fate and transport of steroids in the environment: what goes in, … · 2010. 10. 15. · fate and...
TRANSCRIPT
Alan Kolok
Department of Biology Department of Environmental, Agricultural
& Occupational Health
Fate and transport of steroids in the environment:
What goes in, must come out?
Institute of Agriculture and Natural Resources
October 14, 2010 University of Nebraska – Lincoln
East Campus Union.
Steroids and the U.S. beef cattle industry
More than 90% of US beef cattle are given growth promoting implants.
The most common implant contains trenbolone acetate and
estradiol.
28 mg 200 mg Synovex Plus
Estradiol Trenbolone
Acetate
Brand
Name
Endogenous steroid metabolites
(but not Testosterone)
Unimplanted
17 -Trenbolone, 17 -Trenbolone
17 -estradiol, estrone
Trenbolone acetate
Estradiol benzoate
Implanted
Na
no
gra
ms r
eco
vere
d
Estrone
Androstenedione
0.05
0.10
0.15
0.2 17 Trenbolone
Sellin et al. 2009. Aq. Toxicol.
.1
.2
.3
.4
.5
.6
.7
0
.04
.08
.12
.16
I
I
U
Exposures to exogenous steroids and steroid
mimics disrupt the endocrine function of fish.
Normal Female
17-estradiol
Vitellogenin
17-estradiol
Vitellogenin
Trenbolone
Ankley et al. 2003. Environ Toxicol Chem 22:1350-1360.
17-TB reduces female plasma vitellogenin levels
Exposures to steroids and steroid mimics disrupt
the endocrine function of fish.
Normal Female
17-estradiol
Vitellogenin
Normal Male
17-estradiol
Vitellogenin
Seki et al. 2006. Environ Toxicol Chem. 25:2742-2752.
Vitellogenin
Estrogens
Vit
ello
gen
in (
mg
/mL
)
Estradiol concentration (ng/L)
17-E2 increases male plasma vitellogenin levels
Rela
tive
Gen
e E
xp
ressio
n
Steer Feces (mg/L)
0
.5
1
1.5
2
2.5
3
3.5
Control 0.012 1.25 125 6250
Vtg/L8
Sellin et al. 2009. Aq.Tox. 92:221-227.
Steer Feces (mg/L)
Vtg/L8
Rela
tive
Gen
e E
xp
ressio
n
0
.2
.4
.6
.8
1
1.2
1.4
0 1.25 125 6250 1250
*
Implanted
Unimplanted
Sellin et al. 2009. Aq.Tox. 92:221-227.
Laboratory
Field
No
TBA,
Estrogenic
effect
* detection limit = 1 ng
Compound
17-estradiol
Estrone
Estriol
17-trenbolone
17-trenbolone
Pearl Cr.
ND
ND
ND
ND
ND
Bow Cr.
ND
ND
ND
ND
ND
E. Bow Cr.
ND
ND
ND
ND
ND
Compound
17-estradiol
Estrone
Estriol
17-trenbolone
17-trenbolone
Niobrara
ND
ND
ND
ND
ND
Elkhorn
ND
ND
ND
ND
ND
Platte
ND
ND
ND
ND
ND
Elkhorn River Bow Creek
Niobrara
River
Re
lative
gene
exp
ressio
n
Elkhorn
River
Platte
River
0.4
0.8
1.2
Field
Laboratory R
ela
tive
ge
ne
exp
ressio
n
0
0.8
1.6
Elkhorn
River
Lab H2O
Rela
tive
ge
ne
exp
ressio
n
0.2
0.6
1
East Bow
Creek
Pearl
Creek
Re
lative
ge
ne
exp
ressio
n
0.1
0.4
0.7
East Bow
Creek Lab water
controls
Sellin et al. 2009. ET&C. 28:2443-2448. Sellin et al. 2010. Aq Tox 96:103-108.
Laboratory
Field
No
TBA,
Estrogenic
effect
No
TBA,
Anti-
estrogenic
effect
Water
Sediment
Elkhorn River -Vtg R
ela
tive g
ene
expre
ssio
n
0.4
0.8
1.2
1.6
2
Bow Creek - ER
Rela
tive g
ene
expre
ssio
n
0
0.2
0.4
0.6
0.8
Sellin et al. 2010. Aq Tox 96:103-108.
Defeminization of female fathead minnows and sediment exposure.
Lab
water Field
water Field
exposure Sediment,
field water
Sediment,
lab water
Is the trenbolone in the sediment ?
Tb in
Water
(+ control)
A
Tb in
sediment
B
Lab
Water
(neg. control)
Vitellogenin
0
Rela
tive
gene
exp
resso
in
0.4
0.8
1.2
1.6
C
Kolok et al. In prep. Env Biol Fish