Exposure To Urban Air Pollution Nanoparticles and
CNS Disease Volume 5 - Issue 5
Mojtaba Ehsanifar1,2*, Seyyed Shahabeddin Banihashemian3 and Farzaneh Farokhmanesh4
1Department of environmental health engineering, School of public health, Iran University of medical sciences, Tehran, Iran
2Anatomical Sciences Research Center, Kashan University of Medical Sciences, Kashan, Iran
3AJA University of Medical Sciences, Tehran, Iran
4M.A in Psychology in Clinical psychology at the University of Al-Zahra (SA), Tehran, Iran
Received:June 24, 2021 Published:July 7, 2021
Corresponding author:Mojtaba Ehsanifar, Department of environmental health engineering, School of public health Iran University
of medical sciences, Iran
Exposure to urban air pollutants has been established as a source of oxidative stress and neuroinflammation that causes
central nervous system (CNS) disease. Nitrogen oxides, particulate matter (PM), including fine particles (PM with aerodynamic
diameters ≤ 2.5μm, PM 2.5) and ultra-fine particles (UFPs, PM <0.1μm, PM 0.1), transition metals, and ozone are potent or oxidant
capable of producing reactive oxygen species (ROS). While the mechanisms underlying CNS pathology due to air pollution are not
well understood, recent findings suggest that changes in the blood brain barrier (BBB) and or leakage and transmission along the
olfactory nerve into the olfactory bulb (OB) and microglial activation are the key factors of CNS damage following air pollution
exposure. The incidence of stroke and the pathology of Parkinson’s (PD) and Alzheimer’s disease (AD) are associated with air
pollution exposure. Some of the recent research shows that air pollutants reach the brain and in addition to cardiovascular and lung
diseases, affect the health of the CNS too. This review cites evidence that exposure to air pollution fine particles is one of the causes
of CNS disease.
Keywords: Air pollution exposure; Nanoparticles; Airborne particulate matter; CNS disease
Recent studies report that the CNS may be a vital target for
exposure to air pollutants, and especially for traffic air pollutants, of
which diesel exhaust particles (DEPs) are common sources. As said
earlier, there is a strong convergence between experimental animal
studies and human epidemiological studies concerning the ultimate
biochemical and behavioral considerations that are affected by air
pollution exposure [1]. Furthermore, in vitro researches support
the in vivo findings that exposure to DEPs activates microglia and
stimulates neuroinflammation and oxidative stress [2-4]. The
effects of air pollutants pass from periphery to the brain through
systemic inflammation and the movement of UFPs into brain,
where both physical properties of its particles and toxic compounds
adsorbed on the PM can cause damage. Brain capillaries, astroglia,
and especially microglia, respond to air pollution components by
chronic activation, oxidative stress, and inflammation. Exposure to
a high concentration of urban air pollutants is problematic given
the proposed associations between exposure to air pollution and
neurodegenerative diseases such as autism spectrum disorders
(ASD) or dementia. Furthermore, given that even short-term
exposure can cause biochemical changes associated with such
diseases, air pollutants exposure in work places are commonly
low but is also of very concern. Generally, other studies aimed
at better describing the effects of traffic air pollutants exposure
on the CNS, its role and its underlying mechanisms in the
cause of neurodegenerative and neurodevelopmental diseases
are indispensable. Especially, given the greater prevalence of
neurodevelopmental (such as ASD) and neurological disorders
neurodegenerative (such as PD) in males, gender may be affected
by air pollution exposure [5].
Air Pollution Exposure and Developmental Neurotoxicity
Animal surveys and epidemiological surveys suggest that
young people may be particularly vulnerable to the neurotoxicity
of exposure to air pollution [6-11]. Hyperactivity in 7-yearolds
is associated with air pollutants exposure early in life [12].
Research findings in Mexico City show that in addition to cognitive
deficits due to exposure to air pollution, there is a high level of
inflammatory markers in children’s brains [6, 7, 13]. Prenatal
exposure to air pollution, in six groups, was related to delayed
psychomotor development [11]. Some studies show that exposure
to DEPs may cause neurotoxicity [14-16]. Research findings also
show that exposure to urban air pollutants is inversely related to
sustained attention in adolescents [17], and to reduce cognitive
development in preschool children [18]. Prenatal exposure to
the high concentration of DEPs (1.0 mg / m3) causes changes in
locomotor activity, impulsive behavior, and motor coordination in
male mice [19, 20]. Behavioral alteration (enhanced bias toward
immediate rewards), impulsivity-like behavior, and also long term
impairment of short term memory, was reported following early
postnatal ambient PM exposure in mice [16, 21, 22]. Exposure
to UFPs in pregnancy causes depression-like responses in mice
[23,24]. Experimental studies show that long term DEPs exposure
in mice causes changes in motor activity, spatial memory and
learning, and the ability to detect new objects, resulting in oxidative
damage, neurodegeneration, and alterations in gene expression
[25-28].
Autism is a type of neurodevelopmental disorder that
characterized by a significant decrease in social and communication
skills and presence of the stereotyped behaviors [29], and term of
ASD is commonly utilized, include the autism and a range of the
similar disorders. Much attention has been paid to autism among
the neurological disorders that may be associated with exposure
to air pollutants, and some of the recent research has found
associations between exposure to urban air pollutants and autism.
Symptoms of the ASD often present before age of three and usually
accompanied by the abnormalities of attention, learning, cognitive
function, and sensory processing [29]. ASD in the males is common
4 to 12 times more than females [30], and incidence of the ASD
appears to be have increased over past few decades, that is now
estimated to be around 7-9/1000 [31,32]. Findings indicate the
higher levels of oxidative stress in the children with ASD [33, 34],
also higher neuroinflammation, increased systemic inflammation,
and microglia activation [35-38]. Studies showed that residential
proximity to the freeways and prenatal and early-life urban air
pollutants exposure was associated with autism [39,40]. Another
study also showed a related between exposure to PM and ASD,
especially when exposure to PM occurred in third trimester of
pregnancy [41]. Another epidemiological study had also similar
results [42] and the other study showed that maternal DE
exposure was significantly related to ASD, especially in boys [43].
Also, a cohort study evidenced the higher susceptibility following
exposure in the third trimester [44]. The results of some animal
studies are consistent with human observations [1]. Reported that
postnatal exposure to a high level of urban air pollution PM in male
mice causes persistent various neurochemical changes, glial cell
activation, and ventriculomegaly [45]. While has been shown that
prenatal DEPs exposure, to disrupt DNA methylation in the brain,
especially affecting genes involved in neurogenesis and neuronal
differentiation in mice [46]. Prenatal exposure to DEPs at urban
air pollution relevant concentrations (350–400 μg/m3) causes
a behavioral alteration in adult male mice [23]. Human studies
showed that when exposure occurs in the third trimester of the
pregnancy, association between ASD and PM exposure is stronger
[41, 44], which is the equivalent to the first few of postnatal weeks
in rats or mice [47]. As said, our studies in the behavioral alterations
of exposure to DEPs encompassing both prenatal and the postnatal
periods in the mice will be continues.
Air Pollution Exposure and Neurodegeneration
Many epidemiological studies that identify the effects of
exposure to air pollutants on behavior, especially cognitive
behavior, have shown significant effects also in the elderly. So, in
addition to the susceptibility of developing the brain, also aging
brain may be especially sensitive to the neurotoxicity caused by
air pollution [48-51]. As mentioned, the primary mechanisms of
the harmful effects of air pollutants exposure on the CNS appear
to be related to neuroinflammation and oxidative stress [52-55].
There are amples evidence that neuroinflammatory and oxidative
processes occur in the various neurodegenerative diseases [56,
57]. Air pollutants are the CNS inflammatory stimulants which have
been largely overlooked as a risk factor for the neurogenic diseases.
Furthermore, millions are exposed to the air pollutants in job
disasters such as fires, war, and terrorist attacks [58]. Diseases that
are likely to be affected by exposure to air pollutants, including PD
and AD, are also widespread [59]. PD is a devastating motor disorder
and the second most common neurological disorder affecting 23-
1% of the population over 50 years. Given these statistics, there is
considerable concern that the recent findings link exposure to air
pollutants to neurodegenerative and neuropathological conditions
associated with AD and PD. The earliest studies of this transplant
were performed on populations of wild animals naturally exposed
to contaminated urban environments [60].
The other of the important early symptom of the
neurodegenerative diseases and particularly of PD is olfactory
dysfunction [61], in which, actually precedes neuropathology
in motor areas such as striatum and substantianigra, the OB is
damaged [62]; in people exposed to high-level of air pollution,
olfaction problems have also been reported [63]. Wild dogs living in
areas of high contamination show enhanced oxidative damage, prepuberty
sporadic maturation, and the significant increase in DNA
damage (apurinic /apyrimidinic sites) in OB, hippocampus (HI)
and frontal cortex. Besides, dogs exposed to a high level of urban
contamination exhibit accumulated metals (vanadium and nickel)
and tissue damage in the target regions of the brain by gradient
method (olfactory mucosa>OB > frontal cortex) and indicate Enter
the nasal route as a key portal [60]. In striking similarity, both
PD and AD share primary pathology in OB, nuclei, and related
pathways, with olfactory deficiency being one of the first findings in
both diseases [64]. This work established the first link between air
pollution exposure and accelerating the pathology of neurological
disease.
Recently, these findings have been extended and confirmed
in animal models and humans. Brain tissue from highly infected
individuals showed increased CD-68, CD-163, and HLA-DR-positive
cells (a marker of infiltrating monocytes or activation of resident
microglia), increased pro-inflammatory markers, increased
deposition of Ab42 (characteristic of AD protein), endothelial
cell activation, BBB, [6] and brain lesions in frontal lobe [65]. The
rearrangement of pro-inflammatory markers such as interleukin-1b
(IL1-b) and cyclooxygenase 2 (COX2) as well as the CD-14 marker
have been localized for innate immune cells in the frontal cortex,
Niger essence, and vagal nerves [6]. In addition, animal studies have
shown that exposure to air pollutants induces cytokine production
[66, 67], increased MAP kinase signaling through JNK [67], lipid
peroxidation, enhanced NFkb expression [66] neurochemical
changes [68], and behavioral alteration [69] Taken together,
these studies show that exposure to air pollutants has effects on
CNS [70]. While there is no survey yet to find a direct effect of air
pollutants on defined levy bodies (a pathological feature of PD) or
beta-amyloid plaques (Ab) (a pathological feature of AD), urban
air pollution exposure causes neurological inflammation [6]. For
example, exposure to high dose of air pollutants in dogs, exhibits
scattered amyloid plaque deposits a decade earlier than their fresh
air exposure counterparts [60, 71].
In addition, accumulation of Ab42 and a-synuclein in early
childhood begins [6] after high level of air pollutant exposure, from
the view that exposure to air pollutants may cause premature aging
in brain and/or stimulate disease progression. One of the plausible
mechanisms is that nanoparticles [72-74] and oxidative stress [75-
77] alter the accumulation and rate of protein fibrosis, potentially
affecting the AB solution and a-synuclein. Changes in protein
accumulation associated with exposure to air pollutants may be
the primary pathology in neurodegenerative processes. Ambient
toxins may exert their effects at various points throughout human
development leading to CNS disease, a theory called the “multiimpact
hypothesis” [78]. According to this assumption, studies
show that PM affects the CNS at an early age [65]. For example, MRI
analysis revealed structural damage (white matter lesions) in the
frontal cortex in children exposed to high levels of air pollutants,
potentially related to cognitive impairment [65]. Interestingly,
air pollution exposure in the same condition in dogs also show
vascular/endothelial pathology and neurogenesis of frontal lesions
[65]. Therefore, the inflammatory effects of air pollution exposure
may be harmful to humans and young animals, and these effects
may accumulate throughout one’s lifetime. Whereas ischemic
stroke [79, 80], multiple sclerosis (exposure to secondhand smoke
increases risk) [81], and PD (airborne manganese content is
associated with increased risk) [82] Currently, only CNS diseases
are epidemiologically based. Many other unexplained diseases are
likely to be air pollution exposed. These risks may be distributed
between individual differences in population sensitivity, as genetic
prediction may be vulnerable to CNS effects of air pollutant
exposure, such as in inherited APOE4 allelic vectors [6] in humans
apoE and knockout mice [83]. Due to the high prevalence of PD
and AD, the association between neurodegeneration and the
pathogenesis of PD/AD, CNS pathology induced by air pollutants
and the high prevalence of air pollution exposure, the expansion of
mechanical studies and epidemiological follow-up is needed.
Air Pollution Exposure and Ischemic Stroke
Human epidemiological studies and animal experimental
surveys in recent years, suggesting that air pollutants may
adversely affect to CNS and cause disease [84-86]. The impact of
urban air pollutants on brain was first reported as an increase in
the ischemic stroke in persons was internal coal smoke exposed.
While it is clear that air pollution exposure can affect human health
through respiratory, cardiovascular, and mortality complications,
recently it has been shown also to have a detrimental effect on the
brain [87, 88]. Whereas data on the association between ambient
air pollution and cerebrovascular disease is limited, various air
pollutants exposure (e.g., carbon monoxide, ozone, nitrogen
dioxide, and particles) is epidemiologically at increased risk. It is
associated with ischemic cerebrovascular events [79, 80, 89-91].
Indeed, current reports indicate that the risk of ischemic stroke is
associated with exposure to air pollutants, even in relatively low
pollutant communities [88, 89, 92]. Ozone and particles rapidly
modulate the expression of genes involved in the major pathways
of cerebrovascular vascularization, while pathological mechanisms
are still unknown [91,93]. Current findings also show that effects
of exposure to air pollutants invade brain parenchyma and cause
pathological signs of neurological disease.
In conclusion, air pollutants are a mixture combination of
ambient toxins that invade the CNS through several molecular and
cellular pathways and cause disease. The effects of CNS are chronic,
start in childhood, and may require time (years) to accumulate
in the pathology. Particularly, exposure to air pollutants causes
neuritis, oxidative stress, brain injury, and neuropathology. Either
way, based on recent findings, the more emission from diesel
engines than mentioned above has created a major concern that
needs to be addressed with further studies into the health effects
of UFPs exposure thus further experimental and epidemiological
surveys of the association between UFPs and CNS disease are of
particular importance.
All authors contributed to the study conception and design. The
first draft of the manuscript was written by Mojtaba Ehsanifar and
also he read and approved the final submitted manuscript.