ArticlePDF Available

Abstract and Figures

The increase in air pollution over the years has had major effects on the human skin. Various air pollutants such as ultraviolet radiation, polycyclic aromatic hydrocarbons, volatile organic compounds, oxides, particulate matter,ozone and cigarette smoke affect the skin as it is the outermost barrier. Air pollutants damage the skin by inducing oxidative stress. Although human skin acts as a biological shield against pro‑oxidative chemicals and physical air pollutants, prolonged or repetitive exposure to high levels of these pollutants may have profound negative effects on the skin. Exposure to ultraviolet radiation has been associated with extrinsic skin aging and skin cancers. Cigarette smoke contributes to premature aging and an increase in the incidence of psoriasis, acne and skin cancers. It is also implicated in allergic skin conditions such as atopic dermatitis and eczema. Polyaromatic hydrocarbons are associated with extrinsic skin aging, pigmentation, cancers and acneiform eruptions. Volatile organic compounds have been associated with atopic dermatitis. Given the increasing levels of air pollution and its detrimental effects on the skin, it is advisable to use strategies to decrease air pollution. Key words: Ozone, particulate matter, pollution, polycyclic aromatic hydrocarbons, skin, ultraviolet radiation, volatile organic compounds
Content may be subject to copyright.
1
© 2017 Indian Journal of Dermatology, Venereology, and Leprology | Published by Wolters Kluwer - Medknow
Effects of air pollution on the skin: A
review
Poonam Puri, Shashi Kumar Nandar1, Sushruta Kathuria, V. Ramesh
Department of Skin and STD, Vardhman Mahavir Medical College, Safdarjung Hospital, 1Department of
Environmental Toxicology Laboratory, National Institute of Pathology‑ICMR, Safdarjung Hospital Campus,
New Delhi, India
Review Arcle
Abstract
The increase in air pollution over the years has had major effects on the human skin. Various air pollutants such
as ultraviolet radiation, polycyclic aromatic hydrocarbons, volatile organic compounds, oxides, particulate matter,
ozone and cigarette smoke affect the skin as it is the outermost barrier. Air pollutants damage the skin by inducing
oxidative stress. Although human skin acts as a biological shield against pro‑oxidative chemicals and physical air
pollutants, prolonged or repetitive exposure to high levels of these pollutants may have profound negative effects on
the skin. Exposure to ultraviolet radiation has been associated with extrinsic skin aging and skin cancers. Cigarette
smoke contributes to premature aging and an increase in the incidence of psoriasis, acne and skin cancers. It is also
implicated in allergic skin conditions such as atopic dermatitis and eczema. Polyaromatic hydrocarbons are associated
with extrinsic skin aging, pigmentation, cancers and acneiform eruptions. Volatile organic compounds have been
associated with atopic dermatitis. Given the increasing levels of air pollution and its detrimental effects on the skin, it
is advisable to use strategies to decrease air pollution.
Key words: Ozone, particulate matter, pollution, polycyclic aromatic hydrocarbons, skin, ultraviolet radiation,
volatile organic compounds
Correspondence:
Dr. Sushruta Kathuria,
Department of Skin and STD,
Vardhman Mahavir Medical
College, Safdarjung Hospital,
New Delhi ‑ 110 029, India.
E‑mail: drsushruta@gmail.com
Introducon
Pollution is dened as contamination of the earth’s environment
with materials which interfere with human health, quality of life,
or the natural functioning of the ecosystem. The major types of
pollution are water pollution, air pollution, noise pollution and soil
pollution. The World Health Organization denes air pollution
as contamination of the indoor or outdoor environment by any
chemical, physical, or biological agent that modies the natural
characteristics of the atmosphere.1 The sources of air pollution
could be natural sources such as volcanic eruptions, forest
res, biological decay, pollen grains, marshes and radioactive
materials or human‑made sources such as thermal power plants,
industries, vehicular emissions, household combustion devices,
fossil fuel burning and agricultural activities. Pollutants of the
major public health concern include particulate matter, carbon
monoxide, ozone, nitrogen dioxide and sulfur dioxide.1 Air
pollution is responsible for a large proportion of health‑related
problems.2
Mechanism of Skin Damage by Air Pollutants
Living organisms are exposed to air pollutants which have major
effects on the human skin. Air pollutants can exist as solids,
liquids, gases and particulate matter. These are absorbed directly
through the skin into the subcutaneous tissue or via hair follicles
and sweat/sebaceous glands. Rapid urbanization and increased
energy consumption worldwide have exposed the human body to
increased quantities of ambient air pollution. The skin, being the
largest and outermost body organ, acts as a physical, chemical and
an immunological barrier against the environmental factors. Human
skin is exposed not only to natural environmental factors but also
to pollutants of anthropic origin.3 Whenever a prolonged and
repetitive exposure to environmental stressors exceeds the skin’s
normal defensive potential, there is a disturbance in the skin barrier
function leading to the development of various skin diseases.3 Major
air pollutants which affect the skin are solar ultraviolet radiation,
polycyclic aromatic hydrocarbons, volatile organic compounds,
How to cite this article: Puri P, Nandar SK, Kathuria S, Ramesh V.
Effects of air pollution on the skin: A review. Indian J Dermatol
Venereol Leprol 0;0:0.
Received: January, 2016. Accepted: June, 2016.
This is an open access article distributed under the terms of the Creative
Commons Attribution‑NonCommercial‑ShareAlike 3.0 License, which allows
others to remix, tweak, and build upon the work non‑commercially, as long as the
author is credited and the new creations are licensed under the identical terms.
For reprints contact: reprints@medknow.com
Access this article online
Quick Response Code: Website:
www.ijdvl.com
DOI:
10.4103/0378-6323.199579
PMID:
*****
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX 2
nitrogen oxides, particulate matter, cigarette smoke, heavy metals
and arsenic.
Air pollutants exert a harmful effect on the skin by increasing
oxidative stress which counters the skin’s antioxidant defenses.
There is a depletion of enzymatic (glutathione peroxidase,
glutathione reductase, superoxide dismutase and catalase) and
non‑enzymatic (Vitamin E, Vitamin C and glutathione) antioxidant
capacity. Free radicals and reactive oxygen species are generated
that interact with the lipid‑rich plasma membrane to initiate the
lipid peroxidation reaction cascade. Reactive oxygen species also
stimulate the release of pro‑inammatory mediators which results
in the accumulation of neutrophils and other phagocytic cells that
further generate free radicals, thereby resulting in a vicious cycle.
Oxidative stress initiates complex biological processes resulting in
genetic damage, activation of transcription factors such as activator
protein 1 and nuclear factor kappa B, and signalling pathways such
as extracellular signal‑regulated kinases, c‑Jun N‑terminal kinases
and p38 mitogen‑activated protein kinases, involved in cell growth
and differentiation and in the degradation of the connective tissue
of the dermis. Air pollutants induce severe alterations of the normal
functions of lipids, deoxyribonucleic acid and/or proteins in the
human skin via oxidative damage, leading to extrinsic skin aging,
inammatory or allergic conditions such as contact dermatitis,
atopic dermatitis, psoriasis, acne and skin cancer.4,6‑8
Air Quality Guidelines
The World Health Organization air quality guidelines are based on
four major air pollutants, namely particulate matter, ground‑level
ozone, nitrogen dioxide and sulfur dioxide.1 The World Health
Organization guidelines for the various air pollutants are shown in
Table 1. The Revised National Ambient Air Quality Standards, 2009,
are also shown in Table 1.9 Another measure for air pollution is air
quality index based on ve major air pollutants regulated by the Clean
Air Act:‑ ground‑level ozone, particulate matter, carbon monoxide,
sulfur dioxide and nitrogen dioxide. Its value lies between 1 and 500,
with higher values indicating more air pollution. Air quality index
value of 50 represents a good air quality with some potential to affect
public health, while an air quality index value over 300 represents
hazardous air quality. Real‑time records of air quality index in
New Delhi show that it is between 150 and 170, which is categorized
as unhealthy.10 This article focuses on the detrimental effects of air
pollutants on various skin disorders.
Air Pollutants and their Role in Skin Diseases
Ultraviolet radiation
Ultraviolet radiation is a physical pollutant. The solar spectrum
consists of ultraviolet A (320–400 nm), ultraviolet B (290–320 nm)
and ultraviolet C (200–290 nm). More than 95% of ultraviolet
A and 1–5% of ultraviolet B reach the Earth’s surface, whereas
most ultraviolet C is absorbed by the ozone layer and oxygen
in the atmosphere.11 The depletion of stratospheric ozone by
environmental pollutants such as photochemical smog, supersonic
aircraft ights and refrigerant gases increases the penetration
of the shorter ultraviolet wavelengths to the ground level. The
effects of ultraviolet radiation on human skin differ depending on
the wavelength. Ultraviolet A exposure results in extrinsic skin
aging (photoaging) characterized by coarse wrinkles, solar elastosis
and pigment irregularities. Aging results from the combined action
of intrinsic and extrinsic factors. The general aging process which
is genetically determined and occurs in all skin by passing time is
called intrinsic aging [Figures 1 and 2] whereas skin aging induced
by environmental factors is termed as extrinsic aging. Clinical
signs of extrinsic aging include solar elastosis [Figure 3], pigment
spots [Figure 4], coarse wrinkles and telangiectasias. The differences
between intrinsic and extrinsic aging are tabulated in Table 2.12‑15
Photoaging is mainly caused by ultraviolet A. In an in vitro study,
it was seen that ultraviolet B may also contribute to photoaging
by increasing stratin. Stratin is a member of the 14‑3‑3 protein
family, secreted by keratinocytes and its expression was more in
skin exposed to ultraviolet B than in skin protected by ultraviolet
B.16 The mechanism of premature/extrinsic skin aging induced by
ultraviolet rays is a complex process, which is triggered by various
pathways, namely activation of receptors, mitochondrial damage,
protein oxidation, alteration of Ca2+ levels, telomere damage and
arylhydrocarbon receptor activation. The stimulation of receptor
pathway is induced by the generation of reactive oxygen species
on exposure to ultraviolet radiation, smoking and air pollutants. As
a result, the cell surface receptors of cytokines and growth factors
in keratinocytes as well as broblasts are activated which leads to
the intracellular stimulation of intracellular kinases, inducing the
transcription of nuclear transcription factor activator protein 1 and
nuclear factor kappa B. Increased activator protein 1 transcription
decreases the gene expression of the major dermal collagens I and III
in broblasts leading to a reduction in collagen synthesis. Activator
protein 1 also increases the synthesis of matrix metalloproteinases in
keratinocytes and broblasts resulting in the increased degradation
of mature dermal collagen. On the other hand, nuclear factor kappa
B stimulates the transcription of inammatory cytokines resulting
in the accumulation of neutrophils. The collagenases in neutrophils
help in collagen degradation.
Ultraviolet B alone is responsible for sunburn. Ultraviolet A and B
both have been implicated in cutaneous immunosuppression and
skin cancers (photocarcinogenesis) such as malignant melanoma,
basal cell carcinoma and squamous cell carcinoma.3,7,17 There is
a growing concern worldwide regarding the increased incidence
of skin cancer. Excessive exposure to sunlight and tanning
Table 1: Guidelines for limit of air pollutants1
Air pollutant Maximum limit (WHO,2006) Revised National Ambient air quality
standards (2009)
Particulate matter having size
between 2.5 and 10 μm
Mean value of 20 μg/m3 over a year or 50 μg/m3
over 24 h
Mean value of 60 μg/m3 over a year or 100 μg/m3
over 24 h
Ozone at ground level Mean value of 100 μg/m3 over 8 h Mean value of 100 μg/m3 over 8 h
Nitrogen dioxide Mean value of 0 μg/m3 over a year or 200 μg/m3
over 1 h
Mean value of 40 μg/m3 over a year or 80 μg/m3
over 24 h
Sulfur dioxide Mean value of 20 μg/m3 over 24 h or 500 μg/m3
over 10 min
Mean value of 50 μg/m3 over a year or 80 μg/m3
over 24 h
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
3Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX
lamps is responsible for cumulative damage, which induces
immunosuppression responsible for skin cancer.18 Fair‑skinned
people are more susceptible than dark‑skinned individuals.
Australia has the world’s highest rate of skin cancer which is due to
high sunshine levels. Depletion of ozone increases the penetration
of ultraviolet rays to the earth’s surface, leading to an increase in
incidence of skin cancers, and a decrease in their age of onset.19,20
Ultraviolet A and B damage deoxyribonucleic acid through
different mechanisms. Melanocytes in the basal layer of epidermis
produce the pigment melanin, which protects the neighbouring
keratinocytes from ultraviolet radiation. However, prolonged
exposure to sunlight can induce carcinogenesis. Ultraviolet A
and B are absorbed by proteins, lipids, nuclear and mitochondrial
deoxyribonucleic acid, causing a cascade of oxidative events
Figure 1: Intrinsic aging. Sagging and lax skin with deep wrinkles in a
63‑year‑old woman
Figure 2: Intrinsic aging. Fine wrinkles in a 45‑year‑old woman
Figure 3: Extrinsic aging. Solar elastosis in a 40‑year‑old woman living in
hilly region
Figure 4: Extrinsic aging. Freckles in a 55‑year‑old woman
Table 2: Differences between intrinsic and extrinsic (photoaging)12-15
Intrinsic aging Extrinsic (photoaging)
Texture of skin Dry, pale with certain degree of laxity Very dry, atrophic, sallow, very lax
Sagging of skin More prominent Less prominent14
Wrinkles Fine wrinkles In addition, coarse wrinkles forming deep
furrows (pathognomic)
Hyperpigmentation Some freckles Lot of irregularly pigmented freckles, heterogeneity of
pigmentation (specic for photoaging)
Other features Benign neoplasms Premalignant lesions, actinic keratoses, telangiectasias
Histology (epidermis) Flattening of the dermal‑epidermal junction, decrease in
melanocyte and Langerhans cell density
Variable epidermal thickness, some cytologic atypia,
uneven distribution of melanocytes, signicant decrease in
Langerhans cells
Histology (dermis) Loss of extracellular matrix, increased levels of
collagen‑degrading metalloproteinases, loss of broblasts and
vascular network, and, in particular, loss of the capillary loops
that occupy the dermal papillae
Dermal elastosis (deposition of abnormal amorphous elastic
material in the papillary dermis), abundant inammatory
cells in the dermis, and degenerative changes in collagen
and elastic bers
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX 4
which results in the deterioration of structure and function of cells.
Ultraviolet A causes mutation of tumor suppressor p53 gene in the
basal layer which has stem cells, and thus leads to carcinogenesis,
which is due to deoxyribonucleic acid damage, gene mutation and
immune suppression.
Ultraviolet A in combination with common environmental
pollutants, such as polycyclic aromatic hydrocarbons, signicantly
increases visible photodamage in the skin.21 Ultraviolet A in
combination with ozone causes synergistic oxidative stress in
human skin.22 Some air pollutants (ozone, nitrogen dioxide and
sulfur dioxide) and scattering particulates (clouds and soot) in the
troposphere reduce the effects of shorter wavelength ultraviolet
radiation, mainly ultraviolet B, and cause signicant reduction in
ultraviolet B irradiance in polluted urban areas. There is a reduction
of more than 50% in ultraviolet radiation (mainly ultraviolet B)
on days with high levels of air pollution. An inverse relationship
exists between the total ozone content and ground levels of
ultraviolet B radiation. Ultraviolet A, however, is not affected
much in the presence of air pollutants and ozone. Therefore, the
ratio of ultraviolet B/ultraviolet A is highly dependent on factors
such as thickness of ozone layer and air pollution.23
Cigarette smoke
Cigarette smoke is a highly complex aerosol composed of
thousands of chemical substances, including reactive oxygen
species, carbon monoxide, reactive nitrogen species and
electrophilic aldehydes.3 Reactive oxidants and free radicals from
cigarette smoke cause oxidative stress or secondary oxidative
events and inhibition of antioxidant mechanisms.24‑26 Chemical
substances from cigarette smoke increase transepidermal water
loss, degeneration of connective tissue in the skin and upregulation
of matrix metalloproteinases‑1 and 3 which degrade collagen and
elastic bers.3,27,28
Smoking causes premature aging which clinically manifests as
deeper periorbital wrinkling.29‑31 Premature facial skin aging in
smokers, with a characteristic pattern of wrinkling and orange‑purple
skin discoloration, was dened as smoker ’s face.32 Smoker’s face
typically has lines or wrinkles radiating at the right angles from the
upper and lower lips or corners of the eyes, deep lines on the cheeks,
or numerous shallow lines on the cheeks and lower jaw. The bony
contours become prominent, and the skin is slightly pigmented gray
with orange, purple and red complexion. Heavy cigarette smokers
were 4.7 times more likely to have facial wrinkles than nonsmokers,
independent of sun exposure, although the combination of smoking
and sun exposure may have a synergistic effect.31‑33 It has been
observed that wrinkling in a 40‑year‑old smoker resembles that
of a 70‑year‑old nonsmoker.34 Sometimes, large open and closed
comedones with furrows (smoker’s comedones) [Figure 5] are seen
in the periorbital area, similar to those seen in Favre–Racouchot
syndrome. There is yellow discoloration of nails, and in persons
who have stopped smoking, a sharp demarcation line may be seen
between the yellow nail plate and the newly formed pink nail
plate (known as Harlequin nail or quitter’s nail). Other changes
noticed in smokers include yellowish discoloration of the hair and
beard (e.g. smoker’s moustache), premature graying and loss of
hair, gingival pigmentation (smoker’s melanosis), leukoplakia of
the tongue (smoker’s tongue), oral leukoplakia [Figure 6] and a
gray‑white keratinized palate with multiple red umbilicated papules
that represent inamed salivary glands (smoker’s palate/nicotine
stomatitis).35 Various mechanisms have been postulated for
premature aging caused by cigarette smoke. In mice models,
second‑hand smoke, also known as environmental tobacco smoke,
involuntary smoke and passive smoke caused premature aging
by increased cytoplasmic translocation of high‑mobility group
box 1 protein, and hence, the loss of collagen.36 Transcription of
p16INK4a has been associated with aging, and p16INK4a is a known
gerontogen. In murine models, cigarette smoke and ultraviolet light
have augmented the transcription of p16INK4a.37 Cigarette smoke
extract caused senescence of broblasts, possibly by oxidative
stress injury and inhibition of antioxidant defense activity in in vitro
studies.38 Cigarette smoke‑induced early growth response‑1 induces
the expression of cysteine‑rich 61 in human skin dermal broblasts
which may be the cause of premature aging.39
An association between cigarette smoke and psoriasis has been
reported in several epidemiologic studies. In a Norwegian
cross‑sectional study, male smokers had a signicantly increased
risk of developing psoriasis.40 A meta‑analysis suggested that there
is a signicant association between smoking and psoriasis with a
relative risk of 1.88 for smoking in patients with psoriasis versus
patients without psoriasis.41 In addition, there is a dose‑dependent
relationship between the development of psoriasis and the number
of cigarettes smoked. A population‑based twin study showed
that childhood exposure to environmental tobacco smoke was
signicantly associated with psoriasis in the whole population, with
an odds ratio of 1.28. Smokers with a history of >5 pack‑years of
cigarette had an increased risk of psoriasis with an odds ratio of
2.18. The same study showed that genetic factors could explain only
20% of the correlation between psoriasis and smoking, whereas
non‑shared environmental factors explained even less at 8 percent.42
Several single nucleotide polymorphisms located in the CHRNA5/
A3/B4 gene cluster have been linked to smoking behaviour
and nicotine dependence, but these known single nucleotide
polymorphisms were not found to be linked with psoriasis incidence
or severity in the Chinese population.43 The effect of smoking could
be mediated by the reactive oxygen species and by the imbalance
between oxidants and antioxidants indicated by low levels of
Figure 5: Smokers comedones. Comedones in periorbital area and ne
wrinkles in a 35‑year‑old man
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
5Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX
vitamin C and glutathione, and high levels of superoxide dismutase
and malonaldehyde.3,44
Schäfer et al. reported a high prevalence of acne among smokers and
described a correlation between the acne severity and the number of
smoked cigarettes in post adolescent women, where predominantly
comedonal acne was seen compared to the papulopustular form.45
The authors reported that although the correlation between acne and
smoking is still controversial, there is a hyperkeratinizing effect of
cigarette smoke compounds, and in particular, of nicotine. Nicotine,
an agonist of acetylcholine present in the cigarette, induces
comedogenesis via the stimulation of acetylcholine‑nicotinic
receptor on epidermal keratinocytes.46
A meta‑analysis done in 2010 shows that tobacco smoking is associated
with cutaneous squamous cell carcinoma with an odds ratio of 1.52
while the association between smoking and basal cell carcinoma
and other nonmelanoma skin cancers is controversial.3,25,47‑50 In mice
models, 4‑(methylnitrosoamino)‑1‑(3‑pyridyl)‑1‑butanone acted as
tumor initiator causing skin cancer and lung adenomas.19
Interestingly, many case series and case‑control studies report
that smoking is associated with a lower prevalence of aphthous
ulcers, Behcet’s disease, herpes labialis, Kaposi’s sarcoma (in
acquired immune deciency syndrome) and pemphigus vulgaris.49
The various skin diseases aggravated by smoking are tabulated in
Table 3.
Polycyclic aromatic hydrocarbons
Polycyclic aromatic hydrocarbons are among the most widespread
and dangerous organic pollutants.20 Polycyclic aromatic
hydrocarbons are absorbed on the surface of suspended particulate
matter in the air in urban areas.51 They are converted into quinines,
redox‑cycling chemicals that produce reactive oxygen species.52
Irrespective of the route of entry in the human body, they are
found in almost all the internal organs, especially in the lungs and
digestive tract. The main source of atmospheric polycyclic aromatic
hydrocarbon benzo(a) pyrene is residual wood burning, the other
sources being automobile exhaust, diesel fumes, metallurgical
industry, production of plastics, pesticides, dyes, cigarette smoke
and smoke resulting from the combustion of organic material.21
Polycyclic aromatic hydrocarbons are associated with extrinsic skin
aging, pigmentation, cancers and acneiform eruption. Melanocyte
proliferation and skin pigmentation have been observed in mice.53
Scrotal cell carcinoma due to coal soot in British chimney sweeps
was reported in 1775, and polycyclic aromatic hydrocarbon was the
carcinogen responsible for it. Coal soot is more carcinogenic than
wood soot as it contains a higher amount of polycyclic aromatic
hydrocarbons. Among polycyclic aromatic hydrocarbons, benzo(a)
pyrene has been shown to cause nonmelanoma cancers whereas
7,12‑dimethylbenz(a) anthracene is capable of inducing lymphoma
in hamsters. Ultraviolet A enhances the carcinogenic action of
benzo(a) pyrene.54 However, Sowada et al. have demonstrated that
resident skin ora, predominantly micrococci, can degrade benzo(a)
pyrene, thus forming an innate mechanism of defense against
polycyclic aromatic hydrocarbons.55,56
Epoxides and diols produced by activated polycyclic
aromatic hydrocarbons bind to deoxyribonucleic acid, leading
to carcinogenesis.7,54 Polycyclic aromatic hydrocarbons
can lead to acneiform eruptions due to the presence of
2,3,7,8‑tetrachlorodibenzo‑p‑dioxin which is a polyhalogenated
aromatic hydrocarbon.7 It is formed in any burning, waste
incineration, metal production and fossil‑fuel and wood combustion.
Sorg et al. described chloracne in Viktor Yushchenko’s poisoning
with 2,3,7,8‑tetrachlorodibenzo‑p‑dioxin in 2005.57 Chloracne is
Figure 6: Oral leukokeratosis in a smoker
Table 3: Skin diseases aggravated by cigarette smoke
Commonly associated skin changes
Premature skin aging
Hyperpigmentation of oral mucosa
Submucous brosis
Yellowish discoloration of nails
Smokers comedones
Skin diseases with denite evidence of aggravation with smoking
Cutaneous squamous cell carcinoma
Hidradenitis suppurativa
Systemic lupus erythematosus
Oral cancers
Palmoplantar pustulosis
Psoriasis
Skin diseases with conicting evidence of aggravation with smoking
Basal cell carcinoma
Discoid lupus erythematosus
Acne
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX 6
a systemic toxic disease caused by the exposure to halogenated
aromatic hydrocarbons. It is characterized by comedones and cysts
mainly on the face (outer sides of the eye and behind the ears)
and neck. Other manifestations of chloracne include fatigue, liver
dysfunction, neuropathy and arthritis.58
Ground‑level ozone
Ozone is a ubiquitous pollutant in the urban environment. Its
concentrations in urban environment can range from 0.2 to 1.2 ppm.59
Mexico City has the highest ozone levels in the world. It is a gaseous
oxidant that exists in the stratosphere and troposphere.70,50 Normally,
the concentrations of ozone at ground‑level are low. Ozone, after
interaction with sunlight (ultraviolet radiation), hydrocarbons,
volatile organic compounds and nitrogen oxides, forms a major
active component of the photochemical smog.7,50
The effect of ozone is mediated by its ability to induce oxidative
stress. It leads to the formation of peroxides, aldehydes and lipid
ozonation products, as a result of unsaturated fatty acid oxidation
and damages the barrier function of epidermis. Thiele et al.
reported that ozone causes a reduction in the level of antioxidants
such as tocopherol (vitamin E) and ascorbic acid (vitamin C) and
increases malondialdehyde, a lipid peroxidation product in murine
skin causing impairment of barrier function and inammation.22,60
In human skin, exposure to ozone caused a 70% decrease in
vitamin E concentration in stratum corneum, and 50% reduction
in skin microora.61 Ozone causes disturbed activity of matrix
metalloproteinases. Ozone‑induced inammation is mainly
mediated through redox‑sensitive transcription factor, nuclear factor
kappa B. In an in vitro study, cells exposed to ozone demonstrated
a dose‑dependent increase in p65 subunit nuclear expression as a
marker of nuclear factor kappa B activation, while pretreatment with
vitamin C mixtures which acted as antioxidants abolished nuclear
factor kappa B nuclear translocation. In addition, a signicant
activation of Nrf2 was observed in keratinocytes treated with the
mixtures.62 Nrf2 is a basic leucine zipper protein that regulates the
expression of antioxidant proteins that protect against oxidative
damage triggered by injury and inammation.
Ozone along with ultraviolet A rays and cigarette smoke is a powerful
oxidizing agent of squalene. Oxidation of squalene produces
squalene by‑products, mostly peroxidized forms, which lead to
comedogenesis, thus aggravating inammatory acne. Oxidation of
epidermal lipids and disturbed activity of matrix metalloproteinases
contribute to wrinkling and extrinsic skin aging.63 Tropospheric
ozone exposure has been associated with urticaria, eczema, contact
dermatitis, rashes and infected skin disease.64
Particulate matter
Particulate matter in the air consists of complex and varying
mixtures of different size and composition. Factories, power plants,
refuse incinerators, automobile, construction activities, res and
natural windblown dust are some of the main sources of particulate
matter.65,66
Particulate matter penetrates skin either through hair follicles
or transdermally, and exerts its detrimental effects through the
generation of oxidative stress, which contributes to extrinsic skin
aging, characterized particularly by pigment spots on the face and
nasolabial folds, and less so by coarse wrinkles, solar elastosis
and telangiectasia.67‑69 The most harmful components of ambient
particulate matter are nanosize particles from trafc sources; these
particles can serve as carriers for organic chemicals and metals that
are capable of localizing in mitochondria and generating reactive
oxygen species. It has been noted that an increase in soot (per
0.5 × 10−5/m) and particles from trafc (per 475 kg per year and
square km) was associated with 20% more pigment spots on the
forehead and cheeks. Polycyclic aromatic hydrocarbons are adsorbed
on the surface of suspended particulate matter in air of urban
areas.68 Polycyclic aromatic hydrocarbons can activate xenobiotic
metabolism which converts polycyclic aromatic hydrocarbons to
quinones. Quinones are redox‑cycling chemicals which produce
reactive oxygen species responsible for particulate matter toxicity.52
Although many cohort studies report that there is no association
between air pollutants and incidence and prevalence of atopic
dermatitis, the severity of symptoms of atopic dermatitis may have
a direct association with increased particulate matter.70 Kim et al.
also report that with indoor air quality improvement program, the
level of particulate matter decreased and there was a signicant
decrease in the prevalence and severity of atopic dermatitis.71 The
exact mechanism is unclear, but it is proposed that particulate matter
may induce inammation in the skin in a similar fashion as that in
the respiratory system.70
Volatile organic compounds
Emission of volatile organic compounds occurs from the use of
organic solvents in paints, varnishes (aliphatic hydrocarbons, ethyl
acetate, glycol ethers, methylene chloride and acetone) vehicle
renishing products in repairing car paint, environmental tobacco
smoke, stored fuels, exhaust from cars (benzene) and from emissions
from industrial facilities (tetrachloroethylene).6,72,73 It is an important
indoor source of air pollutants. A longitudinal study has shown
that symptoms of atopic dermatitis increase in children shifted to
a new building due to an increase in exposure to volatile organic
compounds.74 Volatile organic compounds along with sunlight and
nitrogen oxides form photochemical oxidant products such as ozone
at ground level which is the summer photochemical smog. Volatile
organic compounds (ingestion of hexachlorobenzene) may induce
precancerous skin lesions in rats.75 Exposure to volatile organic
compounds increases cytokines (interleukin‑8 and interleukin‑1B)
in cultured keratinocytes which cause atopic dermatitis or eczema.
Oxides
Nitrogen oxides are emitted mainly from mobile and stationary
combustion sources. They react with ozone‑forming nitrogen
dioxide. Among nitrogen oxides, nitrogen dioxide causes oxidative
damage leading to the formation of free radicals that oxidize
amino acids in tissue proteins and initiate lipid peroxidation of
polyunsaturated fatty acids.76
Atmospheric sulfur dioxide is formed from fuel combustion from
industrial processes, volcanic activity and forest res. Carbon
monoxide, a product of incomplete combustion from mobile
sources, acts on cell metabolism which binds to heme and alters
its function.6 Flexural eczema was associated with trafc‑related
air pollutants, including nitrogen oxides and carbon monoxide in
Taiwan in middle‑school children. A study comparing atopic eczema
in East and West Germany showed that the prevalence was higher
in East Germany (sulfurous type pollution) and also exhibited a
stronger association with nitrogen oxides and close proximity to
heavy trafc.77
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
7Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX
Heavy metals
Cadmium, lead and mercury are common air pollutants that pose
health hazards. The main sources are volcanoes, waste incineration,
cement, iron and steel production and leaded gasoline.56
Prevenon Strategies
Control of air pollution is necessary to improve the health conditions.
There are two steps in the prevention of dermatological diseases due
to air pollution: the rst is to reduce air pollution and the second
is to use strategies to protect oneself from pollutants. In Korea,
indoor air quality improvement program was conducted in nine
kindergarten classes, following which mean particulate matter 10
levels decreased signicantly from 182.7 to 73.4 µg/m3. Along with
that, the prevalence, severity of atopic dermatitis in children and
the number of hospital visits per month also decreased signicantly,
thus showing the benet of improvement of air quality.71 The Health
Event project in Europe for the improvement of indoor air quality
is based on three components, namely optimizing ventilation rates,
ltration of outdoor air and indoor source control.78 This project has
shown an improvement in different cardiovascular and respiratory
diseases. Such strategies should be studied for dermatological
diseases too.
Control of air pollution
The natural sources of pollution are difcult to predict and prevent
such as volcano eruptions or forest res. However, human‑made
sources can be controlled. Some strategies include less use of
personal vehicles, increase in the use of car pools and public modes
of transport, supply of low‑sulphur petrol, shifting of industries to
areas away from the cities, development and usage of industrial
machines and methods which are eco‑friendly, avoiding burning
of garbage in the open, avoidance of smoking and no use of wood
and crop residues as fuel for the purpose of household cooking and
heating. Various methods have been tried to reduce trafc induced
pollution. For example, in New Delhi, biofriendly fuels such as
compressed natural gas is used by all public transport vehicles,
odd‑even formula for private vehicles has been implemented and
old diesel vehicles are gradually being phased out.
Personal protection
Strategies for personal protection include physical photoprotection;
use of sunscreens; avoidance of areas with public smoking, and
around industries; usage of topical antioxidants such as vitamin
C and E in formulations along with sunscreen; and of indoor air
puriers and ventilators. People with high occupational risk, such as
trafc police and sweepers, should use masks while at work.
Conclusions
Skin is the largest organ of human body, and any factor affecting skin
health will impact the body as a whole. Major air pollutants having
detrimental effects on the skin include solar ultraviolet radiation,
polycyclic aromatic hydrocarbons, volatile organic compounds,
nitrogen oxides, particulate matter, ozone and cigarette smoke.
Sunlight, cigarette smoke and ambient particulate matter have a role
to play in extrinsic skin aging. Smoking has also been associated
with skin cancer, psoriasis, acne and skin malignancy. Exposure to
ozone has been associated with urticaria, eczema, contact dermatitis
and other nonspecic eruptions. Polyaromatic hydrocarbons cause
skin cancer, extrinsic skin aging, pigmentation and acneiform
eruptions. Oxides have been associated with increased prevalence,
as well as exacerbations of atopic dermatitis in children.
Financial support and sponsorship
Nil.
Conicts of interest
There are no conicts of interest.
References
1. WHO Air Quality Guidelines for Particulate Matter, Ozone, Nitrogen
Dioxide and Sulfur Dioxide, Global Update 2005, Summary of
Risk Assessment; 2006. Available from: http://www.who.int/phe/
health_topics/outdoorair/outdoorair_aqg/en/. [Last accessed on 2016
Apr 04].
2. Rizwan S, Nongkynrih B, Gupta SK. “Air pollution in Delhi:
Its magnitude and effects on health”. Indian J Community Med
2013;38:4‑8.
3. Valacchi G, Sticozzi C, Pecorelli A, Cervellati F, Cervellati C, Maioli E.
Cutaneous responses to environmental stressors. Ann N Y Acad Sci
2012;1271:75‑81.
4. Halliwell B, Cross CE. Oxygen‑derived species: Their relation to
human disease and environmental stress. Environ Health Perspect
1994;102 Suppl 10:5‑12.
5. Jomova K, Jenisova Z, Feszterova M, Baros S, Liska J, Hudecova D,
et al. Arsenic: Toxicity, oxidative stress and human disease. J Appl
Toxicol 2011;31:95‑107.
6. Kampa M, Castanas E. Human health effects of air pollution. Environ
Pollut 2008;151:362‑7.
7. Baudouin C, Charveron M, Tarroux R, Gall Y. Environmental pollutants
and skin cancer. Cell Biol Toxicol 2002;18:341‑8.
8. Kohen R, Gati I. Skin low molecular weight antioxidants and their role
in aging and in oxidative stress. Toxicology 2000;148:149‑57.
9. National Ambient Air Quality Standards by Central Pollution Control
Board 2009, New Delhi; 2009. Available from: http://www.envfor.nic.
in/division/air‑pollution. [Last accessed on 2016 Apr 04].
10. Air Pollution in India, Real‑time Air Quality Index. Available from:
http://www.aqicn.org/map/india/. [Last accessed on 2016 Apr 04].
11. Dessinioti C, Antoniou C, Katsambas A, Stratigos AJ. Basal cell
carcinoma: What’s new under the sun. Photochem Photobiol
2010;86:481‑91.
12. Yaar M, Gilchrest BA. Skin aging: Postulated mechanisms and
consequent changes in structure and function. Clin Geriatr Med
2001;17:617‑30, v.
13. Gilchrest BA, Murphy GF, Soter NA. Effect of chronologic aging and
ultraviolet irradiation on Langerhans cells in human epidermis. J Invest
Dermatol 1982;79:85‑8.
14. Gilchrest BA, Stoff JS, Soter NA. Chronologic aging alters the response
to ultraviolet‑induced inammation in human skin. J Invest Dermatol
1982;79:11‑5.
15. Flament F, Bazin R, Laquieze S, Rubert V, Simonpietri E, Piot B. Effect
of the sun on visible clinical signs of aging in Caucasian skin. Clin
Cosmet Investig Dermatol 2013;6:221‑32.
16. Adachi H, Murakami Y, Tanaka H, Nakata S. Increase of stratin
triggered by ultraviolet irradiation is possibly related to premature
aging of human skin. Exp Dermatol 2014;23 Suppl 1:32‑6.
17. Aubin F. Mechanisms involved in ultraviolet light‑induced
immunosuppression. Eur J Dermatol 2003;13:515‑23.
18. Fabbrocini G, Triassi M, Mauriello MC, Torre G, Annunziata MC,
De Vita V, et al. Epidemiology of skin cancer: Role of some
environmental factors. Cancers (Basel) 2010;2:1980‑9.
19. Abarca JF, Casiccia CC. Skin cancer and ultraviolet‑B radiation under
the Antarctic ozone hole: Southern Chile, 1987‑2000. Photodermatol
Photoimmunol Photomed 2002;18:294‑302.
20. English JS, Dawe RS, Ferguson J. Environmental effects and skin
disease. Br Med Bull 2003;68:129‑42.
21. Burke KE, Wei H. Synergistic damage by UVA radiation and pollutants.
Toxicol Ind Health 2009;25:219‑24.
22. Thiele JJ, Podda M, Packer L. Tropospheric ozone: An emerging
environmental stress to skin. Biol Chem 1997;378:1299‑305.
23. Sabziparvar AA, Shine KP, Forster PM. A model‑derived global
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX 8
climatology of UV irradiation at the earth’s surface. Photochem
Photobiol 1999;69:193‑202.
24. Chow CK. Cigarette smoking and oxidative damage in the lung. Ann N
Y Acad Sci 1993;686:289‑98.
25. Boyd AS, Shyr Y, King LE Jr. Basal cell carcinoma in young women:
An evaluation of the association of tanning bed use and smoking. J Am
Acad Dermatol 2002;46:706‑9.
26. Dietrich M, Block G, Norkus EP, Hudes M, Traber MG, Cross CE,
et al. Smoking and exposure to environmental tobacco smoke decrease
some plasma antioxidants and increase gamma‑tocopherol in vivo
after adjustment for dietary antioxidant intakes. Am J Clin Nutr
2003;77:160‑6.
27. Jorgensen LN, Kallehave F, Christensen E, Siana JE, Gottrup F. Less
collagen production in smokers. Surgery 1998;123:450‑5.
28. Just M, Ribera M, Monsó E, Lorenzo JC, Ferrándiz C. Effect of smoking
on skin elastic bres: Morphometric and immunohistochemical
analysis. Br J Dermatol 2007;156:85‑91.
29. Solly S. Clincial lectures on paralysis. Lancet 1856;68:641‑3.
30. Daniell HW. Smoker’s wrinkles. A study in the epidemiology of
“crow’s feet”. Ann Intern Med 1971;75:873‑80.
31. Freiman A, Bird G, Metelitsa AI, Barankin B, Lauzon GJ. Cutaneous
effects of smoking. J Cutan Med Surg 2004;8:415‑23.
32. O’Hare PM, Fleischer AB Jr., D’Agostino RB Jr., Feldman SR,
Hinds MA, Rassette SA, et al. Tobacco smoking contributes little to
facial wrinkling. J Eur Acad Dermatol Venereol 1999;12:133‑9.
33. Kadunce DP, Burr R, Gress R, Kanner R, Lyon JL, Zone JJ. Cigarette
smoking: Risk factor for premature facial wrinkling. Ann Intern Med
1991;114:840‑4.
34. Urbanska M, Nowak G, Florek E. Cigarette smoking and its inuence
on skin aging. Przegl Lek 2012;69:1111‑4.
35. Thomsen SF, Sørensen LT. Smoking and skin disease. Skin Therapy
Lett 2010;15:4‑7.
36. Chaichalotornkul S, Nararatwanchai T, Narkpinit S, Dararat P,
Kikuchi K, Maruyama I, et al. Secondhand smoke exposure‑induced
nucleocytoplasmic shuttling of HMGB1 in a rat premature skin aging
model. Biochem Biophys Res Commun 2015;456:92‑7.
37. Sorrentino JA, Krishnamurthy J, Tilley S, Alb JG Jr., Burd CE,
Sharpless NE. p16INK4a reporter mice reveal age‑promoting effects of
environmental toxicants. J Clin Invest 2014;124:169‑73.
38. Yang GY, Zhang CL, Liu XC, Qian G, Deng DQ. Effects of cigarette
smoke extracts on the growth and senescence of skin broblasts
in vitro. Int J Biol Sci 2013;9:613‑23.
39. Kim JN, Kim HJ, Jeong SH, Kye YC, Son SW. Cigarette smoke‑induced
early growth response‑1 regulates the expression of the cysteine‑rich
61 in human skin dermal broblasts. Exp Dermatol 2011;20:992‑7.
40. Bø K, Thoresen M, Dalgard F. Smokers report more psoriasis, but not
atopic dermatitis or hand eczema: Results from a Norwegian population
survey among adults. Dermatology 2008;216:40‑5.
41. Richer V, Roubille C, Fleming P, Starnino T, McCourt C, McFarlane A,
et al. Psoriasis and smoking: A systematic literature review and
meta‑analysis with qualitative analysis of effect of smoking on psoriasis
severity. J Cutan Med Surg 2016;20:221‑7.
42. Lønnberg AS, Skov L, Skytthe A, Kyvik KO, Pedersen OB,
Thomsen SF. Smoking and risk for psoriasis: A population‑based twin
study. Int J Dermatol 2016;55:e72‑8.
43. Zhu KJ, Liu Z, Liu H, Li SJ, Zhu CY, Li KS, et al. An association study
on the CHRNA5/A3/B4 gene cluster, smoking and psoriasis vulgaris.
Arch Dermatol Res 2014;306:939‑44.
44. Isik B, Ceylan A, Isik R. Oxidative stress in smokers and non‑smokers.
Inhal Toxicol 2007;19:767‑9.
45. Schäfer T, Nienhaus A, Vieluf D, Berger J, Ring J. Epidemiology of
acne in the general population: The risk of smoking. Br J Dermatol
2001;145:100‑4.
46. Capitanio B, Sinagra JL, Bordignon V, Cordiali Fei P, Picardo M,
Zouboulis CC. Underestimated clinical features of postadolescent
acne. J Am Acad Dermatol 2010;63:782‑8.
47. El‑Hakim IE, Uthman MA. Squamous cell carcinoma and
keratoacanthoma of the lower lip associated with “Goza” and “Shisha”
smoking. Int J Dermatol 1999;38:108‑10.
48. Leonardi‑Bee J, Ellison T, Bath‑Hextall F. Smoking and the risk of
nonmelanoma skin cancer: Systematic review and meta‑analysis. Arch
Dermatol 2012;148:939‑46.
49. McBride P, Olsen CM, Green AC. Tobacco smoking and cutaneous
squamous cell carcinoma: A 16‑year longitudinal population‑based
study. Cancer Epidemiol Biomarkers Prev 2011;20:1778‑83.
50. Madronich S, Wagner M, Groth P. Inuence of tropospheric ozone
control on exposure to ultraviolet radiation at the surface. Environ Sci
Technol 2011;45:6919‑23.
51. Menichini E. Urban air pollution by polycyclic aromatic hydrocarbons:
Levels and sources of variability. Sci Total Environ 1992;116:109‑35.
52. Penning TM. Dihydrodiol dehydrogenase and its role in
polycyclic aromatic hydrocarbon metabolism. Chem Biol Interact
1993;89:1‑34.
53. Krutmann J, Jux B, Luecke S, Fritsche E, Abel J, Essel C, Rannug A.
Involvement of arylhydrocarbon receptor (AhR‑) signaling in skin
melanogenesis. J Invest Dermatol 2008;128:S220.
54. Kelfkens G, de Gruijl FR, van der Leun JC. Tumorigenesis by
short‑wave ultraviolet A: Papillomas versus squamous cell carcinomas.
Carcinogenesis 1991;12:1377‑82.
55. Sowada J, Schmalenberger A, Ebner I, Luch A, Tralau T. Degradation
of benzo[a] pyrene by bacterial isolates from human skin. FEMS
Microbiol Ecol 2014;88:129‑39.
56. Mancebo SE, Wang SQ. Recognizing the impact of ambient air pollution
on skin health. J Eur Acad Dermatol Venereol 2015;29:2326‑32.
57. Sorg O, Zennegg M, Schmid P, Fedosyuk R, Valikhnovskyi R, Gaide O,
et al. 2,3,7,8‑tetrachlorodibenzo‑p‑dioxin (TCDD) poisoning in Victor
Yushchenko: Identication and measurement of TCDD metabolites.
Lancet 2009;374:1179‑85.
58. Tindall JP. Chloracne and chloracnegens. J Am Acad Dermatol
1985;13:539‑58.
59. Mustafa MG. Biochemical basis of ozone toxicity. Free Radic Biol
Med 1990;9:245‑65.
60. Thiele JJ, Traber MG, Tsang K, Cross CE, Packer L. In vivo
exposure to ozone depletes Vitamins C and E and induces lipid
peroxidation in epidermal layers of murine skin. Free Radic Biol
Med 1997;23:385‑91.
61. He QC, Tavakkol A, Wietecha K, Begum‑Gafur R, Ansari SA,
Polefka T. Effects of environmentally realistic levels of ozone on
stratum corneum function. Int J Cosmet Sci 2006;28:349‑57.
62. Valacchi G, Sticozzi C, Belmonte G, Cervellati F, Demaude J, Chen N,
et al. Vitamin C compound mixtures prevent ozone‑induced oxidative
damage in human keratinocytes as initial assessment of pollution
protection. PLoS One 2015;10:e0131097.
63. Rittié L, Fisher GJ. UV‑light‑induced signal cascades and skin aging.
Ageing Res Rev 2002;1:705‑20.
64. Xu F, Yan S, Wu M, Li F, Xu X, Song W, et al. Ambient ozone pollution
as a risk factor for skin disorders. Br J Dermatol 2011;165:224‑5.
65. Pöschl U. Atmospheric aerosols: Composition, transformation, climate
and health effects. Angew Chem Int Ed Engl 2005;44:7520‑40.
66. Dagouassat M, Lanone S, Boczkowski J. Interaction of matrix
metalloproteinases with pulmonary pollutants. Eur Respir J
2012;39:1021‑32.
67. Lademann J, Schaefer H, Otberg N, Teichmann A, Blume‑Peytavi U,
Sterry W. Penetration of microparticles into human skin. Hautarzt
2004;55:1117‑9.
68. Vierkötter A, Schikowski T, Ranft U, Sugiri D, Matsui M, Krämer U,
et al. Airborne particle exposure and extrinsic skin aging. J Invest
Dermatol 2010;130:2719‑26.
69. Mills NL, Miller MR, Lucking AJ, Beveridge J, Flint L, Boere AJ,
et al. Combustion‑derived nanoparticulate induces the adverse vascular
effects of diesel exhaust inhalation. Eur Heart J 2011;32:2660‑71.
70. Kim J, Kim EH, Oh I, Jung K, Han Y, Cheong HK, et al. Symptoms of
atopic dermatitis are inuenced by outdoor air pollution. J Allergy Clin
Immunol 2013;132:495‑8.e1.
71. Kim HO, Kim JH, Cho SI, Chung BY, Ahn IS, Lee CH, et al.
Improvement of atopic dermatitis severity after reducing indoor air
pollutants. Ann Dermatol 2013;25:292‑7.
72. Dales R, Liu L, Wheeler AJ, Gilbert NL. Quality of indoor residential
air and health. CMAJ 2008;179:147‑52.
73. Okada Y, Nakagoshi A, Tsurukawa M, Matsumura C, Eiho J, Nakano T.
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
Puri, et al. Air pollution and the skin
9Indian Journal of Dermatology, Venereology, and Leprology | Volume XX | Issue X | Month XXXX
Environmental risk assessment and concentration trend of atmospheric
volatile organic compounds in Hyogo Prefecture, Japan. Environ Sci
Pollut Res Int 2012;19:201‑13.
74. Kim EH, Kim S, Lee JH, Kim J, Han Y, Kim YM, et al. Indoor air
pollution aggravates symptoms of atopic dermatitis in children. PLoS
One 2015;10:e0119501.
75. Michielsen CC, van Loveren H, Vos JG. The role of the immune system
in hexachlorobenzene‑induced toxicity. Environ Health Perspect
1999;107 Suppl 5:783‑92.
76. Eberlein‑König B, Przybilla B, Kühnl P, Pechak J, Gebefügi I,
Kleinschmidt J, et al. Inuence of airborne nitrogen dioxide or
formaldehyde on parameters of skin function and cellular activation
in patients with atopic eczema and control subjects. J Allergy Clin
Immunol 1998;101(1 Pt 1):141‑3.
77. Drakaki E, Dessinioti C, Antoniou CV. Air pollution and skin. Front
Environ Sci 2014: 2;1‑6.
78. Asikainen A, Carrer P, Kephalopoulos S, Fernandes Ede O, Wargocki P,
Hänninen O. Reducing burden of disease from residential indoor
air exposures in Europe (HEALTHVENT project). Environ Health
2016;15 Suppl 1:35.
[Downloaded free from http://www.ijdvl.com on Tuesday, February 14, 2017, IP: 14.139.60.66]
... Air pollution and particulate matter cause damage to the epithelial barrier through oxidation of reactive oxygen species. 11 Pollution may also worsen dermatologic conditions such as atopic dermatitis through this oxidative barrier disruption and immune system activation cascades. 12 These mechanisms of skin integrity damage are an important consideration for those living in industrialised regions, and in combination with climate conditions, it may help identify individuals at higher risk for transient increases in TEWL based on geographic location. ...
Article
Full-text available
Introduction: Transepidermal water loss (TEWL) is an objective measurement of skin integrity measured as the amount of water lost across the stratum corneum. TEWL varies greatly across variables such as age and anatomic location, and disruptions in the skin barrier have been linked to inflammatory dermatoses such as psoriasis and atopic dermatitis. Impact of environmental conditions and pollution on TEWL has yet to be determined. Accordingly, this review summarizes effects of environmental conditions and pollution on TEWL. Methods: A comprehensive literature search was performed using Embase, PubMed, and Web of Science to find human studies that provided data on environmental conditions and/or pollution and TEWL. Results: In total, 15 studies were included, with 11 studies examining environmental and seasonal conditions on TEWL and four examining pollution. All studies examining pollution showed increased TEWL in people exposed to particulate matter or NO2. Contradictory results were found on the effects of season and climate across the 11 studies, with no consensus reached. Conclusion: Exposure to pollution is reported to cause increases in TEWL, likely through free radical damage. Significant discrepancies exist among current literature as to the effects of season and climate on TEWL. There is a need to continue examining environmental variables other than temperature and relative humidity, such as atmospheric and steam pressure, that may impact TEWL.
... Given the increasing global level of waste and pollution and its detrimental effects on air, water and the human health, The safeness environment became a mast for worldwide consumers together with wellbeing and longevity [1,2]. It is to underline in fact that according to the World Health Organization (WHO),every year occurs 4.2 million deaths as a result to outdoor pollution (Figure1) [3], also if it isn't to be forgotten the indoor nanoparticulates represented from 10.000 to 240.000 nanoparticles/ml air [4]. ...
... 3 The effects of exposure to ultraviolet radiation and air pollution increases risk factors for skin cancer (melanoma), extrinsic aging, elasticity, sunburn, damage to collagen, and inflammation, such as contact and atopic dermatitis psoriasis, and acne. 4,5 Therefore, it is necessary to protect the body from air pollution and ultraviolet radiation using antioxidants and sunscreen products. [6][7][8] The sun protection factor (SPF) of sunscreen is described as the amount of UV energy needed to create a minimum erythema dose (MED) on protected skin separated by the UV energy demanded to provide a MED on unprotected skin. ...
Article
Full-text available
Indonesia is geographically located on the equator and is presently faced with several complex problems, among which are air pollution and ultraviolet radiation. On average, Indonesians lose approximately 1.2-5 years of their life expectancy due to air pollution and high exposure to ultraviolet radiation, which tends to increase risk factors for skin cancer (melanoma), skin aging, sunburn, damage to collagen, inflammation, and skin elasticity. However, some plants, such as black glutinous rice (Oryza sativa var. glutinosa) are believed to have hereditary protection against ultraviolet radiation and contain antioxidant compounds. Therefore, this study tries to find out the antioxidant activity and sun protection factor of O. sativa extract applying DPPH (1,1-diphenyl-2-picrylhydrazyl) and UV-Vis spectrophotometry. The result showed that the O. sativa extract showed weak antioxidant activity with an IC50 value of 318.883 µg/mL, while the SPF (Sun protection factor) test was at the ultra-protection level against UV-B with a value of 36.65 ± 0.377 at a concentration of 10,000 µg/mL. Therefore, O. sativa extract has antioxidant activity and protection against ultraviolet rays and has the potential to be considered as a new sunscreen agent.
... 3 The effects of exposure to ultraviolet radiation and air pollution increases risk factors for skin cancer (melanoma), extrinsic aging, elasticity, sunburn, damage to collagen, and inflammation, such as contact and atopic dermatitis psoriasis, and acne. 4,5 Therefore, it is necessary to protect the body from air pollution and ultraviolet radiation using antioxidants and sunscreen products. [6][7][8] The sun protection factor (SPF) of sunscreen is described as the amount of UV energy needed to create a minimum erythema dose (MED) on protected skin separated by the UV energy demanded to provide a MED on unprotected skin. ...
Article
Full-text available
Indonesia is geographically located on the equator and is presently faced with several complex problems, among which are air pollution and ultraviolet radiation. On average, Indonesians lose approximately 1.2-5 years of their life expectancy due to air pollution and high exposure to ultraviolet radiation, which tends to increase risk factors for skin cancer (melanoma), skin aging, sunburn, damage to collagen, inflammation, and skin elasticity. However, some plants, such as black glutinous rice (Oryza sativa var. glutinosa) are believed to have hereditary protection against ultraviolet radiation and contain antioxidant compounds. Therefore, this study tries to find out the antioxidant activity and sun protection factor of O. sativa extract applying DPPH (1,1-diphenyl-2-picrylhydrazyl) and UV-Vis spectrophotometry. The result showed that the O. sativa extract showed weak antioxidant activity with an IC50 value of 318.883 µg/mL, while the SPF (Sun protection factor) test was at the ultra-protection level against UV-B with a value of 36.65 ± 0.377 at a concentration of 10,000 µg/mL. Therefore, O. sativa extract has antioxidant activity and protection against ultraviolet rays and has the potential to be considered as a new sunscreen agent.
... 3 The effects of exposure to ultraviolet radiation and air pollution increases risk factors for skin cancer (melanoma), extrinsic aging, elasticity, sunburn, damage to collagen, and inflammation, such as contact and atopic dermatitis psoriasis, and acne. 4,5 Therefore, it is necessary to protect the body from air pollution and ultraviolet radiation using antioxidants and sunscreen products. [6][7][8] The sun protection factor (SPF) of sunscreen is described as the amount of UV energy needed to create a minimum erythema dose (MED) on protected skin separated by the UV energy demanded to provide a MED on unprotected skin. ...
Article
Full-text available
Indonesia is geographically located on the equator and is presently faced with several complex problems, among which are air pollution and ultraviolet radiation. On average, Indonesians lose approximately 1.2-5 years of their life expectancy due to air pollution and high exposure to ultraviolet radiation, which tends to increase risk factors for skin cancer (melanoma), skin aging, sunburn, damage to collagen, inflammation, and skin elasticity. However, some plants, such as black glutinous rice (Oryza sativa var. glutinosa) are believed to have hereditary protection against ultraviolet radiation and contain antioxidant compounds. Therefore, this study tries to find out the antioxidant activity and sun protection factor of O. sativa extract applying DPPH (1,1-diphenyl-2-picrylhydrazyl) and UV-Vis spectrophotometry. The result showed that the O. sativa extract showed weak antioxidant activity with an IC50 value of 318.883 µg/mL, while the SPF (Sun protection factor) test was at the ultra-protection level against UV-B with a value of 36.65 ± 0.377 at a concentration of 10,000 µg/mL. Therefore, O. sativa extract has antioxidant activity and protection against ultraviolet rays and has the potential to be considered as a new sunscreen agent.
... 3 The effects of exposure to ultraviolet radiation and air pollution increases risk factors for skin cancer (melanoma), extrinsic aging, elasticity, sunburn, damage to collagen, and inflammation, such as contact and atopic dermatitis psoriasis, and acne. 4,5 Therefore, it is necessary to protect the body from air pollution and ultraviolet radiation using antioxidants and sunscreen products. [6][7][8] The sun protection factor (SPF) of sunscreen is described as the amount of UV energy needed to create a minimum erythema dose (MED) on protected skin separated by the UV energy demanded to provide a MED on unprotected skin. ...
Article
Full-text available
Indonesia is geographically located on the equator and is presently faced with several complex problems, among which are air pollution and ultraviolet radiation. On average, Indonesians lose approximately 1.2-5 years of their life expectancy due to air pollution and high exposure to ultraviolet radiation, which tends to increase risk factors for skin cancer (melanoma), skin aging, sunburn, damage to collagen, inflammation, and skin elasticity. However, some plants, such as black glutinous rice (Oryza sativa var. glutinosa) are believed to have hereditary protection against ultraviolet radiation and contain antioxidant compounds. Therefore, this study tries to find out the antioxidant activity and sun protection factor of O. sativa extract applying DPPH (1,1-diphenyl-2-picrylhydrazyl) and UV-Vis spectrophotometry. The result showed that the O. sativa extract showed weak antioxidant activity with an IC50 value of 318.883 µg/mL, while the SPF (Sun protection factor) test was at the ultra-protection level against UV-B with a value of 36.65 ± 0.377 at a concentration of 10,000 µg/mL. Therefore, O. sativa extract has antioxidant activity and protection against ultraviolet rays and has the potential to be considered as a new sunscreen agent.
... Given the increasing global level of waste and pollution and its detrimental effects on air, water and the human health, The safeness environment became a mast for worldwide consumers together with wellbeing and longevity [1,2]. It is to underline in fact that according to the World Health Organization (WHO),every year occurs 4.2 million deaths as a result to outdoor pollution (Figure1) [3], also if it isn't to be forgotten the indoor nanoparticulates represented from 10.000 to 240.000 nanoparticles/ml air [4]. ...
Article
Full-text available
This study is an assessment of the effects of outdoor air pollution and extreme weather events on the health of outdoor workers in Delhi, including auto rickshaw drivers, street vendors, and sweepers. To carry it out, a cross-sectional and perception-based epidemiological research design was used, and the primary tool used for data collection was a questionnaire. Two hundred twenty-eight people participated in the survey, and a pulmonary function test (PFT) was performed on 63 participants. Most of the respondents from different occupational groups complained about headaches/giddiness, nausea, and muscular cramps during extreme heat events due to the physically demanding nature of their jobs in the outdoor environment. Furthermore, autorickshaw drivers reported the highest prevalence of ophthalmic symptoms, such as eye redness (44%) and eye irritation (36%). In comparison, vendors reported a higher prevalence of headaches (43%) and eye redness (40%) due to increased exposure to vehicular emissions. Among sweepers, musculoskeletal problems like joint pain (40%), backache (38%), and shoulder pain (35%) were most prevalent due to occupation-related ergonomic factors. In addition, the majority of autorickshaw drivers (47%), vendors (47%), and sweepers (48%) considered that air quality had a severe impact on their health. PFT results showed that most respondents had restricted lung function. Binary logistic regression analysis showed that lung function impairment had a significant association with smoking (p = 0.023) and age (0.019). The odds ratio for smoking, which was around 4, indicated that respondents who smoked had a nearly four times greater risk of developing lung impairment. The study also highlighted the need for using personal protective equipment and developing guidelines to reduce their exposure level.
Book
PREFACE Cyanobacteria are among the most successful and ancient forms of life ever known. These photosynthetic autotrophs have been studied for decades as model organisms in various aspects, from photosynthesis to biotechnological applications and, more recently, for their pharmacological potential in umpteen fields. In fact, cyanobacteria are now recognized as top metabolic producers of a huge number of bioactive compounds with medical interest and that can revolutionize drug discovery and development. Allied to their metabolic capabilities, cyanobacteria benefit from a cost-effective energy-capturing ability, and high cultivation yields with minimum nutritional requirements, being extremely attractive in terms of industrial-scale production processes. This book was designed to bring together fields in which cyanobacteria derived compounds most stood out, with a special focus on those related to therapeutics, cosmetics, and nutrition, emphasizing unique molecules not found in higher organisms. Of the most promising compounds isolated so far, those acting as anti-inflammatories, anti-carcinogens, antimicrobials, and UV protectors fill a prominent place within drug discovery programs. The metabolic richness of cyanobacteria has also been upholding their key role in the field of cosmetics and nutraceuticals, with the last occupying a prominent place in a rapidly expanding market. Apart from the pharmacological and biotechnological approach, this book does not set aside the well-known cyanobacterial toxins, warning to their substantial economic and social impacts, and drawing attention to the urgency of fully addressing algal blooms and their systematic monitoring. Additionally, and given its extreme importance, this book provides a distinctive approach to cyanobacteria systematics, by exploring general aspects and biodiversity of these organisms to discuss trends in cyanobacterial taxonomy. Overall, The Pharmacological Potential of Cyanobacteria is intended to be a useful resource for students, researchers, and professionals working in the field of cyanobacteria, serving as a guide in the discovery, research, and application of these unique microorganisms. Graciliana Lopes, Marisa Silva and Vitor Vasconcelos
Article
Background: Exposure to solar radiation has been documented as a direct cause of skin changes associated with aging, and its effects have been categorized as photoaging. Objective: To explore the clinical characteristics of photoaging and its relationship with external predisposing factors in a Colombian urban and rural population. Methods: We included 350 patients on outpatient consultation at Clínica Chía in Zipaquirá (rural) and Hospital Universitario Barrios Unidos in Bogotá (urban) in an observational, cross-sectional study with an analytical component included, between 2018 and 2019. A survey was conducted and photographs were taken. A group of experts determined the degree of photoaging. Results: The majority of respondents worked in closed environments (n = 222). The main sociodemographic variable associated was age (p = 0.000). Factors such as smoking, alcohol consumption, use of sunscreen, exercising, and sun exposure were also associated with scale progression (p < 0.05). Exercising (odds ratio (OR) 0.6, 95% confidence interval (CI) 0.3-0.9) and being from Bogotá (OR 0.6, 95% CI 0.2-0.9) appeared as protective factors. Smoking (OR 1.6, 95% CI 1.0-2.6) was defined as a risk factor. Conclusions: Changes related to photoaging and photocarcinogenesis are associated with sun exposure. However, there are environmental factors, such as smoking, alcohol consumption, sedentary lifestyle, woman's age at first delivery, and number of children, among others, that affect the degree of photoaging. It is necessary to explore these relationships in higher evidence level studies to define their causality.
Article
Full-text available
Background: The annual burden of disease caused indoor air pollution, including polluted outdoor air used to ventilate indoor spaces, is estimated to correspond to a loss of over 2 million healthy life years in the European Union (EU). Based on measurements of the European Environment Agency (EEA), approximately 90 % of EU citizens live in areas where the World Health Organization (WHO) guidelines for air quality of particulate matter sized <2.5 mm (PM2.5) are not met. Since sources of pollution reside in both indoor and outdoor air, selecting the most appropriate ventilation strategy is not a simple and straightforward task. Methods: A framework for developing European health-based ventilation guidelines was created in 2010–2013 in the EU-funded HEALTHVENT project. As a part of the project, the potential efficiency of control policies to health effects caused by residential indoor exposures of fine particulate matter (PM2.5), outdoor bioaerosols, volatile organic compounds (VOC), carbon oxide (CO) radon and dampness was estimated. The analysis was based on scenario comparison, using an outdoor-indoor mass-balance model and varying the ventilation rates. Health effects were estimated with burden of diseases (BoD) calculations taking into account asthma, cardiovascular (CV) diseases, acute toxication, respiratory infections, lung cancer and chronic obstructive pulmonary disease (COPD). Results: The quantitative comparison of three main policy approaches, (i) optimising ventilation rates only; (ii) filtration of outdoor air; and (iii) indoor source control, showed that all three approaches are able to provide substantial reductions in the health risks, varying from approximately 20 % to 44 %, corresponding to 400 000 and 900 000 saved healthy life years in EU-26. PM2.5 caused majority of the health effects in all included countries, but the importance of the other pollutants varied by country. Conclusions: The present modelling shows, that combination of controlling the indoor air sources and selecting appropriate ventilation rate was the most effective to reduce health risks. If indoor sources cannot be removed or their emissions cannot be limited to an accepted level, ventilation needs to be increased to remove remaining pollutants. In these cases filtration of outdoor air may be needed to prevent increase of health risks.
Article
Full-text available
One of the main functions of cutaneous tissues is to protect our body from the outdoor insults. Ozone (O3) is among the most toxic stressors to which we are continuously exposed and because of its critical location, the skin is one of the most susceptible tissues to the oxidative damaging effect of O3. O3 is not able to penetrate the skin, and although it is not a radical per se, the damage is mainly a consequence of its ability to induce oxidative stress via the formation of lipid peroxidation products. In this study we investigated the protective effect of defined "antioxidant" mixtures against O3 induced oxidative stress damage in human keratinocytes and understand their underlying mechanism of action. Results showed that the mixtures tested were able to protect human keratinocytes from O3-induced cytotoxicity, inhibition of cellular proliferation, decrease the formation of HNE protein adducts, ROS, and carbonyls levels. Furthermore, we have observed the decreased activation of the redox sensitive transcription factor NF-kB, which is involved in transcribing pro-inflammatory cytokines and therefore constitutes one of the main players associated with O3 induced skin inflammation. Cells exposed to O3 demonstrated a dose dependent increase in p65 subunit nuclear expression as a marker of NF-kB activation, while pre-treatment with the mixtures abolished NF-kB nuclear translocation. In addition, a significant activation of Nrf2 in keratinocytes treated with the mixtures was also observed. Overall this study was able to demonstrate a protective effect of the tested compounds versus O3-induced cell damage in human keratinocytes. Pre-treatment with the tested compounds significantly reduced the oxidative damage induced by O3 exposure and this protective effect was correlated to the abolishment of NF-kB nuclear translocation, as well as activation of Nrf2 nuclear translocation activating the downstream defence enzymes involved in cellular detoxification process.
Article
Full-text available
Most of researches on the impact of indoor air pollutants on atopic dermatitis (AD) have been based upon animal models, in vitro experiments and case-control studies. However, human data to elucidate the role of indoor air pollution on worsening symptoms of pre-existing AD from a longitudinal study are scarce. The objective of this prospective study was to evaluate the effect of indoor air pollution on AD symptoms in children. We surveyed 30 children with AD in a day-care centre, which moved to a new building during the study. These children stayed there for 8 hours a day Monday through Friday, and their daily symptom scores were recorded. Indoor and outdoor air pollutant levels were continuously measured 24 hours a day for 12 months (Period 1 to 4). Data were analyzed using a generalized linear mixed model. Compared to the period before moving (Period 1), concentrations of indoor air pollutants mostly increased after moving (Period 2) and decreased by natural ventilation and bake-out (Periods 3 and 4). The rate of positive AD symptom increased from 32.8% (Period 1) up to 43.8% (Period 2) and 50.5% (Period 3), then decreased to 35.4% in Period 4 (P < 0.0001). When the delayed effects of indoor air pollutants on AD symptoms 2 days later were evaluated, AD symptoms significantly increased by 12.7% (95% CI: -0.01 to 27.1) as toluene levels increased by 1 ppb (P = 0.05). In conclusion, indoor air pollutants increase the risk of AD aggravation in children and toluene in the indoor environment might act as an aggravating factor.
Article
Full-text available
Secondhand cigarette smoke exposure (SSE) has been linked to carcinogenic, oxidative, and inflammatory reactions. Herein, we investigated whether premature skin aging could be induced by SSE in a rat model, and assessed the cytoplasmic translocation of high mobility group box 1 (HMGB1) protein and collagen loss in skin tissues. Animals were divided into two groups: SSE and controls. Whole body SSE was carried out for 12 weeks. Dorsal skin tissue specimens were harvested for HMGB1 and Mallory’s azan staining. Correlations between serum HMGB1 and collagen levels were determined. Rat skin exposed to secondhand smoke lost collagen bundles in the papillary dermis and collagen decreased significantly (p < 0.05) compared with control rats. In epidermal keratinocytes, cytoplasmic HMGB1 staining was more diffuse and there were more HMGB1-positive cells after four weeks in SSE compared to control rats. A negative correlation between HMGB1 serum and collagen levels (r = −0.631, p = 0.28) was also observed. Therefore, cytoplasmic HMGB1 expression in skin tissues might be associated with skin collagen loss upon the initiation of SSE. Additionally, long-term SSE might affect the appearance of the skin, or could accelerate the skin aging process.
Article
Full-text available
The increase of air pollution over the years has major effects on the human skin. The skin is exposed to ultraviolet radiation (UVR) and environmental air pollutants such as polycyclic aromatic hydrocarbons (PAHs), volatile organic compounds (VOCs), oxides, particulate matter (PM), ozone (O3), and cigarette smoke. Although human skin acts as a biological shield against pro-oxidative chemical and physical air pollutants, the prolonged or repetitive exposure to high levels of these pollutants may have profound negative effects on the skin. Exposure of the skin to air pollutants has been associated with skin aging and inflammatory or allergic skin conditions such as atopic dermatitis, eczema, psoriasis or acne, while skin cancer is among the most serious effects. On the other hand, some air pollutants (i.e., O3, nitrogen dioxide, and sulfur dioxide) and scattering particulates (clouds and soot) in the troposphere reduce the effects of shorter wavelength UVR and significant reductions in UV irradiance have been observed in polluted urban areas.
Article
Background: Smoking has been associated with psoriasis prevalence and severity. Objective: To evaluate prevalence of smoking in patients with psoriasis and to examine the relationship between smoking and psoriasis severity. Methods: MEDLINE, EMBASE, and Cochrane databases (1960-2012) and conference proceedings (2010-2012) were systematically searched using keywords relevant to psoriasis and smoking. Controlled studies addressing psoriasis and smoking status were included. A meta-analysis for the relative risk of smoking in psoriasis patients was performed. Results: Meta-analysis identified a significant association between smoking and psoriasis with a relative risk of 1.88 (95% CI, 1.66-2.13) for smoking in patients with psoriasis versus patients without psoriasis. Eight articles of 11 with data on smoking and psoriasis severity suggested that severity increases with smoking status. Conclusions: This literature review is in favor of a positive association between the prevalence of smoking and psoriasis as well as an association between smoking and severity of psoriasis.
Article
Ambient air pollution is a known public health hazard that negatively impacts non-cutaneous organs; however, our knowledge regarding the effects on skin remains limited. Current scientific evidence suggests there are four mechanisms by which ambient air pollutants cause adverse effects on skin health: (i) generation of free radicals, (ii) induction of inflammatory cascade and subsequent impairment of skin barrier, (iii) activation of the aryl hydrocarbon receptor (AhR) and (iv) alterations to skin microflora. In this review, we provide a comprehensive overview on ambient air pollutants and their relevant sources, and highlight current evidence of the effects on skin. © 2015 European Academy of Dermatology and Venereology.
Article
Smoking is a potential risk factor for psoriasis. Both psoriasis and smoking habits are partly explained by genetic factors. However, twin studies investigating the association between these traits are limited. Questionnaire-based data on smoking habits and psoriasis were collected for 34,781 twins, aged 20-71 years, from the Danish Twin Registry. A co-twin control analysis was performed on 1700 twin pairs discordant for lifetime history of smoking. Genetic and environmental correlations between smoking and psoriasis were estimated using classical twin modeling. After multivariable adjustment, age group (50-71 vs. 20-49 years) and childhood exposure to environmental tobacco smoke (ETS) were significantly associated with psoriasis in the whole population (odds ratio [OR] 1.15, 95% confidence interval [CI] 1.02-1.29 [P = 0.021] and OR 1.28, 95% CI 1.10-1.49 [P = 0.002], respectively). Risk for psoriasis increased substantially (OR 2.18, 95% CI 1.82-2.61; P < 0.001) for smokers with a history of >5 pack-years, even after adjusting for age, sex, and childhood ETS. Among twin pairs discordant for smoking, risk for psoriasis in the ever-smoking twin was lower among monozygotic twins (OR 1.23, 95% CI 0.59-2.56; P = 0.578) than among same-sex dizygotic twins (OR 2.21, 95% CI 1.36-3.58; P = 0.001). Genetic factors explained 20% (14-25%; P < 0.001) of the correlation between psoriasis and smoking, whereas non-shared environmental factors explained 8% (0-22%; P = 0.504). Tobacco consumption and childhood ETS are significantly associated with psoriasis. Results indicate shared genetic factors for smoking and psoriasis. © 2015 The International Society of Dermatology.
Article
Genome-wide association and large cohort studies have consistently linked several single nucleotide polymorphisms (SNPs) located in the CHRNA5/A3/B4 gene cluster to smoking behaviors and nicotine dependence. Smoking is one of the well-established environmental risk factors for psoriasis and also associated with severity of the disease. Then we conduct the study to examine whether the genetic variations related to smoking behavior located in the CHRNA5/A3/B4 gene cluster also predict the risk of psoriasis vulgaris (PV). The investigations may help explain the mechanisms of the smoking-PV relationship. This is a hospital base case-control study including 634 subjects (329 PV patients and 305 controls), all Chinese Han population. 8 SNPs were selected based on findings from recent studies on smoking and nicotine dependence, all located in the nicotinic acetylcholine receptor subunits CHRNA5/A3/B4 gene cluster. The variants were typed by SNaPshot Multiplex Kit (Applied Biosystems Co., USA). We confirmed that smoking, alcohol consumption and higher body mass index (BMI ≥25) were risk factors for PV. However, none of the selected SNPs was associated with PV risk in the overall analysis and stratification analysis. And we found no association between the selected SNPs in CHRNA5/A3/B4 gene cluster and the clinical features of PV in case-only analysis. This exploratory study does not provide a relationship between these smoking-related SNPs in the CHRNA5/A3/B4 gene cluster and PV in Chinese Han population.
Article
We present calculations of the geographical distribution of the dose rate at the surface of UVB (280-320 nm), UVA (320-400 nm) and, using biological action spectra, the effective radiation for erythema, cataracts and keratitis. A multistream radiative transfer model is used in conjunction with a multiyear climatology of ozone, cloud, surface pressure, surface albedo, temperature and a rudimentary representation of aerosols to calculate the clear-sky and all-sky irradiances. Model outputs are evaluated using daily UV measurements and found to be accurate to about ±10% for clear skies and ±20% for allsky conditions. The effects of UV-weighted surface albedo, surface altitude, sun-earth separation and the vertical distribution of ozone and temperature are included. The results show that the sun's position is the most important factor in determining the geographical pattern of global daily UV rather than column ozone, cloud, surface pressure, daylength or surface albedo. Over elevated regions, the effect of the differences in surface pressure on daily doses was found to be more significant than the effect of the differences in column ozone. Clouds reduce the clear-sky UV dose from a few percent over arid and semiarid regions to 45% in regions with frequent mid-latitude depressions.