Water Quality Monitoring Programs g EPA Murraylands Team Lake - - PowerPoint PPT Presentation

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Water Quality Monitoring Programs g EPA Murraylands Team Lake - - PowerPoint PPT Presentation

South Australias Environment Protection Authority Water Quality Monitoring Programs g EPA Murraylands Team Lake Albert - Salinity 25000 Meningie Water Level Recorder 20000 Lake Albert: Opening 15000 SPC (uS/cm) 10000 5000 0


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SLIDE 1

South Australia’s Environment Protection Authority

Water Quality Monitoring Programs

g

EPA Murraylands Team

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SLIDE 2
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SLIDE 3

Lake Albert - Salinity

5000 10000 15000 20000 25000 SPC (uS/cm)

Meningie Water Level Recorder Lake Albert: Opening

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SLIDE 4

Salinity Transect – 2011

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SLIDE 5

Salinity Transect – 2015

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SLIDE 6

Salinity Transect – 2015

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SLIDE 7

Groundwater Monitoring

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SLIDE 8

1 2 3 4 5 6 7 8 pH

Groundwater Monitoring

1 2 3 4 5 6 7 8 pH 1 2 3 4 5 6 7 8 9 pH

Campbell Park Currency Creek Point Sturt

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SLIDE 9

200 400 600 800 1000 1200 1400 Acidity (mg/L)

Groundwater Monitoring

200 400 600 800 1000 1200 Acidity (mg/L) 200 400 600 800 1000 1200 1400 1600 Acidity (mg/L)

Campbell Park Currency Creek Point Sturt

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SLIDE 10

Currency & Finniss River

5000 10000 15000 20000 25000 30000 SPC (uS/cm)

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SLIDE 11

Boggy & Hunters Creeks

10000 20000 30000 40000 50000 60000 SPC (uS/cm)

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SLIDE 12

Coorong

20000 40000 60000 80000 100000 120000 140000 SPC (US/CM)

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SLIDE 13

Thankyou

  • Our data is freely available online (www.epa.sa.gov.au)
  • Reports and Papers published
  • Ben Hamilton

Work Phone (08) 8204 2021 benjamin.hamilton@epa.sa.gov.au

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SLIDE 14

Lake Alexandrina

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SLIDE 15

Zooplankton

Zooplankton

  • Zooplankton form a critical step in the food chain, often acting as an

indicator for environmental conditions and water quality. As part of a service provision to DEWNR, the EPA collects zooplankton samples which are sorted by Russ Shiel at Adelaide University.

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Benthic Chambers

Benthic Chambers

  • Despite neutral pH and alkalinity, persistent levels of acidity are recorded

during monitoring at some sites in the CLLMM region (e.g. Boggy and Hunters Creek)

  • Acid-sulfate soils were exposed during the drought. Upon rewetting,

surface water provides a pathway for acidity and dissolved metals to enter surface water.

  • Installation of “benthic chambers” provided a unique insight into how

sediment and overlying surface waters interact, allowing us to measure acidity fluxes directly, and use results to predict interactions under future climate scenarios

  • Results showed that no chamber went acidic (pH<6.5) but fluxes of acidity

(predominantly soluble metals such as Fe) were present but this was counteracted by a greater flux of alkalinity (due to sulfate reduction)

  • Suggests that these “hotspots” may not acidify under lower flow conditions
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SLIDE 17

Benthic chambers are pictured below. Supplied with electricity via solar power, the chamber stirs constantly. Samples were taken by hand every fortnight for six weeks.