Mechanisms of atrazine endocrine disruption
Mechanisms of atrazine endocrine disruption
批准号:
9895294
负责人:
Jennifer L Freeman
金额:
$7.18万
依托单位:
依托单位国家:
美国
项目类别:
财政年份:
2020
资助国家:
美国
项目状态:
已结题
起止时间:
2020-01-15 至 2021-12-31
关键词:
Adrenal GlandsAdultAffectAgricultureAnimal ModelAnterior Pituitary GlandAtrazineBehaviorBiological ModelsBrainCYP17A1 geneCell CycleCell Cycle RegulationChemical ExposureConflict (Psychology)CoupledCouplingCyclic AMPDataDevelopmentDiseaseEmbryoEmbryonic DevelopmentEndocrineEndocrine DisruptorsEndocrine disruptionFemaleFollicular AtresiaGene TargetingGenesGenetic TranscriptionHeadHealthHerbicidesHormonalHumanHypothalamic structureImageKnowledgeLaboratory StudyLarvaLengthLifeLiteratureMalignant NeoplasmsMicroRNAsMidwestern United StatesMolecularMolecular AnalysisNeuraxisNeurologicNeuronal DifferentiationNeuronsNeurosecretory SystemsOutcomeOvarianOvaryPathway interactionsPituitary GlandPosterior Pituitary GlandProgesteroneProtein AnalysisReportingReproductive systemResearchRiskSerotonergic SystemSerotoninSourceSteroid biosynthesisStructureSystemSystems DevelopmentTestingTestisThyroid GlandToxic effectTranscriptTranscription AlterationTranslatingTransport ProcessUnited StatesUnited States Environmental Protection AgencyUp-RegulationVertebratesWaterWater SupplyZebrafishagricultural regionaxon growthbrain tissuecarcinogenesischemical groupdrinking waterepidemiology studyfunctional outcomesmaleneurodevelopmentneuron developmentneurotoxicitynovelpituitary gland developmentpituitary gonadal axisprotein expressionreproductive functionsteroid hormonesuccesstranscriptomics
中文摘要
项目概要
内分泌干扰化学物质 (EDC) 是一类广泛的化学物质,会对健康造成多种不利影响
影响。迄今为止,大多数研究都集中在下游目标系统和不良健康结果上
受到 EDC 暴露的影响,但现在有越来越多的证据表明神经内分泌的主要目标。随着
下丘脑作为多个内分泌轴的中央调节器,具有多种不同的特异性
针对神经内分泌系统的 EDC 可能会导致不良健康后果。阿特拉津,一种
EDC,是美国第二大常用的农业除草剂,也是最常见的除草剂。
饮用水供应中的污染物。阿特拉津受美国环境保护署 (EPA) 监管
饮用水中浓度为十亿分之三 (ppb; µg/L),但浓度高于此规定
经常报告限制。实验室和流行病学研究报告了各种内分泌干扰和
神经系统的不良影响。大多数发现都集中在下丘脑-垂体-性腺轴上,但是
研究还观察到对下丘脑-垂体-甲状腺和下丘脑-垂体-肾上腺的干扰
轴。总体而言,研究支持莠去津影响多个内分泌轴以及以下假设:
下丘脑毒性靶标,但其机制尚未明确阐明,值得进一步研究。在
此外,关于莠去津的内分泌干扰作用,目前美国环保署的报告相互矛盾。
最大污染物水平 (MCL) 为 3 ppb。我们使用斑马鱼模型系统的研究表明
胚胎阿特拉津暴露浓度范围为当前 US EPA MCL 的 1/10 倍至 10 倍,导致
与神经系统和生殖系统发育相关的基因的表达改变
功能、细胞周期和致癌作用;与神经元相关的 microRNA (miRNA) 失调
分化和成熟与癌症;全球低甲基化;并改变了幼虫的头部长度。
此外,我们观察到胚胎暴露于莠去津的成虫产卵成功率下降。
这些成年女性的卵巢黄体酮和卵泡闭锁也有所增加,并且
大脑中的血清素代谢和血清素周转。与不同分子相关的基因改变
在成年女性的脑组织中观察到内分泌和中枢神经系统的通路
男性。这些研究支持胚胎暴露阿特拉津足以导致日后的不良后果
与多个内分泌轴相关的健康结果。本研究的中心假设是
神经内分泌系统是阿特拉津内分泌干扰的目标。我们寻求定义机制
胚胎阿特拉津暴露的毒性可以解释观察到的分子和功能结果
过去对多个内分泌轴的研究。我们将评估几个神经内分泌终点
胚胎发生以确定下丘脑和/或垂体发育和神经元结构的破坏
以及下丘脑-垂体界面的轴突生长改变。
英文摘要
PROJECT SUMMARY
Endocrine disrupting chemicals (EDCs) are a broad group of chemicals resulting in a myriad of adverse health
effects. Most research to date has focused on the downstream target systems and adverse health outcomes
affected by EDC exposure, but there is now increasing evidence for neuroendocrine primary targets. With the
hypothalamus serving as the central regulator of multiple endocrine axes, a multitude of different specific
adverse health outcomes may be observed for EDCs that target the neuroendocrine system. Atrazine, an
EDC, is the second most commonly used agricultural herbicide in the United States and is the most common
contaminant in potable water supplies. Atrazine is regulated by the US Environmental Protection Agency (EPA)
at a concentration of 3 parts per billion (ppb; µg/L) in drinking water, but concentrations above this regulatory
limit are often reported. Laboratory and epidemiology studies report various endocrine disrupting and
neurological adverse impacts. Most findings are focused along the hypothalamus-pituitary-gonadal axis, but
studies also observe interference with the hypothalamus-pituitary-thyroid and hypothalamus-pituitary-adrenal
axes. Overall, studies support that atrazine influences multiple endocrine axes and the hypothesis of a
hypothalamic toxicity target, but the mechanisms are not yet clearly elucidated and warrant further research. In
addition, there are conflicting reports of the endocrine disrupting effects of atrazine near the current US EPA
maximum contaminant level (MCL) of 3 ppb. Our studies using the zebrafish model system show that an
embryonic atrazine exposure at concentrations ranging from 1/10X to 10X the current US EPA MCL resulted in
expression alterations in genes associated with neurological and reproductive system development and
function, cell cycle, and carcinogenesis; deregulation of microRNAs (miRNAs) involved with neuronal
differentiation and maturation and cancer; global hypomethylation; and altered head length in larvae.
Furthermore, we observed a decrease in spawning success in adults with an embryonic atrazine exposure.
These adult females also had an increase in ovarian progesterone and follicular atresia and a decrease in a
serotonin metabolite and serotonin turnover in the brain. Alterations in genes associated with distinct molecular
pathways of the endocrine and central nervous systems were observed in brain tissue of the adult females and
males. These studies support an embryonic atrazine exposure is sufficient to result in later in life adverse
health outcomes associated with multiple endocrine axes. The CENTRAL HYPOTHESIS of this study is that
the neuroendocrine system is the target of atrazine endocrine disruption. We seek to define the mechanisms of
toxicity of an embryonic atrazine exposure that would explain the observed molecular and functional outcomes
of past studies on multiple endocrine axes. We will evaluate several neuroendocrine endpoints during
embryogenesis to identify disruption of the hypothalamus and/or pituitary development and neuronal structure
and axonal growth alterations at the hypothalamus-pituitary interface.
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