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Study of the environmental impact of insecticides by metabolic foot-printing approach - An introduction to
the concept
Chandrashekhar Patil, Amani Ben Jrad, Hikmat Ghosson, Delphine Raviglione, Marie-Virginie Salvia, Cédric Bertrand
To cite this version:
Study of the environmental impact of insecticides by
metabolic foot-printing approach
- An introduction to the concept.
Chandrashekhar Patil
1, Amani Ben Jard
1, Hikmat Ghosson
1, Delphine Raviglione
1, Marie-Virginie Salvia
1,2, Cédric Bertrand
1,2 1 CRIOBE USR3278, Université de Perpignan Via Domitia, F66860, France.² Laboratoire d’excellence “CORAIL”, France
Context :
• Assessment of environmental pollution complex mixtures (new generation biological compounds, e.g. insecticides) is a major challenge.
• Evaluation of insecticides Half-life (t ½) is the time it takes for a certain amount of a pesticide to be reduced by half
• However, half-life dertermination does not apply if active substance is a complex mixture of compounds derived from biological sources (e.g. plant extract, microbs etc)
• Half-live values give restricted information as it does not describe all phenomena occuring such as the formation of by-products and the effect on biodiversity
• We propose an alternative approch: the resilience time, this value could be determined with kinetic study of meta-metabolome with EMF approach
Conclusion and perspectives
Complex natural substances may be tested with this novel analytical protocol.
It could potentially replace half life (t
1/2) concept with resilience time.
Metabolomics approach may help to identify potential markers for environmental diagnosis of environmental contamination by pollutants.
Characterization of selected markers from variables important in projection (VIP) of PLS DA are ongoing in our laboratory.
Setting up of an experiment that mimics seminatural conditions (microclimatic chamber) with extended time and improving experimental and analytical parameters.
Bibliography
Patil C, Calvayrac C, Zhou Y, Romdhane S, Salvia MV, Cooper JF, Dayan FE, Bertrand C. Science of the Total Environment. 2016 Oct 1;566:552-8.
Salvia MV, Jrad AB, Raviglione D, Zhou Y, Bertrand C. Environmental Science and Pollution Research. 2017 Jun 28:1-7 Acknowledgement
This project has received funding from the European Union's Horizon 2020 research and innovation programme under
grant agreement No 746656 (Project: EnvFate) 0 1000000 2000000 3000000 4000000 5000000 6000000 7000000 8000000 0 20 40 60 80 100 120 140 160 Rel at iv e Inte nsit y Time (days) M622T973 Bti H2O 0 5000000 10000000 15000000 20000000 25000000 30000000 35000000 40000000 45000000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (days) M624T1015 Bti H20 0 200000 400000 600000 800000 1000000 1200000 1400000 1600000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (Days) M861T1045 Bti H2O 0 50000 100000 150000 200000 250000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (days) M405T1149 Bti H2O 0 5000 10000 15000 20000 25000 30000 35000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (days) M902T924 Cyp 0 100000 200000 300000 400000 500000 600000 700000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (days) M379T923 Cyp MeOH 0 20000 40000 60000 80000 100000 120000 140000 160000 180000 200000 0 20 40 60 80 100 120 140 160 Rel at iv e int ensit y Time (days) M441T922 Cyp MeOH
PCA and MANOVA of each time
in Positive ion mode
Control
vs
Bti
After 150 days of incubation PCA
analysis still showed difference
between
EMF
of
treated
sediment by Bti and EMF of
Control sediment.
(Bti at 10 times of field dose)
PCA and MANOVA of each time
in Positive ion mode
Control
vs
alpha-cypermethrin
After 150 days of incubation PCA
analysis still showed
difference
profile between EMF of
treated
sediment by Cypermethrin and
EMF of Control sediment.
(α-Cypermethrin at 10 times of
field dose)
Partial-least squares discrimination analysis (PLS-DA) was performed as supervised method to identify important variables with discriminative power (VIP) at day15.
Partial-least squares discrimination analysis (PLS-DA) was performed as supervised method to identify important variables with discriminative power (VIP) at day15.
.
Signif. codes: 0 ‘***’ 0.001 ‘**’ 0.01 ‘*’ 0.05 ‘.’ 0.1 ‘ ’ Type II MANOVA Tests: Pillai test statistic BT : Bti_Vs_Control H2O Values on the PCA plot represents percent (%) variability on the axis 1 and 2 respectively.
Half life (t
1/2)
Vs
Resilience time
Time
Time
Conc
en
tra
tio
n
Conc
en
tra
tio
n
Extractable sediment organic matter XENOMETABOLOME (Active ingredient +formulation ingredients + by products) MICROBIAL METABOLOME (Sediment meta-metabolome) 0 100000 200000 300000 400000 500000 600000 700000 0 20 40 60 80 100 120 140 160 Rela tiv e int ensity Time (days) M861T1045 Cyp MeOH P = 0.6137 P = 0.006083 ** P = 0.4758 P = 0.01735 * P = 0.363 P = 0.0003471 *** P = 0.0001319 *** P = 0.0268 * P = 8.176e-05 *** T0 T30 T15 T8 T4 T2 T150 T90 T60 21.21 14.11 22.72 16.82 24.67 17.10 29.89 16.55 18.56 22.25 30.14 14.60 22.26 15.09 18.27 14.99 23.79 16.30Signif. codes: 0 ‘***’ 0.001 ‘**’ 0.01 ‘*’ 0.05 ‘.’ 0.1 ‘ ’ Type II MANOVA Tests: Pillai test statistic BT : Bti_Vs_Control H2O Values on the PCA plot represents percent (%) variability on the axis 1 and 2 respectively.
P = 0.0001034 *** P = 8.146e-08 *** P = 4.309e-05 *** P = 4.993e-08 *** P = 1.473e-07 *** P = 1.46e-05 *** P = 3.669e-06 *** P = 1.602e-05 *** P = 5.997e-10 *** T0 T30 T15 T8 T4 T2 T150 T90 T60 34.28 38.08 28.46 31.24 30.26 34.68 37.21 33.81 36.21 15.32 14.29 13.10 12.05 13.22 13.72 17.50 16.26 16.12
Environmental Metabolic Foot-printing (EMF) approach
QIIME2 Metabolomics approach
Bti Exotoxin α-Cypermethrin
Meta-barcoding approach
Sediment Microcosm assay Sediment Microcosm assay
1) Resilience time
2) Characterization of Environmental Markers
LCMS-QToF analysis
Data generation
Data analysis Data analysis
Organic extraction
Test Complex mixture
Real Fate…