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IMPOSEX
in Great Harbours
Team Imposexuals
Jenevieve Hara | Jerome Lubry | Paule-Emilie Ruy | Thiviya Nair | Thomas Cansse
© Thomas Monson
tri · butyl · tin
steroid disruptor
organotin
biocide
causes imposex in
disrupts CYP19 enzyme which converts
testosterone  estradiol
lipophilic
 Na+/K+-ATPase
AChE, HSPs
disrupts
homeostasis

nucella lapillus
 population
© Dorling Kindersley/UIG
French Harbours along the English Channel
Brest
Cherbourg
Boulogne
France
England 3 Locations
Annual sampling
2005
2008
2012
Parameters
Sex*
VDS
Penis length
Shell height*
French Harbours along the English Channel
Brest
CherbourgBoulogne
Brest
Cherbourg
Boulogne
French Harbours along the English Channel
Brest
Cherbourg
Boulogne
France
England
- High imposex
- Low imposex
- Lowest VDSI value
- Highest VDSI value
My population
dropped in 2012!
My VDSI values
decreased from
2005 to 2012.
© I. F. Smith
The Mystery of Aber Wrac’h
 VDSI   Sterility
 traffic
 contamination
military port
Harbour works? Leaching?
ILLEGAL USAGE OF TBT!
resuspension
Illegal TBT? Pff… it’s easy!
• Still used for big ships
• If you know the right people…
© Mike Hettwer
Are indices infallible?
QUASIMEME – What is it about?
Provide quality assurances procedures
Critically determine sex status in neogastropod molluscs
To record relevant parameters
Contribute data to the first international project on the
biological effects of TBT compounds
Conduct international laboratory performance studies
for imposex and intersex using live marine snails
standardisation of
analytical techniques
training of
scientists
inter-laboratory
studies
Quality Assurance of Information for Marine Environmental Monitoring in Europe Project
QUASIMEME – Protocol
Parameters
Bioindicator species
Collection method
of samples
Number of
samples collected
Number of
samples analysed
Holding time
Preservation of
samples
Examination
Type
Exclusion of individuals
affected by parasites
Shell height
Sex
determination
Vas deferens
stage (VDS)
description
Measurement of
penis length
Calculation of
summary indices











QUASIMEME – Protocol
Standardized processes of
sample collection, preservation,
analysis and calculations
Proper preparation of samples after
collection, during transport and
before analysis
Should be done at the same
period of the year
More difficult to determine the sex
of the sub-adults than of toothed
adults
S T A N D A R D P R O T O C O L M O N I T O R I N G P E R I O D
T Y P E O F S P E C I M E N S
(SUB-ADULT/ADULT)
H A N D L I N G O F S A M P L E S
All measurements should be
carried out according to
defined protocols
by trained staff
The quality of dataset should be
assured: consistent, complete,
and stored properly
Q U A L I T Y C O N T R O L
O F M E T H O D S F O R
M O R P H O L O G I C A L
A N A L Y S I SQ U A L I T Y C O N T R O L O F
D A T A A N D R E P O R T I N G
QUASIMEME – Indices
VDSI RPSI RPLI Sex Ratio
Average VDS Percentage of female
vs male penis bulk
Percentage of female
vs male penis length
Self-explanatory!
Habitat
Habitat affects food
supply and penis length
Physical
Deformations on subject
organ at high concentrations
Time-Dependence
Maturity rate
Sensitivity periods
Mortality rate
Dependent on the organ and
characteristics of species
Surely then there are limitations!
(Gibbs et. al, 1987)
QUASIMEME – Results [Performance]
Some laboratories produced the following:
Miscalculations
VDSI & RPSI using the
formula in the OSPAR
Guidelines
Conversion errors from
graticule units
Measurement Errors
in the reported
shell height
Misidentification
Of imposex females
as males
Wrong VDSI!
QUASIMEME – Results [Biological]
Homogeneity of
samples
Penis length Sex identification VDSI
QUASIMEME
Paper ✓
Lowest value: 14.74
Highest value: 59.52
Generally proportional:
(47.2%) and females (52.8%)
Overall value
3.8
English
Channel
Dataset
X
Lowest value: 0.03
Highest value: 20
Not proportional  pick of
males or females
Overall values
Brest: 3.65
Cherbourg: 2.90
Boulogne: 1.55
Lack of data on
the shell height Small
Possibility of
Misidentification
Nucella
Results
Our Final Conclusion!
• All VDSI values seem to reduce in all three stations.
• Brest is the most polluted, then Cherbourg, and Boulogne is the least.
• Reduction in females in 2012 could be explained by a non-linear
response to climate change / other environmental disturbances
• Quality control and adherence to protocol is important!
• Imposex indices are not perfect  other parameters and novel
measurments
• Despite of ban on TBT usage, some in France could still use it.
• More awareness and regulation needed!
YOU
EXAM ON
FRIDAY
THANK YOU!S l a y i t o n F r i d a y g u y s !

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Imposex in Great Harbours

  • 1. IMPOSEX in Great Harbours Team Imposexuals Jenevieve Hara | Jerome Lubry | Paule-Emilie Ruy | Thiviya Nair | Thomas Cansse © Thomas Monson
  • 2. tri · butyl · tin steroid disruptor organotin biocide causes imposex in disrupts CYP19 enzyme which converts testosterone  estradiol lipophilic  Na+/K+-ATPase AChE, HSPs disrupts homeostasis  nucella lapillus  population © Dorling Kindersley/UIG
  • 3. French Harbours along the English Channel Brest Cherbourg Boulogne France England 3 Locations Annual sampling 2005 2008 2012 Parameters Sex* VDS Penis length Shell height*
  • 4. French Harbours along the English Channel Brest CherbourgBoulogne Brest Cherbourg Boulogne
  • 5. French Harbours along the English Channel Brest Cherbourg Boulogne France England - High imposex - Low imposex - Lowest VDSI value - Highest VDSI value My population dropped in 2012! My VDSI values decreased from 2005 to 2012. © I. F. Smith
  • 6. The Mystery of Aber Wrac’h  VDSI   Sterility  traffic  contamination military port Harbour works? Leaching? ILLEGAL USAGE OF TBT! resuspension
  • 7. Illegal TBT? Pff… it’s easy! • Still used for big ships • If you know the right people…
  • 8. © Mike Hettwer Are indices infallible?
  • 9. QUASIMEME – What is it about? Provide quality assurances procedures Critically determine sex status in neogastropod molluscs To record relevant parameters Contribute data to the first international project on the biological effects of TBT compounds Conduct international laboratory performance studies for imposex and intersex using live marine snails standardisation of analytical techniques training of scientists inter-laboratory studies Quality Assurance of Information for Marine Environmental Monitoring in Europe Project
  • 10. QUASIMEME – Protocol Parameters Bioindicator species Collection method of samples Number of samples collected Number of samples analysed Holding time Preservation of samples Examination Type Exclusion of individuals affected by parasites Shell height Sex determination Vas deferens stage (VDS) description Measurement of penis length Calculation of summary indices           
  • 11. QUASIMEME – Protocol Standardized processes of sample collection, preservation, analysis and calculations Proper preparation of samples after collection, during transport and before analysis Should be done at the same period of the year More difficult to determine the sex of the sub-adults than of toothed adults S T A N D A R D P R O T O C O L M O N I T O R I N G P E R I O D T Y P E O F S P E C I M E N S (SUB-ADULT/ADULT) H A N D L I N G O F S A M P L E S All measurements should be carried out according to defined protocols by trained staff The quality of dataset should be assured: consistent, complete, and stored properly Q U A L I T Y C O N T R O L O F M E T H O D S F O R M O R P H O L O G I C A L A N A L Y S I SQ U A L I T Y C O N T R O L O F D A T A A N D R E P O R T I N G
  • 12. QUASIMEME – Indices VDSI RPSI RPLI Sex Ratio Average VDS Percentage of female vs male penis bulk Percentage of female vs male penis length Self-explanatory! Habitat Habitat affects food supply and penis length Physical Deformations on subject organ at high concentrations Time-Dependence Maturity rate Sensitivity periods Mortality rate Dependent on the organ and characteristics of species Surely then there are limitations!
  • 13. (Gibbs et. al, 1987)
  • 14. QUASIMEME – Results [Performance] Some laboratories produced the following: Miscalculations VDSI & RPSI using the formula in the OSPAR Guidelines Conversion errors from graticule units Measurement Errors in the reported shell height Misidentification Of imposex females as males Wrong VDSI!
  • 15.
  • 16. QUASIMEME – Results [Biological] Homogeneity of samples Penis length Sex identification VDSI QUASIMEME Paper ✓ Lowest value: 14.74 Highest value: 59.52 Generally proportional: (47.2%) and females (52.8%) Overall value 3.8 English Channel Dataset X Lowest value: 0.03 Highest value: 20 Not proportional  pick of males or females Overall values Brest: 3.65 Cherbourg: 2.90 Boulogne: 1.55 Lack of data on the shell height Small Possibility of Misidentification Nucella Results
  • 17. Our Final Conclusion! • All VDSI values seem to reduce in all three stations. • Brest is the most polluted, then Cherbourg, and Boulogne is the least. • Reduction in females in 2012 could be explained by a non-linear response to climate change / other environmental disturbances • Quality control and adherence to protocol is important! • Imposex indices are not perfect  other parameters and novel measurments • Despite of ban on TBT usage, some in France could still use it. • More awareness and regulation needed!
  • 18. YOU EXAM ON FRIDAY THANK YOU!S l a y i t o n F r i d a y g u y s !

Editor's Notes

  1. TBT levels are known to result in imposex occurrence in indicator gastropods like Nucella lapillus
  2. Data from each location is provided for 2005, 2008 and 2012 We have to note that the data for Brest 2005 and Brest 2008 is inconsistent with the others, Phare du Portzic was selected Main parameters provided were: Location coordinates Date of collection (March, May, June) Sex Vas Deferens stage (VDS) Penis length Shell height (only for 2005 in Cherbourg and Boulogne)
  3. Indicate dockyard, bay,
  4. VDSI – sterility to come automatically Brest comes first Boulogne Then Cherbourg and roscoff Indicate marina
  5. Make it automatic Put in images of bioindicators
  6. All VDSI values seem to reduce in all three stations. Brest is the most polluted, then Cherbourg, and Boulogne is the least. Reduction in females in 2012 could be explained by a non-linear response to climate change / other environmental disturbances The quality control for the use of standard protocols on the method of analysis, data analysis and reporting must be strictly and properly applied. Imposex indices are not perfect for all habitats and are time-dependent  innovative quantification methods are needed to fill in the gaps Despite of ban on use of TBT upon boats under 25 meters in Europe, some users in France continue to use this product. Therefore it is necessary to increase awareness of people about danger for the environment and even for their health.