1. Introduction
As technology is growing in Africa, the exposure and dose of electromagnetic frequency (EMF) to people will continue to rise. EMF pollution is currently one of the foremost environmental qualities and a problem associated with technology in Africa. Implications from electromagnetic radiation pollution exposure are in both urban and rural areas which influence human health before conception, during pregnancy, childhood, adolescence, and up to adult life [
1]. Several anthropogenic activities have resulted in the release of EMF waves, mostly into the urban environment [
2]. Technogenic sources of EMF pollution in populated places include mobile communication, electric base stations, wireless and cable Internet, radio equipment, high energy voltage transmission lines, mobile communication, research and medical devices, and others [
3]. Exposure assessment studies show that people are mostly exposed to EMF from electrical appliances and tools, power lines, and from power building supply. People who work near transformers, electrical closets, circuit boxes, or other high-current electric equipment may have 100 V/m electric field exposure. In ordinary work places such as offices, electric field levels are similar to those found at home; however, these levels may increase dramatically near certain types of equipment [
4]. All these EMF emitters are available in Malawi.
Anthropogenic activities significantly exceed natural background sources, therefore, becoming a dangerous contributing factor to the pollution of the general public and the environment. Since each electric transmission line at any base station is an EMF source, it is difficult to fully eliminate the exposure of EMF source in our living environment [
5]. The science of measuring, evaluating, and monitoring the exposure levels of EMF pollution while also qualifying the deterministic effects of such frequencies on human health has become more crucial to the public. Hence, this topic should comply as ongoing research to be conducted in Malawi. The levels of electric and magnetic exposure levels in Malawi are not known. This work and the upcoming continuous monitoring will provide information on the trends of both electric field and magnetic flux density pollution levels in Malawi. More importantly, these background measurements establish a baseline for future changes to be compared against. Research into electromagnetic pollution, shielding measures, and mitigation of biological effects is also vital to the optimization of electric transmission systems in Africa.
There are international guidelines on limits of exposure of humans to EMF pollution. Malawi has no established guidelines on this subject yet, as such, it adopted the international guidelines [
6]. It is required that each country has to set its guidelines on EMF exposure limits [
7]. It is recommended by the International Commission on Non-Ionizing Radiation Protection (ICNIRP), which is recognized by the World Health Organization (WHO) and the Institute of Electrical and Electronics Engineers (IEEE) that these exposure limits be based on a 24 h duration exposure [
8].
For a person who is standing directly under a high voltage transmission line, he or she may feel a mild shock when touching something that conducts electricity. These sensations are caused by strong electric fields from high voltage electricity in the lines. They occur only in close range vicinity because electric fields highly reduce as a function of distance. Electric fields might be shielded and rapidly weakened by buildings, trees, and other objects that conduct electricity [
9].
In Malawi, the wireless systems and base stations operate with frequencies below 500 GHz, which falls in the non-ionizing range. EMF pollution levels tend to be a function of line of sight, distance from emitting sources, and geographical structure of coverage area [
10]. The continuous monitoring and evaluation of the EMF pollution level in crowded areas with a high density of electrical power signals have become of the utmost importance. This necessitated this study in which electric field (E) and magnetic flux density (B) pollution levels were measured in 30 different locations, namely; in school campuses, hospitals, industrial areas, markets, residential and Blantyre commercial and business center (CBC) over a two-year period during morning and evening hours. Thereafter, statistical computation was carried out to map up distribution levels of both electric and magnetic flux density pollution in the studied areas.
This manuscript briefly covers anthropogenic sources of EMF, possible heathy effects of EMF, and international guidelines for EMF exposure in chapters One and Two. Chapter Three focuses on the type of method of data collection. Geographical location of the study area has also been covered in this Chapter. Results of electric field and magnetic flux density pollution levels were measured in 30 different locations and has been discussed in Chapter Four. The results have been compared to the safety guidelines published by the International Commission on Non-Ionizing Radiation Protection (ICNIRP). Statistical analysis is also presented in Chapter Four. Lastly, the conclusion and recommendations are presented in Chapter Five of the manuscript.
3. Material and Methods
This work aimed at observing the short-term electric field and magnetic flux density pollution levels in frequency band of electromagnetic exposure in school campuses, hospitals, industrial areas, markets, residential areas, and Blantyre CBC in Malawi. The measurements of electric field and magnetic flux density pollution of low and high radiofrequency origin electromagnetic waves broadcast in 30 different locations, with 2000 m intervals with highest population clusters, throughout the city of Blantyre in Malawi were performed. Trifield EMF meter model TF2 Handheld Spectrum Analyzer was used to obtain the measurements. Each measurement at a location lasted for 360 sec (6 min), which is standard measurement set by ICNIRP for a scientific meaningful result [
22]. Maximum electric field and magnetic flux density were recorded with a repetition of three times and then the average value was computed. The measurements of the electric field and magnetic flux density pollution were carried out twice in a day between 10:00 and 12:00 h and 17:00 and 19:00 h. There is more power consumption during the hours of 10:00–12:00 and minimum electric power consumption between 17:00 and 19:00 h in Malawi. It was expected that mobility of people is high and most electrical devices are on during these hours.
It the data analysis, we used the Wilcoxon Signed Rank test to see if there were any significant differences in the median values of two related paired samples. This is a nonparametric test that compared the sum of ranks of absolute differences between paired observations to a critical value, also known as the p-value. Furthermore, we used the Kruskal Wallis test, a nonparametric test that compares the sum of ranks of the observations in each group, to find out the critical value or p-value, to see if there were significant differences in the median values of three or more independent groups based on ordinal or continuous data. This test was used to compare the efficacy of five different treatment groups on our outcome variable.
The map of measurement locations selected in Blantyre City has been presented in
Figure 1 and
Figure 2, showing some technogenic sources of EMF pollution in one of the residential monitored areas.
4. Results and Analysis
The recorded maximum values of electric field (
EMax) and magnetic flux density (
BMax) of the statistical analysis are presented in
Table 4,
Table 5,
Table 6,
Table 7,
Table 8 and
Table 9. From the results, it was shown that the
Emax and
Bmax values in all monitored locations for morning and evening hours were smaller than the public upper exposure limits as defined by ICNIRP of 4.2 kV/m and 2 G respectively. Nevertheless, the fact that recorded values were below the ICNIRP and WHO maximum electric field and magnetic flux density exposure limit values, does not imply that this is totally harmless. Furthermore, cumulative exposure time is much more important as long as intensity of the pollution exposure in concerned.
As shown in
Table 4 and
Table 6, the maximum values of recorded electric field at SCH 1, SCH 4, HSP 4, and IND 5 locations were higher, which also corresponded to higher magnetic flux density. This may be due to the fact that these locations are closer to electric base stations and that some intensive radiative devices were on at the time of monitoring. The average measured value of
E between 10:00 and 12:00 local time in Blantyre was 249.24 mV/m, and between 17:00 and 19:00 local time was 207.85 mV/m. Similarly, maximum short-range results for
B were 0.073 G between 10:00 and 12:00 and 0.057 G between 17:00 and 19:00 which was below the public limits of 2 G for public exposure.
From the monitored results, schools and hospitals showed that for both electric and magnetic pollution, measurements taken between 10:00 h and 12:00 h were generally higher compared to those taken between 17:00 h and 19:00 h. However, the measurements taken at industrial areas, market places, residential areas, and Blantyre CBD suggest slight differences between 10:00 h and 12:00 h and 17:00 h and 19:00 h for both electric and magnetic pollution. To determine whether there was a significant difference in electric and magnetic measurements within and across these locations, we used Wilcoxon Signed Rank test and Kruskal Wallis test. It was observed that there was no significant difference between the electric and magnetic measurements taken from 10:00 h to 12:00 h and 17:00 h to 19:00 h for schools, hospitals, industries, markets, residential, and Blantyre CBD (
p-values > 0.05,
Table 10).
The comparison of the electric field and magnetic flux density measurements across the locations was carried out to see if a particular location provided different measurements compared to the other locations. The results reveal that the electric field experienced by all the six locations was the same, that is, hospitals, schools, industries, markets, residential areas, and Blantyre CBC receive the same effect (
p = 0.243,
Table 11) for measurements carried out between 10:00 h and 12:00 h. For magnetic flux density in all the six cluster locations, the effect was also the same (
p = 0.257,
Table 12). There is no significant difference in measurements for both electric and magnetic flux density carried out from 17:00 h to 19:00 h among the six locations. Hospitals, schools, industries markets, residential, and Blantyre CBD receive the same effect between 17:00 h and 19:00 h (
p = 0.700,
Table 11 and
p = 0.632,
Table 12).
5. Conclusions
This study focused on electric and magnetic pollution measurements in the city of Blantyre, Malawi. The levels of electric and magnetic pollution were compared with the upper safe limits determined by ICNIRP, IEEE, and WHO for public exposure. It was observed that there were no significant differences between the electric and magnetic measurements taken from 10:00 h to 12:00 h and 17:00 h to 19:00 h for schools, hospitals, industries, markets, residential, and Blantyre CBD (p-values > 0.05). The average measured value of E between 10:00 and 12:00 local time in Blantyre was 249.24 mV/m, and between 17:00 and 19:00 local time was 207.85 mV/m. Similarly, maximum short-range results for H were 0.073 G between 10:00 and 12:00 and 0.057 G between 17:00 and 19:00, which was below the public limits of 2 G for public exposure. However, cumulative doses of both electric and magnetic pollution exposure still remain a threat to the people of Blantyre. Although the measured electric and magnetic values were lower than the exposure limits defined by international institutions, it is imperative to minimize the duration of EMF exposures to the citizenry as well as the intensity of EMF exposures to radiation as this leads to dynamic cumulative doses. Most importantly, background measurements from this study establish a baseline for future changes to be compared against.
This study proposes a standard novel mathematical empirical model for the characterization of the total electric and magnetic pollution. Additionally, a long-term measurement study of electric and magnetic pollution in different frequency bands should be conducted. Furthermore, the community awareness and participation programs (CAPPs) about health risks that could originate from exposure of electric and magnetic waves should be encouraged in Malawi. The country may adopt current electric and magnetic exposure guidelines ICNIRP 2010 to protect the public.