- freely available
Int. J. Environ. Res. Public Health 2014, 11(9), 8794-8805; doi:10.3390/ijerph110908794
Abstract: Lack of confirmation of symptoms attributed to electromagnetic fields (EMF) and triggered by EMF exposure has highlighted the role of individual factors. Prior observations indicate intolerance to other types of environmental exposures among persons with electromagnetic hypersensitivity (EHS). This study assessed differences in odor and noise intolerance between persons with EHS and healthy controls by use of subscales and global measures of the Chemical Sensitivity Scale (CSS) and the Noise Sensitivity Scale (NSS). The EHS group scored significantly higher than the controls on all CSS and NSS scales. Correlation coefficients between CSS and NSS scores ranged from 0.60 to 0.65 across measures. The findings suggest an association between EHS and odor and noise intolerance, encouraging further investigation of individual factors for understanding EMF-related symptoms.
Symptoms attributed to electromagnetic field (EMF) exposure are regarded as a subtype of idiopathic environmental intolerance (IEI). IEI is a generic term incorporating disorders attributed to the exposure to environmental factors at levels that are below known limits for toxicity, tolerated by the majority of persons, and that are not explained by other somatic or psychiatric conditions . At the WHO workshop in Prague in 2004 the expression IEI-EMF was suggested . The estimated prevalence of EMF-related symptoms ranges from 1.5 to 5%, depending on definition and geographical region [3,4,5,6,7]. Facial skin symptoms are common; as are neurasthenic and cognitive symptoms, but the reports vary considerably between individuals [3,8,9].
Afflicted persons commonly attribute their symptoms to mobile phones (MP), computer monitors, or electrical equipment in general. These intolerances are here referred to as perceived electromagnetic hypersensitivity (EHS). No direct association between EMF exposure and symptoms has been demonstrated. Instead there is support for a nocebo effect in triggering acute symptoms in IEI-EMF . The importance of individual factors has been emphasized, and associations between IEI-EMF and e.g., anxiety, depression, worry and perceived stress have been reported [9,11,12]. High attention to electrical devices with EMF exposure, likely to be triggered by negative affect, such as anxiety, may play an important role by enhancing the nocebo effect. Increased attention to one type of environmental exposure, believed to be hazardous, may result in increased attention also to other types of environmental exposure. It has been suggested that attention in EHS to a large extent is given environmental factors in general, with stress responses resulting in physiological symptoms that are attributed to factors in the environment . It is therefore of interest whether individuals with EHS to a relatively large extent are intolerant also to other environmental factors, for example to odor and noise. In using either two or three questions to assess annoyance to electrical equipment, odorants and sounds, certain individuals have been identified who report having developed intolerances to all three sources . In another study, the prevalence of disturbance from noise from neighbours, ventilation systems and traffic as well as annoyance from car exhausts and tobacco smoke was higher in individuals with EHS compared to referents . Two recent studies provide further indications of a generalized environmental hypersensitivity. From one of the studies a considerable overlap was reported in both self-reported and physician-diagnosed EHS with corresponding intolerances for odor, noise and certain buildings . In the other study, persons with IEI-EMF were found to be similar to persons who scored high when rating their sensitivity to nine other environmental exposures (including odor and noise). The similarities included various aspects of symptomology as well as illness behavior . However, the intolerances in these reviewed studies were assessed with single questions. The indications of a more general environmental intolerance in EHS call for further investigation with thorough quantification of these intolerances.
As with EHS, odor intolerance has been reported to be associated with anxiety, depression, and stress, but also with increased attention to exposure and somatic sensations as well as with modern health worries [16,17,18,19,20,21]. The similarities in symptomology and psychological profile between EMF-related symptoms and odor intolerance are found in both clinical and non-clinical settings [9,11,22,23,24]. Noise intolerance is commonly defined as an “unusual intolerance to ordinary environmental sounds” . As with other types of IEI, the etiology is not fully known, and an association with personality characteristics was suggested early on . Noise intolerance has been reported to be associated with depression, stress, tension, and elevated sensitivity to other sensory stimuli [27,28,29]. Observations suggest that individuals who report noise intolerance also report odor intolerance, which may indicate a general intolerance to external stimuli [30,31,32,33].
The main objective of this study was to compare individuals with self-reported EHS and healthy controls with respect to extent of intolerance to environmental odor/pungency and noise, by use of validated questionnaire instruments. In addition to the olfactory system that mediates odor sensations, the present assessment included intolerance to the sensation of pungency mediated by the chemosomatosensory system. For simplicity we here use the term odor intolerance when referring to both odor and pungency. Confirmation of prior findings of an association between odor and noise intolerance was also investigated. Based on earlier studies showing that anxiety, depression, worry and stress are associated with EHS as well as with intolerance to odor and noise, it was hypothesized that intolerance to odor and noise would be increased in persons with EHS. It was further hypothesized that odor intolerance would correlate with noise intolerance.
Individuals who based on a general question reported symptoms that they associated with use of MP, computer monitors or electrical equipment in general were invited to participate through advertisement in eight Swedish newspapers with potential to reach a large proportion of persons living in Sweden. Those who responded to the advertisement were mailed a questionnaire. Of 160 persons with EMF-related symptoms who responded to the advertisement, 117 agreed to participate. In addition to the general question of symptoms associated with use of MP/wireless phones, computer monitors or electrical equipment, an inclusion criterion was reporting at least one of the specific symptoms in Table 1 when using MP, computer monitors or other electronic equipment. One-hundred and fifteen of the 117 individuals fulfilled this criterion, of which 113 responded to questions about odor and noise intolerance, and thus constituted an EHS group. The prevalence of specific symptoms attributed to MP/wireless phones, computer monitors or other electronic equipment are presented in Table 1. Mean (SD) time of having had EMF-related symptoms in the EHS group was 11.2 (6.7) years.
For each of the 117 person with EMF-attributed symptoms, two controls, matched with respect to age and sex, were recruited through the Swedish population register and sent the same questionnaire. Of these 234 individuals, 106 agreed to participate. Forty-eight of these fulfilled the inclusion criterion of reporting none of the specific symptoms (Table 1) when using MP, computer monitors or other electronic equipment. The EHS and control groups are further described in Table 2. The two groups did not differ significantly in age (t-test) or sex distribution (chi2-test), but the groups did differ in employment status and work capacity (chi2-test; Table 2).
|Symptom||Mobile/Wireless Phone||Computer Monitors||Other Electronic Equipment|
|Dizziness||41 (36.3)||25 (22.1)||40 (35.4)|
|General discomfort||67 (59.3)||45 (39.8)||56 (49.6)|
|Concentration difficulties||45 (39.8)||41 (36.3)||37 (32.7)|
|Memory loss||32 (28.3)||24 (21.2)||28 (24.8)|
|Fatigue||40 (35.4)||43 (38.1)||39 (34.5)|
|Headache||52 (46.0)||38 (33.6)||36 (31.9)|
|Warmth behind/around the ear||77 (68.1)||8 (7.1)||13 (11.5)|
|Warmth on the ear||76 (67.3)||10 (8.8)||10 (8.8)|
|Burning skin||49 (43.4)||50 (44.2)||42 (37.2)|
|Tingling/tightness||39 (34.5)||43 (38.1)||36 (31.9)|
|Sleeping problems||29 (25.7)||28 (24.8)||37 (32.7)|
|Tinnitus||28 (24.8)||18 (15.9)||25 (22.1)|
|Numbness||29 (25.7)||29 (25.7)||27 (23.9)|
|Characteristic||EHS (n = 113)||Controls (n = 48)||t-/chi2-Value||p-Value|
|Age, mean (SD)||49.2 (12.5)||51.7 (11.8)||1.16||0.246|
|Female sex, n (%)||83 (73.5)||35 (72.9)||0.01||0.944|
|Employment status, n (%)||43 (38.1)||32 (66.7)||17.96||<0.001|
|Full or part time employment|
|Full or part time sick leave||25 (22.1)||3 (6.2)|
|Disability pension||30 (26.5)||3 (6.2)|
|Unemployed or retired||15 (13.3)||7 (14.6)|
|Not responding||0 (0)||3 (6.2)|
|Work capability, n (%)||8.20||0.017|
|Good||51 (58.6)||33 (84.6)|
|Moderate||17 (19.5)||3 (7.7)|
|Moderate||19 (21.8)||3 (7.7)|
2.2. Questionnaire Instruments
The questionnaire included questions about specific symptoms attributed to EMF sources (Table 1), demographics, employment status and work capacity (Table 2), time of having had EMF-related symptoms, and intolerance to odor and noise. Odor intolerance was assessed with the Chemical Sensitivity Scale (CSS) , and noise intolerance with the Noise Sensitivity Scale (NSS) . The CSS and NSS are analogous tools for quantifying self-reported affective reactions and behavioral disruptions in daily activities caused by odorous/pungent environmental substances and by noise, respectively. They consist of 21 statements each (e.g., “At movies, other persons’ perfume and aftershave disturb me” and “At movies, whispering and crinkling candy wrappers disturb me”) to be responded to on a six-point Likert scale and summed to give an overall score that ranges from 1 to 105 (high score indicating high sensitivity). Both the CSS and NSS have good test-retest reliability, internal consistency, and predictive validity, and generate approximately normal distributions [26,32,34,35]. The CSS has two subscales for each of its two dimensions . The dimension symptom type consists of the subscales sensory/somatic symptoms (13 items; e.g., “I would not mind living in an apartment that has a weak smell”) and neurasthenic symptoms (8 items; e.g., “Even food odors that I normally like will bother me if I am trying to concentrate”), and the dimension reactivity consists of the subscales negative affective reactions (12 items; e.g., “I am easily alerted by odorous/pungent substances”) and behavioral disruptions (8 items; e.g., “If it is smelly/pungent where I am studying, I try to shut it out or move someplace else”). The last item is of general character (“I am sensitive to odorous/pungent substances”). A global measure incorporates all 21 items. Each of the 21 item statements about the noise environment in the NSS have their corresponding statement about the odor environment in the CSS, being as similar as possible, and the response alternatives in the two scales are identical for each corresponding statement . It was therefore assumed that the item statements in the NSS would constitute the same four subscales of the CSS, but referring to noise environments. The internal consistency in the present study (n = 161) for the CSS and NSS, respectively, was 0.89 and 0.88 for the subscale sensory symptoms, 0.86 and 0.83 for neurasthenic symptoms, 0.87 and 0.81 for affective reactions, 0.88 and 0.89 for behavioral disruptions, and 0.94 and 0.92 for the global measures.
Nonresponders in both groups received one reminder. The data collection was carried out during a period of five months (December 2005–April 2006). Informed consent was obtained from each participant, and they were paid for their participation. Ethical approval was given by the Regional Ethical Research Board at Umeå University.
2.4. Statistical Analysis
The EHS and control groups were compared on the variables that describe participant characteristics (Table 2) using t-test and chi-square test, and on the CSS and NSS subscales and global measures using t-test (α = 0.05). Pearson correlation coefficients were calculated between scores on the CSS and NSS for the subscales and global measures for the two participant groups separately and for all participants (α = 0.01). All variables were approximately normally distributed. The statistical analyses were performed using SPSS Statistics 21 for Windows (IBM Corporation, Armonk, NY, USA).
Mean scores on the CSS and NSS for each participant group are shown in Table 3. Results from the t-tests (Table 2) show that the EHS group had significantly higher scores than the controls on the five CSS and five NSS scales. Pearson correlation coefficients between scores on the CSS and NSS for the subscales and global measures for the two participant groups separately and for all participants are given in Table 4. For the two groups the coefficients ranged between 0.54 and 0.66, and for all participants between 0.60 and 0.65. All correlations were statistically significant at p < 0.001.
|Sensitivity Scale||EHS (n = 113)||Controls (n = 48)||t-Value||p-Value|
|Sensory/somatic||32.8 (10.0)||29.5 (8.5)||2.07||0.041|
|Neurasthenic||12.5 (5.4)||10.7 (4.1)||2.31||0.023|
|Affective||39.0 (11.3)||35.4 (9.6)||2.07||0.041|
|Behavioral||21.5 (8.5)||18.4 (7.3)||2.30||0.023|
|Global||63.9 (20.3)||56.7 (16.7)||2.34||0.021|
|Sensory/somatic||34.2 (10.0)||27.5 (8.9)||4.26||<0.001|
|Neurasthenic||15.6 (5.3)||12.4 (4.6)||3.84||<0.001|
|Affective||35.4 (10.0)||29.4 (7.9)||4.04||<0.001|
|Behavioral||24.7 (8.4)||19.8 (7.4)||3.68||<0.001|
|Global||63.4 (18.8)||51.6 (15.4)||4.15||<0.001|
|Sensitivity Scale||EHS (n = 113)||Controls (n = 48)||Overall (n = 161)|
All correlations were significant at p < 0.001.
Prior research, in which environmental intolerances were assessed using only single questions, indicate that individuals with symptoms attributed to EMF may also suffer from complaints related to environmental odor and noise [3,13,14,15]. This motivated the present study using valid and reliable questionnaire instruments for quantifying odor and noise intolerance.
In accordance with the hypotheses, perceived intolerance to odor/pungency and noise was found to be more common among persons with EHS compared to healthy controls. The results correspond with previous observations of hyperresponsiveness to sensory stimuli in subjects with EHS [36,37,38]. Deviations in heart rate variability, suggesting autonomic nervous system (ANS) changes toward elevation in sympathetic tone, have been found in EHS without MP-related symptoms during rest as well as in response to induced stress; whereas a similar investigation of subjects with MP-related symptoms revealed signs of elevation in sympathetic tone only during induced stress [37,38,39].
It is of interest to note that the effects sizes, expressed as t-values, were larger for the NSS scales than for the CSS scales, suggesting that intolerance in EHS is higher for noise than for odor. A link between noise intolerance and EMF-related symptoms may pertain to tinnitus. This condition is common among patients with noise intolerance, and has been shown to be relatively common also in EMF-related symptoms [40,41]. It has been suggested that vulnerability, probably due to an over-activated cortical distress network, may be responsible for both tinnitus and EMF-related symptoms . In the present study group, the prevalence of self-reported tinnitus (not restricted to use of electrical equipment) at least on a weekly basis was as high as 35% in the EHS group, to be compared with none of the participants in the control group. However, these speculations call for further investigation.
The data suggest that persons with EHS are high on odor and noise intolerance in a broad sense, since the EHS group scored higher than the controls on all four subscales of the CSS and NSS. Thus, the intolerance to odor/pungency and noise included the subscales sensory symptoms such as annoyance and disturbance, neurasthenic symptoms such as concentration difficulties and nervousness, affective reactions such as becoming alerted and irritated, and behavioral disruptions such as shutting out the exposure and moving someplace else. Normative data is available for the CSS (but not for the NSS), which has a mean (SD) of 62.3 (15.2) . As would be expected for the normative data that is based on a population sample in which individuals with odor intolerance are not excluded, it is lower than that for the EHS group and higher than that for the control group.
The overlap between self-reported EMF-related symptoms and odor and noise intolerance favors the notion that individual factors play an important role in EMF-related symptoms. Such factors may include anxiety, depression and stress that have previously been reported in this particular group of individuals, but also ANS derangement and general hyperresponsiveness to sensory stimuli. However, importantly, the cross-sectional nature of the data does not enable conclusions about cause and effect. It cannot be excluded that anxiety, depression, stress and exhaustion, as well as physiological changes may be consequences of living with EMF-related symptoms. A second purpose of the study was to verify prior findings of an association between odor and noise intolerance. Fairly strong correlations (r = 0.60–0.65) for the five measures of intolerance based on all participants can be considered to verify earlier observations [30,32].
Data from a Swedish population-based study show that 58% of those with self-reported EHS also experienced hypersensitivity to odors, noise and/or certain buildings . Results from that study, as well as other studies [3,4,14,15,43], suggest large overlap in prevalence between environmental hypersensitivities in general. Interestingly, there is also large overlap in prevalence between environmental hypersensitivity and other forms of medically unexplained conditions for which ANS imbalance has been proposed as contributing to the clinical picture, such as fibromyalgia, chronic fatigue syndrome and irritable bowel syndrome [44,45,46]. Sensitization has been proposed as an explanatory model for many of these forms of medically unexplained symptoms . Sensitization, the increase in response to repeated exposure, is the opposite of habituation and may manifest at a cellular, systemic or cognitive level. Cognitive sensitization refers to an increased attention to symptoms and symptom-related environmental threats. At all levels sensitization may increase somatic sensations and cause or aggravate pre-existing complaints [48,49]. Sensitization has also been suggested to activate the hypothalamic-pituitary-adrenal (HPA) axis and shift the ANS activity in a direction toward hypersympathotone, explaining many of the symptoms in the medically unexplained conditions such as those mentioned . Support for effects on the HPA axis in EHS has been provided by elevated levels of arousal in EHS , and for effects on the ANS in terms of a general imbalance in its regulation in EHS [37,38,39,52]. The tight link between emotional factors (e.g., anxiety and stress), HPA axis activation, and increased sympathetic nervous system activity may explain many of the symptoms commonly reported by individuals with EMF-related symptoms (e.g., general discomfort, difficulties concentrating, memory loss, heart palpitation, paresthesia, sleeping disorders). The concept of cognitive sensitization is of interest concerning the differences in perceived intolerance to environmental factors other than EMF, such as odor and noise, and when addressing the question why EMF-related symptoms generalize in some individuals but not in others. The possibility of sensitization (based predominantly on visual and auditory cues of electrical equipment) in EHS does not exclude the possibility of a nocebo effect, and that high attention to electrical devices with potential EMF exposure may play an important role by enhancing sensitization as well as a nocebo effect. This would imply that attention in EHS to a large extent may be given environmental factors in general.
Limited representativeness in the present study calls for caution. Thus, only 46% of the invited participants from the population register agreed to participate, and the sample of EHS cases was not population-based. Rather than representing EHS cases in general, the EHS sample is likely to have had fairly severe degree of hypersensitivity attributed to EMF since the symptom prevalence, varying depending on type of symptom, in general was quite high. The prevalence ranged between 25 and 68% for MP/wireless phones, between 7 and 44% for computer monitors, and between 9 and 50% for other electric equipment (Table 1). The high symptom prevalence together with the EHS group having had EMF-related symptoms for quite a long time (on average about 11 years) may explain the relatively large proportion of the EHS cases reporting sick leave (22%) and disability pension (26%).
An implication of the present findings is that individual factors appear to play an important role in EHS/IEI-EMF. The results support the notion that different types of environmental intolerance share similar underlying mechanisms, which may possibly include a nocebo effect and sensitization, although further studies are needed to clarify these issues.
The results suggest that symptoms attributed to EMF are associated with odor/pungency and noise intolerance. Furthermore, prior findings of an association between odor and noise intolerance was verified. Taken together, the findings encourage further investigation of individual factors for understanding EMF-related symptoms as well as other types of medically unexplained symptoms.
This study was supported by grants from the Centre for Environmental Research, Umeå, the Swedish Insurance Society, the European regional cooperation program Botnia-Atlantica, Region Västerbotten (Sweden), and the Regional Council of Ostrobothnia (Finland). We are very thankful to Amanda Johansson for valuable contributions in planning the study and data collection, and for giving comments on a previous version of the manuscript. We also acknowledge Hans Pettersson and Lena Jonsson for their help with data collection, and Annika Glader for supervising the TEMA project of which this work was part.
Monica Sandström initiated the study, Monica Sandström and Steven Nordin planned the study, David Olsson and Steven Nordin conducted the statistical analyses, Steven Nordin and Gregory Neely interpreted the results, and SN drafted the manuscript which was revised by all authors.
Conflicts of Interest
The authors declare no conflict of interest.
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