121
with harmful substances, the soil at those unauthorized dumpsites have been closely
examined for the presence of chemical substances. Guiyu, South China, which is
perceived as the world’s largest e-waste dumpsite reported to have exceedingly high
amounts of lead (Pb), cadmium (Cd), chromium (Cr), polychlorinated biphenyls
(PCBs), polybrominated diphenyl ethers (PBDEs), polychlorinated dibenzodioxins/
dibenzofurans (PCDD/Fs), and polycyclic aromatic hydrocarbons (PAH) [26]. Food
and water in the surrounding areas have also become extremely contaminated. In
villages alongside the rivers where e-waste dumps are destroyed, residents utilize
the polluted river water for drinking, cooking, and cleaning [29]. High levels of lead
and cadmium have been found in rice in the Taizhou region, which are reported to
be 2–4 times higher than the permitted level (0.2 mg/k) [30]. Extreme contaminant
exposure rates, via food, water, or air, have been identified in e-waste recycling
areas for workers and natives [31].
Conclusion
Amid progress in several other sectors in the third world countries, there is still
rather little data collected in this field. The populace subjected to endocrine disruptors in those countries and their level of toxicity are not adequately recorded and
may not be accurately measured. In the future, we need to have better data about
how and when the EDC act is required to avoid the occurrence of disease by reducing exposures to endocrine disruptors [7]. The chemicals list presently investigated
needs to be expanded to include other materials and also chemical byproducts.
EDCs’ source and exposure routes should be analyzed further [32]. There needs to
develop, finance, and implement our chemical strategies at the local, national, and
global levels to guarantee public health [8]. To evaluate the EDCs exposure during
growth periods, it is essential to develop potential biomarkers that can help to detect
the EDCs susceptibility windows and early therapeutic measures can be developed.
Furthermore, there should be easy to understand health information tools for public
awareness. Eventually, due to the shortcomings found in clinical and epidemiological trials, the data remains complex. Even though the proof is often incomplete, the
adverse effects of EDCs must be decreased.
Conflicts of Interest The authors declare no conflict of interest.
References
1. Gore AC, Chappell V, Fenton S, Flaws JA, Nadal A, Prins GS, et al. EDC-2: the Endocrine
Society’s second scientific statement on endocrine-disrupting chemicals. Endocr Rev.
2015;36(6):E1–E150.
2. Colborn T, Vom Saal FS, Soto AM. Developmental effects of endocrine-disrupting chemicals
in wildlife and humans. Environ Health Perspect. 1993;101(5):378–84.
7 Endocrine-Disrupting Chemicals: Occurrence and Exposure to the Human Being
with harmful substances, the soil at those unauthorized dumpsites have been closely
examined for the presence of chemical substances. Guiyu, South China, which is
perceived as the world’s largest e-waste dumpsite reported to have exceedingly high
amounts of lead (Pb), cadmium (Cd), chromium (Cr), polychlorinated biphenyls
(PCBs), polybrominated diphenyl ethers (PBDEs), polychlorinated dibenzodioxins/
dibenzofurans (PCDD/Fs), and polycyclic aromatic hydrocarbons (PAH) [26]. Food
and water in the surrounding areas have also become extremely contaminated. In
villages alongside the rivers where e-waste dumps are destroyed, residents utilize
the polluted river water for drinking, cooking, and cleaning [29]. High levels of lead
and cadmium have been found in rice in the Taizhou region, which are reported to
be 2–4 times higher than the permitted level (0.2 mg/k) [30]. Extreme contaminant
exposure rates, via food, water, or air, have been identified in e-waste recycling
areas for workers and natives [31].
Conclusion
Amid progress in several other sectors in the third world countries, there is still
rather little data collected in this field. The populace subjected to endocrine disruptors in those countries and their level of toxicity are not adequately recorded and
may not be accurately measured. In the future, we need to have better data about
how and when the EDC act is required to avoid the occurrence of disease by reducing exposures to endocrine disruptors [7]. The chemicals list presently investigated
needs to be expanded to include other materials and also chemical byproducts.
EDCs’ source and exposure routes should be analyzed further [32]. There needs to
develop, finance, and implement our chemical strategies at the local, national, and
global levels to guarantee public health [8]. To evaluate the EDCs exposure during
growth periods, it is essential to develop potential biomarkers that can help to detect
the EDCs susceptibility windows and early therapeutic measures can be developed.
Furthermore, there should be easy to understand health information tools for public
awareness. Eventually, due to the shortcomings found in clinical and epidemiological trials, the data remains complex. Even though the proof is often incomplete, the
adverse effects of EDCs must be decreased.
Conflicts of Interest The authors declare no conflict of interest.
References
1. Gore AC, Chappell V, Fenton S, Flaws JA, Nadal A, Prins GS, et al. EDC-2: the Endocrine
Society’s second scientific statement on endocrine-disrupting chemicals. Endocr Rev.
2015;36(6):E1–E150.
2. Colborn T, Vom Saal FS, Soto AM. Developmental effects of endocrine-disrupting chemicals
in wildlife and humans. Environ Health Perspect. 1993;101(5):378–84.
7 Endocrine-Disrupting Chemicals: Occurrence and Exposure to the Human Being