Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2009 May;117(5):778-83.
doi: 10.1289/ehp.0800026. Epub 2009 Jan 5.

Differential regulation of dopamine transporter function and location by low concentrations of environmental estrogens and 17beta-estradiol

Affiliations

Differential regulation of dopamine transporter function and location by low concentrations of environmental estrogens and 17beta-estradiol

Rebecca A Alyea et al. Environ Health Perspect. 2009 May.

Erratum in

  • Environ Health Perspect. 2009 Oct;117(10):A435

Abstract

Background: The effects of 17beta-estradiol (E2) and xenoestrogens (XEs) on dopamine transport may have important implications for the increased incidence of neurologic disorders, especially in women during life stages characterized by frequent hormonal fluctuations.

Objective: We examined low concentrations of XEs [dieldrin, endosulfan, o', p'-dichlorodiphenyl-ethylene (DDE), nonylphenol (NP), and bisphenol A (BPA)] for nongenomic actions via action of membrane estrogen receptors (ERs).

Methods: We measured activity of the dopamine transporter (DAT) by the efflux of 3H-dopamine in nontransfected nerve growth factor-differentiated PC12 rat pheochromocytoma cells expressing membrane DAT, ER-alpha, ER-beta, and G-protein-coupled receptor 30. We used a plate immunoassay to monitor trafficking of these proteins.

Results: All compounds at 1 nM either caused efflux or inhibited efflux, or both; each compound evoked a distinct oscillatory pattern. At optimal times for each effect, we examined different concentrations of XEs. All XEs were active at some concentration < 10 nM, and dose responses were all nonmonotonic. For example, 10(-14) to 10(-11) M DDE caused significant efflux inhibition, whereas NP and BPA enhanced or inhibited efflux at several concentrations. We also measured the effects of E2/XE combinations; DDE potentiated E(2)-mediated dopamine efflux, whereas BPA inhibited it. In E2-induced efflux, 15% more ER-alpha trafficked to the membrane, whereas ER-beta waned; during BPA-induced efflux, 20% more DAT was trafficked to the plasma membrane.

Conclusions: Low levels of environmental estrogen contaminants acting as endocrine disruptors via membrane ERs can alter dopamine efflux temporal patterning and the trafficking of DAT and membrane ERs, providing a cellular mechanism that could explain the disruption of physiologic neurotransmitter function.

Keywords: dopamine efflux; low concentrations; nongenomic; xenoestrogens.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Effects of 10−9 M E2 (n = 18), DES (n = 23), DDE (n = 14), NP (n = 18), dieldrin (n = 14), BPA (n = 14), and endosulfan (n = 18) on the dopamine efflux time course. The 10−9 M E2 time course is reproduced from Alyea et al. (2008), with permission of Journal of Neurochemistry, and is included here for purposes of comparison. Values are means and SEs. Points above the zero point line indicate a positive efflux of dopamine from the cells. *p < 0.05 compared with control. #p < 0.05 compared with E2 treatment.
Figure 2
Figure 2
Concentration-dependent dopamine efflux patterns for E2 and XEs at 9 (A) and 5 min (B), using optimal time points for each compound chosen from the 10−9 M time course (Figure 1). (A) A 9-min dopamine efflux for E2, DES, endosulfan, DDE, NP, and BPA at concentrations ranging from 10−14 to 10−9 M. (B) A 5-min dopamine efflux for E2, dieldrin, NP, and BPA at concentrations ranging from 10−14 to 10−9 M. Values are means and SEs; numbers per treatment are as follows: E2, n = 18; dieldrin, n= 12; DES, n= 18; endosulfan, n= 12; DDE, n= 12; BPA, n= 23; NP, n= 15. Points above the zero point line indicate a positive efflux of dopamine from the cells. *p < 0.05 compared with control. #p < 0.05 compared with E2 treatment.
Figure 3
Figure 3
Quantitative plate assay measuring immunoreactive protein levels for plasma membrane and total ER-α, ER-β, GPR30, and DAT after treatment with E2 for 9 min (A), or BPA for 5 (B) or 9 min (C). (A) 10−9 M E2 for 9 min (dopamine efflux was significantly increased at this time point and concentration). (B) 10−14 M BPA for 5 min (DA efflux was significantly increased at this time point and concentration). (C) 10−12 M BPA for 9 min (DA efflux was significantly inhibited at this time point and concentration). (A) is modified from Alyea et al. (2008) with permission of Journal of Neurochemistry. Values are means and SEs; n = 24 for all compounds. Points above the zero point line indicate a positive efflux of dopamine from the cells. *p < 0.05 compared with control. #p < 0.05 compared with membrane, shown here for comparison with changes caused by BPA alone.
Figure 4
Figure 4
Effects of physiologic levels of E2 (10−9 M) combined with multiple concentrations of DDE or BPA measured by dopamine efflux assay. (A) E2 plus increasing concentrations of DDE during a 9-min dopamine efflux assay compared with E2-mediated dopamine efflux and DDE-mediated dopamine efflux. (B) E2 plus increasing concentrations of BPA during a 5-min dopamine efflux assay compared with E2-mediated dopamine efflux and BPA-mediated dopamine efflux. Values are means and SEs; numbers per treatment are as follows: E2, n = 18; BPA, n = 14; DDE, n = 14; DDE + E2, n = 15; BPA + E2, n = 15. Points above the zero point line indicate a positive efflux of dopamine from the cells. *p < 0.05 compared with control for combinations. #p < 0.05 compared with E2 treatment. ##p < 0.05 compared with control for E2.

References

    1. Agency for Toxic Substances and Disease Registry. Toxicological Profile for Aldrin and Dieldrin. Atlanta:GA: Agency for Toxic Substances and Disease Registry; 2002. [[accessed 1 April 2009]]. Available: http://www.atsdr.cdc.gov/toxprofiles/tp1.html.
    1. Alyea RA, Laurence SE, Kim SH, Katzenellenbogen BS, Katzenellenbogen JA, Watson CS. The roles of membrane estrogen receptor subtypes in modulating dopamine transporters in PC-12 cells. J Neurochem. 2008;106:1525–1533. - PMC - PubMed
    1. Arnold SF, Klotz DM, Collins BM, Vonier PM, Guillette LJ, McLachlan JA. Synergistic activation of estrogen receptor with combinations of environmental chemicals. Science. 1996;272:1489–1492. - PubMed
    1. Bemis JC, Seegal RF. PCB-induced inhibition of the vesicular monoamine transporter predicts reductions in synaptosomal dopamine content. Toxicol Sci. 2004;80:288–295. - PubMed
    1. Bornman MS, Pretorius E, Marx J, Smit E, van der Merwe CF. Ultrastructural effects of DDT, DDD, and DDE on neural cells of the chicken embryo model. Environ Toxicol. 2007;22:328–336. - PubMed

Publication types

LinkOut - more resources