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Phosphorus eutrophication in an inter-drumlin lake: causes Phosphorus eutrophication in an inter-drumlin lake: causes

Phosphorus eutrophication in an inter-drumlin lake: causes - PowerPoint Presentation

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Phosphorus eutrophication in an inter-drumlin lake: causes - PPT Presentation

Lucy Crockford Walsh Fellow Trinity College Dublin Whats impeding this lakes recovery Outline Policy Pollution sources and eutrophication Work on the lake Results so far Interpretation ID: 478169

sonde lake chl data lake sonde data chl loading external volume1223389 independent concentrations significance statistical thermocline east 245684 abstraction

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Slide1

Phosphorus eutrophication in an inter-drumlin lake: causes and effects

Lucy CrockfordWalsh FellowTrinity College Dublin

What’s impeding this lake’s recovery?Slide2

Outline

Policy

Pollution sources and eutrophication

Work on the lakeResults so far

InterpretationSlide3

Policy

OECD and Tierney, 2008

SI 272 2009Slide4

Pollution Sources in Rural Catchments

Diffuse

Point

UnknownSlide5

Project Objective:

To determine the main processes that are contributing to the increased P concentrationsExternal P loads

Internal P loadsWind induced resuspension in shallow areasResearch Questions

What are the main contributors of P?Which contributors are the primary factor in the impediment of lake recovery despite source recovery?

How are the dynamics of the lake contributing to the P concentrations – biological, chemical, morphological, catchment use etc.?

How can high frequency monitoring improve our understanding of lake dynamics particularly the impact of episodic events, DO fluctuations, and the signal of the

Chl

a sensor?

Internal Lake Sources

Source: SØNdergaard et al., 2001Slide6

Work on the Lake

Buoys

Data Sondes – Chlorophyll a, conductivity, dissolved oxygen, temperature, redox, pH - hourly

Manual sampling – P fractions, phytoplankton, zooplankton

Bi-monthlySlide7

Cross Section of the LakeSlide8

Neighbouring CatchmentSlide9

Results so Far

Weather and external loadingSlide10
Slide11

Manual Sampling P fractions, Nitrate and Chl aSlide12

Surface Sondes Chl a

Deep Sonde DOSlide13

Summary Statistics Water Year Oct 2010 to Sept 2011Slide14

ConclusionsLake is switching between meso and eutrophic status.

The external load of P is low - inline with source reduction?Internal loading is occurring in anoxic water.The lake suddenly mixing fertilises photic zone – May 2011Wind factor seems to not be increasing P concentrations at eastern end.Slide15

Future Work

Chl a crash in spring not determined yet...Lack of Chl a response to high nutrients at end of summer during fine weather also not determinedQuantify P loads and signal from sondes wrt chlorophyll a

Draw conclusions on the factors impeding lake recovery.Slide16

Algal Bloom

July 2011Slide17

References

SØNdergaard M, Jensen JP, Jeppesen E. Retention and internal loading of phosphorus in shallow, eutrophic lakes. TheScientificWorld 2001; 1: 427-442.Tierney D. Water Quality of Lakes. State of the Environment in Ireland. Environmental Protection Agency, Johnstown Castle, Wexford, 2008.

Acknowledgements

The Agricultural Catchments Programme, Teagasc

Profs Philip Jordan and David Taylor

Drs Alice

Melland

and Per-Erik

Mellander

Mr John Kennedy

GLEON technical groupSlide18

Questions?Slide19

Hypotheses – Spring Chl a crash

Grazing pressure.Lake overturning and “diluting” the Chlorophyll a concentration.Reduction in available nutrients so population could not be sustained.Slide20

Hypotheses – Increased Deep Water SRP concentrations

Release from sediments aka internal loading.External inputs from the catchment.Wind induced resuspension of sediments.Slide21

Hypotheses – Increased Surface SRP concentrations at end of Summer

Lake overturning due to poor weather.External loading from the catchment.Wind induced resuspension.Slide22

1 m Data Sonde

9 m Data Sonde

1 m Data Sonde

Lake Sediment

WEST

EAST

Abstraction

(245684 m

3

yr

-1

)

Lake Volume

1223389 m

3

Thermocline (6-7m)

Statistical Significance Testing

N = 11

Independent T test

P = 0.9243

Difference in annual means is not statistically significantSlide23

1 m Data Sonde

9 m Data Sonde

1 m Data Sonde

Lake Sediment

WEST

EAST

Abstraction

(245684 m

3

yr

-1

)

Lake Volume

1223389 m

3

Thermocline (6-7m)

N = 11

Independent T test

P = 0.9609

Difference in annual means is not statistically significant

Statistical Significance TestingSlide24

1 m Data Sonde

9 m Data Sonde

1 m Data Sonde

Lake Sediment

WEST

EAST

Abstraction

(245684 m

3

yr

-1

)

Lake Volume

1223389 m

3

Thermocline (6-7m)

N = 11

Independent T test

P = 0.9362

Difference in annual means is not statistically significant

Statistical Significance TestingSlide25

1 m Data Sonde

9 m Data Sonde

1 m Data Sonde

Lake Sediment

WEST

EAST

Abstraction

(245684 m

3

yr

-1

)

Lake Volume

1223389 m

3

Thermocline (6-7m)

N = 11

Independent T test

P =

0.1752

Difference in annual means is not statistically significant – but p value much lower than other sample combinations

Statistical Significance TestingSlide26

High Frequency Turbidity