First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and...

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First experiences with tools for monitoring and predicting non-indigenous species (NIS) in the Arctic Klaas Kaag, Andrea Sneekes, Hilde van Pelt, Martine van den Heuvel-Greve, Anneke van den Brink, Bas Bolman & Jeroen Jansen P.O. Box 57, 1780 AB Den Helder, The Netherlands email: [email protected]

Transcript of First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and...

Page 1: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

First experiences with tools for monitoring and

predicting non-indigenous species (NIS) in the Arctic

Klaas Kaag, Andrea Sneekes, Hilde van Pelt, Martine van den Heuvel-Greve, Anneke van den Brink, Bas Bolman & Jeroen Jansen

P.O. Box 57, 1780 AB Den Helder, The Netherlands

email: [email protected]

Page 2: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

IMARES

Institute for Marine Resources and Ecosystem Studies

A scientific institute for strategic and applied marine ecological research in support of maritime policies and innovations.

Sustainable maritime economy and seafood production in harmony with the protection of the seas.

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IMARES in the (Ant)arctic

� TripleP@Sea – Standards and guidelines

for ‘sustainable development’ (4 PhDs)

� SYMBIOSIS – Modelling oil spill effects on

zooplankton and cod

� Arctic Handbook – Generic EIA

� EIA Arctic Naval Operations

� Scientific Expedition Edgeøya Spitsbergen

(SEES.NL)

� Contaminants in the Arctic (‘Silent snow’)

� Association of Polar Early Career

Scientists (APECS)

� Antarctic expeditions (>30 yr)

Page 4: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

Global warming

1980 2012

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Recent Arctic developments

� Decrease in sea ice coverage results in an increase of human activities:

Offshore oil & gas explorationHarbour development and shipping

Tourism Fishery

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What are the risks?

� Introductions of non-indigenous species in the Arctic

� Transfer of NIS via the Arctic

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25-30 % of North Sea invaders by ballast water

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25% as hull fouling

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Non-Indigenous Species in the Arctic

� Gollasch (2006): 18 NIS in European Arctic waters

� Ruiz et al. (2006): 12 NIS in Alaskan waters

� Hines & Ruiz (2000): 24 NIS & 29 cryptogenic species

� Ware et al. (2012): Probably no established NIS in high Arctic (Svalbard area), but planktonic species in ballast water able to survive local conditions

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Transfer of NIS through the Arctic

� Shorter trips, result in increased survival of ‘passengers’

� Lewis et al. (2003): transfer of potential NIS in and on ships in Antarctic

� Lewis et al. (2003): Regrowth experiments show different species compared to direct analysis of ballast water

� DNA analysis of viable organisms

Page 11: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

DNA barcoding: a short DNA sequence that can characterize every species on the planet

DNA metabarcoding: automated identification of multiple species in an environmental sample

DNA barcoding as monitoring tool

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Biodiversity description:species listspecies richness

Biodiversity description

- Species list

- Species richness

- Compare sources

DNA based biodiversity assessmentDNA barcoding as monitoring tool

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Ballast water treatment

�2004 Ballast Water Management Convention

�14 guidelines

�Reducing load of non-indigenous species in ballast water, without harming the receiving environment

Page 14: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

Temperate biased test facilities

Testing restricted to productive season (April-September)

in order to meet challenge conditions specified in G8

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Seasonal biased testing

But,

� Shipping occurs all year round

� Organisms are present all year round

� Treatment should work all year round

�Winter tests difficult but not impossible

Page 16: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

Specific Arctic challenges

� Low temperatures

�High productivity

�Difficult conditions

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Consequences of low temperatures

� Metabolism slow

� Sensitivity low

� Sensitive life stages last longer

� Reproductive rate slower

� Chemical processes slower

� Do Arctic species react the same as temperate species in winter?

� Insensitive life stages (resting eggs; cysts)

Page 18: First experiences with tools for monitoring and predicting ... · Sustainable maritime economy and seafood production in harmony with the protection of the seas. IMARES in the (Ant)arctic

Effects of temperature on toxicity

� Toxicity generally increases with

temperature. Heugens et al 2001

� Toxicity of hypochlorite and

chloramine increases with

increasing temperature. Capuzzo 1979

� Some pesticides more toxic at

lower temperatures. Weston et al 2009

� Most studies in range 15 to 30 °C

� Little is known about BW biocides

0

10

20

30

40

50

60

70

80

Positive Negative Optimum No correlation

136 tests

15 substances

no biocides used for BW

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Effects of low temperatures on toxicity

� Most effort related to oil & gas. Petroleum hydrocarbons and POP’s most problematic in Arctic. MacDonalds & Brewer 1996

� Arctic species less sensitive to heavy metals. Chapman & McPherson 1993; Chapman et al 2006

� Sensitivity for oil and some PAHs comparable for Arctic and temperate species. Hoop et al 2011

� Longer exposure times may be more realistic. Chapman & Riddle 2005

� Adaptation to low temperatures may result in increased effects. Camus et al 2004

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Are active substances different?

� Not persistent

� Effect instantaneous

� At low temperatures more persistent

� But organisms less sensitive

� Does this change efficacy or ecological risk?

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First testing experiences

� Standard test organisms

� Adapted to different temperatures

� Compare standard test temperature with low temperature

� Compare reference toxicant with BW biocide

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First testing experiences

PERACLEAN(r) Ocean

� Low sensitivity due to slow biological processes

� Higher exposure due to slower degradation

� Net results similar or higher toxicity

Comparison with reference toxicant (K2Cr2O7)

� Lower sensitivity...

� Similar exposure (no degradation)

� Net result less toxicity

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Testing experiencesB. plicatilis (marine)

* *

**

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Testing experiencesB. calyciflorus (freshwater)

Temp °C

LC

50 (

mg

/l)

5 10 15 20 25 300

1

2

3

4PO

Temp °C

LC

50 (

mg

/l)

5 10 15 20 25 300

10

20

30

40K2Cr2O7

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Testing experiences

� Acute effects (1 day)

● less toxicity at low temperature

� Chronic effects (5 days)

● higher toxicity at low temperature

● growth (recovery) at both temperatures

● much slower at 5°C

cilates (marine)

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Preliminary conclusions

� Low temperature testing is slow process

� Biocide shows different response than persistent toxicants

� Different results for marine and freshwater tests

� Different for long-term exposure

� Thanks to Evonik Industries AG for co-funding this research

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Further research

� Sensitivity of natural communities

● 4 seasons

� Dutch Arctic Centre Svalbard

● testing of local species

� Laboratory

● compare effects of BW biocides at different temperature for

different species

● interactions with salinity

� Joint Industry Projects

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Thank you for your attention