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Plast Aesthet Res 2020;7:59.10.20517/2347-9264.2020.154© The Author(s) 2020.
Open AccessReview

Environmental aging of the skin: new insights

Department of Dermatology, Icahn School of Medicine at Mount Sinai, New York, NY 10022, USA.

Correspondence Address: Dr. Karen E. Burke, Department of Dermatology, Icahn School of Medicine at Mount Sinai, River Court Building, 429 East 52nd Street, New York, NY 10022, USA. E-mail:

    This article belongs to the Special Issue Recent Advances in Skin Anti-aging Agents
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    Academic Editor: Salvador Gonzalez | Copy Editor: Cai-Hong Wang | Production Editor: Jing Yu

    © The Author(s) 2020. Open Access This article is licensed under a Creative Commons Attribution 4.0 International License (, which permits unrestricted use, sharing, adaptation, distribution and reproduction in any medium or format, for any purpose, even commercially, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.


    The appearance of aging is determined primarily by extrinsic factors through exposure to environmental sunlight and airborne pollution. That solar ultraviolet B (λ = 290-320 nm) directly causes photoaging (with wrinkles, dryness, and mottled pigmentation) and skin cancer has been recognized for decades; the contribution by ultraviolet A (λ = 320-400 nm) was only more recently understood. New research further implicates visible light (λ = 400-700 nm) as well as the heat rays of infrared radiation (λ > 800 nm). Particularly in urban environments, airborne pollutants such as ozone (O3), polycyclic aromatic hydrocarbons, particulate matter (PM) in smog, and tobacco smoke contribute to photoaging and skin cancer. Furthermore, exposure simultaneously to both solar ultraviolet (UV) and these pollutants results in even greater synergistic damage. The volatile pollutants generate reactive oxygen species which oxidize surface lipids leading to deeper damaging inflammatory reactions. PM carries high concentrations of environmental organic compounds and trace metals. These pollutant-laden particles deliver toxins to the skin transcutaneously through hair follicles and through the blood after respiratory inhalation. The predominant natural mechanism of clearing these xenobiotic chemicals is through the ligand-activated transcription factor the arylhydrocarbon receptor (AHR) found on all skin cells. AHR activity regulates keratinocyte differentiation and proliferation, maintenance of epidermal barrier function, melanogenesis, and immunity. With chronic activation by UV exposure and pollutants, AHR signaling contributes to both extrinsic aging and carcinogenesis.


    Today we live far longer than those in generations before us. The life expectancy of an individual born after 1990 is about 80 years, a substantial increase over the life expectancy of 65 years in those born in 1945. According to the 2018 United States Census Bureau Projections, of the approximately 36% of our present population now over 65 years old, at least a quarter will live to be over 95 years old. Thus it is imperative that our medical research goals emphasize not only lifespan, but also healthspan - maintaining our energy, mind, body, and happiness for all of these extra years.

    Tantamount to healthspan is protecting our skin, the largest organ of our body and the only organ we see - our calling card to the world and shell of interface with external insults. We must be vigilant in protecting our skin from the external onslaught of environmental damage from solar ultraviolet (UV), visible light (VL), and infrared (IR) radiation and airborne pollutants. Science and technology have given us more leisure time so that we can travel to sunny climates and high altitudes where we stay outdoors for many hours swimming, sailing, or skiing, exposing ourselves not only to direct sunlight, but also virtually doubling our UV exposure from the indirect reflection of water, sand, and snow. Also we increasingly live in cities where we are surrounded by the ubiquitous pollutants of traffic and industry outdoors, and cigarette smoke, cleaning agents, and heating and cooking fuel indoors. All of these pollutants - including ozone (O3), polycyclic aromatic hydrocarbons (PAHs), volatile organic compounds (VOCs), and particulate matter (PM) - cause direct oxidative damage that leads to inflammatory responses, resulting in unattractive premature aging of the skin and deforming, dangerous skin cancer. Furthermore, recent research has proven that UV exposure not only directly harms the skin, but synergistically enhances the damage rendered by airborne pollutants[1].

    Recent research has elucidated the precise cellular and molecular mechanisms of the cutaneous damage and of the innate destructive as well as protective responses. A new understanding of how the arylhydrocarbon receptor (AHR) processes xenobiotic insults from UV exposure as well as from airborne pollutants is explained. New evidence demonstrates that topical antioxidants (especially vitamin C, vitamin E, and L-selenomethionine) can indeed not only prevent but also partially reverse extrinsic aging of the skin, though stringent criteria in formulation are required to achieve and maintain optimal delivery, activity, and stability.

    Solar photoaging

    The first protective response of skin to solar UV radiation is production of melanin. After exposure to UV radiation, there is an immediate increase in tyrosinase activity accompanied by an increase in the size of melanosomes. Subsequent exposure results in an increase in the number of active melanocytes with increased transfer of Stage IV melanosomes to keratinocytes. The density of melanosomes in chronically sun-exposed skin is up to double that of non-sun exposed skin[2]. Within minutes after exposure to ultraviolet A (UVA) radiation, there is immediate pigmentary darkening (IPD) - probably due to oxidation of pre-existing melanin and melanin precursors. Because this fades within 20-30 min, it provides no protection. Protective delayed tanning is seen 24 h to 72 h after exposure to UVA + ultraviolet B (UVB) by the mechanisms described above[3].

    All tanning is actually photodamage - extrinsic aging of the skin. In children, the delayed tanning fades within several weeks after terminating summer exposure, though some freckles may persist. However, individuals with no visible hyperpigmentation show the subclinical photodamage of hyperpigmentation when examined with a medical UVA Wood’s light (λ = 367 nm), as seen in the 45-year-old woman shown in Figure 1[3]. With chronic UV exposure, this hyperpigmentation becomes the clearly visible, with unattractive solar lentigines seen commonly in older individuals, especially outdoor sports enthusiasts or those with outdoor professions.

    Figure 1. Subclinical photodamage in a 45-year-old female. No photodamage of hyperpigmentation can be seen unless examined with a Wood’s light (λ = 367 nm), revealing hyperpigmentation from previous sun exposure. VISIA ultraviolet photograph. (Printed with permission by Canfield Imaging Systems, Parsippany, NJ 07054.)

    Individuals with light, sun-sensitive skin (Fitzpatrick phototypes I and II) are at high risk for UV-induced photoaging and skin cancer. The pheomelanin synthesized in response to UV actually produces reactive oxygen species (ROS), leading to increased photoaging and skin cancers, especially in red-heads. Also, damaging DNA photoproducts are produced by chemo-excitation of melanin derivatives, even long after UV exposure[4]. In addition, most red-haired individuals have dysfunction of their melanocortin-1 receptor (MC1R) which hampers the possibility of developing a tan.

    Studies with confocal microscopy have demonstrated that individuals of Fitzpatrick skin types I and II not only have lower melanin but also significantly fewer dermal papillae than those with higher Fitzpatrick skin types and darker skin[5]. With age, there is an even greater disparity between light and dark skin in density of dermal papillae, with increasingly fewer in light-skinned individuals as they age. This is a less-recognized manifestation of photoaging, probably contributing to the crepe-like texture of extrinsically aged skin in light-skinned phototypes.

    UV radiation

    Only about 5% of solar terrestrial radiation is UV radiation. Of the UV component, 95% is UVA and 5% is UVB. The primary chromophore of UVB (λ = 290-320 nm) radiation is DNA which suffers specific “UVB fingerprint mutations” resulting in intrastrand pyrimidine dimers[6]. Further mutations are incited by the generation of ROS. With cumulative UVB damage and natural aging, there is a decreased ability for nucleotide excision repair so that mutations persist, directly leading to pre-cancerous actinic keratoses and skin cancers[6] - basal cell carcinomas (BCCs), squamous cell carcinomas (SCCs), and malignant melanomas (MMs) - of which SSCs and MMs are potentially lethal.

    Ninety-five percent of our daily UV exposure is UVA (λ = 320-450 nm) which, unlike UVB, is not filtered by glass and does not vary seasonally in intensity. Like UVB, UVA exposure results in “signature mutations” with T → G transversions and formation of specific pyrimidine dimers[6]. UVA generates ROS with resultant DNA mutations, in particular oxidation of guanosine to 8-hydroxy-deoxyguanosine (8-OHdG). UVA penetrates the skin more deeply than does UVB: UVA reaches the epidermal stem-cell rich basal layer and the dermis to inactivate the tumor suppressor p53 gene and to decrease immune functions so that early skin cancers are not recognized. Only extremely high exposure to UVA might directly initiate skin cancer, while the lower doses of UVA to which we are exposed do inhibit the normal immune response so that UVB-initiated skin carcinomas proliferate unchecked. Furthermore, it is UVA that activates dermal matrix metalloproteinases (MMP) to degrade collagen and elastic tissue, resulting in the wrinkled, crepe-like, and saggy quality of photo-damaged skin.

    High-energy visible blue light

    Of the solar radiation that reaches the earth’s surface, 39% is visible light (VL, with λ = 400-700 nm) with the high-energy VL in the low wavelength range (blue light). We are exposed to the high-energy VL not only from sunlight but also from computer screens and smart phones! Early observations by Kollias et al.[7] showed that VL does induce skin pigmentation that can last for 10 weeks. Further research demonstrated by exposure to a xenon-mercury lamp, that VL (up to 470 nm) induces IPD, as does UVA-I[8]. The peak IPD response is at wavelengths λ = 300-500 nm, including all UVA-II (λ = 320-340 nm), UVA-I (λ = 340-400 nm), and visible blue light (λ = 400-500 nm)[9]. This tanning (with erythema) was only seen in dark-skinned individuals of Fitzpatrick skin type IV-VI, probably because of the large amount of melanin in their skin; light-skin type I individuals showed no tanning after VL exposure[10]. The corresponding coinciding erythema may be because as melanin absorbs VL, thereby generating heat to cause vasodilation. More exposure to VL leads to darker and more sustained pigmentation as seen also in UV-induced post-inflammatory hyperpigmentation.

    Exposure of human skin equivalents to VL has been shown in vitro and in human skin ex vitro to generate ROS leading to induction of pro-inflammatory cytokines and MMP-1 and MMP-9[11]. Dose-dependent generation of hydrogen peroxide was also measured after exposure to VL. Certainly this oxidative insult, the inflammatory cascades, and the MMPs destroy dermal matrix to contribute to extrinsic photoaging.

    IR solar radiation

    Almost 50% of the solar energy reaching the earth’s surface is IR or heat energy: IR-A (λ = 700-1400 nm), IR-B (λ = 1400-3000 nm), and IR-C (λ = 3000 nm - 1 mm). Solar terrestrial radiation is about 30% IR-A. IR-B and IR-C do not penetrate deeply into the skin, but they do contribute to heating the skin. Direct sunlight can raise the temperature of human skin from 37 °C to 40 °C, with darker skin types IV-VI responding to IR exposure with greater rises in temperature than experienced by light-skinned individuals (types I and II). Although more than 65% of incipient IR-A penetrates to the dermis and 10% to the subcutaneous fat, normal (non-excessive) exposure does not raise the skin’s temperature[12].

    The reaction to IR-A varies with skin type: In darker skin, melanin synthesis is stimulated with little effect in dermal MMPs, while in lightly pigmented skin, collagen in the dermal extracellular matrix is altered not only by destruction through activation of MMPs, but also by a direct reduction in synthesis[12]. Thus lightly pigmented skin manifests wrinkles and a crepe-like quality, while darkly pigmented skin responds with increased solar lentigos - both suffering from premature extrinsic aging. In addition, chronic exposure to IR-A induces angiogenesis and unattractive erythema ab igne as seen in “bakers’ arms” and “glassblowers’ faces”[12].

    Although the clinical manifestations of photoaging of the skin are similar after UV and IR-A exposure, the mechanisms of damage are different. IR-A affects the mitochondrial electron transport chain, increasing mitochondrial superoxide anion production[13]. In human fibroblasts in vitro, IR-A induces genes regulating apoptosis, extracellular matrix, calcium regulation, and other signaling[14]. Solar elastosis is markedly exacerbated by IR-A in two ways: (1) stimulation of MMP-12 which specifically degrades elastin; and (2) abnormal production of the major components of elastin-fibrillin-1,2 and tropoelastin[13]. Along with degradation of collagen, this accumulation of abnormal, clumped elastin in the dermis is the paramount cause of the crepe-like, saggy, wrinkled appearance of photoaged skin.

    Synergy: UVA and pollutants

    Atmospheric pollutants fill the air in modern cities. Outside, traffic exhausts, power plants and factories pollute, and, inside, stoves, heaters, fireplaces, candles, and cigarette smoke. Organic and inorganic compounds are emitted. PAHs are ubiquitous in our air, water, and food. The most significant PAH in urban environments is benzo[a]pyrene (BaP). These PAHs are absorbed onto and within the larger PM pollutants. When inhaled or absorbed after direct contact with mucosa or skin, these PAHs are metabolized to quinones which generate ROS.

    Today, the levels of PAHs are lower than those of 40-50 years ago, well below a toxic or carcinogenic level. However, with simultaneous exposure of the skin to PAHs and UVA radiation, synergistic interactions increase oxidative damage, leading to increased extrinsic damage to the skin with resultant photoaging and skin cancer.

    In mouse model experiments, exposure to low doses of BaP alone, or to UVA alone, does not initiate skin cancer. However, exposure to 1.8% of the carcinogenic dose of BαP with simultaneous exposure to 12.5% of the carcinogenic dose of UVA could initiate skin cancer[1,15], as shown in Figure 2 (this exposure to UVA is comparable to 2 h of midday sunlight on a summer day in New York City).

    Figure 2. Squamous cell carcinoma multiplicity (number of tumors/mouse) in Skh:1 female mice after topical application of BaP (8 nmol) followed by exposure to ultraviolet A (UVA) (40 kg/m2) three times weekly for 25 weeks. For 5 weeks after treatments were discontinued, tumors were still counted (Wang et al.[1]). (Printed with consent of the authors.). BaP: benzo[a]pyrene

    Synergistic damage was further demonstrated in vitro. High concentrations of d-OHdG and hydrogen peroxide (H2O2) were generated when calf-thymus DNA was exposed to UVA after incubation with BaP; in contrast, only minimal concentrations were measured when exposed to UVB after BaP[16]. Cells exposed to UVA after having been incubated with BaP increased 8-OHdG by a factor of 17, while exposure to UVB resulted in only an increase by a factor of 3[1]. Another experiment exposed human keratinocytes to UVA after incubation with BαP: H2O2 production increased 6-fold compared to only a factor of 1.2 after exposure to UVB[1]. In the skin, all of this oxidative damage manifests clinically as photoaging and proclivity to carcinogenesis.

    With exposure to UV, BaP forms diol epoxide (BPDE) which combines covalently to DNA to form BPDE-DNA adducts that directly initiate carcinogenesis[17]. Exposure to UVA generates more than double the number generated by exposure to UVB[18]. These adducts directly produce ROS. Furthermore, the BaP is recycled within cells, a reaction enhanced by UVA exposure, making even small amounts of BaP extremely damaging. This sequence of reactions leading to photoaging of the epidermis and dermis as well as to initiation and promotion of skin cancer is shown in Figure 3.

    Figure 3. Mechanisms of solar-induced photoaging and carcinogenesis of the skin. Solar ultraviolet B (UVB) directly mutates cellular DNA to cause photoaging and to initiate carcinogenesis. Ultraviolet A (UVA) interacts synergistically with pollutants to form DNA-adducts, initiating carcinogenesis. Both UVA and UVB generate ROS that oxidize DNA to form 8-OHdG, leading directly to photoaging and tumor initiation. ROSs further activate signal transduction of inflammatory cytokines and matrix-destructive enzymes, which exacerbate photoaging and cellular proliferation to promote carcinogenesis. Exposure to solar (and technological) VL and IR heat also induces photoaging of the skin. (Modified from Saladi et al.[18] with consent of authors.). ROS: reactive oxygen species; 8-OHdG: 8-hydroxy deoxyguanosine; VL: visible light; IR: infrared light


    In the stratosphere (10-30 miles above the earth’s surface), O3 protects us by blocking dangerous solar UVC and dangerous high-energy UVB. On the other hand, low level tropospheric O3 causes significant oxidative damage, particularly to the skin. The average level of O3 on the earth’s surface is about 0.05-0.1 ppm, quite low in comparison with the stratosphere with concentrations of 10 ppm. However, especially during the summer, in densely populated cities such as Mexico City (with the highest levels) and even Rome and Paris, industry and traffic emit VOCs including nitrogen oxides, methane, carbon monoxide, and sulfuric compounds which accumulate, causing a progressive increase in O3 concentrations up to 0.8 ppm.

    Although O3 cannot penetrate the skin, it oxidizes lipids on the skin’s surface, thereby triggering destructive inflammatory cascades in deeper cellular layers, turning on genes to produce inflammatory cytokines - interleukin-8 (Iℓ-8), tumor necrosis factor-alpha (TNF-α), transforming growth factor beta (TGF-β), cyclooxygenase-2 (COX-2), intercellular adhesion molecule (ICAM), and vascular cell adhesion molecule (VCAM)[19,20] - all of which have been measured in response to surface O3. This inflammatory onslaught certainly disrupts dermal cells and extracellular matrix to exacerbate photoaging[21]. Further damage is rendered by O3 generation of the protein adduct 4-hydroxy-2-nonenal (HNE) and carbonyl protein adducts[22].

    Direct proof that O3 exposure contributes substantially to accelerating extrinsic aging was demonstrated in Skh:1 hairless mice[22,23]. With exposure to O3, dermal MMP-2 (a gelatinase that digests collagen I and IV) and MMP-12 (an elastase) are activated; MMP-9 (a gelatinase with activity similar to MMP-2) is activated only in older mice[23]. O3 further inhibits activation of inhibitors of MMPs[24], thus increasing matrix degradation with resultant manifestations of dermal aging: Wrinkles, crepe-like skin, and sagging due to loss of support, seen histologically as loss of collagen with disorganization of fibrillar alignment and loss of elastin with clumping of dysfunctional elastic tissue fragments. This degradation of firm extracellular matrix allows and promotes enhanced tumor growth[25].

    Defending against this damage are antioxidants vitamin C and vitamin E on the skin’s surface. However, exposure to O3 rapidly depletes these essential antioxidants[26], probably because the resident levels of these vitamins are rapidly depleted by quenching the initial onslaught of O3-induced oxidative damage. Thus, the first antioxidant defense is lost. Another protective mechanism is the induction of epidermal heat shock proteins (HSP) sequentially: HSP 27 (at 2 h), HSP 70 (at 12 h), and HSP 32 (maximally at 24 h). HSP 27 actually increases 20-fold and HSP 70 by 8-fold in response to O3. These HSPs may mitigate the oxidative harm from surface O3[19]. Further defending against all of the O3-induced oxidative stress is activation of the antioxidant transcription factor nuclear factor of kappa-light-chain-enhancers of activated B-cells (NF-κB) in keratinocytes as well as in dermal cells, as demonstrated in vitro and in vivo[19,22].

    A recently published epidemiological study from two cohort groups in Germany (of 2013 Caucasian men and women)[27] provides direct proof that exposure to tropospheric O3 does indeed exacerbate extrinsic skin aging. Five-year cumulative residential exposure to ambient O3 was calculated for each of the two neighborhoods (within a 5-digit postal code). Course wrinkles and hyperpigmentation (solar lentigines) on the forehead, under eyes, crow’s feet area, and upper lip and facial lentigines were quantitated by visual scoring according to the validated Score of Intrinsic and Extrinsic Skin Aging (SCINEXATM)[27]. Correlation of course facial wrinkles with cumulative neighborhood O3 exposure was confirmed, but increased pigmented lentigines were not noted. This correlation was independent of other possible environmental confounders and airborne pollutants including particulate matter.

    Particulate matter

    Even the earliest humans suffered from particulate matter exposure: Dust storms from the Sahara, and pollen and particulate fecal matter from grazing herds on the savannah caused respiratory, cardiovascular, and skin disease. Today, city environments are filled with larger PM10 and PM2.5 particles (≤ 10 μm and ≤ 2.5 μm diameter, respectively) of soot, primarily emitted by diesel engines, factories, power plants, and incinerators as well as smaller ultrafine particles (UFPs) (≤ 100 nm, 0.1 μm, diameter) from traffic. Up to 475 kg/km2 are spewed into urban air each year[28]. Even rural dwellers suffer from nearby highways and inside furnaces and fireplaces as well as from forest fires and wind-blown dust. Polluting compounds (PAHs, NO2, SO2, and trace minerals) cover the surfaces and are incorporated into the cores of the PMs[29,30]. These PMs contacting skin are absorbed to the mid-stratum corneum, as shown by tape-stripping chimney sweeps[31]. UFPs not only penetrate the skin transdermally and through hair follicles[32,33], but also are inhaled through the lung to enter pulmonary circulation; PM contaminants can be measured in the blood within one hour and can remain for weeks[34].

    Direct damage to the skin by larger PMs was shown by exposing reconstituted human epidermis in vitro to concentrated PM2.5[35]. Oxidation of surface lipids and apoptosis correlated with increasing dose and exposure time. The impact of larger PM10 pollution has been demonstrated by in vitro exposure of human dermal fibroblasts to PM10 for 24 h[36]. Surprisingly, 1,977 genes were expressed, most significantly pro-inflammatory genes for interleukins (Iℓ) Iℓ-1β, Iℓ-6, Iℓ-8, and Iℓ-33, resulting in increases especially in Iℓ-6 and -8, cytochrome (CYP) P450 (CYP1A1, CYP1B1), and MMP-1 and -3, and accompanied by substantial decreases in transforming growth factor-β (TGF-β) and in collagen I and elastin mRNA. All of these factors directly result in the crepe-like, wrinkled, and sagging quality of extrinsic aging.

    The mechanism of PM cutaneous insult is by oxidation of surface lipids with resultant ROS that activate inflammation through transcription factors such as NF-κB, turning on gene transcription for cytokines and Iℓ-1α, Iℓ-8, COX-1 and -2[37,38]. In particular, PMs containing quinones or trace metals localize in keratinocyte mitochondria, altering the mitochondrial ultrastructure with first dilation and vacuolization and loss of cristae, then thickening and shrinking[39].


    VOCs such as car exhaust with benzene and industrial emissions (mainly tetrachloroethylene) pollute the outdoor environment, while organic solvents in paints, varnishes, refinishing chemicals, glues, cleaning agents, cosmetics (especially nail polish) such as aliphatic hydrocarbons (formaldehyde and acetone) fill indoor closed spaces. Indoor pollution is particularly exacerbated in all homes in winter when windows are kept closed, and throughout the year in cities where skyscrapers and other buildings have sealed windows to maintain energy conservation. This VOC-contaminated air is recirculated, leading to “sick building syndrome.” Workers experience conjunctivitis, rhinitis, atopic dermatitis, eczema, and other contact or irritant dermatitis, particularly after reconstruction, painting, installation of new rugs and draperies, and after thorough cleaning. These airborne irritants contribute to extrinsic aging of exposed skin, particularly on the hands, neck, and face.

    Tobacco smoke

    A major indoor pollutant is cigarette (and cigar and pipe) smoke which exposes not only the smoker but also others to the “sidestream” smoke. In the closed environments of our modern world - with urban skyscrapers and airplanes and mass transit of subways - the VOCs and tobacco contaminants linger. In a cinema which had been designated “nonsmoking” for over 5 years, 35 tobacco-related chemicals were measured, carried inside by smokers’ hair, skin, and clothes - leading to “third-hand exposure”[40].

    More than 4,700 different chemicals are released by burning tobacco[41], some as PM (including nicotine, quinone, and benzopyrenes), some as VOCs (PAHs, CO2, CO, formaldehyde, nitrosamine and many others). One dominant component of tobacco smoke, 4-aminobiphenyl, is particularly dangerous because it forms adducts on hemoglobin, albumin, and collagen[42]. These adducts remain for the “lifetime” of each component: On hemoglobin, adducts remain for 120 days at levels 5.5 times higher in smokers than nonsmokers; on albumin, adducts remain for 30 days, and on collagen, for up to 10 months. Oxygen delivery is impeded and collagen structure is disrupted, leading to extrinsic aging of the skin.

    The long-term exposure of mice to cigarette smoke and UV results in barrier disruption, with transepidermal water loss, erythema, telangiectasis, decreased elasticity, visible crepe-like skin, and an increased incidence of benign epitheliomas and squamous cell carcinomas[43]. Increased mRNA for the metalloproteinases MMP-1 and -3 with consequent breakdown of collagen I and III[44] as well as of elastic tissue is seen, accelerating extrinsic aging.

    Mechanism of detoxification: the AHR

    AHR evolved to detoxify food and airborne toxins. The AHR is found on cells of the gastrointestinal tract, pulmonary epithelium, and is especially highly expressed on all cells of the skin - keratinocytes, fibroblasts, and melanocytes as well as on regulatory T-cells and dendritic cells. The AHR recognizes and binds xenobiotic pollutants, then signals gene transcription of enzymes and inflammatory cytokines to metabolize these foreign substances[45]. The AHR plays a key role in barrier function, pigmentation regulation responding to environmental onslaughts, and skin inflammation[46]. Specific ligands activate specific genes. In the epidermis, UVB is absorbed by the amino acid tryptophan to form the photoproduct 6-formylindolo[3,2-b]carbazole (FICZ) and indoles which bind with high affinity to the AHR to induce the protective signaling cascade. Other potent ligands are the PAHs of tobacco smoke and city pollution as well as pesticide components such as tetrachlorodibenzo-p-dioxin (TCDD), the contaminant of Agent Orange, and even normal skin flora such as bacteria (non-pathogenic as well as pathogenic staphylococci) and yeasts (Malassezia furfur).

    As seen in Figure 4, the inactive AHR is incorporated into a multi-protein complex in the cellular cytoplasm. Binding of the pollutant ligand generates a conformational change that breaks this complex so that ligand-AHR enters the nucleus where it dimerizes with AHR nuclear translocator (ARNT). This dimer is a transcription factor which binds to genes to induce DNA transcription. AHR can selectively induce transcription of NF-κB, leading to inflammatory cytokines such as NRF2 (which activates antioxidants) as well as to cell cycle (proliferation) and immune modulators.

    Figure 4. The aryl hydrocarbon receptor (AHR). The AHR is found in the cytoplasm bound to protein chaperone molecules, including AHR interacting protein, heat shock protein-90, the p53 protein, and the tyrosine kinase oncogene cSRC. When a pollutant ligand binds to this complex, conformational changes dissemble the complex so that the ligand-AHR unit translocates into the nucleus where it dimerizes with ARNT. The ligand-AHR-ARNT entity induces transcription of target genes, specific for each xenobiotic ligand. Overstimulation by the ligand-AHR complex is prevented (1) by RNA transcription of the AHR repressor (AHRR) gene to synthesize co-repressors; and (2) by cytoplasmic degradation of the ligand-AHR entity after expulsion from the nucleus. After release from the initial cytoplasmic AHR complex, the chaperone protein oncogene cSRC binds to the epidermal growth factor receptor (EGFR), activating the cSRC protein kinase to induce carcinogenesis. (Modified from Figure 1 of Vogeley et al.[47] with the author’s consent.). cSRC: “cellular sarcoma”, photo oncogene tyrosine-protein kinase; ARNT: AHR nuclear translocator

    Alternatively, the ligand-AHR can induce the AHRR gene which inactivates the AHR by transcribing co-repressors[47]. Other inhibition of AHR is regulated by expulsion of the ligand-AHR from the nucleus for degradation in the cytoplasm. Thus overstimulation by the pollutant-ligand-AHR complex is curtailed. The co-chaperones that are released by the dissociation of the initial cytoplasm AHR complex after ligand binding lead to important cellular reactions: The heat shock proteins which are co-chaperoned by p23 stabilize or refold proteins that act to mitigate cellular stress; p23 also binds to the progesterone receptor that transports progesterone to the nucleus; the oncogene cSRC binds to the EGFR leading to activation of cSRC kinase and carcinogenesis.

    Epidemiological correlation of extrinsic skin aging and pollution

    Outdoor pollution

    Vierkötter et al.[48] published an impressive epidemiological study showing the impact of urban pollution on aging skin on four-hundred Caucasian women (70-80 years old) who had previously enlisted in a study of the effect of industrial pollution on pulmonary aging. Half lived in urban Rohr and half in rural Bergen. All were evaluated by the SCINEXA scale which distinguishes intrinsic from extrinsic aging. Childhood sun exposure and smoking history were evaluated for each patient, and exposure to traffic and industrial emission at each individual’s home were measured. The researchers concluded that traffic-generated PM nanoparticles produced 16% more lentigines on the forehead and 17% more on the cheeks for each quartile increase in pollution measured. Concentrated soot increased lentigines by 27% on the forehead and 20% on the cheeks. Women living within 100 m of a busy road showed an increase of 25% and 20% in forehead and cheeks lentigines, respectively, for each interquartile increase in pollution.

    A further study looked at the VOC NO2 released by traffic, known to cause lung damage and lung cancer[49]. Facial cheek lentigines were evaluated in women over 50 years old - 806 European Caucasians and 1,072 Chinese, making this the largest study to date of traffic-induced lentigines. Indeed, NO2 exposure increased lentigines in both cohorts. Lentigines develop at a younger age in Asians despite their cultural avoidance of sun exposure (in contrast to many Caucasians). This proclivity for lentigines may be due to a particular genetic marker in the SLC45A2 gene similarly noted in Japanese, a marker known to be involved in melanin synthesis[50].

    Indoor pollution

    Cigarette smoke is the most significant indoor contaminant; second-hand side-stream smoke permeates indoor space and is recycled in closed environment; third-hand smoke is carried by the hair, skin, and clothes of smokers entering a closed space[40]. In 1969, Henry Daniell recognized that smokers look older than non-smokers[51]. Several epidemiological papers confirm this observation[52,53,54]. Analysis shows that men who smoke have 2.3 times as many wrinkles as nonsmoking males, and women have 3.1 times as many as non-smoking women[53]. Smokers’ skin displays extensive aging with a leathery texture, dryness, deep wrinkles, a crepe-like quality, and sagging. This appearance of prematurely aged skin can be clearly seen in Figure 5. The 52-year-old smoker has far more severe periorbital wrinkles than her non-smoking 57-year-old cousin and neighbor[55]. A further dramatic demonstration of the ravages of photoaging in smokers was shown in photographs of identical twins with a greater than 5-year difference in smoking[56]. Especially upper eyelid skin redundancy, lower lid bags, molar bags, nasolabial folds, upper and lower lip wrinkles, and jowls are markedly worse in the twin who smoked.

    Figure 5. The 52-year old smoker (A) has more severe, deeper periorbital wrinkles than her 57-year-old non-smoking cousin (B). These cousins are neighbors who experienced the same environmental conditions throughout their lives (reprinted from Great Skin for Life, with consent of the author)

    The other primary sources of indoor pollution, especially in underdeveloped countries, is cooking and heating with coal or wood. In China, more than 20% and up to 70% of households cook with solid fuel[57], causing chronic obstructive pulmonary disease, compromised lung function, and lung cancer[58]. To study the effect on the appearance of the skin, Li et al.[59] compared 405 women (of age 30 to 70 years) from northern China with 857 women from southern China, using the standardized SCINEXA evaluation. Correcting for age, cooking and heating with solid fuel significantly increased severe facial wrinkling by 5%-8% and by 75% the fine wrinkles of the hands.

    Not only do underdeveloped countries suffer with indoor pollutants, but also throughout the world, gas stoves spew pollutants (primarily nitrogen dioxide and carbon monoxide) which make indoor air factors dirtier than outdoors, as reported by The Guardian (United Kingdom) recently. Candles and fireplaces further contribute. No specific studies on the effect of these frequent enjoyments on aging skin have been completed as yet, but certainly we know that these airborne contaminants are detrimental to skin.

    Skin cancer

    The most severe and devastating manifestation of photoaging is skin cancer. Here there is no doubt that environmental pollution directly initiates and propagates skin cancer. The first realization of environmental pollutants causing skin damage was in London in 1775 when Dr. Percivall Pott correlated SCC on the underside of the scrotum after exposure to soot in young boy chimney sweeps[60].

    That UVB directly initiates all types of skin cancer - SCC, BCC, and MM - has been proven beyond doubt. UVA promotes skin cancer by generating specific DNA mutations, by production of labile ROS and subsequent oxidation of DNA, and by suppressing the immune response. As described above and shown in Figure 2, UVA also interacts synergistically with environmental airborne pollutants to form mutagenic DNA adducts leading to skin carcinogenesis.

    The highly complex regulation of cellular physiology by the AHR and its influence on the initiation and propagation of skin cancer has been excellently reviewed by Vogeley et al.[47]. Some downstream reactions initiated by AHR suppress or inhibit initiation and promotion of carcinogenesis; others stimulate carcinogenesis. The regulation is highly specific for each xenobiotic pollutant, and concentration and interaction with UVA certainly contribute.

    UVB invokes the AHR by generating the photoproducts, most prominently FICZ. The AHR-FICA complex initiates rapid metabolism of FICZ to limit carcinogenesis. On the other hand, high levels of UVB trigger other cytokines which stimulate SCC growth. Nitrosamines and aromatic amines from tobacco smoke and high levels of PAHs encountered with high industrial exposure activate the AHR, often leading to downstream metabolism of these xenobiotics to genotoxins within keratinocytes. AHR activation by these pollutants in Langerhans cells changes these antigen-presenting dendritic cells from stimulatory to regulatory, enhancing immunosuppression to allow tumor growth. Vietnam veterans had an increased incidence of melanoma after exposure to the Agent Orange carcinogen TCDD[61], which through the AHR-TCDD complex initiated reactions that alter the microenvironment by activating destructive MMPs[62], inducing angiogenesis, and increasing cancer cell motility[63].

    Perhaps the most studied clinical correlation of skin (and lung) cancer to environmental pollutants is the correlation to cigarette smoking. Smokers statistically have twice as many melanomas as non-smokers, 1.5 times as many cutaneous SCCs, 15 times as many SCCs of the lip, and 78 times as many oral epithelial cancers. Another direct chemical correlation of the incidence of mortality of skin cancer induced by environmental exposure was studied in São Paulo, Brazil[64]. Indeed, higher PM10 pollution is directly associated with an increased incidence of skin cancer.


    The appearance of aging on our skin is primarily caused by exposure to solar radiation and environmental airborne pollutants. Recent research has elucidated new insights into the molecular mechanisms of skin damage and natural defenses. We now realize that not only is UVB the main instigator of photoaging, but also UVA as well as visible light and long wavelength IR heat contribute to extrinsic aging. Environmental airborne pollutants - particularly the PAHs released by industry and traffic, O3, VOCs, PM coated with and containing xenochemicals - all directly cause the hallmark appearance of premature aging of the skin. Furthermore, exposure to UVA and airborne pollutants simultaneously causes synergistic damage and accelerated extrinsic aging with increased carcinogenesis.

    The new epidemiologically-proven realizations about the specific causes of damage can teach how to prevent or lessen the adverse results of exposure. Avoidance of sun exposure and use of broad-spectrum sunscreen; improvements in technology to minimize industrial pollution and decreasing traffic emissions; stopping smoking; avoiding cooking and heating with fossil fuels in closed, indoor spaces; choosing rural over urban dwellings if possible - these all reduce the risk. In Korea, indoor air quality was improved in nine kindergarten classes, decreasing PM10 significantly from 182.7 μg/m to 73.4 μg/m[28]. The European Health Event project improved indoor air quality by optimizing ventilation, filtering outdoor air, and controlling indoor sources of pollution (especially by prohibiting smoking)[65]. Industry is developing technology to be ecofriendly - for example, the use of compressed natural gas as fuel instead of coal and petroleum decreases PM pollution.

    All environmental exposure - whether from solar energy or airborne toxins - leads to skin damage by generation of ROS, either directly or via the AHR receptor. Our bodies’ primary protective mechanism is our complex endogenous antioxidant network which is dependent upon external supplementation - either orally, topically, or both. These antioxidant-induced reactions have been shown to combat extrinsic aging of the skin and skin cancer. Indeed, the resident epidermal antioxidants vitamin C and vitamin E are depleted 55% and 25%, respectively, as they protect surface skin after exposure to high concentrations of O3[26].

    Antioxidants can best be replenished or delivered to the skin by topical application giving far higher concentrations than attained by oral ingestion. For example, L-ascorbic acid (vitamin C) 15% gives 27-40 times the skin concentration resulting from high oral intake[66], d-α-tocopherol 5% (the only one of 32 forms of vitamin E that is effective on skin), by a factor of 12[67], and selenium (L-selenomethionine 0.05%), by a factor of 8[68]. These three antioxidants have been extensively studied and proven to prevent and even reverse photoaging of the skin in mice[67,68,69], pigs[70], and humans[71,72], and to inhibit UV-induced skin cancer in mice[67,68,69,73]. However, stringent criteria are required for topical formulations to be stable, to be successfully absorbed, as to be active as antioxidants. Esterified forms of vitamins C[66] and E[67] are not absorbed transcutaneously, and the ester is not reduced to the -OH form required for antioxidant activity. Only the isomer d-α-tocopherol is effective; the other 31 isomers (eight “dl” isomer configurations and four α, β, γ, δ forms) are not[67]. High concentrations are required, optimally 15%-20% for l-ascorbic acid[72] and 2%-5% for d-α-tocopherol[67]. Biologic L-selenomethionine is the optimal form of the multiple valence forms of selenium (at concentrations of 0.02%-0.05%)[68]. Combining L-ascorbic acid (15%) with α-tocopherol (1%) gives four-fold protection against clinical minimal erythema dose (MED) and against thiamine dimer formation alone[74]; addition of another plant antioxidant ferulic acid (0.5%) yields 8-fold protection[72]. This formulation was shown to prevent the up-regulation of oxidative and inflammatory markers in human skin explants exposed to UV plus O3 and diesel engine exhaust[75]. Many other topical antioxidants are being actively studied, including lycopene[76], genistein[77], plant-derived phenolic compounds (such as green tea, pomegranate, grape, and cocoa), and certain marine algae[78].

    Current research is also focused on understanding at a cellular level how the AHR binds and metabolizes xenochemicals, leading to complex cascades of protective or damaging inflammatory reactions, depending upon the specific pollutant, simultaneous exposure to UVA and to other pollutants, and concentration of these foreign substances. This understanding may lead to the discovery of methods to modulate the AHR response in order to prevent and protect the skin from extrinsic damage.



    The author would like to thank Xueyan Zhou, MD, MS, for assistance with literature research and Heather Nolan, MA, for excellent artistic rendition of the figures, literature research, and editing of text.

    Authors’ contributions

    The sole author wrote this review article.

    Availability of data and materials

    Not applicable.

    Financial support and sponsorship


    Conflicts of interest

    The author declared that there are no conflicts of interest.

    Ethical approval and consent to participate

    Not applicable.

    Consent for publication

    Subjects shown in Figures 1 and 5 did give consent.


    © The Author(s) 2020.


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    Cite This Article

    Burke KE. Environmental aging of the skin: new insights. Plast Aesthet Res 2020;7:59.



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