Title: Pesticide ecotoxicology of lobster larvae and post larvae: Do the twain ever meet?
1Pesticide 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
2Acknowledgements
- 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
3Oh, 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
4Todays 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
5Little 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.
6Why 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?
7What 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
8What 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)
9Contaminant 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(No Transcript)
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
12Acute 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
13Pyrethroid 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
14Histological 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
15Larval Behaviour
16(No Transcript)
17Introduction 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.
18Experimental 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
19Results Metabolic scope
Significant difference t2,14 -2.63 (p 0.0160)
20Genomics - Sample Preparation
- Sample preservation-Trizol
- RNA extraction-Phenol Chloriform
- Amplification labeling-Cy3 Cy5
- Microarray hybridization
21Microarray
22Cluster 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
23Bugs 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.
24Mayflies on Weather Station Doppler Radar Lake
Erie
De http//seagrant.psu.edu/publications/fs/Mayfly_
12-2003.pdf
25Surely 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
26Little 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.
28What 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.
29Some 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
30Sagittal 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?