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JUVENILES FROMAQUACULTURE
RESTOCKING OFNATURAL HABITATS
SPORTFISHING
COMMERCIALAQUACULTURE
COMMERCIALFISHING
AQUARIUMTRADE
ENVIROMENTALPOLLUTION
ASSESSMENT
HANDYCRAFTS &
TROPHEES
BYPRODUCTSUTILIZATION
DIGESTIVEENZYMES
• Native species from the Native species from the Atlantic coast of North Atlantic coast of North AmericaAmerica
• Availability of individuals Availability of individuals raised under controlled raised under controlled conditionsconditions
• Able to tolerate different Able to tolerate different physicochemical physicochemical conditions (e.g.saltwater, conditions (e.g.saltwater, OO22, , ammonia, etc) ammonia, etc)
• Top position in the food Top position in the food web and occasional web and occasional scavengerscavenger
• High metabolic rate (e.g. High metabolic rate (e.g. growth)growth)
• Continuous contact with Continuous contact with the bottomthe bottom
• Ancient fish (simple Ancient fish (simple metabolic pathways)metabolic pathways)
Establishment of lab and field
methodologies to asses the impact of
aquatic pollution by means of
biomarkers in Alligator gar (A. spatula)
Establishment of lab and field
methodologies to asses the impact of
aquatic pollution by means of
biomarkers in Alligator gar (A. spatula)
1) BIOMARKERS SELECTION:
Implementing lab techniques for the evaluation of different biomarkers
Determining the response of alligator gar, of different ages to known environmental disruptors
1) BIOMARKERS SELECTION:
Implementing lab techniques for the evaluation of different biomarkers
Determining the response of alligator gar, of different ages to known environmental disruptors
1) Esterases • Carboxylesterases• Acetyl cholinesterase• Butiryl cholinesterase
2) Detoxification Glutathione S-transferase
3) Oxidative stress Superoxide Dismutase
4) Tissue injury Alkaline phosphatase
1) Esterases • Carboxylesterases• Acetyl cholinesterase• Butiryl cholinesterase
2) Detoxification Glutathione S-transferase
3) Oxidative stress Superoxide Dismutase
4) Tissue injury Alkaline phosphatase
1) DetoxificationCytochrome P450(CYP1A)
2) Endocrine Disruption Vitellogenin
(VTG)
1) DetoxificationCytochrome P450(CYP1A)
2) Endocrine Disruption Vitellogenin
(VTG)
1) Hydrocarbure (H)-naphtophlavone
2) Pesticide (P) Organophosphorate (Diazinon) 3) Endocrine Disruptor (ED) 17-Estradiol 4) Control (C) Fish Oil (Menhaden Oil)
1) Hydrocarbure (H)-naphtophlavone
2) Pesticide (P) Organophosphorate (Diazinon) 3) Endocrine Disruptor (ED) 17-Estradiol 4) Control (C) Fish Oil (Menhaden Oil)
Alligator gar: 3/Treatments
1 year: 60 g; 23 cm 2 years: 309 g; 38 cm Treatments application 50 mg/1000g in fish oil Intraperitoneal injection (exposure: 48 h)Tissue samples: Liver (L); Plasma (P); Gills (G); Mucus (M)
Alligator gar: 3/Treatments
1 year: 60 g; 23 cm 2 years: 309 g; 38 cm Treatments application 50 mg/1000g in fish oil Intraperitoneal injection (exposure: 48 h)Tissue samples: Liver (L); Plasma (P); Gills (G); Mucus (M)
ALLIGATOR GARALLIGATOR GAR
500 L Fiber glass tanks
500 L Fiber glass tanks
Treatment application(50 mg / 1000 g)
Treatment application(50 mg / 1000 g)
FILTER
FILTER
TissuesampleTissuesample
Sample inliquid N2
Sample inliquid N2
BiomarkerDetermination
BiomarkerDetermination
•A group of isozymes mainly located in RERA group of isozymes mainly located in RER
•Involved in metabolism of a wide variety of xenobiotics Involved in metabolism of a wide variety of xenobiotics containing esther, thioesther and amide groups. containing esther, thioesther and amide groups.
•Highest affinity for pesticides than related family of Highest affinity for pesticides than related family of cholinesterases (acetyl and butiryl)cholinesterases (acetyl and butiryl)
•Pesticides cause activity inhibition in most tissues Pesticides cause activity inhibition in most tissues • e.g. Livere.g. Liver
•Other xenobiotics cause Increase of activityOther xenobiotics cause Increase of activity
ASSAY METHODASSAY METHODEnzyme kinetics in 96-well microtiter plate using Enzyme kinetics in 96-well microtiter plate using
p-nitrophenyl acetate as substrate (Munilla & Starck, 1990p-nitrophenyl acetate as substrate (Munilla & Starck, 1990)
0.2 ml0.2 mlsubstratesubstrate
0.2 ml0.2 mlsubstratesubstrate
0.02 ml0.02 mlBufferBuffer
0.020.02 mlmlEnzymeEnzymeextractextract
Plus
Abs.Abs.405 nm405 nm10 min.10 min.
Carboxylesterase activity in 1 year alligator gar
0
0.1
0.2
0.3
0.4
0.5
0.6
ED H C
Treatments
Abs
/min
/mg
prot
ein
L
G
A
B
B
A A A
Carboxylesterase activity in 2 years alligator gar
0
0.1
0.2
0.3
0.4
0.5
0.6
ED H C P
Treatments
Abs/
min
/mg
prot
ein
P
L
G
A A A A
A A A
B
ABA A B
•Nonspecific phosphomono-esterase that removes a Nonspecific phosphomono-esterase that removes a phosphate group and transfers it to other molecules.phosphate group and transfers it to other molecules.
•Pollutants cause activity variation in several tissues. Pollutants cause activity variation in several tissues.
•Increased activity in the plasma in a variety of disease Increased activity in the plasma in a variety of disease conditions.conditions.
•Biomarker of tissue injury.Biomarker of tissue injury.
ASSAY METHODEnzyme kinetics in 96-well microtiter plate using
4-nitrophenyl phosphate as substrate (Moyano et al , 1996)
0.2 ml0.2 mlsubstratesubstrate
0.2 ml0.2 mlsubstratesubstrate
0.02 ml0.02 mlBufferBuffer
0.020.02 mlmlEnzymeEnzymeextractextract
Plus
Abs.Abs.405 nm405 nm10 min.10 min.
Alkaline phosphatase activity in 1 year alligator gar
0
0.2
0.4
0.6
0.8
1
1.2
ED H C
Treatments
Abs
/min
/mg
prot
ein
L
G
A
B
B
A A A
Alkaline phosphatase activity in 2 years alligator gar
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
ED H C P
Treatments
Abs
/min
/mg
prot
ein
L
G
AB
B
B
A
A AA
A
•Vtg is an estrogen-inducible protein synthesized by the liver.
•Males do not produce Vtg in measurable quantities under normal conditions, however have the capacity to synthesize it.
•Many chemicals that are released into the environment possess estrogenic properties.
•Measurement of Vtg in males and juveniles provides an excellent biomarker for estrogenic compounds.
washing
VTG Alligator gar VTG
VTG VTG
VTG Saturation
defatted milk
Secondary antibody
washing
washing
washing
enzyme substrate OPD
VTG immobilization
VTG VTG
VTG
IncubationVTGStandar Vtg or Sample
anti-VTG
VTG+
Competition
VTGVTG VTG
VTG
incubation
VTG VTG
VTG
Optical density measure
VTG VTG
VTG
METHOD:METHOD:Homologus competitive Homologus competitive
ELISAELISA
(Mendoza et al., In Press)(Mendoza et al., In Press)
VTG concentration in 1 year Alligator gar
0102030405060708090
100
ED H C
Treatments
ng
de
vtg
/mg
pro
tein
L
G
M
A
B BAB B
A
VTG concentration in 2 years alligator gar
0
20
40
60
80
100
120
ED H C P
Treatments
ng
vtg
/mg
pro
tein
P
L
G
M
A
B B B
BiomarkerEnvironmental disruptorEnvironmental disruptor
HydrocarbureHydrocarbure PesticidePesticide EstrogenicEstrogenic
Carboxyl -Carboxyl -esteraseesterase
Slight Reduction
(1 year)Reduction Increase
Alkaline Alkaline phosphatasephosphatase
Slight Reduction Increase Increase
VitellogeninVitellogenin Increase