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Paul Boon Institute for Sustainability & Innovation Victoria University, Melbourne Salinization of Melaleuca- dominated wetlands of the Gippsland Lakes, Australia

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  • Paul Boon

    Institute for Sustainability & Innovation

    Victoria University, Melbourne

    Salinization of Melaleuca-

    dominated wetlands of the

    Gippsland Lakes, Australia

  • Australian distribution of Melaleuca

    Gippsland Lakes

  • The Gippsland Lakes

    Lakes Entrance

    Opened in 1889

    Melbourne

    Dowd Morass study site

  • Lakes Entrance

  • Gippsland Sustainable Water Strategy (2010)

    Lakes Entrance

    LaTrobe Rv & Dowd Morass Melaleuca wetlands

    Saltmarshes

  • LaTrobe Rv – Dowd

    Morass estuary

    Early 1950s RAAF photo from Eric Bird

    November 2010

    Phragmites beds

    Retreat of Phragmites australis

    Consequences of

    artificial opening

  • Death of Eucalyptus camaldulesis

  • Death of Melaleuca ericifolia

  • Within Dowd Morass:

    Death of adult plants

    Little floristic diversity

  • Loss of sexual reproduction

    Root suckers

  • Morass kept full to prevent saline

    intrusions since 1992

    Year

    1992

    1993

    1994

    1995

    1996

    1997

    1998

    1999

    2000

    2001

    2002

    2003

    Wa

    ter

    Dep

    th (

    m)

    0.0

    0.2

    0.4

    0.6

    0.8

    1.0

    Parks Victoria drawdown

    Full even over drought

  • But salinity is still very high

    PV’s salinity goal (< 4000 EC)

    ½ seawater salinity

  • Rehabilitation predictions

    Re-instating a dry phase in Dowd Morass would

    • Improve condition of adult Melaleuca

    • Allow Melaleuca to recruit sexually

    • Increase floristic diversity of understorey

    Risks included

    • Activating acid sulfate soils

    • Increasing water-column and sediment salinity

    • Being too short to achieve desired outcomes

    • Too ambitious with too little resources

  • Experimental manipulations

    Lake Wellington

    LaTrobe River

    Big Drain

    Little Drain

    1 km

    N

    Pre-existing levees

  • Lake

    Wellington

    Beyond-BACI experimental design

    Control (Flooded)

    Impact

    (Drawdown)

    Heywood’s

    levee

    Reference

    Water in

    Water out

  • Passive draw-down 2003-2004

  • Going well – then vandalism

    Duck season

    vandalism

  • 2nd intervention: active draw-down 2005

    Response to

    2004 vandalism

    in 2005: Pumping!

    • 1 x 12” pump

    • 1 x 10” pump

    Pumped continuously for 28 days in early 2005

  • Active draw-down

    2005

  • Beyond-BACI vegetation assessment

    45 x 100-m long transects across wetland

    • 20 in Control (flooded) sites

    • 20 in Impact (drawdown) sites

    • 5 in Reference (shoreline) sites

    Dates: April 2003 (B), June 2004 (D), April 2005 (D), April 2006 (A)

    Variables:

    • Continuous water depth and salinity (data loggers)

    • Water depth along transects every 0.5 m (36,000 data pts)

    • Vegetation floristics and structure (overstorey &

    understorey cover and floristics etc) (>120,000 data pts)

  • Wate

    r le

    vel (m

    AH

    D)

    -0.4

    -0.3

    -0.2

    -0.1

    0.0

    0.1

    0.2

    0.3

    0.4

    0.5

    Impact

    Control

    Impact (Interpolated)

    Apr 0

    3

    Jul 0

    3

    Oct 0

    3

    Jan

    04

    Apr 0

    4

    Jul 0

    4

    Oct 0

    4

    Jan

    05

    Apr 0

    5

    Jul 0

    5

    Oct 0

    5

    Jan

    06

    Apr 0

    6

    Jul 0

    6

    Oct 0

    6

    Survey 3 Survey 4

    Impact

    Control

    Vandalism

    Pumpingcommences

    Survey 1 Survey 2

    Drawdown 2 commences

    Drawdown 1 commences

    30

    25

    20

    15

    10

    5

    0

    Storm Storm Storm

    Ele

    ctr

    ical conductivity (

    mS

    cm

    -1)

    No big difference

    between Control

    and Impact water

    levels

    B) Salinity

    A) Water level

    2003 2004 2005 2006

    Impact

    Control

    Confounding

    variability in

    salinity between

    Control and

    Impact sites

    Results

  • Alternative: non-BACI (gradient) analysis

    Instead of ANOVA,

    use gradient analysis

    Classification of the hydrology as per

    Brownlow et al. (1994)

    Four water regimes In Dowd Morass

    1

    2

    3

    4

    Permanently wet

    Driest sites

  • Gradient analysis much better than

    original BACI-ANOVA approach

    Water regimes 1 (dry) – 4 (wet)

    Species richness

    Raulings, Morris & Boon (2010) Freshwater Biology 55: 701-715

    Raulings, Morris & Boon (2011) Freshwater Biology 56: 2347-2369

    Projective

    cover

    wet

    dry

    wet

    dry

  • What causes the diversity of

    hydrologies? Microtopographic relief

    Caused by Melaleuca, Phragmites

    and Paspalum humps

  • Photo by Matt Hatton

  • Implications for wetland rehabilitation

    Success after 1 year

  • Large-scale hummock creation, 2006

  • Results after 4 years

    July 2010

  • More information?

    Copies of two technical handbooks (2005, 2007)

    Summary hand-out of papers to date

    Over some beers tonight