Farm Intake Water Treatment (FIWT) project FRDC 2017/231 start July - - PowerPoint PPT Presentation

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Farm Intake Water Treatment (FIWT) project FRDC 2017/231 start July - - PowerPoint PPT Presentation

Farm Intake Water Treatment (FIWT) project FRDC 2017/231 start July 2018 Water treatment to control influent water biosecurity risk on Australian prawn farms. Effectiveness and impacts on production ponds. David Mann Co-invest. Paul


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SLIDE 1

Farm Intake Water Treatment (FIWT) project

FRDC 2017/231 – start July 2018

‘Water treatment to control influent water biosecurity risk on Australian prawn farms. Effectiveness and impacts on production ponds.’

David Mann Co-invest. Paul Palmer Tom Gallagher Stephen Wesche Bribie Island Research Centre DAF

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SLIDE 2

Project context

Enhancing farm biosecurity

  • Intake water is a significant potential vector
  • 2018/19 farms in the Logan River Region operating in

the white spot control zone Filtration to remove disease vectors is a common biosecurity measure

  • alone or in combination with a

following disinfection step

  • rotating drum filters – best tech. for

high flow volume

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SLIDE 3

Project context

“From a biosecurity standpoint, WSSV risk decreases with screen size.”

Responsible Aquaculture Foundation / World Bank. 2013.

Case Study…Mozambique and Madagascar: Impacts and Management Recommendations.

Intake water filtration

  • Farms now screen pond inflow water
  • This project is about the next level of protection
  • requires large farm investment
  • Need to optimise the cost:benefit
  • Fine filtration (sub-100µm) as well as water disinfection

will impact plankton bloom dynamics

  • Need to manage adverse impacts
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SLIDE 4

Project results

Part 1. Farm monitoring

  • Performance of commercially operated rotating drum

filtration system

  • Impact of filtration on downstream plankton composition

Part 2. Filter mesh size tests

  • Direct comparison of different filter sizes (20-150µm)

Outcomes

  • What do the results mean for farm biosecurity and
  • perations
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SLIDE 5

Results: Part 1. Farm monitoring

Gold Coast Marine Aquaculture

Hosted project monitoring activities over the whole 2018/19 production season Operating parameters

  • two filters in parallel at

start, third installed later

  • nominal 80µm mesh
  • estimated 5 ML/h flow rate
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SLIDE 6

Results: Part 1. Farm monitoring

Farm intake water filtration

What it did do…

  • 1. removed large quantities of small crustaceans
  • in raw water and backwash water - not in filtrate
  • amphipods, shrimp, crab and other decapod larvae
  • filter feeders, scavengers, predators
  • large proportion of these in the 0.3 to 4mm range
  • 2. potentially obstructed entry by Penaeid prawns
  • very few non-P. monodon prawns within the farm
  • different from previous years
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SLIDE 7

Small crustaceans in filter backwash

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SLIDE 8

Results: Part 1. Farm monitoring

Farm intake water filtration

What it didn’t do…

  • 1. Did not greatly affect the copepod population
  • 2. Did not stop glass shrimp (Acetes sp) from colonising

the farm

  • passage of larval stages?
  • 3. Did not stop barnacles
  • heavy colonisation occurred within first few weeks

Barnacles on pond liner Glass shrimp Copepods

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SLIDE 9

Copepods at different points within the farm

  • no statistically significant differences

Results: Part 1. Farm monitoring

number / m3

  • Adult copepods of

the four groups present

  • Some larger adults

restricted - Calanoids

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SLIDE 10

Results: Part 1. Farm monitoring

Nauplii at different points within the farm

  • no statistical differences within water supply system

number / m3

  • Nauplii not affected

by filtration

  • No difference in body

size pre- and post- filter

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SLIDE 11

Plankton much larger than the 80µm nominal mesh size pass through the filters

  • copepods over 200µm width
  • almost all nauplii (to 340µm)

HOW?

  • 1. Plankton tend to be bendy,

squishy and variably shaped

  • 2. Filter mesh actual pore size and

shape

Results: Part 1. Farm monitoring

Acartia sp. copepod Barnacle nauplii

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SLIDE 12

Nominal 80µm mesh – [absolute 125µm]

Results: Part 1. Farm monitoring

Plain weave Weft Warp

167µm

167µm ̴166µm ̴250µm

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SLIDE 13

Location

Results: Part 2. Mesh size tests

Pumicestone Passage Bullock Creek Prawn Farm

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SLIDE 14

Mesh size comparison...

  • 1. Tested range (20, 40, 80,150µm), nominal pore size

greatly affects copepod population

  • 20µm retains virtually all copepods and nauplii
  • 150µm retains around half of copepods and nauplii
  • 2. All copepod groups pass through 40µm & above
  • 3. Copepods and nauplii passing through 40µm are viable
  • 4. Rotifers can pass through 20µm
  • small species? ; eggs?

Results: Part 2. Mesh size tests

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SLIDE 15

Testing set-up

  • Inshore estuarine water
  • prawn farm standard
  • Scaled down drum filter
  • Reparator Pty. Ltd

(manuf. by Adriyatic)

  • Stainless woven mesh
  • 20, 40, 80, 150µm, (raw)
  • 80µm same weave as GCMA
  • 21 tank array
  • plankton mesocosms to

assess animal viability

Results: Part 2. Mesh size tests

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SLIDE 16

Results: Part 2. Mesh size tests

Copepod density post-filter Initial

# / m3

Day 14

# / m3

  • Comparatively large restriction step from 150 to 80 µm
  • Copepod size did not follow same pattern as abundance
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SLIDE 17

Results: Part 2. Mesh size tests

All nauplii density post-filter Initial

# / m3

Day 14

# / m3

  • 150µm mesh restricts ̴50% of nauplii, 40µm ̴25%
  • Average body size of filtrate nauplii same for all mesh sizes
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SLIDE 18
  • 1. Logan River plankton and glass shrimp samples WSSV

negative (intake and in farm; over the season).

  • 2. Drum filtration at nominal 80µm effectively excludes higher

WSSV risk organisms at practical flow rates.

  • 3. Nominal 80µm stainless filter has a low impact on pond bloom.
  • time to peak copepod density delayed but main groups

present to form normal productive pond bloom

  • 4. To prohibit barnacle entry need 40µm or less filter mesh.
  • larval stages of crustaceans still enter (lower risk?)
  • 5. Nominal 40µm stainless filter would allow some copepod entry

but retard pond population development.

  • 6. Filtration alone lowers probability of vector intrusion.
  • chemical disinfection – high protection

Outcomes

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SLIDE 19

This project

  • sampling completed
  • final report will have more detailed analyses

What next…

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What next…

Future work on water biosecurity…

  • 1. Continue farm monitoring and testing
  • performance and impacts of the re-developed systems

being implemented on farms this season – ‘Growing together’ theme – sharing information

  • 2. Optimise chemical disinfection for high water biosecurity
  • options – oxidants, eg ozone, other oxidants; trichlorfon
  • conditioning of disinfected water important
  • 3. Creating healthy pond systems
  • water/pond biome management
  • adapting overseas innovations to the Australian context
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SLIDE 21
  • FRDC and DAF funded the project
  • Gold Coast Marine Aquaculture opened their Logan River

farm to regular sampling and assisted on farm activities

  • Frank Coman and Julian Uribe Palomino (CSIRO) assisted

pond sampling method development and conducted training

  • f DAF staff in zooplankton identification
  • Bullock Creek Prawn Farm allowed use of hatchery and

intake facility and assisted in systems set-up

  • Reparator Pty. Ltd supplied the fully equipped drum filter

and different size mesh screen replacements for tests

Acknowledgements

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SLIDE 22

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