prepare a proposal

(iii) Submit the proposal to Council and residents;

(iv) Amend the OCP and Land Use bylaw to accommodate biodiversity.

  • Action 3.2 Make available to property owners detailed information on the process of providing for covenants.

KNOWLEDGE

Objective 3: Improve information on native species and natural communities of Metchosin and on introduced species that threaten them.

  • Action 4.1 Prepare and maintain an inventory of native species and natural communities of Metchosin. This would be part of the Metchosin Environmental Inventory which has already been started.

Immediate needs:(i) Compile a list of native species (plants; vertebrates; macro-fungi)

(ii) Compile a list of natural communities

(iii) Identify native species of concern( endangered, threatened, rare)

(iv) Identify natural communities of concern (endangered, threatened, rare)

(v) Complete mapping of natural communities.

  • Action 4.2 Prepare a list of introduced species of concern ( i.e. that threaten native species or natural communities) and identify priority species for control.
  • Action 4.3 Identify a process for updating the inventories in order to keep information current.
  • Action 4.4 Involve all components of the community in the inventory process. Develop incentives for school children to contribute to the inventory.

ORGANIZATION

Objective 5: Improve information on native species and natural communities of Metchosin and on introduced species that threaten them.

  • Action 5.1 Form an organization of property owners and other individuals who will commit themselves to taking particular actions. (The Metchosin Organization on Biodiversity)
  • Action 5.2 Form an alliance with other community groups, service clubs, Environmental Organizations. Explain the strategy and enlist them as partners. Discuss what they and their members could do to develop and implement the strategy.
  • Action 5.3 Encourage and link up with similar activities in other municipalities.

RESOURCES

Objective 6: Obtain the resources required to maintain native species and natural communities.

  • Action 6.1 Prepare a budget for actions 1 through 6 . define preliminary targets for meeting the budget
  • Action 6.2 Ask council to commit itself to its share and front the money for actions 1.1 and 1.2 (required for fund raising and recruiting partners)
  • Action 6.3 Prepare and implement a plan to raise the balance of the budget.

SPECIAL ISSUES

Control of Introduced Species:

The introduced species that are of concern are those that because of their opportunistic nature, have a negative impact on native species and the re-establishment of native species.

  • Action 7.1 : Prepare and distribute to property owners a pamphlet emphasizing the importance of control of introduced species. Develop a recognition method for certification of areas that are free of introduced species.
  • Action 7.2 : Prepare priority plans for the removal of other introduced species that can destroy species diversity. Gray squirrels, starlings and rabbits may be appropriate candidates. Recognition may be made of some species, e.g. Blackberry that should be controlled in areas that could be rehabilitated with native species.
    For a reference on current research on Gray Squirrels see: This link. 
  • Action 7.3 : Encourage property owners to remove Scotch broom and gorse from their land. Develop an incentive scheme for broom eradication and restoration of native species.
  • Action 7.4.: The municipality of Metchosin will commit themselves to removing appropriate introduced species such as broom from their properties. Other public authorities, (e.g. BC Hydro) will be advised of the need for a control program .

Management of land to Encourage Native Species and Natural Communities.

  • Action 7.5 : Produce and distribute advice to landowners on ways they can manage their land to best encourage native species and natural communities.
  • Action 7.6 : Prepare and implement a plan for management of public lands, including right of ways, trails, to encourage native species, and to control introduced species.

PROTECTION:

  • Action 7.7 : Identify and protect by legislation priority areas in the municipality. Emphasis will be placed on the largest remaining intact areas of natural or near- natural ecosystems. Comprehensive management plans to ensure long-term protection must be done for each area.