Long-term exposure to environmental concentrations of the pharmaceutical ethynylestradiol causes reproductive failure in fish.
Heightened concern over endocrine-disrupting chemicals is driven by the hypothesis that they could reduce reproductive success Reproductive success is defined as the passing of genes onto the next generation in a way that they too can pass those genes on. In practice, this is often a tally of the number of offspring produced by an individual. and affect wildlife populations, but there is little evidence for this expectation. The pharmaceutical ethynylestradiol (E[E.sub.2]) is a potent endocrine modulator Modulator
Any device or circuit by means of which a desired signal is impressed upon a higher-frequency periodic wave known as a carrier. The process is called modulation. The modulator may vary the amplitude, frequency, or phase of the carrier. and is present in the aquatic environment at biologically active concentrations. To investigate impacts on reproductive success and mechanisms of disruption, we exposed breeding populations (n = 12) of zebrafish (Danio da·ni·o
n. pl. da·ni·os
Any of various small, often brightly colored freshwater fishes of the genera Danio and Brachydanio, native to Asia and popular as aquarium fish. rerio) over multiple generations to environmentally relevant concentrations of E[E.sub.2]. Life-long exposure to 5 ng/L E[E.sub.2] in the [F.sub.1] generation caused a 56% reduction in fecundity fecundity /fe·cun·di·ty/ (fe-kun´dit-e)
1. in demography, the physiological ability to reproduce, as opposed to fertility.
2. ability to produce offspring rapidly and in large numbers. and complete population failure with no fertilization. Conversely, the same level of exposure for up to 40 days in mature adults in the parental [F.sub.0] generation had no impact on reproductive success. Infertility in the [F.sub.1] generation after life-long exposure to 5 ng/L E[E.sub.2] was due to disturbed sexual differentiation sexual differentiation See Hermaphroditism, hirsutism, Müllerian ducts, Precocious puberty, Pseudoprecocious puberty, Tanner staging, Testis-determining factor, Virilization, Wolffian ducts, XXX, XXY, XXXY, XYY syndromes, Y Chromosome. , with males having no functional testes testes
Male reproductive organs (see reproductive system). Humans have two oval-shaped testes 1.5–2 in. (4–5 cm) long that produce sperm and androgens (mainly testosterone), contained in a sac (scrotum) behind the penis. and either undifferentiated or intersex intersex /in·ter·sex/ (in´ter-seks)
female intersex a female pseudohermaphrodite. gonads. These [F.sub.1] males also showed a reduced vitellogenic response when compared with [F.sub.0] males, indicating an acclimation acclimation /ac·cli·ma·tion/ (ak?li-ma´shun) the process of becoming accustomed to a new environment.
1. to E[E.sub.2] exposure. Depuration depuration (dēˈ·py studies found only a partial recovery in reproductive capacity after 5 months. Significantly, even though the [F.sub.1] males lacked functional testes, they showed male-pattern reproductive behavior Reproductive behavior
Behavior related to the production of offspring; it includes such patterns as the establishment of mating systems, courtship, sexual behavior, parturition, and the care of young. , inducing the spawning act and competing with healthy males to disrupt fertilization. Endocrine disruption is therefore likely to affect breeding dynamics and reproductive success in group-spawning fish. Our findings raise major concerns about the population-level impacts for wildlife of long-term exposure to low concentrations of estrogenic endocrine disruptors. Key words: ecotoxicology The term ecotoxicology was coined by Truhaut in 1969, who defined it as "the branch of toxicology concerned with the study of toxic effects, caused by natural or synthetic pollutants, to the constituents of ecosystems, animal (including human), vegetable and microbial, in an , endocrine disruption, ethynylestradiol, mating systems, population effects, reproductive success, zebrafish. Environ Health Perspect 112:1725-1733 (2004). doi: 10.1289/ehp.7209 available via http://dx.doi.org/ [Online 4 November 2004]
Major worldwide attention has focused on the possibility that disruption of reproductive systems by endocrine-disrupting chemicals (EDCs) may be affecting the reproductive health Within the framework of WHO's definition of health as a state of complete physical, mental and social well-being, and not merely the absence of disease or infirmity, reproductive health, or sexual health/hygiene of wildlife populations (Guillette and Gunderson 2001; Kime 1998; Tyler et al. 1998; Van Der Kraak 1998) and possibly, of humans (Colborn and Clement 1992; Ohtake et al. 2003). In fish, exposure to EDCs alters their reproductive physiology and morphology (Kime 1998; Tyler et al. 1998), resulting in, for example, the induction of female-specific proteins in male fish (Tyler and Routledge 1998), induction of gonopodia in females (Bortone and Davis 1994), reduced sperm counts (Haubruge et al. 2000), skewed skewed
curve of a usually unimodal distribution with one tail drawn out more than the other and the median will lie above or below the mean.
skewed Epidemiology adjective Referring to an asymmetrical distribution of a population or of data sex ratios (Larsson et al. 2000), and prevalence of intersexuality intersexuality /in·ter·sex·u·al·i·ty/ (in?ter-sek?shoo-al´i-te)
3. androgyny. (Jobling et al. 1998). Concern over the effects of EDCs on wildlife is driven by the hypothesis that disruption to the reproductive system may have serious deleterious consequences on the reproductive success of populations, but there is little evidence bearing on this expectation. An exception to this in a natural population is recent work on the roach (Rutilus rutilus); this study shows that sexual disruption (intersex) as a consequence of exposure to sewage treatment Sewage treatment
Unit processes used to separate, modify, remove, and destroy objectionable, hazardous, and pathogenic substances carried by wastewater in solution or suspension in order to render the water fit and safe for intended uses. works effluents (STWs)--which contain a complex mixture of EDCs--results in gametes with reduced fertilizing capacity, as determined by in vitro in vitro /in vi·tro/ (in ve´tro) [L.] within a glass; observable in a test tube; in an artificial environment.
In an artificial environment outside a living organism. studies (Jobling et al. 2002b). Direct population-level consequences of exposure to a specific EDC EDC
See: Export Development Corp. are known only for the antifouling an·ti·foul·ing
Counteracting or preventing the building up of deposits on underwater surfaces, such as the undersides of boats: antifouling paint. agent tributyltin, which disrupts steroidogenesis steroidogenesis /ste·roi·do·gen·e·sis/ (ste-roi?do-jen´e-sis) production of steroids, as by the adrenal glands.steroidogen´ic
The biological synthesis of steroids. , inducing an imposex condition that reduces reproductive success and causes localized extinctions in marine gastropods in the United Kingdom (Gibbs et al. 1991; Matthiessen and Gibbs 1998).
Many EDCs have a weak capacity to disrupt reproductive function. In contrast, natural steroidal estrogens Estrogens
Hormones produced by the ovaries, the female sex glands.
Mentioned in: Acne, Polycystic Ovary Syndrome
n. control sexual differentiation and/or development in vertebrates and are potent modulators of sexual development and capacity (Bern 1992; Dawson 1998; Nagahama 1994; Strussmann and Nakamura 2002). Steroidal estrogens in effluents from STWs are believed to be responsible for, or contribute to, the feminized responses in some wild fish (Jobling et al. 1998, 2002a) and include the natural estrogens estradiol ([E.sub.2]) and estrone estrone /es·trone/ (es´tron) an estrogen isolated from pregnancy urine, human placenta, palm kernel oil, and other sources, also prepared synthetically; for properties and uses, see estrogen. ([E.sub.1]) and the synthetic estrogen E[E.sub.2], a component of the contraceptive pill (Desbrow et al. 1998; Tyler and Routledge 1998). In Europe, E[E.sub.2] is present in effluents and surface waters at concentrations between 0.5 and 7 ng/L (Desbrow et al. 1998; Larsson et al. 1999; Ternes et al. 1999) but in some cases up to 50 ng/L (Ahern and Briggs 1989). A recent study of 139 streams in the United States United States, officially United States of America, republic (2005 est. pop. 295,734,000), 3,539,227 sq mi (9,166,598 sq km), North America. The United States is the world's third largest country in population and the fourth largest country in area. found that 5.7% had concentrations > 5 ng/L (Kolpin et al. 2002a). In that study extremely high concentrations of E[E.sub.2] up to 273 ng/L were reported at some riverine riv·er·ine
1. Relating to or resembling a river.
2. Located on or inhabiting the banks of a river; riparian: "Members of a riverine tribe ... sites, but these figures may be overestimations and they are controversial (Kolpin et al. 2002b). E[E.sub.2] concentrations are generally lower in surface waters than are natural steroidal estrogens, but the potency of E[E.sub.2] in fish is 10- to 50-fold higher than that of [E.sub.2] and [E.sub.1] in vivo in vivo /in vi·vo/ (ve´vo) [L.] within the living body.
Within a living organism.
in vivo adv. (Segner et al. 2003b; Thorpe et al. 2003) due to its longer half-life and tendency to bioconcentrate (650- and 10,000-fold in whole-body tissues and bile, respectively) (Lange et al. 2001; Larsson et al. 1999). In fish, for example, only 0.1 ng/L E[E.sub.2] induces vitellogenin Vitellogenin (Vg) (from latin vitellus = yolk and gener = to produce) is a synonymous term for the gene and the expressed protein. The molecule is classified as a glyco-lipo-protein, having properties of a sugar, fat and protein. (VTG VTG Variable Turbine Geometry (turbochargers)
VTG Vicksburg Theatre Guild (Vicksburg, MS)
VTG Voice Technologies Group, Inc. ) yolk yolk (yok) the stored nutrient of an oocyte or ovum.
The portion of the egg of an animal that consists of protein and fat from which the early embryo gets its main nourishment and of precursor (Purdom et al. 1994), 0.1-15 ng/L can affect normal sexual development and differentiation (Andersen et al. 2003; Metcalfe et al. 2001; van Aerie et al. 2002; Van den Belt et al. 2003; Weber et al. 2003), 2-10 ng/L can affect fecundity (Lange et al. 2001; Scholz and Gutzeit 2000; Van den Belt et al. 2002), 10 ng/L affects reproductive behavior (Balch et al. 2004), and 1-10 ng/L can reduce the fertilization success or viability of embryos from exposed adults (Hill and Janz 2003; Lange et al. 2001; Segner et al. 2003a). Thus, given its concentration in the environment, E[E.sub.2] is potentially a major contributor to reproductive dysfunction in wild fish populations.
An overall aim of our research was to test whether there are any population-level consequences to reproductive dysfunction(s) induced by exposure to environmentally relevant levels of EDCs. Because of a number of compounding factors (e.g., larval larval
1. pertaining to larvae.
see cutaneous and visceral larva migrans. dispersal, adult migration, etc.; Elliott et al. 2003) it is difficult to directly determine the population-level consequences of endocrine disruption on reproductive success in wild fish populations; even where it is possible to correlate levels of contamination with endocrine disruption and the consequential reproductive dysfunction with reproductive failure, this does not necessarily prove a direct cause-and-effect relationship. For these reasons, one approach to understanding the population-level consequences of reproductive dysfunction is to measure the impact of pollutants on reproductive success in model species bred under laboratory conditions (e.g., Balch et al. 2004; Hill and Janz 2003; Lange et al. 2001), an approach we have taken in our study. Reduced reproductive success may result from disruption of reproductive development, reduced female fecundity and male vitality, altered reproductive behavior, and/or disruption of the normal breeding dynamics. Little attention has been directed to the latter (Balch et al. 2004). To fully assess the potential of EDCs to disrupt reproduction, multigenerational mul·ti·gen·er·a·tion·al
Of or relating to several generations: multigenerational family traditions. full life-cycle exposures are needed that consider all relevant life stages and developmental end points; even where fish have been exposed over their whole life-cycle, the impact of any resulting reproductive dysfunction on their reproductive output has mostly been overlooked in earlier studies (Metcalfe et al. 2001; Van den Belt et al. 2003). A major goal of this study was to determine which stages or reproductive components are relatively most sensitive to endocrine disruption in terms of population-level impairment or failure to allow better priority and focus for future studies. We therefore determined impacts on reproductive success in fish populations over multiple generations and the mechanisms of reproductive impairment/failure investigated using environmentally relevant concentrations of E[E.sub.2] and [E.sub.2]. Our chosen species for this work was the zebrafish because its short generation time facilitates the life-long and multigenerational chemical exposures; it is a group-spawner (a common breeding system in fish); and, most importantly Adv. 1. most importantly - above and beyond all other consideration; "above all, you must be independent"
above all, most especially , small populations will spawn naturally in the laboratory without any manipulation.
Materials and Methods
Fish culture and husbandry. Wild-type zebrafish (Danio rerio, WIK WIK Wissenschaftliches Institut für Kommunikationsdienste GmbH (Bad Honnef, Germany)
WIK Work In Kind strain; Max Plank Institute, Tubingen, Germany) maintained out-bred for three generations since capture were bred in our laboratory for one generation in clean freshwater before their use in this study. Adult fish were fed ad libitum ad libitum
ad libitum feeding
food available at all times with the quantity and frequency of consumption being the free choice of the animal. twice daily on Artemia nauplii. Fry 5-12 days postfertilization (dpf) were fed a special fry diet and cultured rotifers, Brachionus calciflorus. Artemia nauplii were hatched in synthetic seawater seawater
Water that makes up the oceans and seas. Seawater is a complex mixture of 96.5% water, 2.5% salts, and small amounts of other substances. Much of the world's magnesium is recovered from seawater, as are large quantities of bromine. and rotifers reared in synthetic freshwater.
Populations were maintained and exposed to steroidal estrogens in 192 flow-through 18-L glass aquaria a·quar·i·a
A plural of aquarium. . An egg collection system allowed daily embryo collection without disturbance of the adult populations. Natural conditions were mimicked for optimal breeding; with a 13 hr light:11 hr dark photoperiod photoperiod /pho·to·pe·ri·od/ (fo´to-per?e-od) the period of time per day that an organism is exposed to daylight (or to artificial light).photoperiod´ic
n. , artificial dawn/dusk, and water temperature of 28.5 [+ or -] 0.5[degrees]C (differences between tanks < 0.5[degrees]C throughout). Aquaria contained artificial weed for refuge and spawning substrate (glass marbles). Eggs were collected 1 hr after dawn. Embryos were maintained in 50 mL culture vessels modified for continuous flow-through before release into aquaria at 9 dpf.
Water quality and chemical dosing. Tap water was filtered with activated charcoal Charcoal, Activated Definition
Activated charcoal is a fine black odorless and tasteless powder made from wood or other materials that have been exposed to very high temperatures in an airless environment. and reverse osmosis reverse osmosis
The movement of a solvent in the opposite direction from osmosis in such a manner that the solvent moves from a solution of greater concentration through a membrane to a solution of lesser concentration. (RO; Osmonics E625 with cellulose membranes; GE Water and Process Technologies, Trevose, PA, USA). RO water was reconstituted with Analar grade mineral salts to standardized synthetic freshwater, to concur with U.S. Environmental Protection Agency Environmental Protection Agency (EPA), independent agency of the U.S. government, with headquarters in Washington, D.C. It was established in 1970 to reduce and control air and water pollution, noise pollution, and radiation and to ensure the safe handling and (EPA EPA eicosapentaenoic acid.
n.pr See acid, eicosapentaenoic.
n. ) guidelines (U.S. EPA 1986). Water was aerated aer·ate
tr.v. aer·at·ed, aer·at·ing, aer·ates
1. To supply with air or expose to the circulation of air: aerate soil.
2. and heated to 28.5[degrees]C in a reservoir before it was supplied to each aquarium at a rate of 9 L/day to provide an exchange of 3 L/g biomass/day (U.S. EPA 1986). Aquarium water was continuously monitored for temperature, pH, and conductivity and routinely measured for carbonate hardness Carbonate hardness is the measure of Calcium and Magnesium and other hard ions associated with carbonate (CO32-) and bicarbonate (HCO3-) ions contained in a solution, usually water. , oxygen, chlorine, iron, ammonia, nitrate, nitrite nitrite
Any salt or ester of nitrous acid (HNO2). The salts are inorganic compounds with ionic bonds, containing the nitrite ion (NO2−) and any cation. , and periodically for 142 pollutants; all were within acceptable limits of U.S. EPA guidelines (U.S. EPA 1986). The chemical (and control) aquaria were dosed independently at 20 mL/hr by a medical dripper system fed from a 2.5-L glass aspirator as·pi·ra·tor
An apparatus for removing fluid from a body cavity, consisting usually of a hollow needle and a cannula, connected by tubing to a container in which a vacuum is created by a syringe or a suction pump. , and dosing rates were checked twice daily. 17[alpha]-Ethynylestradiol [17a[lpha]-ethinyl-1,3,5(10)-estratriene-3,17[beta]-diol] and estradiol [1,3,5(10)-estratriene-3,17[beta]-diol] were initially dissolved in 100% ethanol at 1 mg/mL and serially diluted with sterile (treated with ultraviolet radiation) distilled water Noun 1. distilled water - water that has been purified by distillation
H2O, water - binary compound that occurs at room temperature as a clear colorless odorless tasteless liquid; freezes into ice below 0 degrees centigrade and boils above 100 degrees centigrade; to a final stock concentration of 50 ng/mL. Fresh final stocks were made every 10 days and stored at 5[degrees]C. Aspirators were refilled every fourth day. Nominal estrogen doses were 0.5, 5, and 50 ng/L for E[E.sub.2] and 5 ng/L for [E.sub.2]. The ethanol concentrations administered to aquaria were < 0.05 [micro]L/L L/L Lids & Lashes
L/L Land Line . Steroids were extracted from 5 L water samples for the E[E.sub.2] (0.5 and 5 ng/L only, because the 50 ng/L treatment was terminated at an early phase of experimentation) and [E.sub.2] (5 ng/L) using solid-phase extraction and measured by gas chromatography-mass spectrometry (Kelly 2000), with a detection limit of 0.1 ng/L.
Impact of multigenerational estrogen exposure on reproductive success. The main measures of reproductive success used in our study were the number of eggs produced by each population and the proportion of these eggs that were not viable at 14 hr post-fertilization (hpf; the mid-segmentation period) (Kimmel et al. 1995). The total reproductive success at 14 hpf was therefore the total number of viable embryos surviving to this stage. We used 14 hpf because infertile in·fer·tile
Not capable of initiating, sustaining, or supporting reproduction.
adj unable to produce offspring. or dead embryos can be quickly differentiated from healthy embryos at this stage. Egg viability at 14 hpf was therefore a cumulative figure that includes the impact of unfertilized Adj. 1. unfertilized - not having been fertilized; "an unfertilized egg"
infertile, sterile, unfertile - incapable of reproducing; "an infertile couple" eggs plus embryo mortality during embryogenesis Embryogenesis
The formation of an embryo from a fertilized ovum, or zygote. Development begins when the zygote, originating from the fusion of male and female gametes, enters a period of cellular proliferation, or cleavage. . Fertilization failure was differentiated from embryo mortality only in selected groups using time lapse videography vid·e·og·ra·phy
The art or practice of using a video camera.
vide·og to determine the mechanism(s) of reproductive failure.
At the begining of the study 720 adult (204 dpf) fish of mixed sex were randomly allocated to 60 aquaria (12 fish/aquarium) and acclimated for 14 days under egg collection conditions. Egg numbers and viability at 14 hpf were assessed in all groups in this [F.sub.0] generation for 5 days before starting exposures. Tanks for the 12 replicates of the five treatments were randomly allocated using Lain square randomization randomization (ranˈ·d·m in both vertical and horizontal gradients, and all experimentation was run blind of treatments. Steroid treatments were then initiated by flushing aquaria with 36 L estrogen-treated water 1 hr after spawning (day 0), and reproductive success was assessed over the following 15 days. The surviving [F.sub.1] embryos were all reared to 100 hpf under continuous estrogen exposure, and the rate of embryo mortality/survival was assessed. We assessed the integrity of the surviving larvae Larvae, in Roman religion
Larvae: see lemures. , the proportion of embryos with developmental abnormalities, and the speed of development (proportion hatch and spine curvature) at 100 hpf as described by Kimmel et al. (1995). After the [F.sub.0] generation had been exposed for a further 25 days (40 days of exposure total), we again assessed reproductive success (egg numbers and viability at 14 hpf), 100 hpf embryo mortality, and larval integrity of the resulting [F.sub.1] offspring in eggs arising from 3 days of spawning. The surviving [F.sub.1] embryos from these 3 days were then pooled within each replicate and reared to adulthood under continued exposure to form the [F.sub.1] exposure generation. The age of the fish is stated as a single day postfertilization although, because the eggs were pooled over 3 days, the actual age may vary by up to an additional 48 hr. At 29 dpf, they were divided between two tanks (24 tanks/treatment) and maintained to 52 dpf, whereby survival and growth rates Growth Rates
The compounded annualized rate of growth of a company's revenues, earnings, dividends, or other figures.
Remember, historically high growth rates don't always mean a high rate of growth looking into the future. were determined. These fish were then pooled and randomly redistributed within treatments to provide 28 individuals/tank. At 72 and 124 dpf, populations were further reduced to 18 and 12 adults/tank, respectively. After the [F.sub.1] generation had been exposed over their entire life time (210 dpf), their reproductive success was measured for 10 days. Any resulting [F.sub.2] progeny were continually exposed to the estrogen treatments, and embryo survival/larval integrity was measured at 100 hpf.
Analysis of estrogenic disruption and reproductive failure. Life-stage sensitivity, transgenerational impacts, and recovery from estrogen exposure. To determine which life stage(s) were primarily responsible for any reproductive failure and to test for any transgenerational effects, we exposed different subgroups to various regimes of noncontinuous estrogen exposure. Eggs were collected over a 4-day period from each treatment group in the [F.sub.0] generation 16-19 days after the start of exposure (i.e., after the main egg collection period on days 0-15). In this first subgroup, the eggs from six of the 12 replicate tanks from each treatment (0.5 and 5 ng/L E[E.sub.2], 5 ng/L [E.sub.2] and control) were removed from the continuous treatment 1 hpf and reared to 100 hpf in clean water. Egg numbers and viability to 14 hpf and embryo survival/integrity to 100 hpf were compared between the [F.sub.0] parent-only exposure, the continuous [F.sub.0]/[F.sub.1] exposure, and the unexposed control group. To test for any transgenerational effects of parental exposure on adult reproductive integrity in their offspring, we set up a second subgroup in which the [F.sub.1] generation was reared to adulthood in clean water. Eggs were collected from the [F.sub.0] generation over 5 days from five replicate tanks in each treatment group (0.5 and 5 ng/L E[E.sub.2], 5 ng/L [E.sub.2] and control) 29 days after the start of exposure. These fish were then reared to adulthood, when end points of reproductive success, adult health, and embryo survival were measured at the same time as the main multigenerational exposure experiment, as described above.
To examine the ability of fish to recover from the effects of estrogen treatments on sexual differentiation and gonadal gonadal
pertaining to or arising from a gonad. See also testicular, ovarian.
cords formed by epithelial cells which migrate from the mesonephric tubules in the embryo to the gonadal ridge and establish the indifferent development, we established a third subgroup in which the [F.sub.1] generation was removed from the treatments at 75 dpf and reared to adulthood in clean water. In this subgroup, we set up three replicate populations of mixed sex juveniles from each treatment (0.5 and 5 ng/L E[E.sub.2], 5 ng/L [E.sub.2] and controls) using the excess fish removed from the main treatments at 75 dpf to reduce stocking densities; these fish were reared in adulthood in clean water. Reproductive success, adult health, and [F.sub.2] embryo survival/integrity were measured in this subgroup at the same times as for the fish in the main multigenerational experiment.
Male replacement experiments. To investigate the cause(s) of reproductive failure in the 5 ng/L E[E.sub.2] treatment group after life-long exposure, males were removed from one-half of the replicate populations in the control group 20 days after embryo collection (240 dpf) to create an all-female group (n = 6) and leaving a mixed-sex control group (n = 6); we also replaced two E[E.sub.2]-exposed males with two control males in one-half of the replicate populations in the 5 ng/L E[E.sub.2] exposure group to create two groups (n = 6), with or without additional healthy males. There was no dosing with E[E.sub.2] during this phase of the experiment. The fish were acclimated, and egg numbers and egg viability were subsequently assessed over 5 days.
Adult health and growth. In the [F.sub.0] generation after 40 days of exposure, a total of 571 fish from 10 of the 12 replicates of each treatment were anesthetized a·nes·the·tize also a·naes·the·tize
tr.v. a·nes·the·tized, a·nes·the·tiz·ing, a·nes·the·tiz·es
To induce anesthesia in.
a·nes , and weighed (wet weight, milligrams), and blood samples were collected from the caudal caudal /cau·dal/ (kaw´d'l)
1. pertaining to a cauda.
2. situated more toward the cauda, or tail, than some specified reference point; toward the inferior (in humans) or posterior (in animals) end of the body. sinus. Gonads were dissected to determine gonadosomatic index (gonad gonad /go·nad/ (go´nad) a gamete-producing gland; an ovary or testis.gonad´algonad´ial
indifferent gonad the sexually undifferentiated gonad of the early embryo. weight as a percentage of body weight). Blood was centrifuged at 3,000 x g for 8 min and the hematocrit Hematocrit Definition
The hematocrit measures how much space in the blood is occupied by red blood cells. It is useful when evaluating a person for anemia.
Blood is made up of red and white blood cells, and plasma. value measured in all samples. In the [F.sub.1] generation (after full life-cycle exposure, 314 dpf), 284 adults from six replicate tanks in each of the remaining exposure groups (0.5 ng/L and 5 ng/L E[E.sub.2] treatments with no [F.sub.1] exposure; 0.5 and 5 ng/L E[E.sub.2] and 5 ng/L [E.sub.2] treatments with exposure stopped at 75 dpf in [F.sub.1]) were weighed; we then collected blood samples and determined the hematocrit value. Whole fish were fixed in Bouin's fixative Bouin's fixative
a tissue preservative composed of saturated picric acid, formaldehyde and glacial acetic acid. Particularly suitable for trichrome connective tissue stains. and embedded in paraffin, and the gonad region was sectioned to 4 [micro]m, stained, and analyzed by light microscopy. Histologic analysis was conducted blind of treatment and was undertaken in three independent laboratories.
Fertilization success, sperm quality. Time-lapse image capture was used to assess whether reductions in egg viability were due to reduced fertilization success or embryo mortality at 14 hpf. Digital images of four developing embryos were taken every 5 min 1 to 24 hpf and repeated for > 10 days per treatment. To assess sperm quality in [F.sub.1] controls and 5 ng/L E[E.sub.2] treatments only, males were stripped manually of expressible milt 1 hr before dawn, and the activated sperm was examined using video microscopy (Kime et al. 1996).
Plasma vitellogenin and steroids. Whole-blood VTG concentrations were measured by enzyme-linked immunosorbent assay enzyme-linked immunosorbent assay
Enzyme-linked immunosorbent assay (ELISA)
A diagnostic blood test used to screen patients for AIDS or other viruses. (ELISA ELISA (e-li´sah) Enzyme-Linked Immuno-Sorbent Assay; any enzyme immunoassay using an enzyme-labeled immunoreactant and an immunosorbent.
n. ), as described by Brion et al. (2002), in all 12 adults from four and three replicate tanks within each treatment sampled in the [F.sub.0] and [F.sub.1] generations, respectively. We assayed [E.sub.2] and 11-ketotestosterone (11-KT) by ELISA (Nash et al. 2000) in 2 individuals from each of the eight replicate groups in each treatment (n = 8) for the [F.sub.0] generation only.
Statistical analyses. Data were checked for normality using the Ryan-Joiner test and homogeneity of variance using Bartlett's test Bartlett's test (Snedecor and Cochran, 1983) is used to test if k samples have equal variances. Equal variances across samples is called homoscedasticity or homogeneity of variances. . Data were transformed, where necessary, using square root (egg numbers and survival data), [log.sub.10] (steroid levels), or arc sine arc sine
The inverse of the sine function.
The inverse of the sine function.
Noun 1. of square root for proportion data (egg viability). When analyzing egg viability, we excluded data points for which egg numbers were < 4/tank (< 2%) because viability on low egg numbers biased the analysis disproportionately. We used analysis of variance (ANOVA anova
see analysis of variance.
ANOVA Analysis of variance, see there ) procedures except where there were unequal sample sizes and imbalance in design; then the GLM GLM Global Language Monitor
GLM Global Marine (stock symbol)
GLM Graduated Length Method (ski instruction)
GLM Good Looking Mom (used in pediatric practices)
GLM God Loves Me procedure was used. Post hoc post hoc
adv. & adj.
In or of the form of an argument in which one event is asserted to be the cause of a later event simply by virtue of having happened earlier: analysis was performed against controls using the Dunnett's test, and we used the Tukey test for between-treatment comparisons (male addition experiments). Data for egg numbers and viability to 14 hpf, survival and mortality of embryos to 100 hpf, and rate of embryo development were nested within the tank replicates to avoid pseudoreplication, and ANOVA was performed on 5-day means. When multiple measurements, such as weights and gonadosomatic index, were made from a single tank, these were also nested. VTG data did not conform to Verb 1. conform to - satisfy a condition or restriction; "Does this paper meet the requirements for the degree?"
coordinate - be co-ordinated; "These activities coordinate well" normality, so we adopted nonparametric analysis (Kruskal-Wallis). Significant deviations from expected sex ratios or levels of abnormal adult and gonadal morphology were tested using the chi-square test chi-square test: see statistics. .
Results and Discussion
Natural variation in fecundity. The average fecundity of this wild type strain of zebrafish was around 13 eggs/female, which is about 50% lower than that in some other inbred in·bred
1. Produced by inbreeding.
2. Fixed in the character or disposition as if inherited; deep-seated.
said of offspring produced by inbreeding. lines that have been selected for growth and reproductive output (Eaton and Farley 1974; Ensenbach and Nagel 1997). We found considerable variation in the numbers of eggs spawned daily in the zebrafish populations (Figure 1A, B), highlighting the need for extensive replication in studies of this nature. Our purpose, however, was to provide an experimental system that includes this natural variation found in wild populations. Cumulative and nested egg production was subsequently assessed over 5-day intervals to normalize normalize
to convert a set of data by, for example, converting them to logarithms or reciprocals so that their previous non-normal distribution is converted to a normal one. measurements across the tanks; because females have a spawning periodicity periodicity /pe·ri·o·dic·i·ty/ (per?e-ah-dis´i-te) recurrence at regular intervals of time.
1. of around 1.9 days (Eaton and Farley 1974), each female spawns at least once during a 5-day period. No significant differences in egg production occurred during the four consecutive 5-day periods in the [F.sub.0] controls (mean, 0.2 eggs/female/day; F = 1.44, p = 0.27, n = 12, on 5-day nested means).
[FIGURE 1 OMITTED]
Exposure concentrations of estrogens. Measured mean concentrations of E[E.sub.2] and [E.sub.2] were between 90 and 100% of nominals: E[E.sub.2] (mean [+ or -] SEM) concentrations were 0.5 [+ or -] 0.0 ng/L (0.5 ng/L E[E.sub.2]), 4.5 [+ or -] 0.3 ng/L (5 ng/L E[E.sub.2]), and [E.sub.2]4.8 [+ or -] 0.1 ng/L (5 ng/L E[E.sub.2]). E[E.sub.2] and [E.sub.2] were undetectable (< 0.1 ng/L) in the control group tanks and [E.sub.2] was undetectable (< 0.1 ng/L) in the E[E.sub.2] treatments. Mean [+ or -] SEM [E.sub.1] concentrations in the control and treated tanks ranged between 0.5 [+ or -] 0.1 and 1.1 [+ or -] 0.1 ng/L and probably originated as an excreted product from the fish. There are no data on the effects of [E.sub.1] in zebrafish, but in the rainbow trout rainbow trout
Species (Oncorhynchus mykiss) of fish in the salmon family (Salmonidae) noted for spectacular leaps and hard fighting when hooked. It has been introduced from western North America to many other countries. , reproductive effects occur only at doses 3 orders of magnitude higher than the [E.sub.1] concentrations found in the exposure aquaria (Thorpe et al. 2003). We used nominal steroid concentrations to describe the exposures in this study.
Impacts of estrogen exposure on reproductive success during multigenerational exposure. [F.sub.0] generation. For the 5-day period prior to the start of the estrogen exposures, we found no significant differences in egg numbers (F = 0.96, p = 0.43, n = 12), numbers of nonviable nonviable /non·vi·a·ble/ (-vi´ah-b'l) not capable of living.
Not capable of living or developing independently. Used especially of an embryo or fetus. eggs at 14 hpf (F = 1.16, p = 0.34, n = 12), or level of mortality at 100 hpf (F = 0.91, p = 0.47, n = 12) between all five experimental groups (n = 12). There were also no differences in the reproductive output between the control groups in the [F.sub.0] generation compared with the [F.sub.1] generation, either in egg numbers (F = 0.52, p = 0.47, n = 12), nonviable eggs at 14 hpf (F = 2.8, p = 0.11, n = 12), or embryo mortality at 100 hpf (F = 0.45, p = 0.51, n = 12) for pooled 15-and 10-day means in each generation. A mean of 91.5% of the eggs were fertilized fer·til·ize
v. fer·til·ized, fer·til·iz·ing, fer·til·iz·es
1. To cause the fertilization of (an ovum, for example).
2. and survived to 100 hpf (posthatch) in all treatments before exposure and in control treatments throughout the experiment. This level of fertilization and survival is high when compared to similar studies on zebrafish (Hill and Janz 2003), sheepshead minnows (Cyprinodon variegatus; Zillioux et al. 2001), and medaka me·da·ka
A small Japanese fish (Oryzias latipes) commonly found in rice fields and often used in biological research or in stocking aquariums. (Oryzias latipes Oryzias latipes
see medehas. ; Balch et al. 2004), where lower survival (70, 65, and 62%, respectively) in controls probably relates to suboptimal Suboptimal
A solution is called suboptimal if a part of the solution has been optimized without regards to the overall objective. breeding conditions or stresses associated with embryo culture.
The short term exposure to 50 ng/L E[E.sub.2] in the [F.sub.0] generation caused a time-related reduction in egg production and egg viability to 14 hpf (Figure 2; two-way ANOVA for all cases: n = 12, p < 0.01) and no survival of their [F.sub.1] offspring to 100 hpf. After 10 days exposure there was complete reproductive failure (no egg production) in the 50 ng/L E[E.sub.2] exposure group. These data support previous findings for high dosage, short-term effects of E[E.sub.2] (Lange et al. 2001; Scholz and Gutzeit 2000; Seki et al. 2002; Van den Belt et al. 2002; Zillioux et al. 2001), and this treatment was subsequendy terminated. There were no effects, however, of any other estrogen treatment on numbers and viability of eggs from the [F.sub.0] generation at 14 hpf (Figure 2), embryo mortality in the [F.sub.1] generation (F = 0.36, p = 0.78, n = 12), or impacts on larval integrity at 100 hpf; the proportion of developmental abnormality, hatch rate, and level of spine curvature were all not significantly different from controls; p > 0.05 for all cases. Similarly, we found no effects after an additional 26-day exposure (40 days continuous exposure) to 0.5 ng or 5 ng/L E[E.sub.2] or 5 ng/L [E.sub.2] on egg production (F = 1.31, p = 0.28, n = 12), egg nonviability (F = 1.30, p = 0.28, n = 12), or [F.sub.1] mortality to 100 hpf (F = 1.71, p = 0.18, n = 12) and larval integrity (p > 0.05 for all cases) at 100 hpf.
[FIGURE 2 OMITTED]
Mean cumulative survival at 52 dpf was between 66% and 79%, with no differences (F = 1.1, p = 0.35, n = 12) between the treatments. This rate of survival is high for cultured zebrafish embryos (Ensenbach and Nagel 1997) and was higher than a comparable study (50%; Hill and Janz 2003). Most (98%) of this mortality occurred during the first stages of exogenous feeding and was not related to treatment. There were no effects of the estrogen treatments on growth at 52 dpf (mean = 65-80 mg, F = 1.45 p > 0.24, n = 12). The mortality rate between 52 dpf and 7 months of age was < 0.2% throughout, and we found no differences (F = 0.65, p > 0.63, n = 12) in fish weight between treatments for either sex at the end of the experiment when fish were slaughtered (9 months; mean = 232-349 mg).
[F.sub.1] generation. In complete contrast, life-long exposure (210 dpf) to 5 ng/L E[E.sub.2] resulted in complete reproductive failure in the [F.sub.1] generation, with no viability in the eggs at 14 hpf (Figure 3); we found no viable eggs in almost 12,000 spawned (F = 7.6, p < 0.001). Egg production was also reduced in fish in the 5-ng/L E[E.sub.2] exposure group, approximately 42-45% of that of the control for the two successive 5-day assessment periods (Figure 3; F = 207, p < 0.001). We found no effects of either 0.5 ng/L E[E.sub.2] or 5 ng/L [E.sub.2] on egg numbers, but proportions of nonviable eggs/total eggs spawned at 14 hpf in both of these treatments were more than twice that in the controls (F = 207, p < 0.001; post hoc comparisons with p < 0.05). A large variation in egg numbers, however, meant that these effects on viability at 14 hpf did not affect total reproductive success at 14 hpf (i.e., total number surviving 14 hpf) in the 0.5 ng/L E[E.sub.2] or 5 ng/L [E.sub.2] treatments (Figure 2). The rate of embryo mortality to 100 hpf in the surviving [F.sub.2] embryos was low (< 1%) and not significantly increased by these low exposures (F = 0.63, p < 0.48, n = 12). Larval integrity (proportion of developmental abnormality, hatch rate, and level of spine curvature) of the [F.sub.2] embryos at 100 hpf in these surviving groups was also not affected.
[FIGURE 3 OMITTED]
Two recent studies have also examined the impact of full life-long exposure to E[E.sub.2] on reproductive success in other fishes. Lange et al. (2001) found that life-long exposure to 0.2 and 1 ng/L E[E.sub.2] in the fathead minnow The fathead minnow (Pimephales promelas), is a species of temperate freshwater fish belonging to the Pimephales genus of the cyprinid family. The natural geographic range extends throughout much of North America, from central Canada south along the Rockies to (Pimephales promelas) caused 20 and 35% reductions, respectively, in the offspring's hatching success and no impact on fecundity, which was comparable with the impact of our 0.5 ng/L E[E.sub.2] exposure. In the Lange et al. study, however, the impact on reproductive success of a higher dose (4 ng/L E[E.sub.2]), one similar to that which would have caused complete reproductive failure in our study (5 ng/L E[E.sub.2]), was not tested because it was not possible to sex these fish for the pair-wise breeding setup used. In a study on medaka, Balch et al. (2004) found no significant effects of life-long exposure at lower doses (0.2 and 1 ng/L E[E.sub.2]), but at 10 ng/L E[E.sub.2] (there was no intermediate dose) they found complete reproductive failure, which was related to suppressed reproductive activity.
Thus, life-long exposures to very low and environmentally relevant concentrations of E[E.sub.2] have severe and deleterious effects on reproductive success for breeding populations of zebrafish, and there is evidence that these strong effects will occur in other species at similar concentrations (Balch et al. 2004; Lange et al. 2001). Furthermore, these effects occur at concentrations that are at least an order of magnitude A change in quantity or volume as measured by the decimal point. For example, from tens to hundreds is one order of magnitude. Tens to thousands is two orders of magnitude; tens to millions is three orders of magnitude, etc. lower than for short-term exposures of mature fish proximate proximate /prox·i·mate/ (prok´si-mit) immediate or nearest.
Closely related in space, time, or order; very near; proximal.
immediate; nearest. to spawning time; Seki et al. (2002), Van den Belt et al. (2002), and Zillioux et al. (2001) provide other examples of lower sensitivity to adult-only exposure.
Analysis of endocrine disruption. Reproductive failure in [F.sub.0] generation. We found that 50 ng/L E[E.sub.2] was acutely toxic and resulted in 35% mortality; in the surviving fish there were negative effects on a wide range of health measures, including reduced hematocrit, increased spinal deformities, and reduced gonad growth. Reproductive failure ensued because of complete cessation of spawning in this treatment group (Denslow et al. 1999; Seki et al. 2002; Van den Belt et al. 2002). There was no reduction in reproductive success or health effects in any of the other estrogen treatment groups.
Reproductive failure in [F.sub.1] generation. We investigated the mechanism(s) of disruption leading to reproductive failure in the [F.sub.1] generation by assessing sperm quality, fertilization success in their offspring ([F.sub.2] generation), gonad development and maturation, and male reproductive behavior in the breeding populations. In the 5 ng/L E[E.sub.2] treatment group, we found no phenotypic males, as discerned by the absence of any secondary sex characteristics secondary sex characteristic
Any of various characteristics specific to females or males but not directly concerned with reproduction.
secondary sex characteristic , such as slightly yellow/bronze coloration col·or·a·tion
1. Arrangement of colors.
2. The sum of the beliefs or principles of a person, group, or institution. and bright anal fin markings. This gave the initial impression that sex reversal sex reversal
A process that changes the sexual identity of an individual from one sex to the other, often through a combination of surgical, pharmacologic, and psychiatric procedures. had been induced, as occurs in some fish species after exposure to steroidal estrogens (Iwamatsu 1999; Lange et al. 2001; Scholz and Gutzeit 2000). Further studies on these [F.sub.1] fish found that no fish contained expressible sperm. The hypothesis that reduced egg viability at 14 hpf was due to nonfertilization rather than early embryo mortality was confirmed through hourly time lapse image analyses of egg/embryo development for this treatment. Gonadal histology on the [F.sub.1] fish after life-long exposure to 5 ng/L E[E.sub.2] established that none of the males had normal testes. Of these fish, 43% had gonads that had not fully differentiated into testes; these undetermined gonads resembled primary stage ovary-type tissue, which is the natural condition of immature fish during early stages of normal male gonadal differentiation (Maack and Segner 2003). Figure 4A shows an example. Gonadal evidence that these fish were indeed feminized males was further supported by the concentrations of blood VTG in these animals. Via histology, we found that all of these life-long exposed fish that were not clearly mature/maturing females had compromised gonads and also had very low concentrations of blood VTG (mean [+ or -] SEM = 1.8 [+ or -] 1.1 [micro]g/mL), whereas fish that were definitively females contained extremely high concentrations of blood VTG (1,092 [+ or -] 106 [micro]g/mL). We found no fish with an intermediate response. This highly dichotomous di·chot·o·mous
1. Divided or dividing into two parts or classifications.
2. Characterized by dichotomy.
di·chot response to the estrogenic treatment after long-term exposure, which was strongly correlated to the histology and behavior--these dysfunctional males showed natural spawning behavior--gives good evidence these differential responses were determined by the underlying genetic sex. The interpretation that long-term exposure to estrogens suppresses male pattern sexual differentiation and arrests testes development rather than producing functional females is confirmed by earlier work on zebrafish (Hill and Janz 2003; Segner et al. 2003a; Van den Belt et al. 2003; Weber et al. 2003). In some of these earlier studies on zebrafish (Hill and Janz 2003; Weber et al. 2003), males with undifferentiated testes have been categorized as females and have been reported as a skewed sex ratio. This is a slightly misleading interpretation in an undifferentiated gonochorist species such as the zebrafish, because males that have arrested sexual differentiation, while superficially resembling early ovary ovary, ductless gland of the female in which the ova (female reproductive cells) are produced. In vertebrate animals the ovary also secretes the sex hormones estrogen and progesterone, which control the development of the sexual organs and the secondary sexual type tissue (as do both sexes at this stage), do not develop into functional females and their gonads will differentiate into testes when removed from exposure (Hill and Janz 2003). It would be more accurate to describe these fish as simply showing undetermined gonadal sex rather than assigning female status.
[FIGURE 4 OMITTED]
We found a low incidence of intersex gonads (four fish; Figure 4B,C) in the 5 ng/L exposure group. Although similarly low occurrences of intersex have been found in various species when exposed to estrogens during development (Van den Belt et al. 2003), the high level of intersex found in some natural species (Jobling et al. 1998) has not been replicated in the laboratory. This may relate to between-species differences in their susceptibility to this intersex condition or it could indicate the involvement of other, as yet, unknown chemical or environmental factors. It is doubtful if the fish with intersex gonads in our study were sexually functional because they also had extensive malformations of the ovarian and sperm ducts, as shown in other species [e.g., carp (Gimeno and Komen 1996) and fathead minnow (van Aerie et al. 2002)]; there was no fertilization in these groups. Further data on the effects on the histopathology his·to·pa·thol·o·gy
The science concerned with the cytologic and histologic structure of abnormal or diseased tissue.
The study of diseased tissues at a minute (microscopic) level. and enhanced images are available online in the "Toxicological Pathology Atlas of Small Laboratory Fish" (RIVM RIVM Rijksinstituut voor Volksgezondheid en Milieu 2004).
Behavioral analysis and male replacement experiments. Close observation of the [F.sub.1] adults in the 5 ng/L E[E.sub.2] treatment group indicated that even though there was no fertilization, natural spawning behavior still occurred and resulted in egg-laying activity, even though these fish were all superficially female. Removing all the males from control tanks in the [F.sub.1] generation caused complete cessation of spawning, showing that the presence of males, or at least male pattern behavior, was needed to stimulate spawning in females (Figure 5).
[FIGURE 5 OMITTED]
When two healthy nonexposed males were taken from the control group and substituted for two males from populations previously exposed to 5 ng/L E[E.sub.2] (six tanks), there was an increase in embryo in an incipient or undeveloped state; in conception, but not yet executed.
See also: Embryo viability, showing that the females in the 5 ng/L E[E.sub.2] group were fertile. Even with healthy males, the rate of survival to 14 hpf was, however, significantly less than in the control group. This reduction in survival to 14 hpf was due to reduced fertilization success (tested using time-lapse videography) and indicates that the effects were not due to reduced egg quality in the E[E.sub.2]-exposed females. Experiments conducted in our laboratory have shown that even when the population sex ratio is strongly biased toward females in normal healthy populations (14 females:2 males), fertilization rates are > 90%. Thus, the high level of unfertilized eggs in the 5 ng/L E[E.sub.2] exposures with replacement males is unlikely to be a function of the presence of only two fertile males. Close observations of the spawning activity in these tanks revealed that sexually compromised males actively participated in the spawning act, chasing females and competing with the healthy males for proximity to the females as they spawned. Thus, it was clear that the reduced fertilization was, at least in part, due to infertile males interfering with the fertilization capability of healthy males. Egg production in the E[E.sub.2]-treated group with healthy males was higher when compared with controls (Figure 5). The presence of vigorous, healthy males may have induced the greater egg production in these females after a prolonged period with E[E.sub.2]-exposed males. Moreover, egg production in this treatment group was similar to previous controls; egg production in the associated controls was relatively low.
The data from this experiment show that normal gonadal differentiation and development is relatively more sensitive to disruption than is male reproductive behavior. We suggest that there is a higher threshold on sensitivity to behavioral disruption relative to exposure concentrations that cause inhibition of functional testes development. Although few studies examine the impact of endocrine disruption on reproductive behavior in relation to reproduction success, Balch et al. (2004) confirmed that medaka behavior was unaffected at doses of E[E.sub.2] < 10 ng/L, even though there were significant gonadal abnormalities at exposures of 2 ng/L.
Retention of a normal pattern of behavior in the infertile males that affects the fitness of other males may have an even greater impact on the reproductive success than if these males did not participate in spawning. The findings illustrate that information on the effects of EDCs and the interactions between fish within a spawning group (i.e., their mating systems) is necessary to develop our understanding of population-level implications of endocrine disruption. In the wild, group-spawning fish come together on a spawning ground; they may have migrated from different areas, and therefore different chemical exposure regimes, and thus they may have different degrees of disruption to their reproductive systems. To date, none of these factors has been taken into consideration when evaluating the potential impacts of EDCs such as E[E.sub.2] on breeding success in wild fish populations.
Transgenerational effects, life stage sensitivity, and recovery from E[E.sub.2] exposure. It is well documented that maternal transfer of the synthetic estrogen diethylstilbestrol diethylstilbestrol: see DES. into the developing fetus in humans resulted in cases of sexual dysfunction sexual dysfunction
Inability to experience arousal or achieve sexual satisfaction under ordinary circumstances, as a result of psychological or physiological problems. , which became manifest at puberty (Bern 1992). Maternal transfer of EDCs may also occur in fish, when pollutants are co-transported with VTG into the developing oocyte oocyte /oo·cyte/ (-sit) the immature female reproductive cell prior to fertilization; derived from an oogonium. It is a primary o. prior to completion of the first maturation division, and a secondary o. (Gray et al. 1999). In the present study we found no transgenerational effects of [F.sub.0] exposure to < 5 ng/L E[E.sub.2] on the level of embryo viability at 14 hpf or [F.sub.1] embryo mortality and larval integrity (proportion of developmental abnormality, hatch rate, and level of spine curvature) at 100 hpf, when the offspring were reared in dean water and compared with the corresponding treatment in continuous [F.sub.0] and [F.sub.1] exposure or control treatment (n = 6, p > 0.05 in all cases). This is not surprising because we also found no effects up to 100 hpf when both the parents ([F.sub.0]) and offspring ([F.sub.1]) were exposed at these same concentrations during the main multigenerational experiment. Moreover, reproductive success in the [F.sub.1] subgroups (n = 5) reared to adulthood in clean water but with parental [F.sub.0] exposure (0.5 and 5 ng/mL E[E.sub.2] and 5 ng/mL [E.sub.2]) was not affected, either in the number of eggs spawned by the [F.sub.1] (F = 1.07, p = 0.39 n = 6) or the 14 hr viability of the resulting eggs (F = 0.84, p = 0.29; six tanks per treatment) when compared to the control eggs collected at the same time. This contrasts with continuous multigenerational exposures ([F.sub.0] and [F.sub.1]) causing significant or complete reproductive failure at similar doses. [F.sub.0]-only exposure also had no consequences for the integrity of the [F.sub.2] offspring, either in the level of embryo mortality or larval integrity at 100 hpf (p > 0.05 in all cases), again consistent with what would be expected if there were no transgenerational impact. These results, therefore, give little evidence of any transgenerational (maternal) effects of exposure to E[E.sub.2] or [E.sub.2], at least when measuring population level consequences for reproductive success and survival. There are no other studies that have reported transgenerational effects of steroid hormones on reproductive success, although a study by Foran et al. (2002) showed transgenerational impacts on VTG and estrogen receptor estrogen receptor A protein of a superfamily of nuclear receptors for small hydrophilic ligands–eg, steroid hormones, thyroid hormone, vitamin D, retinoids; the presence of ERs in breast CA generally is associated with a better prognosis, as they respond to responsiveness in medaka, but only at extremely high doses (> 500 ng/L). Reported transgenerational impacts of other endocrine disruptors, such as DDT DDT or 2,2-bis(p-chlorophenyl)-1,1,1,-trichloroethane, chlorinated hydrocarbon compound used as an insecticide. First introduced during the 1940s, it killed insects that spread disease and feed on crops. on [F.sub.1] gonadal development (Metcalfe et al. 2000) and nonylphenol on [F.sub.1] steroid levels (Schwaiger et al. 2002), may be related to different biochemical properties of these pollutants.
In populations (three tanks) offish off·ish
Inclined to be distant and reserved; aloof.
off exposed to 0.5 and 5 ng/LE[E.sub.2] and 5 ng/L [E.sub.2] to 75 dpf and then reared in clean freshwater to adulthood (a depuration of 5 months), we found no differences in fecundity at 210-220 dpf when compared with the control for these subgroups (F = 0.46 p = 0.72, 10-day means). This is in contrast with the strong impact of continuous full life-long exposure (Figure 6) to 5 ng/L E[E.sub.2] in the [F.sub.1] generation that caused a considerable reduction in egg numbers, thus illustrating a capacity for recovery in their reproductive output (numbers of eggs spawned).
[FIGURE 6 OMITTED]
Interestingly, however, even after a 5 month period of depuration, there was still a highly significant (F = 12.81 p = 0.003) impact of exposure on fertilization success; the proportion of nonviable eggs at 14 hpf increased to 16.2% in 0.5 ng/L E[E.sub.2] and 24% in 5 ng/L E[E.sub.2] compared with a rate of 7.8% in the controls. Even though males were still able to produce sperm (shown by stripping) and fertilize the eggs spawned by females, there was also persistent disruption to testes development, which could explain the reduced fertilization success. Histology showed extensive malformations of the sperm ducts, the presence of an ovarian cavity in the testis testis (tĕs`tĭs) or testicle (tĕs`tĭkəl), one of a pair of glands that produce the male reproductive cells, or sperm. , variation in proportion of testicular testicular /tes·tic·u·lar/ (tes-tik´u-lar) pertaining to a testis.
Of or relating to a testicle or testis.
pertaining to the testis. cell types, and ciliation of sperm ducts (Figure 4D), a feature normally found in ovarian ducts that has been reported in wild intersex roach (Nolan et al. 2001). Persistent effects on testes of developmental exposure to similar levels of E[E.sub.2] in zebrafish were not reported by Weber et al. (2003), but duct morphology was not examined. Partial recovery from E[E.sub.2] exposure during early sexual differentiation can therefore occur with a sufficient period of depuration, but certain morphologic effects are long lived. The persistent nature of EDC-induced gonadal abnormalities has been confirmed in several fishes (Gimeno and Komen 1996; McAllister and Kime 2003; Scholz and Gutzeit 2000; van Aerie et al. 2002), and differences in the level of recovery after depuration probably relate to diverse modes of sexual differentiation found between species.
Vitellogenin and steroid hormone response. In the [F.sub.0] generation after 40 days exposure to the lower, sublethal sublethal /sub·le·thal/ (-le´thal) insufficient to cause death.
Not sufficient to cause death. concentrations of E[E.sub.2], we found a highly significant (F = 41.64, p < 0.001) and dose-related induction of VTG in both sexes (Figure 6A). In males, a dose of only 0.5 ng/L E[E.sub.2] induced a 5,000-fold increase in blood VTG, which concurs with previous studies in fish, including zebrafish (Fenske et al. 2001; Thorpe et al. 2003). There was also a significant (F = 17.59, p < 0.001, n = 8) and dose-related suppression of the major male fish sex hormone sex hormone
Any of various steroid hormones, such as estrogen and androgen, affecting the growth or function of the reproductive organs and the development of secondary sex characteristics. 11-KT in [F.sub.0] males; in the blood of fish treated with 0.5, 5, or 50 ng/L E[E.sub.2] or 5 ng/L [E.sub.2], 11-KT concentrations were 30, 5, 6, and 8% of controls, respectively (mean [+ or -] SEM = 94 [+ or -] 46 ng/mL). The sensitivity of both VTG and 11-KT to exogenous steroidal estrogens reinforces their value as biomarkers for exposure to estrogen after short-term exposure (Brion et al. 2002; Denslow et al. 1999). Very considerable (3 orders of magnitude) changes in blood VTG and up to 95% reduction in 11-KT, however, did not impact the short-term reproductive success of the zebrafish populations, emphasizing their utility as biomarkers of estrogen exposure, rather than necessarily measures of reproductive impact. There were no significant impacts of the estrogen treatments on endogenous blood [E.sub.2], although there was a high level of variability between fish. The measurements of 11-KT and [E.sub.2] are the first data on reproductive steroid hormones in zebrafish, and the method (Nash et al. 2000) could be adapted to other small species ([less than or equal to] 300 mg). To further investigate natural levels of a range of steroids in zebrafish and their response to endocrine disruption, ongoing research in our laboratories is examining a larger number of replicates that were collected in this study and in new experiments.
In contrast with the short-term adult exposure (Figure 6A), we observed no induction of VTG in males after life-long exposure to < 5 ng/L E[E.sub.2] (Figure 6B), suggesting an acclimation to the E[E.sub.2] exposure. Similarly there were no effects of a multigenerational life-long exposure to estrogen on VTG in females, but the VTG concentration in [F.sub.1] controls was higher than in both the [F.sub.0] controls and 5 ng/L E[E.sub.2] fish (Figure 6B). It seems likely that there is strong down-regulation of vitellogenic response after long-term exposure to exogenous estrogens, which has not been reported before. Studies in fish have shown that there are seasonal variations in the number of estrogen receptors and in the ligand affinity of these receptors (Smith and Thomas 1991), and thus responsiveness to estrogen, but we do not know the mechanism for acclimation to estrogen observed here in males. A reduced vitellogenic response (or indeed lack of a response) in males after long-term exposure to low levels of estrogen further complicates the use of VTG as a biomarker for estrogen exposure in wild populations; fish that have been subjected to long-term exposure to estrogen and with no measurable blood VTG could still be reproductively compromised.
The temporal disassociation dis·as·so·ci·ate
tr.v. dis·as·so·ci·at·ed, dis·as·so·ci·at·ing, dis·as·so·ci·ates
To remove from association; dissociate.
dis between the impact of estrogen exposure on reproductive success and the vitellogenic response also clearly shows that the perturbations to reproductive physiology that ultimately cause reproductive failure are probably not directly linked or at least not a direct consequence of the stimulation of vitellogenin.
Overall, our findings on the effective concentration of E[E.sub.2] on reproductive success raise serious concerns for possible population-level effects on fisheries. Concern about population-level consequences associated with exposure to E[E.sub.2] in the aquatic environment is further exacerbated by the fact that detection capabilities for routine assessments of E[E.sub.2] in effluents and environmental samples are generally above concentrations that are biologically significant (Kolpin et al. 2002a). Extremely high potency and persistence in the aquatic environment (Johnson and Williams 2004) is also likely to be mirrored by other persistent pharmaceuticals which are, as yet, not measured in routine assessments of effluents (Metcalfe et al. 2003).
The data presented in this article give evidence that different reproductive components have differential sensitivities to endocrine disruption and that these sensitivities are dependent on the length of exposure and timing of exposure relative to development and maturity. Full life-long exposures had a strong impact on reproductive success at a concentration that was at least one order of magnitude less than when fish were given short-term exposures proximate to spawning. Conversely, after full life-long exposure there was no apparent stimulation of VTG in the [F.sub.1] adults, whereas short-term exposures strongly stimulated VTG in the parental [F.sub.0] generation at similar doses. These data have important implications for bodies devising effective methodologies for the diagnosis of the ecologic risk from endocrine disruptors and for those devising laboratory testing strategies for hazard assessment. Because it is the impacts at the population level that are ultimately of most concern, special care must be taken when interpreting the results from either short-term testing procedures or from biomarkers such as VTG. Although integrative long-term multigenerational studies are expensive and time consuming, the mechanistic information they produce is invaluable if we want to understand both the potential population consequences of endocrine disruption and the mode of action that leads to reproductive failure. Although these longterm studies cannot be repeated for every potential EDC, the mechanistic knowledge gained should be integrated into the design of shorter testing methodologies and new mechanistic approaches such as toxicogenomics, to allow for more accurate predictions of the population level consequences.
The value of an integrative approach can be clearly seen from the data obtained in our male replacement studies. A differential in relative sensitivity to disruption between gonadal and behavioral sexual differentiation had the consequence that male-pattern behavior was more robust to the effects of E[E.sub.2] exposure than was gonadal development, where exposure caused complete male infertility. If behavior is considered in isolation, then a lower impact on behavior may seem to have fewer population consequences; when behavior is considered in combination with infertility, it may actually increase the risk of reproductive failure in natural populations. We suggest that reproductive behavior plays a pivotal role in how chemically induced chemically induced,
adj initiating biologic action or response by the introduction of a chemical. reproductive dysfunction(s) act to affect reproductive success and/or genetic integrity of populations. Moreover, there exists the possibility of other important interactions between endocrine disruption and mating systems that could strongly influence the population-level impact of reduced fertility. Sexual selection and mate choice strategies are complex, and endocrine disruption may interact or interfere with these in both negative and positive ways. Factors that determine the choice of a male by the female could, for example, be exaggerated in males with reduced fertility, giving these fish an even greater potential for interfering with the natural mating process and further increasing the impact of endocrine disruption on reproductive success. We suggest that further studies should examine this previously overlooked area.
We thank C. Spary, E. Saunders, B. McAllister, M. Skidmore, K. Van Look, and S. Holden for help with data collection and C. Kelly (CEFAS CEFAS Centre for Environment Fisheries and Aquaculture Science (UK)
CEFAS Centro Femenino de. Adaptación Social (Honduras) , Burnham-on-Crouch, UK) for the analytical chemistry analytical chemistry: see under chemistry. . We also thank the reviewers for their useful comments.
This study was supported by grant GR3/10840 from the British Natural Environmental Research Council (D.E.K.), an EC Marie Curie fellowship A Marie Curie Fellowship is a mobility research grant funding pre- and post-doctoral researchers in Europe as well as experienced researchers. Fellowships are awarded by the European Commission in various scientific disciplines within the Marie Curie Actions (J.P.N.), and Exeter University (C.R.T.).
The authors declare they have no competing financial interests.
Received 27 April 2004; accepted 22 October 2004.
Aherne GW, Briggs R. 1989. The relevance of the presence of certain synthetic steroids in the aquatic environment. J Pharm Pharmacol 41:735-736.
Andersen L, Holbech H, Gessbo A, Norrgren L, Petersen GI. 2003. Effects of exposure to 17[alpha]-ethinylestradiol during early development on sexual differentiation and induction of vitellegenin in zebrafish (Danio rerio). Comp Biochem Physiol C Toxicol Pharmacol 134:365-374.
Balch GC, Mackenzie CA, Metcalfe CD. 2004. Alterations to gonadal development and reproductive success in Japanese medaka (Oryzias latipes) exposed to 17[alpha]-ethinylestradiol. Environ Toxicol Chem 23:782-791.
Bern HA. 1992. The fragile fetus. In: Chemically-Induced Alterations in Sexual and Functional Development: The Wildlife Human Connection (Colborn T, Clement C, eds). Princeton, NJ: Princeton Scientific Publishing, 9-15.
Bortone SA, Davis WP. 1994. Fish intersexuality as indicator of environmental stress. Bioscience 44:165-172.
Brion F, Nilsen BM, Eidem JK, Goksoyr A, Porcher JM. 2002. Development and validation of an enzyme-linked immunosorbent assay to measure viteliogenin in the zebrafish (Danio rerio). Environ Toxicol Chem 21:1699-1708.
Colborn T, Clement C. 1992. Chemically-Induced Alterations in Sexual and Functional Development: The Wildlife Human Connection. Princeton, NJ:Princeton Scientific Publishing.
Dawson A. 1998. Comparative reproductive physiology of nonmammalian species. Pure Appl Chem 70:1657-1669.
Denslow ND, Chow MC, Kroll KJ, Green L. 1999. Vitellogenin as a biomarker of exposure for estrogen or estrogen mimics. Ecetoxicology 8:385-398.
Desbrow C, Routledge EJ, Brighty G, Sumpter JP, Waldock MJ. 1998. Indentification of estrogenic chemicals in STW effluent. 1. Chemical fractionation fractionation /frac·tion·a·tion/ (frak?shun-a´shun)
1. in radiology, division of the total dose of radiation into small doses administered at intervals.
2. and in vitro biological screening. Environ Sei (Software Engineering Institute, Pittsburgh, PA, www.sei.cmu.edu) A federally funded research and development center that is under contract to Carnegie Mellon University and is devoted to the advancement of software engineering and the quality of software support systems. Technol 32:1559-1565.
Eaton RC, Farley RD. 1974. Spawning cycle and egg production of zebrafish, Brachydanio rerio, in the laboratory. Copeia 1974:195-204.
Elliott M, Hemmingway KL, Krueger D, Theil R, Hylland K, Arukwe A, et al. 2003. From the individual to the population and community responses to pollution. In: Effects of Pollution on Fish (Lawrence AJ, Hemmingway KL, eds). Oxford, UK:Blackwell, 221-255.
Ensenbach U, Nagel R. 1997. Toxicity of binary chemical mixtures: effects on reproduction of zebrafish (Brachydanio rerio). Arch Environ Contain Toxicol 32:204-210.
Fenske M, Van Aerie R, Brack S, Tyler CR, Segner H. 2001. Development of a homologous homologous /ho·mol·o·gous/ (ho-mol´ah-gus)
1. corresponding in structure, position, origin, etc.
1. zebrafish (Danio rerio Hamilton-Buhanan) vitellogenin enzyme-linked immunosorbent assay (ELISA) and its application for studies on estrogenic chemicals. Comp Biochem Physiol C 129:217-232.
Foran CM, Peterson BN, Benson WH. 2002. Transgenerational and developmental exposure of Japanese medaka (Oryzias latipes) to ethinylestradiol results in endocrine and reproductive differences in the response to ethinyrestradiol as adults. Toxicol Sci 68:389-402.
Gibbs PE, Bryan GW, Pascoe PL. 1991. TBT-induced imposex in the dogwhelk, Nucella-Lapillus- geographical uniformity of the response and effects. Mar Environ Res 32:79-87.
Gimeno S, Komen H. 1996. Feminization feminization /fem·i·ni·za·tion/ (fem?i-ni-za´shun)
1. the normal development of primary and secondary sex characters in females.
2. the induction or development of female secondary sex characters in the male. of male carp. Nature 384:221-222.
Gray MA, Teather KL, Metcalfe CD. 1999. Reproductive success and behavior of Japanese medaka (Oryzias latipes) exposed to 4-tert-octylphenor. Environ Toxicol Chem 18:2587-2594.
Guillette LJ, Gunderson MP. 2001. Alterations in development of reproductive and endocrine systems of wildlife populations exposed to endocrine-disrupting contaminants. Reproduction 122:857-864.
Haubruge E, Petit F, Gage MJG MJG Miller Japanese Garden (California State University, Long Beach) . 2000. Reduced sperm counts in guppies ''This article is about an American pop-culture term. For the fish, see Guppy
Guppies is an acronym which stands for Generation X Yuppies. The combination of the two nelogistic generational terms is used to loosely identify anyone who was in their twenties during the 1990s, (Poecilia reticulate re·tic·u·late
Resembling or forming a net or network: reticulate veins of a leaf.
v. re·tic·u·lat·ed, re·tic·u·lat·ing, re·tic·u·lates
1. ) following exposure to low levels of tributyltin and bisphenol A Bisphenol A is a chemical compound containing two phenol functional groups. It belongs to the phenol class of aromatic organic compounds. It is widely prepared and sold and various important polymers/plastics are made from it. . Proc Roy Soc London Ser B 267:2333-2337.
Hill RL, Janz DM. 2003. Developmental estrogenic exposure in zebrafish (Danio rerio). I. Effects on sex ratio and breeding success. Aquatic Toxicol 63:417-429.
Iwamatsu T. 1999. Convenient method for sex reversal in a freshwater teleost teleost
fish of the class Osteichthyes, having the skeleton completely ossified. , the medaka. J Exp Zool 283:210-214.
Jobling S, Beresford N, Nolan M, Rodgers-Bray T, Brighty BC, Sumpter JP, et al. 2002a. Altered sexual maturation and gamete gamete (găm`ēt): see reproduction. production in wild roach (Rutilus rutilus) living in rivers that receive treated sewage effluents. Biol Reprod 86:272-281.
Jobling S, Coey S, Whitmore JG, Kime DE, Van Look KJW KJW Kwan Ju Works (Airsoft company) , McAllister BG, et at. 2002b. Wild intersex roach (Rutilus rutilus) have reduced fertility. Bier bier
1. A stand on which a corpse or a coffin containing a corpse is placed before burial.
2. A coffin along with its stand: followed the bier to the cemetery. Reprod 67:515-524.
Jobling S, Nolan M, Tyler CR, Brighty G, Sumpter JP. 1998. Widespread sexual disruption in wild fish. Environ Sci Technol 32:2498-2506.
Johnson AC, Williams RJ. 2004. A model to estimate influent in·flu·ent
Flowing in or into.
1. An inflow, especially a tributary.
2. Ecology A nondominant organism in a community that exerts an important modifying effect. and effluent concentrations of estradiol, estrone, and ethinylestradiol at sewage treatment works. Environ Sci Technol 38:3649-3658.
Kelly C. 2000. Analysis of steroids in environmental water samples using solid-phase extraction and ion-trap gas chromatography-mass spectrometry and gas chromatography-tandem mass spectrometry mass spectrometry
or mass spectroscopy
Analytic technique by which chemical substances are identified by sorting gaseous ions by mass using electric and magnetic fields. . J Chromatogr A 872:309-314.
Kime DE. 1998. Endocrine Disruption in Fish. Boston:Kluwer.
Kime DE, Ebrahimi M, Nysten K, Roelants I, Rurangwa E, Moore HDM HDM - SPECIAL , et el. 1996. Use of computer assisted sperm analysis sperm analysis See Semen analysis. (CASA Ca´sa
n. 1. A house or mansion.
I saw that Enriquez had made no attempt to modernize the old casa, and that even the garden was left in its lawless native luxuriance.
- Bret Harte. ) for monitoring the effects of pollution on sperm quality of fish; application to the effects of heavy metals heavy metals,
n.pl metallic compounds, such as aluminum, arsenic, cadmium, lead, mercury, and nickel. Exposure to these metals has been linked to immune, kidney, and neurotic disorders. . Aquat Toxicol 36:223-237.
Kimmel CB, Ballard WW, Kimmel SR, Ullmann B, Schilling TF. 1995. Stages of embryonic development of the zebrafish. Dev Dyn 203:253-310.
Kolpin DW, Furlong ET, Meyer MT, Thurman EM, Zaugg SD, Barber LB, et at. 2002a. Pharmaceuticals, hormones, and other organic wastewater contaminants in U.S. streams, 1999-2000: a national reconnaissance. Environ Sci Technol 36:1202-1211.
Kolpin DW, Furlong ET, Meyer MT, Thurman EM, Zaugg SD, Barber LB, et el. 2002b. Response to comment on, "Pharmaceuticals, hormones, and other organic wastewater contaminants in U.S. streams, 1999-2000: a national reconnaissance". Environ Sci Technol 36:4007-4008.
Lange R, Hutchinson TH, Croudace CP, Siegmund F. 2001. Effects of the synthetic estrogen 17[alpha]-ethinylestradiol on the life-cycle of the fathead minnow (Pimephales promelas). Environ Toxicol Chem 20:1216-1227.
Larsson DGJ, Adolfsson-Erici M, Parkkonen J, Pettersson M, Berg AH, Olsson PE, et el. 1999. Ethinyloestradior--an undesired fish contraceptive? Aquat Toxicol 45:91-97.
Larsson DGJ, Hallman H, Forlin L. 2000. Environmental toxicology --more male fish near a pulp mill A pulp mill is a manufacturing facility that converts wood chips or other plant fiber source into a thick fiber board which can be shipped to a paper mill for further processing. . Environ Toxicol Chem 19:2911-2917.
Maack G, Segner H. 2003. Morphological development of the gonads The prenatal development of the gonads is a part of the development of reproductive system and sultimately forms the testes in males and ovaries in females. They initially develop from the mesothelial layer of the peritoneum. in zebrafish. J Fish Biol 62:895-906.
Matthiessen P, Gibbs PE. 1998. Critical appraisal of the evidence for tributyltin-mediated endocrine disruption in mollusks. Environ Toxicol Chem 17:37-43.
McAllister BG, Kime DE. 2003. Early life exposure to environmental levels of the aromatase inhibitor aromatase inhibitor
A drug that inhibits tumor growth, especially breast cancer, by inhibiting the enzyme aromatase and thereby lowering estrogen levels in the blood or in tumor tissues. tributyltin causes masculinisation Noun 1. masculinisation - the abnormal development of male sexual characteristics in a female (usually as the result of hormone therapies or adrenal malfunction)
masculinization, virilisation, virilization and irreversible sperm damage in zebrafish (Danio rerio). Aquat Toxicol 65:309-316.
Metcalfe CD, Koenig BG, Bennie OT, Servos M, Ternes TA, Hirsch R. 2003. Occurrence of neutral and acidic drugs in the effluents of Canadian sewage treatment plants. Environ Toxicol Chem 22:2872-2880.
Metcalfe CD, Metcalfe TL, Kiparissis Y, Koenig BG, Khan C, Hughes RJ, et al. 2001. Estrogenic potency of chemicals detected in sewage treatment plant effluents as determined by in vivo assays with Japanese medaka (Oryzias latipes). Environ Toxicol Chem 20:297-308.
Metcalfe TL, Metcalfe CD, Kiparissis Y, Niimi AJ, Foran CM, Benson WH. 2000. Gonadal development and endocrine responses in Japanese medaka (Oryzias latipes) exposed to o,p'-DDT in water or through maternal transfer. Environ Toxicol Chem 19:1893-1900.
Nagahama Y. 1994. Endocrine regulation of gemetogenesis in fish. Int J Dev Biol 38:217-229.
Nash JP, Cuisset B, Bhattacharyya S, Suter HC, Le Menn F, Kime DE. 2000. An enzyme linked immunosorbant assay (ELISA) for testosterone, estradiol, and 17,20[beta]-dihydrexy-4-pregnen-3-one using acetylcholinesterase acetylcholinesterase /ac·e·tyl·cho·lin·es·ter·ase/ (AChE) (-ko?li-nes´ter-as) an enzyme present in the central nervous system, particularly in nervous tissue, muscle, and red cells, that catalyzes the hydrolysis of acetylcholine to as tracer: application to measurement of diel patterns in rainbow trout (Oncorhynchus mykiss). Fish Physiol Biochem 22:355-363.
Nolan M, Jobling S, Brighty G, Sumpter JP, Tyler CR. 2001. A histological description of intersexuality in the roach. J Fish Biol 58:160-176.
Ohtake F, Takeyama K, Metsumoto T, Kitagawa H, Yamamoto Y, Nohare K, et el. 2003. Modulation of oestrogen oes·tro·gen
Variant of estrogen.
see estrogen. receptor signalling by association with the activated dioxin dioxin
Aromatic compound, any of a group of contaminants produced in making herbicides (e.g., Agent Orange), disinfectants, and other agents. Their basic chemical structure consists of two benzene rings connected by a pair of oxygen atoms; when substituents on the rings are receptor. Nature 423:545-550.
Purdom CE, Hardiman PA, Bye VJ, Eno NC, Tyler CR, Sumpter JP. 1994. Oestrogenic oestrogenic (ōˈ·es·tr effects of effluent from sewage treatment works. Chem Ecol 8:275-285.
RIVM. 2004. Toxicological Pathology Atlas of Small Laboratory Fish. Available: http://www.rivm.nl/fishtoxpat/[accessed 28 October 2004].
Scholz S, Gutzeit HO. 2000. 17[alpha]-Ethinylestradiol affects reproduction, sexual differentiation and aromatase gene expression of the medaka (Oryzias latipes). Aquat Toxicol 50:363-373.
Schwaiger J, Mallow mallow, common name for members of the Malvaceae, a family of herbs and shrubs distributed over most of the world and especially abundant in the American tropics. Tropical species sometimes grow as small trees. U, Ferling H, Knoerr S, Braunbeck T, Kalbfus W, et al. 2002. How estrogenic is nonylphenol? A transgenerational study using rainbow trout (Oncorhynchus mykiss) as a test organism. Aquat Toxicol 59:177-189.
Segner H, Caroll K, Fenske M, Janssen CR, Maack G, Pascoe D, et el. 2003a. Identification of endocrine-disrupting effects in aquatic vertebrates and invertebrates: report from the European IDEA project. Ecotoxicol Environ Sef 54:302-314.
Segner H, Navas JM, Schafers C, Wenzel A. 2003b. Potencies of estrogenic compounds in in vitro screening assays and in life cycle tests with zebrafish in vivo. Eeotoxicol Environ Saf 54:315-322.
Seki M, Yokota H, Matsubara H, Tsuruda Y, Maeda N, Tadokoro H, et al. 2002. Effect of ethinylestradiol on the reproduction and induction of vitellogenin and testis-ova in medaka (Oryzias latipes). Environ Toxicol Chem 21:1692-1698.
Smith JS, Thomas P. 1991. Changes in hepatic estrogen-receptor concentrations during the annual reproductive and ovarian cycles of a marine teleost, the spotted seatrout, Cynoscion nebulosus. Gen Comp Endocrinol 81:234-245.
Strussmann CA, Nakamura M. 2002. Morphology, endocrinology, and environmental modulation of gonadal sex differentiation in teleost fishes. Fish Physiol Biochem 26:13-29.
Ternes TA, Stumpf M, Mueller J, Haberer K, Wilken RD, Servos M. 1999. Behavior and occurrence of estrogens in municipal sewage treatment plants--I. Investigations in Germany, Canada and Brazil. Sci Total Environ 225:81-90.
Thorpe KL, Cummings RI, Hutchinson TH, Scholze M, Brighty G, Sumpter JP, et al. 2003. Relative potencies and combination effects of steroidal estrogens in fish. Environ Sci Technol 37:1142-1149.
Tyler CR, Jobling S, Sumpter JP. 1998. Endocrine disruption in wildlife: a critical review of the evidence. Crit Rev Toxicol 28:319-381.
Tyler CR, Routledge EJ. 1998. Oestregenic effects in fish in English rivers with evidence of their causation. Pure Appl Chem 70:1795-1804.
U.S. EPA. 1986. Fish Life-Cycle Toxicity Tests. EPA 540/9-86-137. Washington, DC:U.S. Environmental Protection Agency.
Van Aerle R, Pounds N, Hutchinson TH, Maddix S, Tyler CR. 2002. Window of sensitivity for the estrogenic effects of ethinylestradiol in early fife-stages of fathead minnow, Pimephales promelas. Ecotoxicology 11:423-434.
Van den Belt K, Verheyen R, Witters H. 2003. Effects of 17alpha-ethynylestradiol in a partial life-cycle test with zebrafish (Danio rerio): effects on growth, gonads and female reproductive success. Sci Total Environ 309:127-137.
Van den Belt K, Wester PW, Van der Ven LTM LTM
long-term memory , Verheyen R, Witters H. 2002. Effects of ethynylestradiol on the reproductive physiology in zebrafish (Danio rerio): time dependency and reversibility. Environ Toxicol Chem 21:767-775.
Van Bet Kraak G. 1998. Observations of endocrine effects in wildlife with evidence of their causation. Pure Appl Chem 70:1785-1794.
Weber LP, Hill RL, Janz DM. 2003. Developmental estrogenic exposure in zebrafish (Banjo rerio): II. Histological evaluation of gametogenesis Gametogenesis
The production of gametes, either eggs by the female or sperm by the male, through a process involving meiosis. In animals, the cells which will ultimately differentiate into eggs and sperm arise from primordial germ cells set aside from the and organ toxicity. Aquat Toxicol 63:431-446.
Zillioux EJ, Johnson IC, Kiparissis Y, Metcalfe CO, Wheat JV, Ward SG, et al. 2001. The sheepshead minnow as an in vivo model for endocrine disruption in marine teleosts: a partial life-cycle test with 17[alpha]-ethynylestradiol. Environ Toxicol Chem 20:1968-1978.
Jon P. Nash, (1,2,3) David E. Kime, (1) Leo Leo, in astronomy
Leo [Lat.,=the lion], northern constellation lying S of Ursa Major and on the ecliptic (apparent path of the sun through the heavens) between Cancer and Virgo; it is one of the constellations of the zodiac. T. M. Van der Ven, (4) Piet W. Wester, (4) Francois Brion, (5) Gerd Maack, (3) Petra Stahlschmidt-Allner, (6) and Charles R. Tyler (3)
(1) Animal and Plant Sciences, University of Sheffield The University of Sheffield is a research university, located in Sheffield in South Yorkshire, England. Reputation
Sheffield was the Sunday Times University of the Year in 2001 and has consistently appeared as their top 20 institutions. , Sheffield ,United Kingdom; (2) Laboratory of Aquatic Ecology, Katholieke Universiteit Leuven The KATHOLIEKE UNIVERSITEIT LEUVEN (Catholic University of Leuven in English) or in short K.U.Leuven, is the largest, oldest, and most prominent university in Belgium. , Leuven, Belgium; (3) School of Biological Sciences, University of Exeter, Exeter, United Kingdom; (4) Rijksinstituut voor volksgezondheid en mileu (RIVM), Bilthoven, The Netherlands; (5) L'Institut national de L'environnement et des risque ris·qué
Suggestive of or bordering on indelicacy or impropriety.
[French, from past participle of risquer, to risk, from risque, risk; see risk.]
Adj. (INERIS INERIS Institut National de l'Environnement Industriel et des Risques (French: National Institute for Environmental Technology and Hazards) ), Verneuil-en-Halatte, France; (6) Hessisches Landesamt for umwelt und geologie (HLUG HLUG Hamilton Linux User Group ), Wiesbaden, Germany
Address correspondence to J.P. Nash, Laboratory of Aquatic Ecology, Katholieke Universiteit Leuven, 3000 Leuven, Belgium. Telephone: 32-16-323966. Fax: 32-16-324575. E-mail: firstname.lastname@example.org