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Effects of Dietary Selenium and Methylmercury on Green and White Sturgeon
Bioenergetics in Response to Changed Environmental Conditions.
1,2Robert C. Kaufman, 1Ann G. Houck, and 1Joseph J. Cech, Jr.
1Wildlife Fish and Conservation Biology, UC Davis
2Pharmacology and Toxicology Graduate Group, UC Davis
SF Bay-Delta is a multiply-stressed ecosystem
•Water diversions
•Salinity fluctuations
•Pollutants e.g., agricultural, industrial, storm-water runoff. Selenium (SeMet) and Mercury (MeHg) are toxicants of concern
•Introduced species, e.g., Asian clam
•Several species are currently imperiled e.g., POD & salmon
•Green and white sturgeon numbers are in decline
•Green sturgeon listed as threatened in 2006
Problems
• Little is known of the effects of Hg on wildlife
• Aquatic food web recognized as the most
efficient process of bioaccumulation of Hg
• Studies have shown reduced capacity for:
– Reproduction when exposed as juveniles
– Growth
– Ability to avoid predators
– Shoaling
– Swimming performance
Problems cont.:
• Selenium: nutritional versus toxicity
• Effects on wildlife well documented
• Studies have shown that Se:
– Teratogenic in fish and avian species e.g., Belews Lake, NC and Kesterson, CA.
– Decreased reproduction
– Concentrations in North SF Bay-Delta are a concern
– Multiple sources of input e.g., agriculture and refining
processes
Objectives
• Determine effects of SeMet and MeHg on
sturgeon bioenergetics
• Determine the effects of environmental
stressors, temperature and salinity, on
previously exposed (SeMet & MeHg) individuals’
bioenergetics
• Determine the feasibility of using non-listed, and
domesticated white sturgeon as a surrogate for
green sturgeon in toxicity testing
56-Day Growth Experiment
Elevated Temperature•25°C
•Gradual increase from ambient to 25°C over 12 hours•Maintain 25°C for all performance experiments
Ambient•18º C
•Air-equlibratedwell water•Hold fish for 24 hours prior to start of experiments
Elevated Salinity•Ambient Temperature
•Increase from 0 ppt to 18 ppt over 8 hours•Maintain 18 pptsalinity for all experiments
Predator avoidance
Routine & Active metabolic rates
Critical SwimmingVelocity
Tissue samples for Se, Hg, & glycogen content
Tissue samples for Proteomic analysis
Dietary MeHg effects on white sturgeon predator
avoidance
0
0.1
0.2
0.3
0.4
0.5
0.6
MeHg-0 ppm MeHg-25 ppm MeHg-50 ppm
MeHg dose (ppm)
qu
ad
ran
ts p
er
seco
nd
ambient
25 C
18 ppt
a
a
b
A
Dietary MeHg effects on green sturgeon predator
avoidance.
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
0.40
0.45
Hg-0 ppm Hg-25 ppm
Hg dose (0 ppm)
qu
ad
ran
ts p
er
seco
nd
ambient
25 C
18 ppt
a
c
b
B
d
SeMet effects on simulated predator avoidance in white
sturgeon
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0.70
Se-0 ppm Se-20 ppm Se-40 ppm Se-80 ppm
Dietary dose SeMet (ppm)
qu
ad
ran
ts p
er
seco
nd
ambient
25 C
18 ppt
a
a a
b
cc
d
d
e
e
f
f
A
SeMet effects on green sturgeon simulated predator
avoidance
0.00
0.10
0.20
0.30
0.40
0.50
0.60
Se-0 ppm Se-20 ppm Se- 40 ppm Se-80 ppm
SeMet dietary dose (ppm)
qu
ad
ran
ts p
er
seco
nd
ambient
25 C
18 ppt
aa
a
b bbb bb
b b
B
b
Routine and ‘active’ metabolic rates determined using Blazka-type
respirometers after
the growth expt.
WS Routine & Active Metabolic Rate (MeHg)
0
100
200
300
400
500
600
hg-1 hg-2 hg-3 hg-1 hg-2 hg-1 hg-2 hg-3
Treatment Group
mg O
2/k
g/h
r
Ambient routine
Ambient active
25 C routine
25 C active
18 ppt routine
18 ppt active
A
GS Routine & Active Metabolic Rates
0
100
200
300
400
500
600
hg-1 hg-2 hg-1 hg-2 hg-1 hg-2
Treatment Group
mg
O2/k
g/h
r
Ambient routine
Ambient active
25 C routine
25 C active
18 ppt routine
18 ppt active
B
GS Metabolic Rates (SeMet)
0
100
200
300
400
500
600
700
Se
-1
Se
-2
Se
-3
Se
-4
Se
-1
Se
-2
Se
-3
Se
-4
Se
-1
Se
-2
Treatment Group
mg
O2
/kg
/hr
Ambient routine
Ambient active
25 C routine
25 C active
18 ppt routine
18 ppt active
B
WS Metabolic Rates (SeMet)
0
100
200
300
400
500
600
700
Se-1
Se-2
Se-3
Se-4
Se-1
Se-2
Se-3
Se-4
Se-1
Se-2
Se-3
Se-4
Treatment Group
mgO
2/k
g/h
r
Ambient routine
Ambient active
25 C routine
25 C active
18 ppt routine
18 ppt active
A
Dietary effects of MeHg on white sturgeon swimming
performance
0
20
40
60
80
100
120
MeHg-0 ppm MeHg-25 ppm MeHg-50 ppm
MeHg dietary dose (ppm)
cri
tical sw
mm
ing
velo
city (cm
/sec)
ambient
25 C
18 ppt
a
b
b
c
d
A
Dietary MeHg effects on green sturgeon swimming
performance
0
10
20
30
40
50
60
70
80
90
100
MeHg-0 ppm MeHg-25 ppm
Dietary dose MeHg (ppm)
critical sw
imin
g v
elo
city
(cm
/sec)
ambient
25 C
18 ppt
a
b
B
c
d
Dietary effects of SeMet on white sturgeon swimming
performance
0
20
40
60
80
100
120
SeMet- 0
ppm
SeMet-20
ppm
SeMet-40
ppm
SeMet-80
ppm
Dietary dose SeMet (ppm)
cri
tical sw
imm
ing
velo
cit
y
(cm
/sec)
ambient
25 C
18 ppt
a
b
c
d,f
e
A
Dietary effect of SeMet on green sturgeon
swimming performance
0
10
20
30
40
50
60
70
80
90
SeMet-0
ppm
SeMet- 20
ppm
SeMet-40
ppm
SeMet-80
ppm
SeMet dietary dose (ppm
cri
tical sw
imm
ing
velo
cit
y
(cm
/sec) ambient
25 C
18 ppt
a e g
b,cf
hb f
b,d
B
Conclusions
• Significant differences in ‘predator’ avoidance observed in both species with the most dramatic effect in GS
• Dietary SeMet treatments produced significant decreases in ‘active’ metabolism in WS at highest dose
• Dietary MeHg treatments produced significant decreases in bioenergetics albeit at very high doses
• Dietary SeMet resulted in significant declines in performance measures in both species with green sturgeon showing a greater sensitivity to this toxicant at all levels tested
• White sturgeon are not an appropriate surrogate for green sturgeon in determining the effects of these toxicants on sturgeon bioenergetics
Future Course
• Develop reliable source of green sturgeon larvae and juveniles for toxicity testing and tracking studies to determine habitat usage by green sturgeon juveniles, e.g., wild-caught broodstock
• Determine the NOEC of SeMet in green sturgeon juveniles
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