Pesticide ecotoxicology of lobster larvae and post larvae: Do the twain ever meet? - PowerPoint PPT Presentation

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Pesticide ecotoxicology of lobster larvae and post larvae: Do the twain ever meet?

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Endosulfan caused the most extensive cellular abnormalities Atrazine, hexazinone and NP caused extensive changes to the cuticle layers; ... – PowerPoint PPT presentation

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Title: Pesticide ecotoxicology of lobster larvae and post larvae: Do the twain ever meet?


1
Pesticide ecotoxicology of lobster larvae and
post larvae Do the twain ever meet?
  • Wayne Fairchild1, Paula Jackman2
  • Ken Doe2,7, Jacqueline Arsenault1, Kadra
    Benhalima1, Art Cook2, Mélanie Thibodeau2, Jamie
    Aubé2, Stéphan Reebs3, Dounia Daoud4, Martin
    Mallet4, Benoit Bruneau5, Denis Chabot5, Megan
    Bauer6, Spencer Greenwood6, Andrea Locke1, Mark
    Hanson1 and Michel Comeau1

1 Fisheries and Oceans Canada, Gulf Fisheries
Centre, Moncton, NB 2 Environment Canada, Science
and Technology Branch, Moncton, NB 3 Département
de biologie, Université de Moncton, Moncton, NB 4
Homarus Inc., Shediac, NB 5 Fisheries and Oceans
Canada, Mont-Joli, QC 6 AVC, Lobster Science
Centre, Charlottetown, PEI 7 Retired, Growing
garlic, Mount Uniac, NS
2
Acknowledgements
  • Fishing Industry through Homarus Inc.
  • Fisheries and Oceans Canada
  • Environment Canada
  • U de Moncton
  • Marine Centre, (Shippagan, NB)
  • Atlantic Cancer Research Institute
  • And many colleagues and students

3
Oh, East is East, and West is West, and never
the twain shall meet From the The Ballad of
East and West, by Rudyard Kiplingor a nice
quick summary of the hopes of our regulatory
regime and risk assessment process
Coastal Habitat we have a lot of this in
Atlantic Canada
4
Todays Talk Outline
  • Objectives Why the concern?
  • Background on pesticides/contaminants
  • What we know about these things?
  • What we don't know?
  • What have we being working on?
  • Surely this is all academic, I mean really?
  • Future directions and research questions
  • Some thoughts and conclusions

5
Little lobsters - Objective
  • Investigate the potential for pesticides to
    interfere with the nearshore/estuarine early life
    stage development of American lobster (Homarus
    americanus).
  • Particular emphasis will be placed on high hazard
    pesticides and pesticides with modes of action
    that may act at very low concentrations with only
    transitory exposures.
  • Given the short length of most PEI freshwater
    systems, there is a close link between events in
    rivers and the adjacent salt water.

6
Why a concern to fishing industry?
  • There was a huge die off of lobster in Long
    Island Sound that was co-incident with the
    arrival of West Nile virus
  • To combat West Nile mosquitoes, an insecticide
    spray program was initiated around New York
    (methoprene and others) Was there a link?
  • Nonylphenol was also found in samples and
    implicated
  • Some of the recent workshops are now wondering if
    a synthetic pyrethroid insecticide could have
    been a contributor (very potent to FW aquatic
    invertebrates)
  • These events have received wide media and
    industry attention
  • Can contaminants be a factor (causal, added
    stress) in the incidence of lobster shell disease?

7
What we know about these things?
  • contaminants are in many effluent streams
    (municipal, industrial, agricultural)
  • Contaminants are mostly below regulated
    concentrations for regulated endpoints
  • pesticides are in river runoff, particularly on
    PEI
  • new industrial developments, new crops or use
    patterns, brings new contaminants (or
    concentrations) to the region

8
What we don't know about?
  • Nanoparticles (novel behaviours, fresh to salt
    transition?)
  • Pyrethroid pesticides, safer but more toxic
    (effects at very low concentrations)
  • New chemicals (all classes, 1000s per year)
  • Particle bound contaminants (fate and effects)
  • Drugs, personal care products, endocrine
    disrupting compounds (usually low concentrations,
    but potential high potency)

9
Contaminant exposure
  • Spray Drift, direct and indirect
  • Runoff, especially storm events
  • Water, fields to streams to estuaries to ?
  • Particles, from fields or in natural water
  • Sediments, settling or estuarine processes
  • Food, from all sources
  • Plus interactions with environment for all

10
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11
  • Figure 3 Transfer of individual larvae into
    Mason jars.
  • Figure 4 Lab set-up for Chronic and Acute
    exposure experiments

Environment Canada, Moncton, NB
12
Acute Tests 48-Hour LC50 (as µg/L active
ingredient)
Pesticide Stage I Stage IV
Azinphosmethyl (Guthion) 3.16 (1.0010.0)
Chlorpyrifos (Lorsban) 0.35 (0.27-0.46)
Diflubenzuron (Dimilin) gt 1000 gt 1000 µg/L
Endosulfan (Thiodan) 2.51 (1.73-3.64) 3.98 (2.576.16)
Hexazinone (Velpar) gt 1000 gt 1000 µg/L
Methamidiphos (Monitor) gt 1000
Tebufenozide (Confirm) gt 1000 gt 1000
13
Pyrethroid formulations of deltamethrin
  • AMERICAN LOBSTER Homarus americanus
  • Stage III lobster larvae had acute 96-hr LC50
    values between 3.74 to 4.92 ng/L (n 3). Results
    for the two formulations over three trials were
    within a range of 1.2 ng/L (NOTE units are
    1000x lower that previous table)
  • Stage IV (post larvae) had 96-hr LC50 of 28.2
    ng/L.
  • Stage III lobster larvae given a 1-hr pulse
    exposure followed by 16 days in clean water had
    an LC50 of 36.5 ng/L
  • Chronic exposure of stage III larvae for 16 days
    had an LC50 of 4.45 ng/L
  • This pesticide is released into sea water after
    sea lice treatment, and is in streams from
    agricultural areas

14
Histological effects of nonylphenol and
pesticides on cuticle and hepatopacreatic cells.
Legend Cuticle Ep (Epicuticle), Ex
(Exocuticle), En (Endocuticle), ML (Membraneous
layer), Ct (Connective tissue). Hepatopancreas
N (Nuclei), F (F-cell), B (B-cell), L (Lumen), V
(Vacuole), Ep (Epithelium). Magnification 40 X
15
Larval Behaviour
16
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17
Introduction Metabolism
  • Metabolic rate most fundamental biological rate
    as it represents the rate of energy uptake,
    transformation, and allocation. (Brown et al.
    2004)
  • Standard metabolic Rate (SMR) energy required to
    maintain basic biological functions independent
    of activity, digestion or costs of physiological
    stressors.
  • Active metabolic rate (AMR) energy required to
    perform specific levels of activity (lt Maximum
    MR MMR)
  • Metabolic scope absolute MS difference between
    SMR and MMR. Energy available to grow, digest
    food, support locomotion etc.

18
Experimental setup - metabolism
  • Larvae obtained from Coastal Zones Research
    Institute-Homarus Inc. hatchery
  • Acute Exposure stage V-VI- 0.1 µg L-1- 20 C,
    96-hr
  • One individual per jar (1 L) to avoid
    cannibalism, no renewal
  • Daily feeding of live artemia, frozen artemia,
    and dry food
  • Water quality verified daily

19
Results Metabolic scope
Significant difference t2,14 -2.63 (p 0.0160)
20
Genomics - Sample Preparation
  • Sample preservation-Trizol
  • RNA extraction-Phenol Chloriform
  • Amplification labeling-Cy3 Cy5
  • Microarray hybridization

21
Microarray
22
Cluster Analysis
Down Regulation
Up Regulation
0.01 0.1 0 0.03 0.3 1.0
0.01 0.1 0 0.03 0.3 1.0
23
Bugs as food?
  • Lobster larvae and insects in neuston
  • Insect sampling on land and sea
  • Is there another great circle of life lesson in
    the potential for land based sources to affect
    the near shore marine environment?
  • Insects are eaten by lobster larvae
  • After everything, this still surprises me

Contents of a neuston sample from the
Northumberland Strait. Biota of terrestrial
origin sorted to left in pan, marine origin to
the right in pan and in sieve.
24
Mayflies on Weather Station Doppler Radar Lake
Erie
De http//seagrant.psu.edu/publications/fs/Mayfly_
12-2003.pdf
25
Surely this is all Academic?
  • Leight et al 2005, grass shrimp population
    monitoring, golf and agriculture, South Carolina,
    BMP and IPM more shrimp
  • Hartwell 2011, Chesapeake Bay, mysid relative
    pesticide toxicity (esp. pyrethroids) and crab
    harvest, total pesticide application there in
    range of PEI totals
  • Baldwin et al 2009, Chinook salmon population
    modelling, population effects from sublethal
    pesticide effects, including growth

26
Little lobster - Conclusions
  • Toxicological screening of pesticides of concern
    in our region has generated a number of
    significant results for biological effects on
    lobster larvae
  • In our limited screening we have seen compounds
    that affect survival, moulting, timing of
    development, histology and behaviour
  • The high end of test concentrations for most
    chemicals are above the expected environmental
    concentrations, effects on lobster larvae running
    down into the low µg/L (ppb) range and below 1
    µg/L are a concern
  • There is potential for movement of these
    chemicals into coastal waters, though the
    pathways and likelihood of such an occurrence
    remain to be determined

27
Little lobster Conclusions (cont.)
  • While there is nothing definitive to indicate a
    link between lobster population levels, and
    contaminants in the environment, there is
    certainly enough information now available to ask
    good questions (which ironically?)
  • Microarray analyses are being conducted to study
    the gene expression changes that occur following
    exposures of lobster larvae to nonylphenol and
    pesticides.
  • The intent is to correlate these changes with
    effects on survival, growth, moulting, cell
    histology and behaviour.
  • A library of contaminant response in the
    laboratory will be developed to test against
    field collected larvae to verify exposure.

28
What the research opportunities/needs are?
  • Linking contaminants and biological effects in
    real world context. Field studies? Lab-field
    studies? Linked to biological monitoring?
    Mixtures?
  • Below regulated concentrations, but does this
    mean no biological effects?
  • Fate of current use contaminants in the
    environment. Are contaminants accumulating in
    unexpected reservoirs?
  • Fate of some degradation resistant pesticides
    (ex endosulfan). Are these in decline and gone
    as much as we would like to think?
  • Estuaries are great chemistry experiments in
    progress.

29
Some thoughts, and conclusions?
  • Nutrients and sediments, can be good surrogates
    for occurrence of some groups of contaminants,
    integration of projects on these topics might
    provide good synergies
  • Biological effects approaches may provide an
    indication of differences in ecosystem health
    that may go non-detected with a chemical
    measurement approach

30
Sagittal section of the stereomicroscopy
micrographs showing the general view of internal
anatomy with the positions the organs of stage IV
larval lobster (E Eye, G Gill, H Heart, He
Hepatopancreas, M Muscle, CS Cardiac stomach).
Questions?
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