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IMPACT OF OF NANOPARTICLES ON REPRODUCTIVE
SYSTEM
Anju Surendranath
Division of Toxicology
Section 1
 Introduction
 Routes of exposure of NPs
 Reproductive toxicity
 Developmental toxicity
 Teratogenicity
 Future advances in research
 References
Section 2
 Research paper
CONTENTS
The vast growth of nanotechnologies with all their
far-reaching benefits has fostered concerns about the
potential health risks of nanoparticles (NPs).
It is broadly accepted that the fetus may be more
sensitive to chemical exposures than adults.
Overall, it is plausible that NP may translocate from
the different routes of exposure to the placenta and
fetus, but also that adverse effects may occur
secondarily to maternal inflammatory responses.
INTRODUCTION
Malek et al; Curr. Pharm. Biotechnol (2011)
Huang et al; Placenta 36 (2015)
REPRODUCTIVE TOXICITY
BIOCHEMICA
L RESPONSE
CELLULAR
RESPONSE
TOXICANT
ORGAN
RESPONSE ORGANISM
RESPONSE
IMPAIRED
REPRODUCTION
Adverse Outcome
ROS production
on gonad tissue
Oxidative
stress
Germ Cell
Apoptosis
Molecular
initiating event
Key Events
NPs
DEVELOPMENTAL TOXICITY
Yang et al; Sci. Rep. 2 (2012)
Pb
Pb
Soares et al; placenta.2011
TERATOGENICITY
Thalidomide Disaster
COMPLICATIONS OF REPRODUCTIVE TOXICITY
Miscarriage/
Still birth
Low Birth weight Organ
malformation
Birth defects CNS problems Fetal addiction
ABNORMALITIES IN
GESTATIONAL AND FOETAL
PARAMETERS DUE TO NPs
EXPOSURE
Effect of NP on foetal organ abnormalities
Effect of maternal NP exposure on nervous system of foetus
Effect of NP on reproductive system of offspring
Effect of NP in embryonic and extra embryonic tissues
Yang et al; Sci. Rep. 2 (2012)
ANALYSIS PATTERNS
• Overall toxicokinetic pattern of nanoparticles.
• Transplacental transfer.
• Human placental perfusion models
• Animal models.
• Potential mechanisms in developmental
toxicity.
OECD guidelines for reproductive and
developmental toxicity studies
OECD 421 Reproduction/ Developmental toxicity
screening test.
OECD 422 Combined Repeated Dose Toxicity Study
with Reproduction/ Developmental Toxicity
Screening Test.
OECD 414 Prenatal Development Toxicity Study.
OECD 416 Two-Generation Reproduction Toxicity.
OECD 443 Extended One-Generation Reproductive
Toxicity Study.
OECD 426 Developmental Neurotoxicity Study.
Future advances in research
• No in vitro assay can completely recapitulate the
complexities of fetal development or the fetal-
maternal interactions that occur in vivo.
• minimal xenobiotic metabolism occurs in ESCs, it is
likely that most proteratogens will be classified as
false negatives in ESC5 based assays.
• Recently, researchers have utilized placental BeWo
cells to generate toxicokinetic data.
RESEARCH PAPER
Topic: Maternal Placental- foetal
Biodistribution of multimodal
polymeric nanoparticles in a
pregnant rat model in mild and late
gestation.
Determine the biodistribution of both cationic and anionic
multimodal (fluorescent and paramagnetic) PGMA NPs in
pregnant rat model at two different stages of pregnancy
[embryonic day 10 (ED10) and day 20 (ED20)] using
pharmacological doses for the application of multimodal
polymeric nanoparticles during pregnancy.
Fluorescently-labelled and super paramagnetic
PGMA nanoparticles to evaluate nanomaterial
biodistribution and maternal-fetal exposure.
HYPOTHESIS
AIM
Quantitative assessment of
nanoparticle biodistribution.
In vitro and in vivo
assessment of
NP biocompatibility.
Synthesis and characterization
of PGMA and PGMA-PEI NPs.
Placental biodistribution
analysis
Qualitative assessment
using
confocal imaging
Qualitative assessment
using
fluorescence imaging
Experimental Outline
RESULTS & DISCUSSION
(a) TEM image of PGMA-PEI NPs, scale bar: 100 nm. (b) Excitation (solid line) and emission
(discontinuous line) spectra of PGMA/PGMA-PEI NPs containing P10 fluorophore.
(c)Hydrodynamic size distribution of PGMA (solid) and PGMA-PEI(discontinuous) NPs. (d) Zeta
potentials of PGMA (solid) and PGMA-PEI (discontinuous)
NPs.
(a)Hydrodynamic size distribution and (b) zeta potentials of PGMA and PGMA-PEI nanoparticles
after incubation in serum-supplemented media for 4 h. Cytotoxicity assays of PGMA (red bars) and
PGMA-PEI (blue bars) at 10 and 100 µg/ml after (c) 4 h and (d) 24 h incubation.
Fluorescence intensity measurements of ED10 and ED20 tissue
homogenates. Data as mean±SD (n=4).
(a) Liver of ED10 dams. High levels of fluorescence were observed in liver from both PGMA
and PGMA-PEI treated dams. (b) Other organs of ED10 dams. With the exception of the spleen
of the PGMA-PEI treated dam, none of the organs showed a visible level of P10 fluorescence. (c)
Uterine horns containing conceptuses of ED10 dams. In spite of spectral unmixing, low levels of
autofluorescence was observed in controls and treated dams. (d) Uterine horns containing
placenta and fetuses of ED20 dams. The placentae showed a visible level of auto fluorescence in
theP10 spectral region around the junctional zones in all dams.
Representative tissue section of a maternal liver. Higher magnification images
show the accumulation of PGMA and PGMA-PEI nanoparticles in the maternal
liver at ED10 (b & c) and ED20 (d & e). PGMA and PGMA-PEI nanoparticles
were found to be accumulating mainly within Kupffer cells (white arrowheads).
(a) Representative tissue section of a maternal spleen. Higher magnification
images show the accumulation of PGMA and PGMA-PEI nanoparticles in the
maternal spleen at ED10 (b & c) and ED20 (d & e). Nanoparticles (white
arrowheads) were observed throughout the red pulp with higher quantities
amassing around the peripheries of white pulp (denoted by dashed lines)
(a-f) PGMA and (g-i) PGMA-PEI NPs in the ED10 conceptus , (b ) outline of sections denoting tissue
regions. (c and e) higher magnification images of areas shown in “fig: a”. Even higher magnification images
of areas shown in “fig c and e”. PGMA NPs were found in ectoplacental cone and primary decidual cone.
Fig: (g) represents PGMA-PEI treated dams placenta in ED10 conceptus. (h) outline of sections denoting
tissue regions. (i and k) higher magnification images of areas shown in rectangles in “g”. (j and l) higher
magnification images of panels shown in “i and k” respectively. PGMA-PEI were observed in decidua,
venous sinusoids and tissues close to ectoplacental cone.
(a-d) PGMA and (e-h) PGMA-PEI NPs in placenta ED20. (b-d) higher magnification
images of areas depicted in rectangles in “a”. PGMA NPs were observed in chorionic
plate, junctional zone and in labyrinth. (e) representative tissue section from PGMA-PEI
dams placenta. (f-h) higher magnification images of the areas indicated by the rectangles
in “fig: e”. PGMA-PEI NPs were observed in chorionic plate, junctional zone and
labyrinth zone respectively.
CONCLUSION
•Biocompatible polymeric materials such as PGMA and PGMA-PEI were
investigated as delivery platforms for therapeutics.
•Despite of techniques such as relaxometry and multispectral imaging, confocal
microscopy using a differential charge based approach provided a relatively sensitive
representation of tissue uptake in the pregnant rat.
•It has been reported that, in general, smaller particles exhibit greater placental
uptake and passage than larger particles; the increased placental uptake of PEI-
PGMA nanoparticles is therefore likely to be not dependant on size.
•This work highlights the advantages and limitations of the use of multimodal
nanoparticles to accurately measure the uptake of polymeric nanoparticles and
subsequently the extent and impact of maternal, fetal and placental exposure.
1. Menezes, V., Malek, A. & Keelan, J. A. Nanoparticulate drug delivery in
pregnancy: placental passage and fetal exposure. Curr.Pharm. Biotechnol. 12,
731–742, doi:10.2174/138920111795471010 (2011).
2. 2. Huang, J.-P. et al. Nanoparticles can cross mouse placenta and induce
trophoblast apoptosis. Placenta 36, 1433–41, doi:10.1016/j. placenta.2015.10.007
(2015).
3. Soares, M. J., Chakraborty, D., Karim Rumi, M. A., Konno, T. & Renaud, S. J.
Rat placentation: An experimental model for investigating the hemochorial
maternal-fetal interface. Placenta 33, 233–243,
doi:10.1016/j.placenta.2011.11.026 (2012).
4. Keelan, J. A., Leong, J. W., Ho, D. & Iyer, K. S. Therapeutic and safety
considerations of nanoparticle-mediated drug delivery in pregnancy. Nanomed. 10,
2229–2247, doi:10.2217/nnm.15.48 (2015).
5. Yang, H. et al. Effects of gestational age and surface modification on materno-
fetal transfer of nanoparticles in murine pregnancy. Sci. Rep. 2, 847–855,
doi:10.1038/srep00847 (2012).
REFERENCES
Reproductive toxicity induced by nanoparticles

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Reproductive toxicity induced by nanoparticles

  • 1. IMPACT OF OF NANOPARTICLES ON REPRODUCTIVE SYSTEM Anju Surendranath Division of Toxicology
  • 2. Section 1  Introduction  Routes of exposure of NPs  Reproductive toxicity  Developmental toxicity  Teratogenicity  Future advances in research  References Section 2  Research paper CONTENTS
  • 3. The vast growth of nanotechnologies with all their far-reaching benefits has fostered concerns about the potential health risks of nanoparticles (NPs). It is broadly accepted that the fetus may be more sensitive to chemical exposures than adults. Overall, it is plausible that NP may translocate from the different routes of exposure to the placenta and fetus, but also that adverse effects may occur secondarily to maternal inflammatory responses. INTRODUCTION
  • 4.
  • 5. Malek et al; Curr. Pharm. Biotechnol (2011)
  • 6. Huang et al; Placenta 36 (2015)
  • 7. REPRODUCTIVE TOXICITY BIOCHEMICA L RESPONSE CELLULAR RESPONSE TOXICANT ORGAN RESPONSE ORGANISM RESPONSE IMPAIRED REPRODUCTION Adverse Outcome ROS production on gonad tissue Oxidative stress Germ Cell Apoptosis Molecular initiating event Key Events NPs
  • 8. DEVELOPMENTAL TOXICITY Yang et al; Sci. Rep. 2 (2012)
  • 9. Pb Pb Soares et al; placenta.2011
  • 11.
  • 12.
  • 13. COMPLICATIONS OF REPRODUCTIVE TOXICITY Miscarriage/ Still birth Low Birth weight Organ malformation Birth defects CNS problems Fetal addiction
  • 14. ABNORMALITIES IN GESTATIONAL AND FOETAL PARAMETERS DUE TO NPs EXPOSURE
  • 15. Effect of NP on foetal organ abnormalities
  • 16. Effect of maternal NP exposure on nervous system of foetus
  • 17. Effect of NP on reproductive system of offspring
  • 18. Effect of NP in embryonic and extra embryonic tissues
  • 19. Yang et al; Sci. Rep. 2 (2012)
  • 20. ANALYSIS PATTERNS • Overall toxicokinetic pattern of nanoparticles. • Transplacental transfer. • Human placental perfusion models • Animal models. • Potential mechanisms in developmental toxicity.
  • 21. OECD guidelines for reproductive and developmental toxicity studies OECD 421 Reproduction/ Developmental toxicity screening test. OECD 422 Combined Repeated Dose Toxicity Study with Reproduction/ Developmental Toxicity Screening Test. OECD 414 Prenatal Development Toxicity Study. OECD 416 Two-Generation Reproduction Toxicity. OECD 443 Extended One-Generation Reproductive Toxicity Study. OECD 426 Developmental Neurotoxicity Study.
  • 22. Future advances in research • No in vitro assay can completely recapitulate the complexities of fetal development or the fetal- maternal interactions that occur in vivo. • minimal xenobiotic metabolism occurs in ESCs, it is likely that most proteratogens will be classified as false negatives in ESC5 based assays. • Recently, researchers have utilized placental BeWo cells to generate toxicokinetic data.
  • 23. RESEARCH PAPER Topic: Maternal Placental- foetal Biodistribution of multimodal polymeric nanoparticles in a pregnant rat model in mild and late gestation.
  • 24.
  • 25. Determine the biodistribution of both cationic and anionic multimodal (fluorescent and paramagnetic) PGMA NPs in pregnant rat model at two different stages of pregnancy [embryonic day 10 (ED10) and day 20 (ED20)] using pharmacological doses for the application of multimodal polymeric nanoparticles during pregnancy. Fluorescently-labelled and super paramagnetic PGMA nanoparticles to evaluate nanomaterial biodistribution and maternal-fetal exposure. HYPOTHESIS AIM
  • 26. Quantitative assessment of nanoparticle biodistribution. In vitro and in vivo assessment of NP biocompatibility. Synthesis and characterization of PGMA and PGMA-PEI NPs. Placental biodistribution analysis Qualitative assessment using confocal imaging Qualitative assessment using fluorescence imaging Experimental Outline
  • 28. (a) TEM image of PGMA-PEI NPs, scale bar: 100 nm. (b) Excitation (solid line) and emission (discontinuous line) spectra of PGMA/PGMA-PEI NPs containing P10 fluorophore. (c)Hydrodynamic size distribution of PGMA (solid) and PGMA-PEI(discontinuous) NPs. (d) Zeta potentials of PGMA (solid) and PGMA-PEI (discontinuous) NPs.
  • 29. (a)Hydrodynamic size distribution and (b) zeta potentials of PGMA and PGMA-PEI nanoparticles after incubation in serum-supplemented media for 4 h. Cytotoxicity assays of PGMA (red bars) and PGMA-PEI (blue bars) at 10 and 100 µg/ml after (c) 4 h and (d) 24 h incubation.
  • 30. Fluorescence intensity measurements of ED10 and ED20 tissue homogenates. Data as mean±SD (n=4).
  • 31. (a) Liver of ED10 dams. High levels of fluorescence were observed in liver from both PGMA and PGMA-PEI treated dams. (b) Other organs of ED10 dams. With the exception of the spleen of the PGMA-PEI treated dam, none of the organs showed a visible level of P10 fluorescence. (c) Uterine horns containing conceptuses of ED10 dams. In spite of spectral unmixing, low levels of autofluorescence was observed in controls and treated dams. (d) Uterine horns containing placenta and fetuses of ED20 dams. The placentae showed a visible level of auto fluorescence in theP10 spectral region around the junctional zones in all dams.
  • 32. Representative tissue section of a maternal liver. Higher magnification images show the accumulation of PGMA and PGMA-PEI nanoparticles in the maternal liver at ED10 (b & c) and ED20 (d & e). PGMA and PGMA-PEI nanoparticles were found to be accumulating mainly within Kupffer cells (white arrowheads).
  • 33. (a) Representative tissue section of a maternal spleen. Higher magnification images show the accumulation of PGMA and PGMA-PEI nanoparticles in the maternal spleen at ED10 (b & c) and ED20 (d & e). Nanoparticles (white arrowheads) were observed throughout the red pulp with higher quantities amassing around the peripheries of white pulp (denoted by dashed lines)
  • 34. (a-f) PGMA and (g-i) PGMA-PEI NPs in the ED10 conceptus , (b ) outline of sections denoting tissue regions. (c and e) higher magnification images of areas shown in “fig: a”. Even higher magnification images of areas shown in “fig c and e”. PGMA NPs were found in ectoplacental cone and primary decidual cone. Fig: (g) represents PGMA-PEI treated dams placenta in ED10 conceptus. (h) outline of sections denoting tissue regions. (i and k) higher magnification images of areas shown in rectangles in “g”. (j and l) higher magnification images of panels shown in “i and k” respectively. PGMA-PEI were observed in decidua, venous sinusoids and tissues close to ectoplacental cone.
  • 35. (a-d) PGMA and (e-h) PGMA-PEI NPs in placenta ED20. (b-d) higher magnification images of areas depicted in rectangles in “a”. PGMA NPs were observed in chorionic plate, junctional zone and in labyrinth. (e) representative tissue section from PGMA-PEI dams placenta. (f-h) higher magnification images of the areas indicated by the rectangles in “fig: e”. PGMA-PEI NPs were observed in chorionic plate, junctional zone and labyrinth zone respectively.
  • 36. CONCLUSION •Biocompatible polymeric materials such as PGMA and PGMA-PEI were investigated as delivery platforms for therapeutics. •Despite of techniques such as relaxometry and multispectral imaging, confocal microscopy using a differential charge based approach provided a relatively sensitive representation of tissue uptake in the pregnant rat. •It has been reported that, in general, smaller particles exhibit greater placental uptake and passage than larger particles; the increased placental uptake of PEI- PGMA nanoparticles is therefore likely to be not dependant on size. •This work highlights the advantages and limitations of the use of multimodal nanoparticles to accurately measure the uptake of polymeric nanoparticles and subsequently the extent and impact of maternal, fetal and placental exposure.
  • 37. 1. Menezes, V., Malek, A. & Keelan, J. A. Nanoparticulate drug delivery in pregnancy: placental passage and fetal exposure. Curr.Pharm. Biotechnol. 12, 731–742, doi:10.2174/138920111795471010 (2011). 2. 2. Huang, J.-P. et al. Nanoparticles can cross mouse placenta and induce trophoblast apoptosis. Placenta 36, 1433–41, doi:10.1016/j. placenta.2015.10.007 (2015). 3. Soares, M. J., Chakraborty, D., Karim Rumi, M. A., Konno, T. & Renaud, S. J. Rat placentation: An experimental model for investigating the hemochorial maternal-fetal interface. Placenta 33, 233–243, doi:10.1016/j.placenta.2011.11.026 (2012). 4. Keelan, J. A., Leong, J. W., Ho, D. & Iyer, K. S. Therapeutic and safety considerations of nanoparticle-mediated drug delivery in pregnancy. Nanomed. 10, 2229–2247, doi:10.2217/nnm.15.48 (2015). 5. Yang, H. et al. Effects of gestational age and surface modification on materno- fetal transfer of nanoparticles in murine pregnancy. Sci. Rep. 2, 847–855, doi:10.1038/srep00847 (2012). REFERENCES

Editor's Notes

  1. Nanoparticle exposure may directly or indirectly affect embryonic/ foetal development. Indirect effect due to inhaled nanoparticle deposit in maternal alveoli and generation of ROS, in amounts that result in oxidative stress and inflammation. The inflamed lung may release cytokines and acute phase proteins to the blood stream to be transported to organs and tissues relevance for pregnancy and development (uterus, placenta, foetus) as well as maternal neuro endocrine and immune circuits. Here, the biologically active mediators may trigger a range of responses which in turn may interfere with development of foetus. If NP translocate to the maternal stream, they may reach the placenta and taken up by placental cells. Particle induced ROS generation and inflammation has been proposed to interfere with placental vascularisation. If NP passes through the placenta, they may directly interfere with cellular and extracellular constituents and thereby alter vital cellular processes.
  2. Phocomelia (refer)
  3. Positively charged NPs exert toxic effect on BBB. BBB distruction leads to NP entry into the foetal brain which is very sensitive and under developed leads to severe developmental abnormalities.
  4. The literature, to date, provides some, limited evidence, that NP may affect fetal development of the male reproductive system. A recent study, with oral exposure, examined maternally mediated toxicity of ZnO NPs in rats. Mothers were exposed daily via oral route to 500mg/kg ZnO NPs starting 2 weeks prior to mating and continuing until postnatal day 4. Exposure reduced the number of live pups and their body weights. Histopathological examination of offspring ovaries, testes and epididymis revealed no abnormal findings .
  5. Whole tissue fluorescence imaging of representative ED10 and ED20 tissues. Spectral unmixing was performed using a tube containing PGMA-PEI nanoparticles as reference
  6. (a–f) PGMA and (g–l) PGMA-PEI nanoparticles in the ED10 conceptus. De: decidua; ch: chorion; epc: ectoplacental cone; pdz: primary decidual zone. Images are representative of n = 4 per group. . PGMA-PEI nanoparticles (indicated by arrowheads) were observed in the decidua, specifically in the venous sinusoids and tissue close to the ectoplacental cone as well as in the primary decidual zone.
  7. (a–d) PGMA and (e–h) PGMA-PEI nanoparticles in the placenta at ED20. . (b–d)Higher magnification images of the areas indicated by the rectangles in . (e). PGMA-PEI nanoparticles (indicated by arrowheads) were observed in the (f) chorionic plate, in the tissue adjacent to the (g) junctional zone and in the (h) labyrinth zone. Scale bars: (a,e) 1000 μm; (b–d,f–h) 200 μm. JZ: junctional zone; LZ: labyrinth zone; cp: chorionic plate.