SlideShare a Scribd company logo
The Priming Effect:
Discovering the future
of lake carbon cycling
Cassie Craig
Mentor: Jake Zwart
Lakes
 Lakes have recently been recognized as important
components of the global carbon cycle.
 Leaves can fall into lakes and dissolve into the water
column that contain carbon and can alter the internal
carbon cycle.
 CO2 emission from inland lakes is very similar to the
CO2 uptake in the ocean and therefore has the same
effect on the atmosphere.
What is the priming effect?
 When labile organic matter (LOM) such as glucose,
cellouse, or root exudates are in the soil…
 It changes the mineralization rate of recalcitrant organic
matter (ROM) present…
 Therefore altering the amount of CO2 released in the
atmosphere.
 Priming effect can enhance the recalcitrant organic
matter mineralization rate anywhere from 10% to
500%.
Priming Effect
 This all meaning that labile carbon (carbon that is easily broken down
from phytoplankton in aquatic systems) increases the rate that
bacteria breaks down recalcitrant carbon (carbon that is hard to break
down and comes from terrestrial sources such as trees.
Positive or Negative
 It is found that the priming effect could have negative
and positive effects.
 A negative effect is…
 the labile organic matter decreasing recalcitrant organic
matter mineralization rate
 A positive effect is...
 labile organic matter (LOM) can increase recalcitrant
organic matter (ROM) mineralization rate.
(Guenet et al. 2010).
Importance
 Significant findings for understanding current and
predicting future lake carbon cycling.
 Also changing our view of how lakes fit into the global
carbon cycle.
 There has not been much research on the importance
and mechanisms of the priming effect.
 Some scientists do not believe it even exists in aquatic
ecosystems.
Hypothesis
 That higher amount of labile carbon (glucose), the
higher the rate will be of recalcitrant carbon being
broke down, increasing the amount of CO2 into the
atmosphere.
Methods
 Lake water was collected from five lakes on UNDERC
property in the Upper Peninsula Michigan.
 1. East Long
 2. West Long
 3. Hummingbird
 4. Crampton
 5. Morris
Methods Cont..
 The lake water was filtered through 0.2 µm filters to remove
any bacteria from the water.
 Leaving dissolved organic carbon behind with 100 mL of
lake water used in each incubation bottle.
Methods Cont..
 Glucose was used as the source of labile organic
matter.
 Four treatment groups per lake: 0.25, 1.0, 2.25, and 4.0
mg of glucose
 One control treatment for each lake. (no glucose)
 One glucose control treatment per lake. (no lake water)
 Three replicates for each treatment.
Methods Cont..
 All treatments had 1 mL of unfiltered lake water added
as the source of natural lake bacteria.
 Headspace gas from each sample was extracted five
times during the incubation after every 5 days and
analyzed on a gas chromatograph to see how much
CH4 and CO2 was released.
 Another round of glucose was added in the second
week to stimulate a pulse of fresh labile carbon.
 This reflects what would happen in a lake with a
phytoplankton bloom.
Results
0
1000
2000
3000
4000
5000
6000
1 2 3 4 5
Respiration
Week
MO Control Cumulative
MO 0.25 Cumulative
MO 1.0 Cumulative
MO 2.25 Cumulative
MO 4.0 Cumulative
ANOVA Test on Slopes
 Morris overall had a p-value of 0.0246
 Within the treatments, only the control and the 4.0 mg
of glucose were statically different in their slopes of
carbon respired.
 p-value of 0.0194313
ANOVA Test on Respiration
 Morris overall had a p-value significant at 0.01617.
 The respiration rate that was statically different was
between the treatment groups of the control and 4.0
mg.
0
500
1000
1500
2000
2500
3000
1 2 3 4 5
Respiration
Week
EL Control Cumulative
EL 0.25 Cumulative
EL 1.0 Cumulative
EL 2.25 Cumulative
EL 4.0 Cumulative
ANOVA test on Slopes
 East Long slopes overall showed were significant at a
p-value of 0.00555.
 The treatments that were statically different from one
another was 2.25 and 0.25 with a p-value of 0.0448610
ANOVA Test on Respiration
 East Long overall was significant at 0.125
 The respiration rate that was statically different was
between the treatment groups was the control and 1.0
mg.
0
500
1000
1500
2000
2500
3000
3500
4000
4500
1 2 3 4 5
Respiration
Week
WL Control Cumulative
WL 0.25 Cumulative
WL 1.0 Cumulative
WL 2.25 Cumulative
WL 4.0 Cumulative
ANOVA Test on Slopes
 West Long overall had a significant p value at 0.00509.
 Within in West Long, the treatment slopes that were
statistically different from each other were…
 4.0 mg and 0.25 at a p-value of 0.0588166.
 The control and 2.25 with a p-value at 0.02434633.
 The control and 4.0 mg at a p-value of 0.0037442.
ANOVA Test on Respiration
 West Long was significant overall at 0.00138.
 The respiration rate that was statically significant was
between…
 The control and 0.25 mg at a p-value of 0.0035390
 The control and 4.0 mg at a p-value 0.0011113.
0
500
1000
1500
2000
2500
3000
3500
4000
1 2 3 4 5
Respiration
Week
HB Control Cumulative
HB 0.25 Cumulative
HB 1.0 Cumulative
HB 2.25 Cumulative
HB 4.0 Cumulative
ANOVA Test on Slopes
 Overall the slopes of Hummingbird were not statistically
significant.
 p-value of 0.162
 None of the treatment groups in that lake were
statistically different from one another.
ANOVA Test on Respiration
 Hummingbird respiration values overall were not
statically significant.
 p-value of 0.262.
 The treatment groups compared to one another
showed no significance as well.
0
200
400
600
800
1000
1200
1400
1600
1800
2000
1 2 3 4 5
Respiration
Time
CR Control Cumulative
CR 0.25 Cumulative
CR 1.0 Cumulative
CR 2.25 Cumulative
CR 4.0 Cumulative
ANOVA Test on Slopes
 Overall the slopes of Crampton were not statistically
significant
 p-value of 0.134.
 None one of the treatment groups in that lake were
statistically different from one another.
ANOVA Test on Respiration
 Cramptons’ respiration values overall were not
statically significant.
 p-value of and 0.147.
 The treatment groups compared to one another
showed no significance as well.
Conclusion
 The results of this experiment supported the hypothesis
that stated that the higher amount of labile carbon
(glucose), the higher the rate of recalcitrant carbon
being broke down there would be, increasing the
amount of CO2 into the atmosphere.
 The priming effect does exist in aquatic environments.
 Further tested whether the contents of the lakes had an
effect on how much CO2 was released such as the
nutrients present.
References
 Attermeyer, K., Hornick, T., Kayler, Z. E., Bahr, A., Zwirnmann, E.,
Grossart, H.-P., and Premke, K. 2014. Enhanced bacterial
decomposition with increasing addition of autochthonous to
allochthonous carbon without any effect on bacterial community
composition, Biogeosciences, 11, 1479-1489, doi:10.5194/bg-11-
1479-2014.
 Guenet B, Michael Danger, Luc Abbadie, and Gérard Lacroix
2010. Priming effect: bridging the gap between terrestrial and
aquatic ecology. Ecology 91:2850–2861. doi.org/10.1890/09-
1968.1
 Tranviket Lars J. et.al. 2009. Lakes and reservoirs as regulators of
carbon cycling and climate. Limnology and Oceanography, 54 part
2, 2298-2314. 10.4319/lo.2009.54.6_part_2.2298
Questions?

More Related Content

Viewers also liked

Chapter 5 (part2) enzymes - michaelis-menton kinetics
Chapter 5 (part2)   enzymes - michaelis-menton kineticsChapter 5 (part2)   enzymes - michaelis-menton kinetics
Chapter 5 (part2) enzymes - michaelis-menton kinetics
Ammedicine Medicine
 
Plant defenses
Plant defensesPlant defenses
Plant defenses
heman568
 
Structural defence mechanism in plants
Structural defence mechanism in plantsStructural defence mechanism in plants
Structural defence mechanism in plants
raichur agri
 
Molecular basis of plant resistance and defense responses to pathogens
Molecular basis of plant resistance and defense responses to pathogensMolecular basis of plant resistance and defense responses to pathogens
Molecular basis of plant resistance and defense responses to pathogens
Senthil Natesan
 
How Plants defend themselves against pathogens.
How Plants defend themselves against pathogens.How Plants defend themselves against pathogens.
How Plants defend themselves against pathogens.
Zohaib Hassan
 
Plant Pathogen Interaction
Plant Pathogen InteractionPlant Pathogen Interaction
Plant Pathogen Interaction
poojamaggi
 
Bacterial secretion
Bacterial secretionBacterial secretion
Bacterial secretion
Dr.B.V. Ramana
 
Slideshare ppt
Slideshare pptSlideshare ppt
Slideshare ppt
Mandy Suzanne
 

Viewers also liked (8)

Chapter 5 (part2) enzymes - michaelis-menton kinetics
Chapter 5 (part2)   enzymes - michaelis-menton kineticsChapter 5 (part2)   enzymes - michaelis-menton kinetics
Chapter 5 (part2) enzymes - michaelis-menton kinetics
 
Plant defenses
Plant defensesPlant defenses
Plant defenses
 
Structural defence mechanism in plants
Structural defence mechanism in plantsStructural defence mechanism in plants
Structural defence mechanism in plants
 
Molecular basis of plant resistance and defense responses to pathogens
Molecular basis of plant resistance and defense responses to pathogensMolecular basis of plant resistance and defense responses to pathogens
Molecular basis of plant resistance and defense responses to pathogens
 
How Plants defend themselves against pathogens.
How Plants defend themselves against pathogens.How Plants defend themselves against pathogens.
How Plants defend themselves against pathogens.
 
Plant Pathogen Interaction
Plant Pathogen InteractionPlant Pathogen Interaction
Plant Pathogen Interaction
 
Bacterial secretion
Bacterial secretionBacterial secretion
Bacterial secretion
 
Slideshare ppt
Slideshare pptSlideshare ppt
Slideshare ppt
 

Similar to Priming Effect Presentation

Be 4101 project
Be 4101 projectBe 4101 project
Be 4101 project
TyWilliams24
 
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
Jonathan Damora
 
Animal physiology and biochemistry lab manual
Animal physiology and biochemistry lab manualAnimal physiology and biochemistry lab manual
Animal physiology and biochemistry lab manual
Vidya Kalaivani Rajkumar
 
Effects of Acid on Chlorophyll Production of Common
Effects of Acid on Chlorophyll Production of CommonEffects of Acid on Chlorophyll Production of Common
Effects of Acid on Chlorophyll Production of Common
Corinne Breymeier
 
Montana_Weitzel_LehighinIreland_FinalReport
Montana_Weitzel_LehighinIreland_FinalReportMontana_Weitzel_LehighinIreland_FinalReport
Montana_Weitzel_LehighinIreland_FinalReport
Montana Weitzel
 
Study of removal effect on mesocycops leukarti
Study of removal effect on mesocycops leukartiStudy of removal effect on mesocycops leukarti
Study of removal effect on mesocycops leukarti
ricguer
 
Lee Wonjae, Extended Essay
Lee Wonjae, Extended EssayLee Wonjae, Extended Essay
Lee Wonjae, Extended Essay
Wonjae Lee
 
Corinne Breymeier Poster
Corinne Breymeier PosterCorinne Breymeier Poster
Corinne Breymeier Poster
Corinne Breymeier
 
Photosynthesis and environment.pptx
Photosynthesis and environment.pptxPhotosynthesis and environment.pptx
Photosynthesis and environment.pptx
Maddalena16
 
Determination of p h of waste water sample .....................................
Determination of p h of waste water sample .....................................Determination of p h of waste water sample .....................................
Determination of p h of waste water sample .....................................
Hafiz M Waseem
 
Microbiological studies on the wastewater treatment and agricultural fertil...
Microbiological studies on the wastewater treatment and   agricultural fertil...Microbiological studies on the wastewater treatment and   agricultural fertil...
Microbiological studies on the wastewater treatment and agricultural fertil...
Mohamed Younes
 
Environmental Health Presentation
Environmental Health PresentationEnvironmental Health Presentation
Environmental Health Presentation
Kaitlin Zwingert
 
Nitrogen Transformations in Aquaponic Systems
Nitrogen Transformations in Aquaponic SystemsNitrogen Transformations in Aquaponic Systems
Nitrogen Transformations in Aquaponic Systems
National Institute of Food and Agriculture
 
Applications of Algal Technology on a Martian Colony
Applications of Algal Technology on a Martian ColonyApplications of Algal Technology on a Martian Colony
Applications of Algal Technology on a Martian Colony
EricStephens26
 
Applications of Algal Technology for a Martian Colony *Fixed*
Applications of Algal Technology for a Martian Colony *Fixed*Applications of Algal Technology for a Martian Colony *Fixed*
Applications of Algal Technology for a Martian Colony *Fixed*
EricStephens26
 
A water quality field study 2010
A water quality field study 2010A water quality field study 2010
A water quality field study 2010
pauleyler
 
BIO LAB PRESENTATION (1)
BIO LAB PRESENTATION (1)BIO LAB PRESENTATION (1)
BIO LAB PRESENTATION (1)
Garrett Hess
 
Fitzgerald_poster
Fitzgerald_posterFitzgerald_poster
Fitzgerald_poster
Michaela Fitzgerald
 

Similar to Priming Effect Presentation (18)

Be 4101 project
Be 4101 projectBe 4101 project
Be 4101 project
 
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
Water Analysis through High Performance Liquid Chromotography, Ion Exchange R...
 
Animal physiology and biochemistry lab manual
Animal physiology and biochemistry lab manualAnimal physiology and biochemistry lab manual
Animal physiology and biochemistry lab manual
 
Effects of Acid on Chlorophyll Production of Common
Effects of Acid on Chlorophyll Production of CommonEffects of Acid on Chlorophyll Production of Common
Effects of Acid on Chlorophyll Production of Common
 
Montana_Weitzel_LehighinIreland_FinalReport
Montana_Weitzel_LehighinIreland_FinalReportMontana_Weitzel_LehighinIreland_FinalReport
Montana_Weitzel_LehighinIreland_FinalReport
 
Study of removal effect on mesocycops leukarti
Study of removal effect on mesocycops leukartiStudy of removal effect on mesocycops leukarti
Study of removal effect on mesocycops leukarti
 
Lee Wonjae, Extended Essay
Lee Wonjae, Extended EssayLee Wonjae, Extended Essay
Lee Wonjae, Extended Essay
 
Corinne Breymeier Poster
Corinne Breymeier PosterCorinne Breymeier Poster
Corinne Breymeier Poster
 
Photosynthesis and environment.pptx
Photosynthesis and environment.pptxPhotosynthesis and environment.pptx
Photosynthesis and environment.pptx
 
Determination of p h of waste water sample .....................................
Determination of p h of waste water sample .....................................Determination of p h of waste water sample .....................................
Determination of p h of waste water sample .....................................
 
Microbiological studies on the wastewater treatment and agricultural fertil...
Microbiological studies on the wastewater treatment and   agricultural fertil...Microbiological studies on the wastewater treatment and   agricultural fertil...
Microbiological studies on the wastewater treatment and agricultural fertil...
 
Environmental Health Presentation
Environmental Health PresentationEnvironmental Health Presentation
Environmental Health Presentation
 
Nitrogen Transformations in Aquaponic Systems
Nitrogen Transformations in Aquaponic SystemsNitrogen Transformations in Aquaponic Systems
Nitrogen Transformations in Aquaponic Systems
 
Applications of Algal Technology on a Martian Colony
Applications of Algal Technology on a Martian ColonyApplications of Algal Technology on a Martian Colony
Applications of Algal Technology on a Martian Colony
 
Applications of Algal Technology for a Martian Colony *Fixed*
Applications of Algal Technology for a Martian Colony *Fixed*Applications of Algal Technology for a Martian Colony *Fixed*
Applications of Algal Technology for a Martian Colony *Fixed*
 
A water quality field study 2010
A water quality field study 2010A water quality field study 2010
A water quality field study 2010
 
BIO LAB PRESENTATION (1)
BIO LAB PRESENTATION (1)BIO LAB PRESENTATION (1)
BIO LAB PRESENTATION (1)
 
Fitzgerald_poster
Fitzgerald_posterFitzgerald_poster
Fitzgerald_poster
 

Priming Effect Presentation

  • 1. The Priming Effect: Discovering the future of lake carbon cycling Cassie Craig Mentor: Jake Zwart
  • 2. Lakes  Lakes have recently been recognized as important components of the global carbon cycle.  Leaves can fall into lakes and dissolve into the water column that contain carbon and can alter the internal carbon cycle.  CO2 emission from inland lakes is very similar to the CO2 uptake in the ocean and therefore has the same effect on the atmosphere.
  • 3. What is the priming effect?  When labile organic matter (LOM) such as glucose, cellouse, or root exudates are in the soil…  It changes the mineralization rate of recalcitrant organic matter (ROM) present…  Therefore altering the amount of CO2 released in the atmosphere.  Priming effect can enhance the recalcitrant organic matter mineralization rate anywhere from 10% to 500%.
  • 4. Priming Effect  This all meaning that labile carbon (carbon that is easily broken down from phytoplankton in aquatic systems) increases the rate that bacteria breaks down recalcitrant carbon (carbon that is hard to break down and comes from terrestrial sources such as trees.
  • 5. Positive or Negative  It is found that the priming effect could have negative and positive effects.  A negative effect is…  the labile organic matter decreasing recalcitrant organic matter mineralization rate  A positive effect is...  labile organic matter (LOM) can increase recalcitrant organic matter (ROM) mineralization rate. (Guenet et al. 2010).
  • 6. Importance  Significant findings for understanding current and predicting future lake carbon cycling.  Also changing our view of how lakes fit into the global carbon cycle.  There has not been much research on the importance and mechanisms of the priming effect.  Some scientists do not believe it even exists in aquatic ecosystems.
  • 7. Hypothesis  That higher amount of labile carbon (glucose), the higher the rate will be of recalcitrant carbon being broke down, increasing the amount of CO2 into the atmosphere.
  • 8. Methods  Lake water was collected from five lakes on UNDERC property in the Upper Peninsula Michigan.  1. East Long  2. West Long  3. Hummingbird  4. Crampton  5. Morris
  • 9. Methods Cont..  The lake water was filtered through 0.2 µm filters to remove any bacteria from the water.  Leaving dissolved organic carbon behind with 100 mL of lake water used in each incubation bottle.
  • 10. Methods Cont..  Glucose was used as the source of labile organic matter.  Four treatment groups per lake: 0.25, 1.0, 2.25, and 4.0 mg of glucose  One control treatment for each lake. (no glucose)  One glucose control treatment per lake. (no lake water)  Three replicates for each treatment.
  • 11. Methods Cont..  All treatments had 1 mL of unfiltered lake water added as the source of natural lake bacteria.  Headspace gas from each sample was extracted five times during the incubation after every 5 days and analyzed on a gas chromatograph to see how much CH4 and CO2 was released.  Another round of glucose was added in the second week to stimulate a pulse of fresh labile carbon.  This reflects what would happen in a lake with a phytoplankton bloom.
  • 12. Results 0 1000 2000 3000 4000 5000 6000 1 2 3 4 5 Respiration Week MO Control Cumulative MO 0.25 Cumulative MO 1.0 Cumulative MO 2.25 Cumulative MO 4.0 Cumulative
  • 13. ANOVA Test on Slopes  Morris overall had a p-value of 0.0246  Within the treatments, only the control and the 4.0 mg of glucose were statically different in their slopes of carbon respired.  p-value of 0.0194313
  • 14. ANOVA Test on Respiration  Morris overall had a p-value significant at 0.01617.  The respiration rate that was statically different was between the treatment groups of the control and 4.0 mg.
  • 15. 0 500 1000 1500 2000 2500 3000 1 2 3 4 5 Respiration Week EL Control Cumulative EL 0.25 Cumulative EL 1.0 Cumulative EL 2.25 Cumulative EL 4.0 Cumulative
  • 16. ANOVA test on Slopes  East Long slopes overall showed were significant at a p-value of 0.00555.  The treatments that were statically different from one another was 2.25 and 0.25 with a p-value of 0.0448610
  • 17. ANOVA Test on Respiration  East Long overall was significant at 0.125  The respiration rate that was statically different was between the treatment groups was the control and 1.0 mg.
  • 18. 0 500 1000 1500 2000 2500 3000 3500 4000 4500 1 2 3 4 5 Respiration Week WL Control Cumulative WL 0.25 Cumulative WL 1.0 Cumulative WL 2.25 Cumulative WL 4.0 Cumulative
  • 19. ANOVA Test on Slopes  West Long overall had a significant p value at 0.00509.  Within in West Long, the treatment slopes that were statistically different from each other were…  4.0 mg and 0.25 at a p-value of 0.0588166.  The control and 2.25 with a p-value at 0.02434633.  The control and 4.0 mg at a p-value of 0.0037442.
  • 20. ANOVA Test on Respiration  West Long was significant overall at 0.00138.  The respiration rate that was statically significant was between…  The control and 0.25 mg at a p-value of 0.0035390  The control and 4.0 mg at a p-value 0.0011113.
  • 21. 0 500 1000 1500 2000 2500 3000 3500 4000 1 2 3 4 5 Respiration Week HB Control Cumulative HB 0.25 Cumulative HB 1.0 Cumulative HB 2.25 Cumulative HB 4.0 Cumulative
  • 22. ANOVA Test on Slopes  Overall the slopes of Hummingbird were not statistically significant.  p-value of 0.162  None of the treatment groups in that lake were statistically different from one another.
  • 23. ANOVA Test on Respiration  Hummingbird respiration values overall were not statically significant.  p-value of 0.262.  The treatment groups compared to one another showed no significance as well.
  • 24. 0 200 400 600 800 1000 1200 1400 1600 1800 2000 1 2 3 4 5 Respiration Time CR Control Cumulative CR 0.25 Cumulative CR 1.0 Cumulative CR 2.25 Cumulative CR 4.0 Cumulative
  • 25. ANOVA Test on Slopes  Overall the slopes of Crampton were not statistically significant  p-value of 0.134.  None one of the treatment groups in that lake were statistically different from one another.
  • 26. ANOVA Test on Respiration  Cramptons’ respiration values overall were not statically significant.  p-value of and 0.147.  The treatment groups compared to one another showed no significance as well.
  • 27. Conclusion  The results of this experiment supported the hypothesis that stated that the higher amount of labile carbon (glucose), the higher the rate of recalcitrant carbon being broke down there would be, increasing the amount of CO2 into the atmosphere.  The priming effect does exist in aquatic environments.  Further tested whether the contents of the lakes had an effect on how much CO2 was released such as the nutrients present.
  • 28. References  Attermeyer, K., Hornick, T., Kayler, Z. E., Bahr, A., Zwirnmann, E., Grossart, H.-P., and Premke, K. 2014. Enhanced bacterial decomposition with increasing addition of autochthonous to allochthonous carbon without any effect on bacterial community composition, Biogeosciences, 11, 1479-1489, doi:10.5194/bg-11- 1479-2014.  Guenet B, Michael Danger, Luc Abbadie, and Gérard Lacroix 2010. Priming effect: bridging the gap between terrestrial and aquatic ecology. Ecology 91:2850–2861. doi.org/10.1890/09- 1968.1  Tranviket Lars J. et.al. 2009. Lakes and reservoirs as regulators of carbon cycling and climate. Limnology and Oceanography, 54 part 2, 2298-2314. 10.4319/lo.2009.54.6_part_2.2298