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Fernando Galvez
Dept. of Biological Sciences,
Louisiana State University
How was the biology of a marsh fish affected by the Deepwater
Horizon oil spill?
Gulf Killifish (Fundulus grandis)
• most abundant vertebrate in coastal
marshes
• easy to raise in captivity
• relatively sensitive to chemical toxicity
• transparent embryos
• extensive characterization of embryology,
physiology, biochemistry, ecology, and
population genetics
• growing genomics tool kit (genome
sequence, RNA-seq, bioinformatics,
morpholinos)
Photo: A. Whitehead
Research model
Overview of Presentation
1. What are the physiological and molecular
impacts of oil exposure at different stages of
fish development?
- fitness level consequences
2. What is the geographical and temporal extent
of oiling in the field?
3. How does evolutionary history and exposure
history affect the sensitivity of fish to DWH oil?
Experimental Questions
Basic Facts of the Deepwater Horizon Oil Spill
• Approximately 800 million liters of
oil was released during 87 days
• Oil was spread over 180,000 km2
• Approximately 6.9 million liters of
chemical dispersant was added
Exxon Valdez oil spill released
approximately 40 million liters
Maps of Shoreline Oiling Data
1,770 km of shoreline
were oiled
790 km of Louisiana
shoreline were oiled
Sample Sites for Gulf Killifish Monitoring
GT
FMABLBBFPBSL
MB
• Grande Terre (GT), Louisiana
• Bay St. Louis (BSL) and Belle Fontaine Point (BFP),
Mississippi
• Bayou La Batre (BLB), Fort Morgan (FMA) and Upper
Mobile Bay (MB), Alabama
Track marsh fish health before, during DWH
oil exposure, and during a recovery period
GT
FMABLBBFPBSL
MB
• In our sampling, GT was the only location that oil made
landfall (between June 9-14, 2010).
• Extremely high concentrations of polyaromatic
hydrocarbons in the sediment.
Experimental Design
1. Measured tissue-specific responses in field-
collected fish.
• Physiology and protein-level expression changes
• Genome-wide mRNA transcript changes
2. Performed early-life exposures to field-collected
waters and sediments.
• time-to-hatch, hatching success, gene expression.
physiology
Genome expression: Microarray
GT BSL BFP BLB MB FMA
AHR ligand regulated -4 +4
• Divergent gene
expression in livers of
GT fish
• Coincident with
location & timing of oil
• AHR ligand regulated
genes were
differentially expressed
PNAS (2012) 50: 20298-20302
-4 +4
Genome Expression Response in Livers of
Field-Collected Gulf Killifish
PAH
Hsp90AhR
AIP
Arnt
Nuclear
mRNA
Endoplasmic
Reticulum
CY
P1A
The Aryl-hydrocarbon Receptor (AhR)
-Biomarkers of Exposure
PNAS (2012) 50: 20298-20302
AhR-mediated CYP1A Protein
Expression in Gulf Killifish Gills
Dark red stain = CYP1A protein in gills from fish collected in situBlue stain = hematoxylin (nuclei)
Trip 48/28/2011
PNAS (2012) 50: 20298-20302
GT BSL BFP BLB MB FMA
AHR ligand regulated -4 +4
• Divergent gene
expression in livers of
GT fish
• Coincident with
location & timing of oil
• AHR ligand regulated
genes were
differentially expressed
PNAS (2012) 50: 20298-20302
-4 +4
Genome Expression Response in Livers of
Field-Collected Gulf Killifish
HYPOTHESIS:Exposure to toxic components of oil
GT BSL BFP BLB MB FMA
Reproduction +4-4
• Genes turned OFF coincident with timing/location of oiling:
Zona pellucida
Choriogenin
Vitellogenin
Genome Expression Response in Livers of
Field-Collected Gulf Killifish
PNAS (2012) 50: 20298-20302
Ligand (PAH)-activated AHR
Ubiquitin-ligase activity
Proteolytic degradation of
sex steroid receptors
Suppression of sex
hormone induced gene
expression
Proteolysis -4 +4
GT BSL BFP BLB MB FMA
Genome Expression Response in Livers of
Field-Collected Gulf Killifish
PNAS (2012) 50: 20298-20302
Ligand (PAH)-activated AHR
Ubiquitin-ligase activity
Proteolytic degradation of
sex steroid receptors
Suppression of sex
hormone induced gene
expression
Proteolysis -4 +4
GT BSL BFP BLB MB FMA
Genome Expression Response in Livers of
Field-Collected Gulf Killifish
PNAS (2012) 50: 20298-20302
HYPOTHESIS:Compromised reproduction
(altered estrogen signaling)
Cardiovascular+4-4
GT BSL BFP BLB MB FMA
-2 +2Cardiovascular
GT BSL BFP BLB MB FMA
Genome Expression Response in Livers of
Field Collected Gulf Killifish
PNAS (2012) 50: 20298-20302
Cardiovascular+4-4
GT BSL BFP BLB MB FMA
-2 +2Cardiovascular
GT BSL BFP BLB MB FMA
Genome Expression Response in Livers of
Field Collected Gulf Killifish
PNAS (2012) 50: 20298-20302
HYPOTHESIS:Altered cardiac
physiology
Conclusions
• Large signal of hydrocarbon exposure exists in
Louisiana marsh fish collected in situ.
• CYP1a expression is highly elevated in the gills
and livers of fish collected from oil-contaminated
sites.
• Transcriptomics data suggest potential for
reduced reproductive capacity and alterations in
cardiovascular physiology
Gulf of
Mexico
Bay
Batiste
Bay Jimmy
Barataria
Bay
Grand Terre
Island, LA
***
**
***
* ** *
**
*
Sampling Sites in Southern Louisiana
*
*
Gulf of
Mexico
Bay
Batiste
Bay Jimmy
Barataria
Bay
Grand Terre
Island, LA
***
**
***
* ** *
**
*
Sampling Sites in Southern Louisiana
Gulf of
MexicoNBS WB GT GT
To
tal
[PA
H]
µg
/g
0204060
300
350
400
2011 2010
Killifish embryo exposures to
field-collected sediments
EST (2013) 47: 5074-5082
“Clean” 12 ppt water
Sediment
EST (2013) 47: 5074-5082
Killifish embryo exposures to
field-collected sediments
Effects of PAHs on Heart Function
Sampling Locations
NBS 2011WB 2011 GT 2011 GT 2010
tPA
Hs
(ng
/g)
0
15x1
03
30x1
03
300x
103
325x
103
350x
103
NBS WB GT GT
20
11
20
10
20
10
2011
2011
2011
Sampling Locations
NBS 2011 WB 2011 GT 2011 GT 2010
Hea
rt
Ra
te (
BP
M)
0
20
40
60
80
100
120
*
*
NBS WB GT GT
P≤0.05
EST (2013) 47: 5074-5082
20
10
2011
2011
2011
Hatching and tPAHs
Sampling Locations
NBS 2011WB 2011 GT 2011 GT 2010
tPA
Hs
(ng
/g)
0
15x1
03
30x1
03
300x
103
325x
103
350x
103
Days Post Fertilization
8 10 12 14 16 18 20 22
Per
cen
tag
e H
atc
h
-20
0
20
40
60
80
100
NBS 2011
WB 2011
GT 2011
GT 2010
*
**
* *
* *
**
** * *
*****
NBS WB GT GT
2011
2010
2010
2011
2011
2011
P≤0.05
EST (2013) 47: 5074-5082
Hatch
Influence of Oiled Sediments on Fish Hatch
EST (2013) 47: 5074-5082
NBS WB GT GT
Pe
rcen
t o
f T
ota
l
0
25
50
75
100
2011 2010
Dead
Hatched
Unhatched
PAH-induced Teratogenesis
Elongated Heart and Improper Folding
Pericardial Edema
Craniofacial Deformities Hemorrhage
Conclusions
• Exposure to field-collected sediments increases
time-to-hatch and reduces the percent hatch of
killifish embryos.
• DWH oil leads to teratogenic effects and affects
cardiovascular fitness
Oceans and Human Health Centers:
Mechanisms of reproductive,
developmental, and early life stage
impacts of marine
DWH Oil Spill: NEXT?...
Andrew WhiteheadFernando Galvez Christopher Green
Health risk
Early-life development
Juvenile/adult
performance
Reproduction
Low level exposures during critical developmental stages impacts in later life
Early-life development
Juvenile/adult performance
Reproduction
+
Health risk
Low level exposures during critical developmental stages impacts in later life
Adult exposures impacts on reproduction
Early-life development
Juvenile/adult performance
Reproduction
+
Health risk
Low level exposures during critical developmental stages impacts in later life
Adult exposures impacts on reproduction
Adult & early-life exposures trans-generational impacts
Early-life development
Juvenile/adult performance
Reproduction
+
Health risk
Low level exposures during critical developmental stages impacts in later life
Adult exposures impacts on reproduction
Adult & early-life exposures trans-generational impacts
Mechanisms morphology, physiology, genome expression, genome imprinting
Early-life development
Juvenile/adult performance
Reproduction
Health risk
Low level exposures during critical developmental stages impacts in later life
Adult exposures impacts on reproduction
Adult & early-life exposures trans-generational impacts
Mechanisms morphology, physiology, genome expression, genome imprinting
Genetic variation & exposure history protect or sensitize individuals
Early-life development
Juvenile/adult performance
Reproduction
1 2
3
1 TX
2 LA
3 FL
4
4 LA – recent exposure history
5
5 TX – long exposure history
Genetic diversity
Health risk
Gulf killifish with different “exposure”
histories were collected along the nGOM
1 Gang’s Bayou, TX
2 LSU Aquaculture, LA
3 St. Teresa, FL
4 Grande Terre, LA (2015) – prior DWH oil exposure
5 Vince Bayou, TX – long exposure history
Reference populations
1 2
3
45
Gulf killifish with different “exposure”
histories were collected along the nGOM
• Each population of adult fish were exposed to control
water (i.e., parental controls; PC) or to 25% high-
energy oiled WAF for at least 40 days (i.e., parental
exposed; PE)
Brood fish collection
Parental exposures
LSU, LA
PEPC
Grand Terre, LA (2015)
PEPC
Gang’s Bayou, TX
PEPC
Vince Bayou, TX
PEPC
Fertilization
Gulf killifish with different “exposure”
histories were collected along the nGOM
Brood fish collection
Parental exposures
LSU, LA
PEPC
Grand Terre, LA (2015)
PEPC
Gang’s Bayou, TX
PEPC
Vince Bayou, TX
PEPC
Fertilization
0
20
40
60
80
100
VinceBayou
Gang'sBayou
GrandeTerre
LSU-LA
Fert
iliz
ati
on
(%
)
PC
PE
Gulf killifish with different “exposure”
histories were collected along the nGOM
Brood fish collection
Parental exposures
LSU, LA
PEPC
Grand Terre, LA (2015)
PEPC
Gang’s Bayou, TX
PEPC
Vince Bayou, TX
PEPC
Fertilization
0% 10% 32% 56%
Embryo DWH Oil exposures for all treatments
Conclusions
• Genetic variation & exposure history can either
protect or sensitize individuals to subsequent oil
exposure
• F1 embryos from Louisiana populations are more
sensitive to DWH oil
• F0 adults from an adapted population are
recalcitrant to DWH oil (i.e., retains high
reproductive capacity
• F1 embryos from an adapted population is more
resistant to cardiovascular teratogenesis
Acknowledgements
Whitehead lab• Jennifer Roach
• Jan Park
Galvez lab• Charles Brown
• Tiffany Simms
• Chelsea Adams
• Ben Dubansky
Green lab• Chelsea Bonner
• Zachary McDaniel
QUESTIONS?