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Lead promotes abnormal angiogenesis induced by CCM3 gene defects via mitochondrial pathway

Published online by Cambridge University Press:  07 November 2017

Y. Sun
Affiliation:
Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong, China
H. Zhang
Affiliation:
Interdepartmental Program in Vascular Biology and Therapeutics, Yale University School of Medicine, New Haven, CT, USA
X. Xing
Affiliation:
Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong, China
Z. Zhao
Affiliation:
Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong, China
J. He
Affiliation:
MRC-Mitochondrial Biology Unit, Wellcome Trust, Cambridge, UK
J. Li
Affiliation:
Department of Clinical Epidemiology, Aarhus University, Aarhus, Denmark
J. Chen
Affiliation:
Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong, China
M. Wang
Affiliation:
Interdepartmental Program in Vascular Biology and Therapeutics, Yale University School of Medicine, New Haven, CT, USA
Y. He*
Affiliation:
Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong, China
*
*Address for correspondence: Prof. Y. He, Guangzhou Key Laboratory of Environmental Pollution and Risk Assessment, Sun Yat-sen University School of Public Health, Guangzhou, Guangdong 510080, China. (Email heyun7@mail.sysu.edu.cn)
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Abstract

Lead is one of the environmental pollutants with cardiovascular toxicity. The embryos are particularly sensitive to lead exposure, because it can move through the blood-placental barrier and the blood-brain barrier easily during embryonic development. Cerebral cavernous malformations 3 (CCM3) gene plays an important role in cardiovascular development, mainly affecting cell proliferation, differentiation and apoptosis. In this study, we established a blood vessel development model of mouse embryos in order to imitate human people with CCM3 genes defects and exposing to environment toxin Pb in utero. We would like to determine the interaction of Pb and CCM3 gene on vascular development, and to explore the mechanisms. We found that the yolk sac of CCM3 heterozygous mice embryo showed abnormal morphology at E11.5 after lead treatment comparing with wild type (WT) mice without lead exposure, meanwhile it showed more angiogenesis and vascular remodeling in the hematoxylin and eosin stained sections of the CCM3+/− yolk sac with lead exposure. We also found that the similar effect of Pb and CCM3 gene on mitochondrial DNA (mtDNA) copy number in vivo and in vitro. Mitochondrial morphology and function also changed in primary human umbilical vein endothelial cells after lead exposure. Besides, it was found that the HIF-1α and TFAM which have close relationship with mtDNA biogenesis showed similarly increasing messenger RNA expression in both human and mouse-derived primary cells with lead treated and CCM3 gene knockout. All of the above results indicated that lead and CCM3 might damage endothelial cells through mitochondria pathway and eventually both affected angiogenesis.

Information

Type
Original Article
Copyright
© Cambridge University Press and the International Society for Developmental Origins of Health and Disease 2017 
Figure 0

Table 1 The procedure of graphite furnace atomic absorption spectrometry

Figure 1

Fig. 1 The effect of PbAC exposure on the angiogenesis of CCM3+/− embryo at E11.5. (a) The blood lead concentrations of pregnant mice at E11.5 from control and 0.05% PbAC group were analyzed with atomic absorption spectrometry. The blood lead mean was 310.44±89.20 μg/l in the 0.05% PbAC group. **P<0.01, compared with the control group. (b) Morphology changes of yolk sac of WT and CCM3+/− at E11.5 after PbAC exposure. It was observed significantly opaque yellow and yolk sac blood vessels branches in the CCM3+/− embryonic yolk sac of 0.05% PbAC group. (c) Hematoxylin and eosin (HE) pathological of yolk sac results showed that there were more small blood vessels and structural abnormalities in yolk sac of CCM3+/− embryo after PbAC exposure. (d) Either CCM3 genetic defects or lead exposure caused mitochondrial DNA (mtDNA) copy number decrease. There was the statistical significance lead–CCM3 interactions (F=6.563, P=0.045). (e) The statistical analysis of the yolk sac vascular diameter in HE staining at E11.5. There was the lead–CCM3 interaction (F=6.664, P=0.024) in the vessel diameter in the range of 20–30 μm, and >100 μm range, the control group CCM3+/− macrovascular ratio is greater than the other groups with statistically significant difference between groups (F=9.428, P=0.009). aRepresents control and PbAC exposure statistically differences; cRepresents a statistically significant lead–CCM3 interaction; *P<0.05, comparing with the control group WT genotype embryos.

Figure 2

Fig. 2 The mitochondrial changes after PbAC exposure in human umbilical vein endothelial cells (HUVECs). (a) The mitochondrial morphology in HUVECs was observed (200×) with MitoTrackery fluorescent probe staining. The mitochondrial dendritic network distributed around the nucleus in the normal cells, while the mitochondrial structures were destroyed characterized with fragmentation and cyclic structures appearing in the PbAC exposure group. (b) The fluorescence intensity quantitative results showed the fluorescence intensity increased after PbAC exposure with statistical positive correlation (r=0.679, P<0.01). **P<0.01, compared with the control group (n=3 times). (c) The fluorescence images of HUVECs with mitochondrial membrane potential (MMP) probe JC-1 staining (200×). (d) The fluorescence intensity quantitative results of MMP in HUVECs. **P<0.01, *P<0.05; comparing with control group (n=3 times). The results showed that the ratio of red and green fluorescence decreased as the PbAC level increasing, and there were the statistical significance dose–response relationship (r=−0.665, P<0.05). (e) The results showed that AMP/ATP ratio increased compared with the control group, and there was a statistically significant difference (P<0.01), and a dose–response correlation between PbAC dose and AMP/ATP value (r=0.997, P<0.01). Note: **P<0.01, compared with the control group (n=3 times).

Figure 3

Fig. 3 The effect of PbAC exposure and CCM3 gene defect on the mitochondrial DNA (mtDNA) copy number and HIF-1α (a) and TFAM. (a) The results showed that the lead exposure made the mtDNA copy number less compared with the control group in HUVECs and there was the statistically significant difference (P<0.01) and a dose-effect negative correlation (r=−0.775, P<0.01). (b) The mtDNA copy number decreased in CCM3−/− imHUVECs compared with imHUVECs, and the result made it clear that CCM3 gene and lead both injured the mtDNA and there was statistically significant PbAC and CCM3 interaction (F=169.7, P<0.001). **P<0.01, compared with the imHUVECs with empty plasmid transfection and no PbAC treated (n=3 times). (c) HIF-1α mRNA expression level increased in the HUVECs after PAC exposure compared with control cell. (d) The expression of TFAM mRNA level in HUVECs increased along with PbAC level rising and there was a significant difference in the TFAM change compared with the control group. **P<0.01, compared with the control group. (e) The HIF-1α and TFAM mRNA expression in CCM3+/− mouse brain microvascular endothelial cells (BMC) increased compared with in WT. **P<0.01, compared with the WT BMC (n=3 times).