Reviewing putative industrial triggering in pemphigus: cluster of pemphigus in the area near the wastewater treatment plant

Introduction to the issue of pemphigus triggering

Pemphigus belongs to autoimmune blistering dermatoses (ABD). The commonest entities of these are pemphigus vulgaris (PV) and pemphigus foliaceus (PF), severe chronic and relapsing life-threatening disorders requiring individualized immunosuppressive medications [1]. Desmoglein 3 and 1 (DSG3, DSG1) – desmosomal cadherins, participate in epithelial cells adhesion as well as signalling pathways regulating keratinocyte proliferation and differentiation [2–6]. The autoantibodies to these proteins lead to desmosomal adhesion loss, acantholysis and suprabasal blister formation in the skin and mucous membranes by decreasing DSG3/DSG1 half-life and inducing their cleavage [7, 8]. Yearly pemphigus incidence in Europe is estimated to be ca. 1/million population [9–12], yet still a possible restriction to relatively well-defined geographic areas (endemic form of pemphigus) is noted in the world (e.g. Brazil, Colombia, Tunisia). Commonly, there is no apparent inducing factor and the lesions appear spontaneously, while in some patients the medical history gives some clues on potential and/or not infrequently alleged triggers. The aetiology of autoimmunity in ABD seems to be multifactorial, combining both inducing and predisposing factors (“the seed and the soil” theory) [13], and is yet not well understood being largely speculative. Among all those divergent factors, genetic predisposition, physical agents, infections, hormonal disorders, malignancies, emotional stress, various drugs and chemical compounds are listed [13–16]. There have been reports indicating a possible role of environmental/industrial factors in the development of pemphigus in predisposed individuals [13]. Chemical factors that seem to be culprits are: chronic methyl mercury poisoning [16], inhaled silica dust [17–19], inhaled/topical pesticides [20–22], topical insecticides [23], topical or ingested thiols, amides, phenols and miscellaneous drugs [13, 15, 24].

Clinical and laboratory features of pemphigus patients living near the wastewater treatment plant

Clinical examination and single-step direct immunofluorescence of perilesional skin using FITC-conjugated antibodies to human IgA, IgM, IgG, IgG1, IgG4 and C3 for the evaluation of pattern and intensity of deposits of immunoreactants [25] as well as semiquantitative ELISA (MBL, Japan, levels in AU/ml or Euroimmun, Germany, levels in RU/ml) for serum IgG antibodies to DSG1 and DSG3 were used to diagnose pemphigus. In a relatively short time period (4 years), in our university department we diagnosed 3 novel cases of pemphigus (1 PV, 1 PF and 1 shift PF  PV) (Figure 1, Table 1) living near the wastewater treatment plant. These middle-aged patients (2 men and 1 woman) were not related to one another and had nothing in common, apart from inhabiting one estate of the Poznan suburbia (Kozieglowy, population < 12,000), Greater Poland district, Poland. The female patient with the shift PF  PV diagnosed as the first pemphigus case of the three had a stubborn course of her pemphigus which was clinically active at the time of diagnosis of the remaining pemphigus cases. All patients are currently doing well on supportive treatment with oral methylprednisolone or oral methylprednisolone combined with oral dapsone.

Discussion of the issue of pemphigus triggering in relation to a cluster of pemphigus in the vicinity of the wastewater treatment plant

Living in the vicinity of the wastewater treatment plant and data of the measurement of concentration of substances incriminated to be pemphigus triggers in the air around the plant are the only hints we have concerning the evidence of exposure to the substances originating from this particular plant. Nonetheless, any in vivo provocation test as a conceivable method to get more definitive data regarding plausible industrial triggering with substances incriminated is unadvisable due to life-threatening nature of pemphigus. Importantly, since the installation of protective domes over sludge tanks (Figure 2), no new cases of pemphigus have been diagnosed in the Kozieglowy estate. Concerning the relative rarity of pemphigus type of dermatoses, the diagnosis of 2 novel cases from one estate in a short time period could be regarded purely coincidental, yet 3 novel cases led us to take a look at a possible common “seed”. Due to proximity of the wastewater treatment plant (ca. 1 km) to the housing estate located uphill 30 m above the level of the settlement tanks, considering the prevalence of western winds in the Greater Poland district [26] and terrain characteristics (slope, natural forest barrier limiting the eastern winds in the area), we suspect a common factor – presumably waterborne and/or volatile waste products. Volatile organic compounds may be dangerous for wastewater treatment plant workers and inhabitants of nearby houses [27, 28]. The highest levels of these compounds are emitted by a primary clarifier, while the concentration of selected chemicals in one reported case exceeded the regulatory threshold limit even within up to 4 km distance from the wastewater treatment plant [28].
There are theories attributing a causative role of chemical compounds in triggering/sustaining autoimmunity to their functional groups, but the precise mechanisms of action still remain to be elucidated and experimentally verified. Despite no scientific data on industrial waste-induced pemphigus, many chemical compounds were reported to induce both PV and PF, whereas the pemphigus-pollution issue is raised incidentally in non-scientific press [29–31]. Such alleged association was also suspected in court by an Australian patient formerly working as a garbage collector [32, 33]. Moreover, there is one old case report on a fatal case of acute pemphigus after putrid eel consumption (presumably due to amides) [34, 35]. Analyzing the composition of sewage, sewage gas and leachate, there are several chemical compounds that are either amides, phenolic compounds, volatile organosulfur compounds (thiols/mercaptans), sulfones or their “masked” forms that could hypothetically contribute to pemphigus pathogenesis [36–39]. Several theories were coined to give an explanation to the assumable mechanisms of chemical compound-driven autoimmunity in PV/PF. It may be suspected that the active radicals of chemical compounds or their metabolites may bind proteins to form haptens triggering T- and B-lymphocyte-related autoimmunity or alter desmosomal proteins thus giving birth to neoantigens [15].
Phenol derivatives were reported to induce acantholysis both in vitro and in vivo, after topical application and consumption [24, 40, 41]. The role of polyphenolic compounds – tannins, contained in food or water, was suggested in research articles and case reports describing fogo selvagem (“wild fire”) endemic PF [41–45]. Such phenol derivatives include liquid diphenyl sulphide [36] and various synthetic phenolic antioxidants (e.g. butylated hydroxytoluene (BHT)) [46–50]. Contemporarily, the reports on BHT and its metabolites’ disruptive activity on the human and animal endocrine system lead to focusing on better assessment and measures to lower the concentration of these compounds in ground water and sewage [47–49, 51]. Apart from the chemical structure of these phenolic compounds, they are characterized by mostly estrogenic activity. Although there is no proven sex-relation reported in either PV or PF, there were single cases indicating the possible association [52]. Due to lifestyle changes in Western countries including increased use of contraceptives (e.g. ethinylestradiol), and increased use of phosphorus organic pesticides in agriculture (that have estrogenic activity), the increased concentration of these chemicals with an estrogenic compound could promote or facilitate development of the disease. Endogenous and exogenous estrogens might play a role as one of the triggering factors or co-factor (“the soil”) in these ABDs [52–54].
Thiol compounds or mercaptans cause acantholysis in vivo and in vitro in cultured tissues [20, 40, 55]. Thiol-mediated cell-cell adhesion loss seem to be caused by direct biochemical aberration of desmosome structure itself, e.g. by inhibition of keratinocyte transglutaminase or acetylcholinesterase or forming thiol-cysteine bonds instead of cysteine-cysteine bonds making the protein dysfunctional [40, 56, 57]. However thiols also are reported to activate the proteases, and considered to bind DSGs that results in neoantigen formation that triggers the autoimmunity [57]. Hazardous volatile and waterborne compounds able to be detected in the vicinity of wastewater treatment plants and present in the sludge (semi-solid waste) and sediments usually include volatile thiols [36, 38, 58–60]. There are also industrial “masked thiols”, compounds with disulfide bridge (–S–S–), potent into forming an active sulfhydryl (–SH) group during biotransformation, e.g. dimethyl disulfide (DMDS) originating in the wastewater treatment plant from anaerobic fermentation [36, 58, 59], liquid dimethyl trisulfide, present in pemphigus-exacerbating Allium family [61] or bis 1-(methylthio)ethyl disulfide [62]. All of these compounds are theoretically able to trigger a range of pemphigus diseases (mostly PF) via ingestion or topical application due to (–SH) radical [63].
Many other mutagens and neurotoxins can be found in waste disposals and may modulate the immune system: hydrogen sulfide, heavy metals, polycyclic aromatic hydrocarbons, polychlorinated biphenyls, di(2-ethylhexyl)phthalates, polychlorinated dibenzodioxins and dibenzofurans [38, 58]. The increased skin, hair and nail concentration of mercury, known neurotoxin, was previously shown in fogo selvagem endemic PF patients [16, 64, 65]. Interestingly, antibodies to diverse neural structures were reported to be detected apart from anti-DSG1 antibodies in El-Bagre endemic PF [65]. The link between cholinergic receptors, naturally occurring in neuronal tissue, and antibodies against them detected in pemphigus patients could support the role of mercury compounds in the development of PF/PV autoimmunity.
The odour is a known stressor [66]. People living near the wastewater treatment plant may report irritation, negative mood and health problems that interfere with their daily activities. Moreover, not only are they concerned about the risk to their and their families’ health posed by the plant, but also the loss of their property value resulting from unwanted neighbourhood [67, 68]. Stress is one of the factors listed as triggers of PF/PV [69]. Thus, we cannot exclude its possible role as a common triggering factor in our 3 cases. The mechanism it drives PV/PF autoimmunity is not yet clear, yet could involve an inflammatory process called neurogenic inflammation [70].
The sewage treatment plant officials respond to odour complaints being aware of the inconvenience to neighbouring estates and are taking measures to reduce their level [38]. This policy is an effort to appear more environmental aware and people-orientated. The sludge drying beds, being the source of 77% of odours, were closed down and grassed in 2011. The other 23% originate from 4 primary clarifiers (15%), 6 aeration tanks (5%) and other hermetized facilities (3%) [38]. The protective domes were installed over the sludge tanks to limit the volatile sulphur-organic compounds. In recent years tree and bush windbreaks were planted on the slope between the sewage treatment plant and the estate to reduce intensiveness of odours emitted. The windbreaks give reduction of spreading odour movement, dispersion and dilution, collection of chemical constituents in wood, leaves and needles, and deposition of aerosols and dusts on the tree barrier on the windward side, reducing their quantity [71]. Although the concentration of phenols and mercaptans are being lowered with coke–oven gas cleaning the performance of these systems is limited, thus constant modernization/alternation to increase the effectiveness of the wastewater treatment is needed [38, 72, 73]. We suspect that topical contact with by-products originating from the wastewater treatment plant followed by systemic absorption might be responsible for the alteration of the skin structure and/or activation of immunological mechanisms leading to blister formation and acantholysis. To our best knowledge, this is the first report investigating the association between pemphigus diseases and vicinity of the wastewater treatment plant.

Conclusions

The above listed compounds belong to potential inductors of pemphigus autoimmunity. The relation between compound structures, its function groups and precise mechanism by which they act in contribution to pemphigus development remain mostly unknown. As not in every individual exposure to alleged chemical PF/PV is clinically manifesting, the development of autoimmunity might depend on combined genetic/environmental/immunologic predisposition. Due to the rarity of the disease and the existence of only a few studies dealing with the effect of the topical exposure or ingestion on induction of acantholysis, the understanding of the disease is unsatisfactory whereas the hypotheses concerning the role of chemical molecules in pemphigus are based mostly on case reports. Thus, notwithstanding other possible indistinguishable triggers of autoimmunity, we speculate that pemphigus autoimmunity previously suspected to develop after topical exposure or ingestion of culprit chemical compounds might also arise from inhalation of volatile by-products originating from the wastewater treatment plant.

Acknowledgments

A part of this review was presented as a poster at the 12th EADV Spring Symposium 2015 in Valencia, CD-ROM abstract P158.

Conflict of interest

The authors declare no conflicts of interest.

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