PROBIEN   20416
INSTITUTO DE INVESTIGACION Y DESARROLLO EN INGENIERIA DE PROCESOS, BIOTECNOLOGIA Y ENERGIAS ALTERNATIVAS
Unidad Ejecutora - UE
capítulos de libros
Título:
Placental Toxicology of pesticides
Autor/es:
GLADIS MAGNARELLI AND NATALIA GUIÑAZU
Libro:
The Human Placenta",
Editorial:
InTech - Open Access Publisher
Referencias:
Año: 2012; p. 95 - 118
Resumen:
Considering
that pathological conditions in the placenta are important causes of
intrauterine, perinatal or maternal death, and a great deal of mother and child
morbidity, understanding the impact of xenobiotics in the placenta is a major
concern to toxicologists.
In
earlier times, the placenta was regarded as an organ protecting the fetus from
exposures to toxic chemicals. We now understand that they may cross through the
placenta and enter fetal blood stream. Placenta also interferes with xenobiotic
delivery to the fetus, by expressing active membrane transporters and xenobiotic
metabolism enzymes. The regulation of these enzymes and
transporters and the effects of genetic polymorphisms on their function may
have important implications in fetal and placental exposure to xenobiotics and
their potential toxicities. In addition, some toxicants may
accumulate in the placenta potentially affecting its development and or
function. Therefore, understanding what the placenta does to xenobiotics and
what they do to the placenta, should provide the basis for the use of this
organ as a tool to investigate and predict some aspects of developmental
toxicity. In this sense, placenta
is a key tool for biomonitoring xenobiotic
exposure. It is easy to collect and provides a large sample
amount for analysis. Placenta
is often the most accessible and readily available component of the triad
mother-infant-placenta. It shows cumulative effects of pregnancy-related
events, reflects the intrauterine environment,
and may be examined to a degree that infant
usually cannot. A critical issue for placenta toxicological analysis is the
avaibility and appropriate use of biomarkers, which provide measures of the exposure, toxic effects
and individual susceptibility to toxicants. However,
as epidemiological studies cannot control all the confounding factors,
experimental designs are also needed. Thus, in vitro, in
vivo and ex vivo models have been used to elucidate toxicology of
toxicants in the human placenta.
However, they have some limitations. Despite
common physiological functions, the placentas of different species are
heterogeneous in their morphology, transport and metabolism of
xenobiotics, raising the difficulty of
obtaining a good representative model of human placenta. Moreover, changes in
placental function due to chemical exposition may also depend on the
gestational period in which exposition occurs. As consequence, information
about biochemical and molecular toxicity of xenobiotics in human
placenta is scarce because it is a difficult subject for research.
This chapter will give an
update about placenta toxicity of two families of pesticides:
Organochhorine (OC) and organophosphate (OP). A link between exposure to these compounds during
the gestational period and adverse reproductive outcomes, recurrent
miscarriage, low birth weight, increased risk of malformations and intrauterine
growth restriction were reported.
OC are persistent and
ubiquiotous environmental contaminants which have been restricted or
banned in industrialized nations, and their
contamination levels have disminished or are expected to decline. However, some
of these chemicals are still used in developing countries. Due to their high lipophilicity and slow breakdown, they
bioaccumulate in the adipose tissue.
During pregnancy, OC stored in maternal adipose tissue can be
mobilized and enter her blood circulation and
reach the placenta. Although there is not a clear and precise model for the
bioaccumulation of OC in this organ, it is known that some OC
metabolites selectively accumulate in the placenta suggesting a tissue specific
metabolic activity. OC high lipophilicity favours their incorporation in
biomembranes. Therefore, membrane bound enzymes, phospholipid metabolism and
signalling pathways are sensible to OC deleterious effects as shown in Table I.
Because of their widespread and intensive use, OP are
considered as a pesticide class of great interest for the study of
environmental health. Conversely to OC, they are
rapidly metabolized and excreted, therefore, OP metabolites are usually determined
in fluids as maternal urine or cord blood. Although the
placenta is a non innervated organ, the presence of cholinergic system has been
demonstrated by unequivocal methods. Acetilcholinesterase, the primary target of
OP derived oxon metabolite as well as carboxilesterases, the secondary one, may
be used as exposition biomarkers.
Regarding the possible mechanisms intervening in
the pathogenesis of placenta injury by OP, a broad spectrum of
non cholinergic targets appears in scene such as: impaired mitochondrial bioenergetics, hormonal
and immune disruption.
Both types of pesticides, OC and OP, have
demonstrated to mediate some of their toxic events by oxidative stress, which is likely
a major contributing factor to trophoblast injury and placenta disfunction.
According to the above
considerations, this chapter would provide a comprehensive discussion on the molecular
and biochemical bases of pesticides
effects on the human placenta,
and on the usefullness of biomarkers in placenta for toxicological
analysis. Future challenges as placenta micro array, epigenetic studies and effects
of pesticide mixtures would be briefly described.