Giant Australian cuttlefish: a globally unique species under threat.

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The Environment Institute Where ideas grow Assoc. Prof. Bronwyn Gillanders Giant Australian cuttlefish: a globally unique species under threat?

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Associate Professor Bronwyn Gillanders presents the fourth installment of the Science Seminar Series entitled "Giant Australian cuttlefish: a globally unique species under threat."

Transcript of Giant Australian cuttlefish: a globally unique species under threat.

Page 1: Giant Australian cuttlefish: a globally unique species under threat.

The Environment InstituteWhere ideas grow

Assoc. Prof. Bronwyn Gillanders

Giant Australian cuttlefish: a globally unique species under threat?

Page 2: Giant Australian cuttlefish: a globally unique species under threat.

Bronwyn Gillanders

Page 3: Giant Australian cuttlefish: a globally unique species under threat.

Population structure Melita de Vries

Steve Donnellan

Mike Gardner

PhD/Hons students Jackie Dupavillon

Nick Payne

Leanne Trott

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Giant Australian cuttlefish & the issues

Population structure

Potential impacts of desalination brine

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Photo: Kaufmann Productions

Weighs up to 13 kgGrows up to 1 mLives 1-2 years

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Ningaloo ReefMoreton Bay

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Adelaide

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8 km of coastlineWinter – May to August

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8 km of coastlineWinter – May to August

Habitat map: SA DEH

Rocky reef

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Males larger than females

High male:female sex ratio

Males ‘battle’ for females

Females may or may not mate with a male

Small males have other strategies (e.g. sneakers)

Shear numbers impressive

Photos: Fred Bavendam

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Skewed towards males (4:1) based on counts of each sex

Assumes individuals on breeding aggregation similar amounts of time

Population sex ratio may be 1:1 with sexes spending different amounts of time on the breeding aggregation

Predict males spend more time than females

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Males n = 13Females n = 6

Payne, PhD project

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Male:Female = 3.7 : 1

Residence time

Male:Female = 4.6 : 1

Residence period

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Population composed of equal numbers of males & females

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Renewable moratorium on fishing introduced in 1998

Now permanently closed to taking of cuttlefish

Need to establish long-term scientific based management plan

From: SARDI Catch Data

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BHP Olympic Dam expansion Preferred option: coastal desalination plant in USG

Point Lowly preferred location (18 ha site)

Bulk commodities export facility Feasibility study by Spencer Gulf Port Link Consortium

(SGPLC), led by Flinders Ports

7-13 million tonnes of ore could be exported through new facility

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Need to understand population structure for appropriate spatial management

Demographic processes & population dynamics may vary

From: Keough & Swearer (2007)

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Strongest inferences use a suite of techniques

Genetic & phenotypic approaches

Might not necessarily expect concordance among approaches

Evolutionary history vs. environmental variation

Spatial resolution varies by technique

Genetic approaches may be more conservative

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Marine populations

Genetic homogeneity over large distances

High dispersal life history characteristics

Squid

High levels of gene flow among populations

Cuttlefish

Sepia officinalis – extensive population structuring

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Determine population structure of giant Australian cuttlefish using a multidisciplinary approach Molecular (microsatellite DNA markers)

Morphometrics

Statolith chemistry

Investigate spatial & temporal variation in population structure

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Microsatellite genotyping

12 microsatellite loci screened per individual Kassahn et al. (2006) Marine Biology

Wheaton et al. (2007) Molecular Ecology Notes

Temporal variation South Australia

Five yrs between 1998 & 2006

Spatial variation 18 sites across Australia

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WA

SA

QLD

NSW

VIC23

4 56

Whyalla

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Breeding aggregation

Spencer

GulfGSV

Ningaloo

Bass Strait

Moreton

Bay

Wallaroo

Glenelg

Aldinga

Cape

Jervis

Edithburg

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20042005

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20052006

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Bayesian clustering approach

Triplicate runs for 1 (panmixia) to 6 populations

Used admixture model

Assumed correlated alleles across populations

Examined each of K populations further to detect sub-population structure

STRUCTURE

1 2 3 4 5 6K, number of populations

-24500

-23500

-22500

-21500

-20500

Ln P

r(X |

K)

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Shows overall population structure & individual assignmentLength of each line proportional to estimated membership in each group

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Gulf St Vincent WA

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emb

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JervisBay

Wollongong Newcastle Coffs Harbour

Northern NSWCentral & Southern NSW

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Spatial information – sampling location 1 to 10 populations (n=5 replicate runs)

Fixed K at modal value to estimate assignment of individuals to populations (n=10)

Continued hierarchical analyses to detect subpopulation structure

GENELAND

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Population 2Population 1 Population 4

Population 3

Population 5

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Population 4

Population 5

Contact zone

Breeding aggregation

100 km

South Australia

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28 measurements per individual

Removed allometric effects of body size

Sexually dimorphic sexes analysed separately (n= 173 females & 342 males)

No difference in size among years pooled years

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-5 -3 -1 1 3 55

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Discriminant function 1

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90% correctly classified

3 variables used for classification

3 variables important: cuttlebone width & 2 beak parameters

LRL UHL

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-5.0 -2.8 -0.6 1.6 3.8 6.0-5

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Discriminant function 1

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8 variables used for classification

3 beak parameters contribute to differences

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Dissolved traceelements

Uptake bycephalopod

Statolithincorporation

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Sr:Ca prehatchling seawater (mmol mol-1

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ith(m

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Trott, Hons thesis

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-7 -3 1 5-5

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Discriminant Function AnalysisAll years – 77% correctly classified2004 – 78% correct2005 – 79% correct2006 – 83% correct

Breeding aggregationGSV & Southern SGWestern SA

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Not one panmictic population Evidence for 5 populations across species range Breeding aggregation differs from elsewhere

Evolutionary & ecological implications

Possibly incipient species

Adaptive divergence along an environmental

gradient

Recent & rapid differentiation

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Ocean again at ~ 7KYA

From: Andrew Hugall

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Mating behaviour differs Physiological tolerance & condition in relation to

temperature & salinity▪ Two populations may be prevented from significant overlap due to

differing tolerances

Are individuals from two populations able to mate, are eggs viable, are offspring fertile▪ Testing degree of reproductive isolation

Determine degree of genetic isolation – genome wide screening

Ecological implications of morphological differences

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Breeding area

Intake pipe

Out take pipe320 ML SW/day

from USG;Salinity >40 ppt

200 ML SW/dayreturned in more

concentrated form;Salinity 78 ppt

120 ML FW/day via 320 km pipeline

From: Olympic Dam EIS website

Proposed locations

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Discharge of large volumes of highly concentrated brine back to ocean

Elevated salt concentration & contaminants

Elevated temperature & turbidity levels

Decreased oxygen levels

Brine high specific density sinks to bottom

Could impact adult mating behaviours, & benthic life history stages

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Salinity effects embryonic development Resources diffuse across membrane Solubility of gases (e.g. O2) decreased in

hyper-saline water Increased salinity causes a diffusion limitation

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Control39ppt 40ppt 45ppt 50ppt

Brine55ppt

n =12

Dupavillon, Hons thesis

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Treatment

Brine: Increased Sr, Ca, K & Mg

High Mg causes mortality and reduced mobility

High concentrations found in 45, 50 and 55‰.

Mean field concentration

Dupavillon & Gillanders (2009)Treatment - salinity

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Increase 1‰ = ~7%

decrease in survival

Total mortality

Treatment - salinity

Dupavillon & Gillanders (2009)

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Treatment - salinity

Smaller size at higher salinitySmaller individuals less well developed for feeding & swimming

Dupavillon & Gillanders (2009)

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If brine disperses & background salinity levels reached close to discharge outfall May be little impact on eggs

But USG already hypersaline environment

Strong tidal currents, but are USG waters flushed & mixed with ocean waters given bathymetry?

Also, dodge tides

Potential for major impact on GAC

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Mating behaviour highly visual Inbound migratory routes of cuttlefish

Will adults move up and over high salinity, benthic plumes?

Will adults migrate around benthic plume to reach breeding sites?

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Only known breeding aggregation of cuttlefish in world!

Population at Point Lowly likely a different species

Little if any input from SSG population

Potential for brine to impact early life history stage

Unsure about impacts on adult behaviour & migration

Species can’t move elsewhere to lay eggs

Cephalopods short lived (1-2 years)

No storage effect in population

Need to be more cautious cf. managing finfish

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Recent ABC Catalyst story:http://www.abc.net.au/catalyst/stories/2695601.htm

Photos: Fred Bavendam, Sean Connell, Jackie Dupavillon, Kaufman Productions, Nick Payne, Tim Rogers

Page 49: Giant Australian cuttlefish: a globally unique species under threat.

The Environment InstituteWhere ideas grow

Next Seminar: 23 October

Assoc. Prof. Veronica Soebarto

Environmentally-sensitive design