SlideShare a Scribd company logo
1 of 4
Introduction
The presence or absence of Atlantic salmon (Salmo salar) in an ecosystem is an important
indicator of the general health of the broader aquatic system and the salmons’ high position in
the food chain makes its presence integral to the future conditions of the system (OMNR and
TRCA, 2005). As one of the most sensitive fish species in the watershed, the Atlantic salmon
is now extirpated in many regions of Ontario due to overfishing, pollution, habitat destruction
and the construction of dams and weirs preventing its migration (Ibid). In the Toronto region,
especially around the Humber River, human-made barriers have made it difficult for Atlantic
salmon to reach historic spawning grounds. Poor water quality from degraded areas along the
river (Ibid) has lead to a low success rate of about 20 percent in the wild (Fleming College,
Frost Campus, Fish Hatchery, 2011).
In the year 2000, 30 adult Atlantic salmon were released into the Humber River, some
with tags, in order to study interactions among salmon populations throughout the spawning
period and to assess spawning success (OMNR, 2002). However, over the winter many of the
embryos were unable to survive and the test results were inconclusive (Ibid). The
reintroduction of Atlantic salmon into the watershed would require stocking and attempts to
expand the range of other important fish species including walleye in order to ensure greater
success (OMNR and TRCA, 2005). The following study assesses why Atlantic salmon have a
lower success rate in the wild based on the health of the sample size in stock tanks.
This study focused on determining if there was a statistically significant difference
between the average length (in millimetres) and weight (in grams) of yearling Atlantic salmon
in Stock Tanks C1-C4 at the Fleming College, Frost Campus, Fish Hatchery. A sample size of
14 fish from each tank were measured by Ecosystem Monitoring and Assessment students.
Variables and control measures of the study will be discussed. The hatchery aims for a 70
percent success rate for release into the wild (Fleming College, Frost Campus, Fish Hatchery,
2011).
1
Discussion
At the Fleming College, Frost Campus Fish Hatchery, many factors were considered that
could affect the growth of the Atlantic salmon in the stock tanks. The most significant
variables were the changes in time of day, individuals performing the assessment, and the
particular day of the week. Every person undergoing the procedure has their own technique
for the assigned protocol. Varying experiences and knowledge may contribute to these
changes. In order for the results to be conclusive and without bias, the same protocol should
be followed, but this is quite difficult to ensure. Equipment variations such as problems with
the weight scale and the level of anaesthetic in parts per million will have a significant impact
on the final results. Personal technique has a considerable impact on the protocol as some
Atlantic salmon yearlings may have been placed in the fresh water and dried for varying
lengths of time which would affect the weight of the specimen. If a yearling was not fully
anaesthetized it made it much more difficult to record its length as it was still in motion. The
sample size remained consistent at 14, but the feeding schedule and quantity of feed affected
the yearlings’ weight so it was important to account for time of day relative to feeding. The
temperature of the water varied which may have affected oxygen levels. Fish density affected
the overall appearance and sometimes weight of specimen because of tank competition for
food and nipping of fins. Bin size and stock tank size are also factors.
As previously discussed, the two main factors of this study, length and weight, have
fluctuating variables that may alter the results of the study. The small sample size of 14
impacted the results of these variables because of low variability. The more reliable method
for indicating fish growth is its individual length as this measurement is less likely to change
than its weight. However, this is not to assume that the Atlantic salmon’s length is not
affected, as it is shaped by many factors such as sex, site, cohorts, or specific environment
(Chambers and Miller, 1995). The measured weight of Atlantic salmon in this experiment
showed much statistical variance most significantly based on feeding; time of day, amount of
food, and even temperature at time of feeding (Arnason, Papst, and Hopky, 1992). The
2
protocol and technique of those experimenting could also affect the weight, such as the length
of time the caught yearling was placed in the fresh water bath, as excess water could
contribute to the weight. Accurate reading of the weight scale, proper use of the scale, and
other factors affect the weight. Therefore, the weight of the Atlantic salmon is most likely
going to exhibit bias due to the many changing variables that could be represented in the
experiment. The best way to control for this is to monitor the time of day the experiment was
conducted relative to the time of feeding to control for variation. This shows that the most
conclusive results would be determined if all participants recorded their results at the same
time of the day while accounting for feeding time.
The difference between the average fish weight and the calculated bulk weight
rapid calculation is 59.58107143 grams for the former and 62.01785929 grams for the latter.
The bulk size should not be equal to but similar to the individual calculation and this is
reflected in the results. The results are different due to the changing variables that also exist
in this section. The protocol in which the assignment was exercised has the potential to alter
the results. The protocol needs to be followed precisely in order for the results to be the
same. The bulk weight rapid calculation measurement may be higher than the individual
measurements because of excess water content, technique including time spent in
anaesthetic, and time of day experiment was taken. Bulk weight could also be larger due to
exposure period and consumed food (Espmark and Baeverfjord, 2008).
Based on this study, it can be concluded that the Atlantic salmon remains an
important, yet sensitive, member of aquatic ecosystems. It should be noted that there were
many variables in this experiment, so a larger sample size might be the more conclusive
method for measurement. The results of this experiment can be used for further studies
about the survival rates of Atlantic salmon in the Sir Sandford Fleming College, Frost Campus,
Fish Hatchery based on the variables and control methods utilized in this exercise.
3
References:
Arnason A.N., Papst M.H., Hopky G.E. 1992. Modelling the Increase in Variation of Fish
Weight. Canadian Journal of Fisheries and Aquatic Sciences. Vol. 49, 1992 Feb 16.
Chambers R. Christopher, Miller Thomas J. 1995. Evaluating Fish Growth by Means of Otolith
Increment Analysis: Special Properties of Individual-Level Longitudinal Data. Recent
Developments in Otolith Research. Columbia, South Carolina: University of South Carolina
Press. p. 735.
Espmark Asa Maria, Baeverfjord Grete. 2008. Effects of hyperoxia on behavioural and
physiological variables in farmed Atlantic salmon (Salmo solar) parr. [online]. Available from:
http://www.springerlink.com/content/94053198753n1327/fulltext.pdf. Accessed: 2011 Feb 1.
Fleming College, Frost Campus, Fish Hatchery. 2011. Personal Communication.
Ontario Ministry of Natural Resources. 2002. Lake Ontario Fish Communities and Fisheries:
2002 Annual Report of the Lake Ontario Management Unit.
Ontario Ministry of Natural Resources and Toronto Regional Conservation Authority (OMNR
and TRCA). 2005. Fisheries Management Plan. [online]. Available from:
https://ozone.scholarsportal.info/bitstream/1873/1698/1/263253.pdf. Accessed: 2011 Jan
28.
4

More Related Content

What's hot

LAUER DenmanPosterFINAL
LAUER DenmanPosterFINALLAUER DenmanPosterFINAL
LAUER DenmanPosterFINAL
Marissa Lauer
 
Hidrodinamica Cardoso&motta marques 2009aeco
Hidrodinamica Cardoso&motta marques 2009aecoHidrodinamica Cardoso&motta marques 2009aeco
Hidrodinamica Cardoso&motta marques 2009aeco
Caline Gally
 
OhioAcademy2016_Poster.pptx (1)
OhioAcademy2016_Poster.pptx (1)OhioAcademy2016_Poster.pptx (1)
OhioAcademy2016_Poster.pptx (1)
Connor Gilmour
 
Final Report NRM 495 FINAL
Final Report NRM 495 FINALFinal Report NRM 495 FINAL
Final Report NRM 495 FINAL
Jared Sartini
 
Relationship_between_plasma_iron_concent
Relationship_between_plasma_iron_concentRelationship_between_plasma_iron_concent
Relationship_between_plasma_iron_concent
Tim Hoffland
 
EOU_2015_mini
EOU_2015_miniEOU_2015_mini
EOU_2015_mini
Kaisa V
 
EEB Group Ecology Report
EEB Group Ecology ReportEEB Group Ecology Report
EEB Group Ecology Report
Lisa Tripp
 
SCANU B129829-Final Project Report
SCANU B129829-Final Project ReportSCANU B129829-Final Project Report
SCANU B129829-Final Project Report
Simona Scanu
 
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
Steve Luell
 
SEA CUCUMBER IT-RYAN.I
SEA CUCUMBER IT-RYAN.ISEA CUCUMBER IT-RYAN.I
SEA CUCUMBER IT-RYAN.I
Ryan Ivarami
 

What's hot (20)

Detection of ecological impact of fine sediment inputs Overview of studies & ...
Detection of ecological impact of fine sediment inputs Overview of studies & ...Detection of ecological impact of fine sediment inputs Overview of studies & ...
Detection of ecological impact of fine sediment inputs Overview of studies & ...
 
Siltflux Leaflet
Siltflux LeafletSiltflux Leaflet
Siltflux Leaflet
 
Siltflux Workshop 1: Assessment of the impact of cattle access points on aqua...
Siltflux Workshop 1: Assessment of the impact of cattle access points on aqua...Siltflux Workshop 1: Assessment of the impact of cattle access points on aqua...
Siltflux Workshop 1: Assessment of the impact of cattle access points on aqua...
 
Jardine, t.d. et al, 2015
Jardine, t.d. et al, 2015Jardine, t.d. et al, 2015
Jardine, t.d. et al, 2015
 
Villegas-Ríos at the 2nd ICFT South Africa
Villegas-Ríos at the 2nd ICFT South AfricaVillegas-Ríos at the 2nd ICFT South Africa
Villegas-Ríos at the 2nd ICFT South Africa
 
LAUER DenmanPosterFINAL
LAUER DenmanPosterFINALLAUER DenmanPosterFINAL
LAUER DenmanPosterFINAL
 
Hidrodinamica Cardoso&motta marques 2009aeco
Hidrodinamica Cardoso&motta marques 2009aecoHidrodinamica Cardoso&motta marques 2009aeco
Hidrodinamica Cardoso&motta marques 2009aeco
 
OhioAcademy2016_Poster.pptx (1)
OhioAcademy2016_Poster.pptx (1)OhioAcademy2016_Poster.pptx (1)
OhioAcademy2016_Poster.pptx (1)
 
Final Report NRM 495 FINAL
Final Report NRM 495 FINALFinal Report NRM 495 FINAL
Final Report NRM 495 FINAL
 
Relationship_between_plasma_iron_concent
Relationship_between_plasma_iron_concentRelationship_between_plasma_iron_concent
Relationship_between_plasma_iron_concent
 
Mc bride, aundrea tribal habitat conference 2010 final
Mc bride, aundrea tribal habitat conference 2010 finalMc bride, aundrea tribal habitat conference 2010 final
Mc bride, aundrea tribal habitat conference 2010 final
 
Magurran estrutura comunidades
Magurran estrutura comunidadesMagurran estrutura comunidades
Magurran estrutura comunidades
 
EOU_2015_mini
EOU_2015_miniEOU_2015_mini
EOU_2015_mini
 
EEB Group Ecology Report
EEB Group Ecology ReportEEB Group Ecology Report
EEB Group Ecology Report
 
SCANU B129829-Final Project Report
SCANU B129829-Final Project ReportSCANU B129829-Final Project Report
SCANU B129829-Final Project Report
 
DE Poster Slide V4
DE Poster Slide V4DE Poster Slide V4
DE Poster Slide V4
 
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
New Jersey's voluntary collection program for bluefish (Pomatomus saltatrix)
 
OSMposter
OSMposterOSMposter
OSMposter
 
SWaRMA_IRBM_Module2_#4, Water ecosystem interaction, Susan Cuddy
SWaRMA_IRBM_Module2_#4, Water ecosystem interaction, Susan CuddySWaRMA_IRBM_Module2_#4, Water ecosystem interaction, Susan Cuddy
SWaRMA_IRBM_Module2_#4, Water ecosystem interaction, Susan Cuddy
 
SEA CUCUMBER IT-RYAN.I
SEA CUCUMBER IT-RYAN.ISEA CUCUMBER IT-RYAN.I
SEA CUCUMBER IT-RYAN.I
 

Viewers also liked

Viewers also liked (11)

Manual emociones def
Manual emociones defManual emociones def
Manual emociones def
 
Smith Property Restoration Project.doc
Smith Property Restoration Project.docSmith Property Restoration Project.doc
Smith Property Restoration Project.doc
 
绣花线电子画册
绣花线电子画册绣花线电子画册
绣花线电子画册
 
Comprender las emociones
Comprender las emocionesComprender las emociones
Comprender las emociones
 
Cod Paper
Cod PaperCod Paper
Cod Paper
 
Port Hope Uranium
Port Hope UraniumPort Hope Uranium
Port Hope Uranium
 
Pepperで翻訳ソフトを作ってみた
Pepperで翻訳ソフトを作ってみたPepperで翻訳ソフトを作ってみた
Pepperで翻訳ソフトを作ってみた
 
Inteligencia emocional3
Inteligencia emocional3Inteligencia emocional3
Inteligencia emocional3
 
Neuropsicolog a de_las_emociones
Neuropsicolog a de_las_emocionesNeuropsicolog a de_las_emociones
Neuropsicolog a de_las_emociones
 
PepperとWatson音声関連API
PepperとWatson音声関連APIPepperとWatson音声関連API
PepperとWatson音声関連API
 
Sentimientos y emociones
Sentimientos y emocionesSentimientos y emociones
Sentimientos y emociones
 

Similar to Atlantic Salmon

Salmon Paper draft 4
Salmon Paper draft 4Salmon Paper draft 4
Salmon Paper draft 4
Taylor Luneau
 
Little Lagoon Oysters
Little Lagoon OystersLittle Lagoon Oysters
Little Lagoon Oysters
mayrebecca
 
3.Environmental variability at a marine cage culture.pdf
3.Environmental variability at a marine cage culture.pdf3.Environmental variability at a marine cage culture.pdf
3.Environmental variability at a marine cage culture.pdf
earambulm3
 
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
Muriel Magnaye
 
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
Innspub Net
 
Helen Oglesby - Project Presentation
Helen Oglesby - Project Presentation Helen Oglesby - Project Presentation
Helen Oglesby - Project Presentation
Helen Oglesby
 
Research Progress Report Table Adjust answer box size as necessar.docx
Research Progress Report Table Adjust answer box size as necessar.docxResearch Progress Report Table Adjust answer box size as necessar.docx
Research Progress Report Table Adjust answer box size as necessar.docx
ronak56
 

Similar to Atlantic Salmon (20)

The influence of estuarine habitats on the expression of life history of char...
The influence of estuarine habitats on the expression of life history of char...The influence of estuarine habitats on the expression of life history of char...
The influence of estuarine habitats on the expression of life history of char...
 
Salmon Paper draft 4
Salmon Paper draft 4Salmon Paper draft 4
Salmon Paper draft 4
 
Little Lagoon Oysters
Little Lagoon OystersLittle Lagoon Oysters
Little Lagoon Oysters
 
Term Paper1
Term Paper1Term Paper1
Term Paper1
 
Effect of Temperature and salinity change in metabolic.pptx
Effect of Temperature and salinity change in metabolic.pptxEffect of Temperature and salinity change in metabolic.pptx
Effect of Temperature and salinity change in metabolic.pptx
 
Silvercup Fish Food Manual
Silvercup Fish Food ManualSilvercup Fish Food Manual
Silvercup Fish Food Manual
 
Comparison of Fatty acids profile of Marine species off Namibia
Comparison of Fatty acids profile of Marine species off NamibiaComparison of Fatty acids profile of Marine species off Namibia
Comparison of Fatty acids profile of Marine species off Namibia
 
2016-Etroplus sur-IJFAStudies
2016-Etroplus sur-IJFAStudies2016-Etroplus sur-IJFAStudies
2016-Etroplus sur-IJFAStudies
 
Methods of stomach contetn analyses of fishes
Methods of stomach contetn analyses of fishesMethods of stomach contetn analyses of fishes
Methods of stomach contetn analyses of fishes
 
2016-Mugil cep IJFAS-June
2016-Mugil cep IJFAS-June2016-Mugil cep IJFAS-June
2016-Mugil cep IJFAS-June
 
2016-Mugil cep IJFAS-June
2016-Mugil cep IJFAS-June2016-Mugil cep IJFAS-June
2016-Mugil cep IJFAS-June
 
Disturbance of benthic algae by spawning Pacific salmon in Thompson Creek, MI
Disturbance of benthic algae by spawning Pacific salmon in Thompson Creek, MIDisturbance of benthic algae by spawning Pacific salmon in Thompson Creek, MI
Disturbance of benthic algae by spawning Pacific salmon in Thompson Creek, MI
 
3.Environmental variability at a marine cage culture.pdf
3.Environmental variability at a marine cage culture.pdf3.Environmental variability at a marine cage culture.pdf
3.Environmental variability at a marine cage culture.pdf
 
Fishery-induced Changes in Pacific Ecosystem
Fishery-induced Changes in Pacific EcosystemFishery-induced Changes in Pacific Ecosystem
Fishery-induced Changes in Pacific Ecosystem
 
RESEARCH ON NUTRITIVE COMPOSITION OF FISH
RESEARCH ON NUTRITIVE COMPOSITION OF FISHRESEARCH ON NUTRITIVE COMPOSITION OF FISH
RESEARCH ON NUTRITIVE COMPOSITION OF FISH
 
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
Repeat and skipped spawning in capelin (Mallotus villosus) on the easter Newf...
 
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
Feeding rate requirements for Schilbe intermedius (Rüppel, 1832) fingerlings ...
 
Helen Oglesby - Project Presentation
Helen Oglesby - Project Presentation Helen Oglesby - Project Presentation
Helen Oglesby - Project Presentation
 
Research Progress Report Table Adjust answer box size as necessar.docx
Research Progress Report Table Adjust answer box size as necessar.docxResearch Progress Report Table Adjust answer box size as necessar.docx
Research Progress Report Table Adjust answer box size as necessar.docx
 
Grimaldo Salvage
Grimaldo SalvageGrimaldo Salvage
Grimaldo Salvage
 

Atlantic Salmon

  • 1. Introduction The presence or absence of Atlantic salmon (Salmo salar) in an ecosystem is an important indicator of the general health of the broader aquatic system and the salmons’ high position in the food chain makes its presence integral to the future conditions of the system (OMNR and TRCA, 2005). As one of the most sensitive fish species in the watershed, the Atlantic salmon is now extirpated in many regions of Ontario due to overfishing, pollution, habitat destruction and the construction of dams and weirs preventing its migration (Ibid). In the Toronto region, especially around the Humber River, human-made barriers have made it difficult for Atlantic salmon to reach historic spawning grounds. Poor water quality from degraded areas along the river (Ibid) has lead to a low success rate of about 20 percent in the wild (Fleming College, Frost Campus, Fish Hatchery, 2011). In the year 2000, 30 adult Atlantic salmon were released into the Humber River, some with tags, in order to study interactions among salmon populations throughout the spawning period and to assess spawning success (OMNR, 2002). However, over the winter many of the embryos were unable to survive and the test results were inconclusive (Ibid). The reintroduction of Atlantic salmon into the watershed would require stocking and attempts to expand the range of other important fish species including walleye in order to ensure greater success (OMNR and TRCA, 2005). The following study assesses why Atlantic salmon have a lower success rate in the wild based on the health of the sample size in stock tanks. This study focused on determining if there was a statistically significant difference between the average length (in millimetres) and weight (in grams) of yearling Atlantic salmon in Stock Tanks C1-C4 at the Fleming College, Frost Campus, Fish Hatchery. A sample size of 14 fish from each tank were measured by Ecosystem Monitoring and Assessment students. Variables and control measures of the study will be discussed. The hatchery aims for a 70 percent success rate for release into the wild (Fleming College, Frost Campus, Fish Hatchery, 2011). 1
  • 2. Discussion At the Fleming College, Frost Campus Fish Hatchery, many factors were considered that could affect the growth of the Atlantic salmon in the stock tanks. The most significant variables were the changes in time of day, individuals performing the assessment, and the particular day of the week. Every person undergoing the procedure has their own technique for the assigned protocol. Varying experiences and knowledge may contribute to these changes. In order for the results to be conclusive and without bias, the same protocol should be followed, but this is quite difficult to ensure. Equipment variations such as problems with the weight scale and the level of anaesthetic in parts per million will have a significant impact on the final results. Personal technique has a considerable impact on the protocol as some Atlantic salmon yearlings may have been placed in the fresh water and dried for varying lengths of time which would affect the weight of the specimen. If a yearling was not fully anaesthetized it made it much more difficult to record its length as it was still in motion. The sample size remained consistent at 14, but the feeding schedule and quantity of feed affected the yearlings’ weight so it was important to account for time of day relative to feeding. The temperature of the water varied which may have affected oxygen levels. Fish density affected the overall appearance and sometimes weight of specimen because of tank competition for food and nipping of fins. Bin size and stock tank size are also factors. As previously discussed, the two main factors of this study, length and weight, have fluctuating variables that may alter the results of the study. The small sample size of 14 impacted the results of these variables because of low variability. The more reliable method for indicating fish growth is its individual length as this measurement is less likely to change than its weight. However, this is not to assume that the Atlantic salmon’s length is not affected, as it is shaped by many factors such as sex, site, cohorts, or specific environment (Chambers and Miller, 1995). The measured weight of Atlantic salmon in this experiment showed much statistical variance most significantly based on feeding; time of day, amount of food, and even temperature at time of feeding (Arnason, Papst, and Hopky, 1992). The 2
  • 3. protocol and technique of those experimenting could also affect the weight, such as the length of time the caught yearling was placed in the fresh water bath, as excess water could contribute to the weight. Accurate reading of the weight scale, proper use of the scale, and other factors affect the weight. Therefore, the weight of the Atlantic salmon is most likely going to exhibit bias due to the many changing variables that could be represented in the experiment. The best way to control for this is to monitor the time of day the experiment was conducted relative to the time of feeding to control for variation. This shows that the most conclusive results would be determined if all participants recorded their results at the same time of the day while accounting for feeding time. The difference between the average fish weight and the calculated bulk weight rapid calculation is 59.58107143 grams for the former and 62.01785929 grams for the latter. The bulk size should not be equal to but similar to the individual calculation and this is reflected in the results. The results are different due to the changing variables that also exist in this section. The protocol in which the assignment was exercised has the potential to alter the results. The protocol needs to be followed precisely in order for the results to be the same. The bulk weight rapid calculation measurement may be higher than the individual measurements because of excess water content, technique including time spent in anaesthetic, and time of day experiment was taken. Bulk weight could also be larger due to exposure period and consumed food (Espmark and Baeverfjord, 2008). Based on this study, it can be concluded that the Atlantic salmon remains an important, yet sensitive, member of aquatic ecosystems. It should be noted that there were many variables in this experiment, so a larger sample size might be the more conclusive method for measurement. The results of this experiment can be used for further studies about the survival rates of Atlantic salmon in the Sir Sandford Fleming College, Frost Campus, Fish Hatchery based on the variables and control methods utilized in this exercise. 3
  • 4. References: Arnason A.N., Papst M.H., Hopky G.E. 1992. Modelling the Increase in Variation of Fish Weight. Canadian Journal of Fisheries and Aquatic Sciences. Vol. 49, 1992 Feb 16. Chambers R. Christopher, Miller Thomas J. 1995. Evaluating Fish Growth by Means of Otolith Increment Analysis: Special Properties of Individual-Level Longitudinal Data. Recent Developments in Otolith Research. Columbia, South Carolina: University of South Carolina Press. p. 735. Espmark Asa Maria, Baeverfjord Grete. 2008. Effects of hyperoxia on behavioural and physiological variables in farmed Atlantic salmon (Salmo solar) parr. [online]. Available from: http://www.springerlink.com/content/94053198753n1327/fulltext.pdf. Accessed: 2011 Feb 1. Fleming College, Frost Campus, Fish Hatchery. 2011. Personal Communication. Ontario Ministry of Natural Resources. 2002. Lake Ontario Fish Communities and Fisheries: 2002 Annual Report of the Lake Ontario Management Unit. Ontario Ministry of Natural Resources and Toronto Regional Conservation Authority (OMNR and TRCA). 2005. Fisheries Management Plan. [online]. Available from: https://ozone.scholarsportal.info/bitstream/1873/1698/1/263253.pdf. Accessed: 2011 Jan 28. 4