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The
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Process
A template
for learning about
the physical world
Atrazine
Hermaphroditic, demasculinized frogs after exposure
to the herbicide atrazine at low ecologically
relevant doses
Tyrone B. Hayes*, Atif Collins, Melissa Lee, Magdelena Mendoza, Nigel Noriega, A. Ali Stuart, and Aaron Vonk
Laboratory for Integrative Studies in Amphibian Biology, Group in Endocrinology, Museum of Vertebrate Zoology, Department of Integrative Biology,
University of California, Berkeley, CA 94720-3140

Communicated by David B. Wake, University of California, Berkeley, CA, March 1, 2002 (received for review December 20, 2001)

Atrazine is the most commonly used herbicide in the U.S. and                  human choriogonadotropin (1,000 international units) 6 h before
probably the world. It can be present at several parts per million in         harvesting gametes. Eggs were manually stripped from the
agricultural runoff and can reach 40 parts per billion (ppb) in               female and fertilized in vitro in 0.3       modified mammalian
precipitation. We examined the effects of atrazine on sexual                  Ringer’s solution by using the sperm obtained from the dissected
development in African clawed frogs (Xenopus laevis). Larvae were             testes of the three males. The embryos were allowed to hatch.
exposed to atrazine (0.01–200 ppb) by immersion throughout                    After 4 days, the larvae were all mixed and netted into tanks 5
larval development, and we examined gonadal histology and                     at a time repeatedly, until all tanks contained 30 larvae. Larvae
laryngeal size at metamorphosis. Atrazine (>0.1 ppb) induced                  were reared in 4 liters of aerated 10% Holtfreter’s solution (15)
hermaphroditism and demasculinized the larynges of exposed                    and fed a solution of ground Purina rabbit chow daily. Food
males (>1.0 ppb). In addition, we examined plasma testosterone                levels were adjusted as the animals grew to maximize growth.
levels in sexually mature males. Male X. laevis suffered a 10-fold
decrease in testosterone levels when exposed to 25 ppb atrazine.              Dosing. In Exp. 1, we exposed larvae to atrazine at nominal
We hypothesize that atrazine induces aromatase and promotes the               concentrations of 0.01, 0.1, 1.0, 10.0, and 25 parts per billion
conversion of testosterone to estrogen. This disruption in steroi-            (ppb), whereas the second experiment used 0.1, 0.4, 0.8, 1.0, 25,
dogenesis likely explains the demasculinization of the male larynx            and 200 ppb atrazine. Concentrations were confirmed by two
and the production of hermaphrodites. The effective levels re-                independent laboratories (PTRL West, Richmond, CA, and the
ported in the current study are realistic exposures that suggest that         Iowa Hygienic Laboratory, Univ. of Iowa, Iowa City, IO). All
other amphibian species exposed to atrazine in the wild could be              stock solutions were made in ethanol (10 ml), mixed in 15-gallon
at risk of impaired sexual development. This widespread com-                  containers, and dispensed into treatment tanks. Controls were
pound and other environmental endocrine disruptors may be a                   treated with ethanol such that all tanks contained 0.004%
factor in global amphibian declines.                                          ethanol. Water was changed and treatments were renewed once
                                                                              every 72 h. Each treatment was replicated 3 times with 30

I n the last 10 years, a great deal of attention has focused on the
  global presence of endocrine-disrupting contaminants in the
environment (1, 2). Similarly, a great deal of attention has
                                                                              animals per replicate (total of 90 animals per treatment) in both
                                                                              experiments. All treatments were systematically rotated around
                                                                              the shelf every 3 days to ensure that no one treatment or no one
focused on global amphibian declines (3, 4). In the case of                   tank experienced position effects. Experiments were carried out
amphibian declines, efforts focus on identifying causes (5),                  at 22°C with animals under a 12-h 12-h light dark cycle (lights
Scientific findings should be
independently verifiable
AtrazineLovers.com
Atrazine.com
0.4
The
Science
of   Life
1.1 - 1.4, 1.9
What properties
does life have?
The Majestic
Plastic Bag

http://www.youtube.com/watch?
v=GLgh9h2ePYw
Cellular Organization
Metabolism
Homeostasis
Growth and Reproduction
Heredity
Biological Themes
Hierarchical
Organization
Emergent
Properties

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Life

  • 2. A template for learning about the physical world
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  • 5. Hermaphroditic, demasculinized frogs after exposure to the herbicide atrazine at low ecologically relevant doses Tyrone B. Hayes*, Atif Collins, Melissa Lee, Magdelena Mendoza, Nigel Noriega, A. Ali Stuart, and Aaron Vonk Laboratory for Integrative Studies in Amphibian Biology, Group in Endocrinology, Museum of Vertebrate Zoology, Department of Integrative Biology, University of California, Berkeley, CA 94720-3140 Communicated by David B. Wake, University of California, Berkeley, CA, March 1, 2002 (received for review December 20, 2001) Atrazine is the most commonly used herbicide in the U.S. and human choriogonadotropin (1,000 international units) 6 h before probably the world. It can be present at several parts per million in harvesting gametes. Eggs were manually stripped from the agricultural runoff and can reach 40 parts per billion (ppb) in female and fertilized in vitro in 0.3 modified mammalian precipitation. We examined the effects of atrazine on sexual Ringer’s solution by using the sperm obtained from the dissected development in African clawed frogs (Xenopus laevis). Larvae were testes of the three males. The embryos were allowed to hatch. exposed to atrazine (0.01–200 ppb) by immersion throughout After 4 days, the larvae were all mixed and netted into tanks 5 larval development, and we examined gonadal histology and at a time repeatedly, until all tanks contained 30 larvae. Larvae laryngeal size at metamorphosis. Atrazine (>0.1 ppb) induced were reared in 4 liters of aerated 10% Holtfreter’s solution (15) hermaphroditism and demasculinized the larynges of exposed and fed a solution of ground Purina rabbit chow daily. Food males (>1.0 ppb). In addition, we examined plasma testosterone levels were adjusted as the animals grew to maximize growth. levels in sexually mature males. Male X. laevis suffered a 10-fold decrease in testosterone levels when exposed to 25 ppb atrazine. Dosing. In Exp. 1, we exposed larvae to atrazine at nominal We hypothesize that atrazine induces aromatase and promotes the concentrations of 0.01, 0.1, 1.0, 10.0, and 25 parts per billion conversion of testosterone to estrogen. This disruption in steroi- (ppb), whereas the second experiment used 0.1, 0.4, 0.8, 1.0, 25, dogenesis likely explains the demasculinization of the male larynx and 200 ppb atrazine. Concentrations were confirmed by two and the production of hermaphrodites. The effective levels re- independent laboratories (PTRL West, Richmond, CA, and the ported in the current study are realistic exposures that suggest that Iowa Hygienic Laboratory, Univ. of Iowa, Iowa City, IO). All other amphibian species exposed to atrazine in the wild could be stock solutions were made in ethanol (10 ml), mixed in 15-gallon at risk of impaired sexual development. This widespread com- containers, and dispensed into treatment tanks. Controls were pound and other environmental endocrine disruptors may be a treated with ethanol such that all tanks contained 0.004% factor in global amphibian declines. ethanol. Water was changed and treatments were renewed once every 72 h. Each treatment was replicated 3 times with 30 I n the last 10 years, a great deal of attention has focused on the global presence of endocrine-disrupting contaminants in the environment (1, 2). Similarly, a great deal of attention has animals per replicate (total of 90 animals per treatment) in both experiments. All treatments were systematically rotated around the shelf every 3 days to ensure that no one treatment or no one focused on global amphibian declines (3, 4). In the case of tank experienced position effects. Experiments were carried out amphibian declines, efforts focus on identifying causes (5), at 22°C with animals under a 12-h 12-h light dark cycle (lights
  • 6. Scientific findings should be independently verifiable
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  • 11. 1.1 - 1.4, 1.9
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