Dear James I would like to add the following quotes from research papers attached to my earlier submission. From : Electromagnetic pollution from phone masts. Effect on wildlife by Alfonso Balmori. Director General of Natural medicine, Council of environmental health in Spain. He concludes: “In light of current knowledge there is enough evidence of serious effects from this technology to wildlife. For this reason precautionary measures should be developed, alongside environmental impact assessments prior to installation, and a ban on installation of phone masts in protected natural areas and in places where endangered species live.” It should be remembered this mast will be covering the Bradford on Avon Country Park where it has been reported 14 species of bat live, which are protected species by UK law. From : Impacts of radio-frequency electromagnetic field (RF-EMF) from cell phone towers and wireless devices on biosystem and ecosystem – a review by S. Sivani and D Sudarsanam published in 2013. They report that “The Ministry of environment and forestry in India set up an inter-ministerial committee who reported in 2010 that there were: 919 research papers covering the effects on wildlife collected 593 (65%) showed negative impacts 180 (19.5%) showed no impact 196 (21%) were inconclusive so could not state if there was an effect or not. I attach copies of the papers for your files. This just goes to show the absolute need for the applicant to provide good quality peer reviewed research by scientists with cross functional expertise in both the science of electromagnetic radiation and in the biological science of the relevant species of bats in the Country Park that must be protected before any planning approval is considered or granted. Regards Richard Ross 78 Bath Road Bradford on Avon COMMENTS ON NOTICE OF INQUIRY ET DOCKET 13-84 eISSN: 09748369 Impacts of radio-frequency electromagnetic field (RF-EMF) from cell phone towers and wireless devices on biosystem and ecosystem – a review Biology and Medicine Review Article Volume 4, Issue 4, Pages 202–216, 2012 Review Article Biology and Medicine, 4 (4): 202–216, 2012 www.biolmedonline.com Impacts of radio-frequency electromagnetic field (RF-EMF) from cell phone towers and wireless devices on biosystem and ecosystem – a review S Sivani*, D Sudarsanam Department of Advanced Zoology and Biotechnology, Loyola College, Chennai, Tamil Nadu, India. *Corresponding Author: [email protected] Accepted: 3rd Dec 2012, Published: 6th Jan 2013 Abstract This paper summarizes the effect of radio-frequency electromagnetic field (RF-EMF) from cell towers and wireless devices on the biosphere. Based on current available literature, it is justified to conclude that RF-EMF radiation exposure can change neurotransmitter functions, blood-brain barrier, morphology, electrophysiology, cellular metabolism, calcium efflux, and gene and protein expression in certain types of cells even at lower intensities. The biological consequences of such changes remain unclear. Short-term studies on the impacts of RF-EMF on frogs, honey bees, house sparrows, bats, and even humans are scare and long-term studies are non-existent in India. Identification of the frequency, intensity, and duration of non-ionizing electromagnetic fields causing damage to the biosystem and ecosystem would evolve strategies for mitigation and would enable the proper use of wireless technologies to enjoy its immense benefits, while ensuring one’s health and that of the environment. Keywords: Radio-frequency electromagnetic field; cell phone tower; power density; SAR; non-ionizing radiation; non-thermal. Introduction There has been an unprecedented growth in the global communication industry in recent years which has resulted in a dramatic increase in the number of wireless devices. Mobile services were launched in India in 1995 and it is one of the fastest growing mobile telephony industries in the world. According to the Telecom Regulatory Authority of India (TRAI, 2012), the composition of telephone subscribers using wireless form of communication in urban area is 63.27% and rural area is 33.20%. By 2013, it is estimated that more than one billion people will be having cell phone connection in India. This has led to the mushrooming of supporting infrastructure in the form of cell towers which provide the link to and from the mobile phone. With no regulation on the placement of cell towers, they are being placed haphazardly closer to schools, creches, public playgrounds, on commercial buildings, hospitals, college campuses, and terraces of densely populated urban residential areas. Hence, the public is being exposed to continuous, low intensity radiations from these towers. Since the BMID: BM-8 electromagnetic radiations, also known as electrosmog cannot be seen, smelt or felt, one would not realize their potential harm over long periods of exposure until they manifest in the form of biological disorders. Various studies have shown the ill-effects of radio-frequency electromagnetic field (RF-EMF) on bees, fruit flies, frogs, birds, bats, and humans, but the long-term studies of such exposures are inconclusive and scarce, and almost non-existent in India (MOEF, 2010; DoT, 2010). In 2011, International Agency for Research on Cancer (IARC), part of WHO, designated RF-EMF from cell phones as a “possible human carcinogen” Class 2B (WHO, 2011). Cancer, diabetes, asthma, infectious diseases, infertility, neurodegenerative disorders, and even suicides are on the rise in India. This invisible health hazard pollution (IHHP) is a relatively new environmental threat. Electromagnetic radiation, in the form of waves of electric and magnetic energy, have been circulating together through space. The electromagnetic spectrum includes radio waves, microwaves, infrared rays, light rays, ultraviolet rays, X-rays, and gamma rays (ARPANSA, 2011; 202 Review Article Biology and Medicine, 4 (4): 202–216, 2012 Power Density and Specific Absorption Rate (SAR) FCC, 1999). The electromagnetic radiations are of two types, one being ionizing radiations such as X-rays and gamma rays, and the other being non-ionizing radiations such as electric and magnetic fields, radio waves, radio-frequency band which includes microwaves, infrared, ultraviolet, and visible radiation (Figure 1). The biological effects of RF-EMF at molecular level induce thermal and non-thermal damage, which may be due to dielectric heating leading to protein denaturation, polar molecular agitation, cellular response through molecular cascades and heat shock proteins, and changes in enzyme kinetics in cells (Instituto Edumed, 2010). The three major physical parameters of RF-EMF radiations is frequency, intensity, and exposure duration. Although the non-ionizing radiations are considered less dangerous than ionizing radiation, over-exposure can cause health hazards (FCC, 1999). Variables used in the measurement of these radiations are power density, measured in watts per meter squared (W/m2) and specific absorption Rate (SAR). The term used to describe the absorption of RF-EMF radiation in the body is SAR, which is the rate of energy that is actually absorbed by a unit of tissue, expressed in watts per kilogram (W/kg) of tissue. The SAR measurements are averaged either over the whole body or over a small volume of tissue, typically between 1 and 10 g of tissue. SAR was set with the help of a phantom, known as specific anthropomorphic mannequin (SAM) derived from the size and dimensions of the 90th percentile large adult male reported in a 1988 US Army study who is 6 feet 2 inches and weighed 200 pounds (Davis, 2010). SAR is set at 1.6 W/kg averaged over 1 g of body tissue in the US and Canada and 2 W/kg averaged over 10 g of body tissue in countries adopting the ICNIRP guidelines. The SAR is used to quantify energy absorption to fields typically between 100 kHz and 10 GHz and encompasses radio-frequency radiation from devices such as cellular phones up through diagnostic magnetic resonance imaging (MRI). The biological effects depend on how much of the energy Electromagnetic Spectrum and RF-EMF Radiation The RF-EMF radiations fall in the range of 10 MHz–300 GHz. Cell phone technology uses frequencies mainly between 800 MHz and 3 GHz and cell tower antenna uses a frequency of 900 or 1800 MHz, pulsed at low frequencies, generally known as microwaves (300 MHz–300 GHz). Non-ionizing Ionizing Radio-frequencies Visible light Radio and television Power lines Microwaves Ultraviolet Infrared X-rays Gamma rays Cellular radio Frequency (Hz) 2 Energy (eV) 3 4 5 10 10 10 10 −13 10 −12 10 −11 6 10 −10 10 10 7 10 −9 10 8 9 10 11 12 10 10 10 10 10 10 10 −8 −7 −5 −4 −2 10 −6 10 10 −3 10 10 10 10 13 14 10 0.1 15 10 16 10 1 10 10 2 17 10 18 19 10 10 3 4 10 10 20 21 10 5 22 10 10 6 10 10 7 10 23 10 8 24 10 9 10 10 10 10 10 25 10 26 10 11 Figure 1: Electromagnetic spectrum from the Federal Communications Commission (FCC), OET Bulletin 56, 1999. BMID: BM-8 203 Review Article Biology and Medicine, 4 (4): 202–216, 2012 is absorbed in the body of a living organism, not just what exists in space. Absorption of RF-EMF radiations depend on frequency of transmission, power density, distance from the radiating source and the organism’s size, shape, mineral, and water content. Exposure will be lower from towers under most circumstances than from cell phones because the transmitter is placed directly against the head during cell phone use whereas proximity to a cell tower will be an ambient exposure at a distance (Levitt and Lai, 2010). Exposure guidelines for RF protection had adopted the value of 4 W/kg averaged over the whole body (SARWB) as the threshold for the induction of adverse thermal effects associated with an increase of the body core temperature of about 18C in animal experiments. This standard is set by International Commission on Nonionizing Radiation Protection (ICNIRP), national Radiological Protection Board (NRPB), and Institute of Electrical and Electronics Engineers (IEEE) (Barnes and Greenebaum, 2007). Cell Phones and Cell Tower Standards in India India has adopted ICNIRP guidelines as the standard for safety limits of exposure to radiofrequency energy produced by mobile handsets for general public as follows: whole-body average SAR of 0.08 W/kg, localized SAR for head and trunk of 2 W/kg, and localized SAR for limbs 4 W/kg. The basic restrictions/proper limits for power density specified in ICNIRP guidelines for safe frequencies between 400 and 2000 MHz, adopted in India, for occupational exposure is 22.5 W/m2, and general public is 4.5 W/m2 for 900 MHz (ICNIRP, 1998). Antennas of cell tower transmit in the frequency range of 869–890 MHz for CDMA, 935–960 MHz for GSM-900, 1805–1880 MHz for GSM-1800, and 2110–2170 MHz for 3G. Wi-Fi frequency range is 2.4 GHz, WiMAX is 2.5–3.3 GHz, and 4G LTE is 2.99 GHz. The antennas for cellular transmissions are typically located on towers mounted on terraces of houses, apartments or other elevated structures including rooftops and the sides of buildings, and also as a freestanding tower. Typical heights for cell towers are 50–200 feet. Sector antennas for 2G and 3G transmission, broader sector antennas for 4G transmission, and parabolic microwave antennas for point-to-point communications are used in urban and suburban areas (Table 1). There are different types of base stations used by operators in India and they include the macro cell, micro cell, or pico cell. Categorization is based on the purpose of the site rather than in terms of technical constraints such as radiated power or antenna height. In India, macro cellular base station provide the main infrastructure for a mobile phone network and their antennas are mounted at sufficient height to give them a clear view over the surrounding geographical area. The maximum power for individual macro cellular base station transmitter is 20 W. According to FCC (1999), depending on the cell tower height, the majority of cellular base stations in urban and suburban areas operate at an effective radiated power (ERP) of 100 W per channel or less. ERP is a quantity that takes into consideration transmitter power and antenna directivity. An ERP of 100 W corresponds to an actual radiated power of about 5–10 W, depending on the type of antenna used. In urban areas, an ERP of 10 W per channel (corresponding to a radiated power of 0.5–1 W) or less is commonly used. In India, cell tower sites transmit hundreds of watts of power with antenna gain of 50, so ERP sometimes equals 5000 W (Kumar, 2010). For installation of mobile towers, the standing advisory committee on radio frequency Table 1: Radio-frequency sources in India. RF source Operating frequency Transmission powers Numbers AM towers 540–1600 kHz 100 KW 197 towers FM towers 88–108 MHz 10 KW 503 towers TV towers 180–220 MHz 40 KW 1201 towers Cell towers 800, 900, 1800 MHz 20 W 5.4 lakh towers Mobile phones GSM-1800/CDMA GSM-900 1 W 2 W 8001 million Wi-Fi 2.4–2.5 GHz 10–100 mW Wi-Fi hot spots BMID: BM-8 204 Review Article Biology and Medicine, 4 (4): 202–216, 2012 allocations (SACFA) clearances are issued by the wireless monitoring organization, Department of Telecommunications (DoT), after getting no objection from defence and airport authority considering aviation hazards, obstruction to line of sight of existing/planned networks and interferences. In many metros in India, there is no restriction on the location of the towers leading to a situation of overlapping of towers, where even more than 30 cell towers can be seen within 1 km2. As mobile technology progresses, the data demands on mobile network increases, coupled with lower costs, their use has increased dramatically and the overall levels of exposure of the population as a whole had increased drastically. Table 2 gives the reference levels for general public exposure adopted by various countries and organizations. Impacts on Biosystem and Ecosystem Every living being is tuned into the earth’s electromagnetism and uses it for various purposes. A natural mineral magnetite, which is found in living tissues, seems to play an important role. These magnetite crystals are found in bacteria, protozoa, teeth of sea mollusks, fish and sea mammals, eye and beak of birds, and in humans. They are also found in the ethmoid bone above the eye and sinuses and blood-brain barrier (Warnke, 2007). Migratory birds rarely get lost, but sometimes there are disruptions due to storms and magnetic disturbances caused by man (Kirschvink et al., 2001). The traditional and most effective approach to study cause–effect relationships in biological sciences is by experimentation with cells and organisms. The areas of enquiry and experimentation of in vitro studies include genotoxicity, cancer-related gene and protein expression, cell proliferation and differentiation, and apoptosis and in vivo studies include thermal effects, animal behavior, brain biochemistry, neuropathology, teratogenicity, reproduction and development, immune function, blood-brain barrier, visual auditory systems and effects on genetic material, cell function, and biochemistry (Repacholi and Cardis, 2002). In human health studies, concerns have been expressed about the possible interactions of RF-EMF with several human organ systems such as nervous, circulatory, reproductive, and endocrine systems. In order to reveal the global effects of RF-EMF on gene and protein expression, transcriptomics, Table 2: Reference levels for the general public. Power density (W/m2) Country/organization Standards 900 MHz 1800 MHz ICNIRP, 1998, adopted by India 4.5 9 FCC, 1999 6 10 IEEE, USA, 1999 6 12 Australia 2 2 Belgium 1.1 2.4 Italy 1 1 Israel x 1 New Zealand x 0.5 China x 0.4 Russia x 0.2 Hungary 0.1 0.1 Toronto Board of Health, Canada, 1999 0.06 0.1 Switzerland 0.04 0.1 France x 0.1 Germany, ECOLOG, 1998 x 0.09 Austria’s precautionary limit 0.001 0.001 BMID: BM-8 205 Review Article and proteomics as high-throughput screening techniques (HTSTs), were eventually employed in EMF research with an intention to screen potential EMF responsive genes and/or proteins without any bias (Nylund and Leszczynski, 2004). The safety standards set by ICNIRP, adopted by India, has only taken into account the short-term effects and not against the biological effects from long-term, non-thermal, low-level microwave exposure from mobile phones, cell phone towers, and many other wireless devices. Biology and Medicine, 4 (4): 202–216, 2012 also be affected by RF-EMF. Some studies have found both growth stimulation and dieback. The browning of tree tops is often observed near cell towers, especially when water is near their root base. The tree tops are known as RF waveguides. In fact, military applications utilize this capability in trees for low-flying weapon systems. In an observational study, it was found that the output of most fruit-bearing trees reduced drastically from 100% to ,5% after 2.5 years of cell tower installation in a farm facing four cell towers in Gurgaon–Delhi Toll Naka (Kumar and Kumar, 2009). Current Research Various studies have shown that even at low levels of this radiation, there is evidence of damage to cell tissue and DNA, and it has been linked to brain tumors, cancer, suppressed immune function, neuroendocrine disruption, chronic fatigue syndrome, and depression (Rogers, 2002; Milham, 2010). Oncogenesis studies at molecular and cellular levels due to RF-EMF radiations are considered particularly important (Marino and Carrubba, 2009). Orientation, navigation, and homing are critical traits expressed by organisms ranging from bacteria through higher vertebrates. Across many species and groups of organisms, compelling evidence exists that the physical basis of this response is tiny crystals of single-domain magnetite (Fe3O4) (Kirschvink et al., 2001). All magnetic field sensitivity in living organisms, including elasmobranch fishes, is the result of a highly evolved, finely-tuned sensory system based on single-domain, ferromagnetic crystals. Animals that depend on the natural electrical, magnetic, and electromagnetic fields for their orientation and navigation through earth’s atmosphere are confused by the much stronger and constantly changing artificial fields created by technology and fail to navigate back to their home environments (Warnke, 2007). Studies on Plants Tops of trees tend to dry up when they directly face the cell tower antennas and they seem to be most vulnerable if they have their roots close to the water (Belyavskaya, 2004). They also have a gloomy and unhealthy appearance, possible growth delays, and a higher tendency to contract plagues and illnesses. According to Levitt (2010), trees, algae, and other vegetation may BMID: BM-8 Studies on Insects Monarch butterflies and locusts migrate great distances using their antennae to sense air currents and earths electromagnetic fields. Moths are drawn to light frequencies. Ants, with the help of their antennas are adept at electrical transmission and found to respond to frequencies as low as 9 MHz. Flying ants are very sensitive to electromagnetic fields (Warnke, 2007). Bees have clusters of magnetite in the abdominal areas. colony collapse disorder (CCD) was observed in beehives exposed to 900 MHz for 10 minutes, with sudden disappearance of a hive’s inhabitants, leaving only queen, eggs, and a few immature workers behind. With navigational skills affected, worker bees stopped coming to the hives after 10 days and egg production in queen bees dropped drastically to 100 eggs/day compared to 350 eggs (Sharma and Kumar, 2010). Radiation affects the pollinators, honeybees, whose numbers have recently been declining due to CCD by 60% at US West Coast apiaries and 70% along the East Coast (Cane and Tepedino, 2001). CCD is being documented in Greece, Italy, Germany, Portugal, Spain, and Switzerland. Studies performed in Europe documented navigational disorientation, lower honey production, and decreased bee survivorship (Kimmel et al., 2007). EMFs from telecommunication infrastructure interfere with bees’ biological clocks that enable them to compensate properly for the sun’s movements, as a result of which, may fly in the wrong direction when attempting to return to the hive (Rubin et al., 2006). Bee colonies irradiated with digital enhanced cordless communications (DECT) phones and mobile handsets had a dramatic impact on the behavior of the bees, namely by inducing the worker 206 Review Article piping signal. In natural conditions, worker piping either announces the swarming process of the bee colony or is a signal of a disturbed bee colony (Favre, 2011). A study by the University of Athens on fruit flies exposed to 6 minutes of 900 MHz pulsed radiation for 5 days showed reduction in reproductive capacity (Panagopoulos et al., 2004). Likewise in 2007, in both 900 and 1800 MHz, similar changes in reproductive capacity with no significant difference between the two frequencies were observed (Panagopoulos et al., 2007). In a third study, it was found it was due degeneration of large numbers of egg chambers after DNA fragmentation (Panagopoulos et al., 2010). When Drosophila melanogaster adult insects were exposed to the radiation of a GSM 900/1800 mobile phone antenna at different distances ranging from 0 to 100 cm, these radiations decreased the reproductive capacity by cell death induction at all distances tested (Levengood, 1969). Studies on Amphibians and Reptiles Salamanders and turtles have navigational abilities based on magnetic sensing as well as smell. Many species of frogs have disappeared all over the world in the last 3–5 years. Amphibians can be especially sensitive because their skin is always moist, and they live close to, or in water, which conducts electricity easily (Hotary and Robinson, 1994). Toads when exposed to 1425 MHz at a power density of 0.6 mW/cm2 developed arrhythmia (Levitina, 1966). Increased mortality and induced deformities were noted in frog tadpoles (Rana temporaria) (Levengood, 1969). It was observed that experimental tadpoles developed more slowly, less synchronously than control tadpoles, remain at the early stages for a longer time, developed allergies and that EMF causes changes in the blood counts (Grefner et al., 1998). In a two-month study in Spain in common frog tadpoles on the effects of mobile phone mast located at a distance of 140 m noted low coordination of movements, an asynchronous growth, resulting in both big and small tadpoles, and a high mortality (90%) in exposed group. For the unexposed group in Faraday cage, the coordination of movements was normal, the development was synchronous, and a mortality of 4.2% was obtained (Balmori, 2009). In the eggs and embryos of Rana sylvatica and Ambystoma maculatum abnormalities at BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 several developmental stages were noted such as microcephalia, scoliosis, edema, and retarded growth. Tadpoles developed severe leg malformations and extra legs, as well as a pronounced alteration of histogenesis which took the form of subepidermal blistering and edema. Effects were noted in reproduction, circulatory, and central nervous system, general health and well being (Balmori, 2010; Balmori, 2005). Studies on Birds A study by the Centre for Environment and Vocational Studies of Punjab University noted that embryos of 50 eggs of house sparrows were damaged after being exposed to mobile tower radiation for 5–30 minutes (MOEF, 2010). Observed changes included reproductive and coordination problems and aggressiveness. Tower-emitted microwave radiation affected bird breeding, nesting, and roosting in Valladolid, Spain (US Fish & Wildlife Service, 2009). House sparrows, white storks, rock doves, magpies, collared doves exhibited nest and site abandonment, plumage deterioration (lack of shine, beardless rachis, etc.), locomotion problems, and even death among some birds. No symptoms were observed prior to construction of the cell phone towers. According to Balmori, plumage deterioration and damaged feather are the first signs of weakening, illnesses, or stress in birds. The disappearance of insects, leading to lack of food, could have an influence on bird’s weakening, especially at the first stages in young bird’s life. In chick embryos exposed to ELF pulsed EMR, a potent teratogenic effect was observed, leading to microphthalmia, abnormal trunkal torsion, and malformations on the neural tube (Lahijani and Ghafoori, 2000). White storks were heavily impacted by the tower radiation during the 2002–2004 nesting season in Spain. Evidence of a connection between sparrow decline in UK and the introduction of phone mast GSM was established (Balmori, 2009). In a study in Spain, the effects of mobile phone mast has been noted in house sparrow (Passer domesticus), white stork (Ciconia ciconia), reporting problems with reproduction, circulatory, and central nervous system, general health and well-being (microwave syndrome) (Balmori, 2009). Deformities and deaths were noted in the domestic chicken embryos subjected to low-level, non-thermal radiation from the standard 915 MHz cell phone 207 Review Article frequency under laboratory conditions (US Fish & Wildlife Service, 2009). Neural responses of Zebra Finches to 900 MHz radiation under laboratory conditions showed that 76% of the neurons responded by 3.5 times more firings (Beason and Semm, 2002). Eye, beak, and brain tissues of birds are loaded with magnetite, sensitive to magnetic fields, interferes with navigation (Mouritsen and Ritz, 2005). Studies on Mammals In a survey of two berry farms in similar habitats in Western Massachusetts (Doyon, 2008), one with no cell phone towers, there were abundant signs of wildlife, migrating and resident birds, bats, small and large mammals, and insects including bees and the other farm with a cellphone tower located adjacent to the berry patch, virtually no signs of wildlife, tracks, scat, or feathers were noted. The berries on bushes were uneaten by birds and insects and the berries that fell to the ground were uneaten by animals. Whole body irradiation of 20 rats and 15 rabbits at 9.3 GHz for 20 minutes revealed statistically significant changes in cardiac activity (Repacholi et al., 1998). Bradycardia developed in 30% of the cases. Separate ventricular extra systoles also developed. In a study on cows and calves on the effects of exposure from mobile phone base stations, it was noted that 32% of calves developed nuclear cataracts, 3.6% severely. Oxidative stress was increased in the eyes with cataracts, and there was an association between oxidative stress and the distance to the nearest mast (Hässig et al., 2009). It was found that at a GSM signal of 915 MHz, all standard modulations included, output power level in pulses 2 W, specific absorption rate (SAR) 0.4 mW/g exposure for 2 hours, 11 genes were up-regulated and one down-regulated, hence affected expression of genes in rat brain cells (Belyaev et al., 2006). The induced genes encode proteins with diverse functions including neurotransmitter regulation, blood-brain barrier (BBB), and melatonin production. When rats were exposed for 2 hours a day for 45 days at 0.21 mW/cm2 power density SAR (0.038 W/kg), a significant decrease in melatonin and increase in both creatine kinase and caspase 3 was found (Kesari et al., 2011). This shows that chronic exposure to these radiations may be an indication of possible BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 tumor promotion. A study on pregnant rats and brains of fetal rats was carried out after irradiating them with different intensities of microwave radiation from cellular phones for 20 days three times a day. Superoxide dismutase (SOD), glutathione peroxidase (GSH-Px), malondialdehyde (MDA), noradrenaline (NE), dopamine (DA), and 5-hydroxyindoleacetic acid (5-HIAA) in the brain were assayed. The significant content differences of noradrenaline and dopamine were found in fetal rat brains (Jing et al., 2012). A study in rabbits exposed to continuous wave and pulsed power at 5.5 GHz found acute effects in the eyes, where lens opacities developed within 4 days (Birenbaum et al., 1969). Behavioral tasks, including the morris water maze (MWM), radial arm maze, and object recognition task have been extensively used to test cognitive impairment following exposure of rodents to mobile phone radiation (GSM 900 MHz) on various frequencies and SAR values (Fragopoulou et al., 2010). Exposed animals in most of the cases revealed defects in their working memory possibly due to cholinergic pathway distraction. Mobile phone RF-EMF exposure significantly altered the passive avoidance behavior and hippocampal morphology in rats (Narayanan et al., 2010). With regards to DNA damage or cell death induction due to microwave exposure, in a series of early experiments, rats were exposed to pulsed and continuous-wave 2450 MHz radiation for 2 hours at an average power density of 2 mW/cm2 and their brain cells were subsequently examined for DNA breaks by comet assay. The authors found a dose-dependent (0.6 and 1.2 W/kg whole body SAR) increase in DNA single-strand and double-strand breaks, 4 hours after the exposure to either the pulsed or the continuous-wave radiation. The same authors found that melatonin and PBN (N-tertbutyl-alpha-phenylnitrone) both known free radical scavengers, block the above effect of DNA damage by the microwave radiation (Lai and Singh, 1995, 1996, 1997). Death in domestic animals like hamsters and guinea pigs were noted (Balmori, 2003). Bats use electromagnetic sensors in different frequencies. Since 1998, a study on a free-tailed bat colony, having Tadarida teniotis and Pipistrellus pipistrellus has been carried out in Spain and a decrease in number of bats were noted with several phone masts 80 m from the colony. A dead specimen of Myotis myotis was found near a small antenna in the city centre (Balmori, 2009). 208 Review Article The most affected of the species are bees, birds, and bats and without these pollinators visiting flowers, 33% of fruits and vegetables would not exist, and as the number of pollinators decline, the agricultural crops will fall short and the price of groceries will go up (Kevan and Phillips, 2001). Studies on Humans The exposure to continuous RF-EMF radiation poses a greater risk to children, particularly due to their thinner skulls and rapid rate of growth. Also at risk are the elderly, the frail, and pregnant women (Cherry, 2001). DNA damage via free radical formation inside cells has also been recorded (Lai and Singh, 1996). Free radicals kill cells by damaging macromolecules such as DNA, protein, and membrane are carcinogenic. In fact, EMR enhances free radical activity. Single- and double-strand DNA breaks are seen in rat brain cells after acute exposure to radiofrequency electromagnetic radiation. Kane (2001) denotes that RF-EMF radiations lead to tissue damage, DNA damage, or chromosome mutations. In 2008, the Austrian Department of Health found a higher risk of cancer among people living within 200 m of a mobile phone base station and that cancer risk rose with increasing exposure, reaching 8.5 times the norm for people most exposed. From a study on in vitro cell response to mobile phone radiation (900 MHz GSM signal) using two variants of human endothelial cell line, it was suggested that the cell response to mobile phone radiation might be genome- and proteome-dependent. Therefore, it is likely that different types of cells and from different species might respond differently to mobile phone radiation or might have different sensitivity to this weak stimulus (Nylund and Leszczynski, 2006). The results of the interphone, an international case–control study to assess the brain tumor risk in relation to mobile telephone use, reveals no overall increase in risk of glioma or meningioma but there were suggestions of an increased risk of glioma at the highest exposure levels (30 minutes per day of cell phone use for 8–10 years) and ipsilateral exposures (ICNIRP, 2011). Children and young adults were excluded from the study and a separate study called MobiKids is underway. According to Santini et al. (2002), comparisons of complaints in relation with distance from base station show significant BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 increase as compared to people living greater than 300 m or not exposed to base station, till 300 m for tiredness, 200 m for headache, sleep disturbance, and discomfort, and 100 m for irritability, depression, loss of memory, dizziness, and libido decrease. Women significantly more often than men complained of headache, nausea, loss of appetite, sleep disturbance, depression, discomfort, and visual perturbations (Santini et al., 2002). According to Oberfeld et al. (2004) in Spain, a follow-up study found that the most exposed people had a higher incidence of fatigue, irritability, headaches, nausea, loss of appetite, sleeping disorders, depression, discomfort, difficulties concentrating, memory loss, visual disorders, dizziness, and cardiovascular problems. Women are more at risk as they tend to spend more time at home and are exposed to radiation continuously. The authors recommended a maximum exposure of 0.0001 µW/cm2 or 0.000001 W/m2. There was prevalence of neuropsychiatric complaints among people living near base stations (Abdel-Rassoul et al., 2007). Urban electromagnetic contamination (electrosmog) 900 and 1800 MHz pulsated waves interfere in the nervous system of living beings (Hyland, 2000). Growing amounts of published research show adverse effects on both humans and wildlife far below a thermal threshold, usually referred to as “non-thermal effects”, especially under conditions of longterm, low-level exposure (Levitt and Lai, 2010). Australian research conducted by De Iuliis et al. (2009) by subjecting in vitro samples of human spermatozoa to radio-frequency radiation at 1.8 GHz and SAR of 0.4–27.5 W/kg showed a correlation between increasing SAR and decreased motility and vitality in sperm, increased oxidative stress and 8-Oxo-2-deoxyguanosine markers, stimulating DNA base adduct formation and increased DNA fragmentation. GSM mobile phone exposure can activate cellular stress response in both humans and animal cells and cause the cells to produce heat shock proteins (HSP27 and HSP70) (Leszczynski, 2002). HSPs inhibit natural programmed cell death (apoptosis), whereby cells that should have committed suicide continue to live. Recent studies have shown that these HSPs inhibit apoptosis in cancer cells. In several cases, melatonin hormone which controls the daily biological cycle and has an oncostatic action, produced by the epiphysis (pineal gland) in mammals, mainly during the night, is found to reduce the action of EMR exposure, but the synthesis of melatonin itself seems to be reduced 209 Review Article by EMR (Panagopoulos et al., 2008). In a study to observe the effects of melatonin in hormone balance in a diabetic, it was found that melatonin caused reduction in serum insulin, serum cortisol, serum ACTH, and serum TSH levels while increase in serum gastrin level. Of the biochemical parameters, melatonin caused reductions in TLC, LDLC, and FBS while increase in HDLC. It also caused reduction in neutrophil and increase in lymphocyte count in a diabetic with increase in faecal fat excretion (Mitra and Bhattacharya, 2008). RF-EMR produces DNA damage via free radical formation inside cells. Free radicals kill cells by damaging macromolecules such as DNA, protein, and membrane, also shown to be carcinogenic. EMR enhances free radical activity. EMR interferes with navigational equipments, lifeline electronic gadgets in hospitals, and affects patients with pacemakers. A short-term exposure (15 and 30 minutes) to RFR (900 MHz) from a mobile phone caused a significant increase in DNA single strand breaks in human hair root cells located around the ear which is used for the phone calls (Çam and Seyhan, 2012). Various in vitro studies have shown that 1800 MHz RF-EMF radiation could cause oxidative damage to mtDNA in primary cultured neurons. Oxidative damage to mtDNA may account for the neurotoxicity of RF radiation in the brain (Xu et al., 2010). Studies carried out on the RF levels in North India, particularly at the mobile tower sites at Delhi have shown that people in Indian cities are exposed to dangerously high levels of EMF pollution (Tanwar, 2006). An independent study was commissioned by the Cellular Operators Association of India (COAI) and Association of Unified Telecom Service Providers of India (AUSPI) as a proactive measure stemming from the concern for the public health and safety issues on electromagnetic radiation measurement at New Delhi showed compliance with ICNIRP standards. 180 areas were studied across the capital to understand the extent of RF-EMF radiations emitting from the mobile towers, revealed that the readings were 100 times below international safety guidelines. The study measured cumulative emissions within the 800–2000 MHz band of frequency (which includes both GSM and CDMA technologies) across in the nation’s capital using carefully calibrated equipment, as per the DoT prescribed procedure in line with the ICNIRP specifications. In a similar, but independent case study in Mumbai, it was found that people living within 50–300 m radius are in BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 the high radiation zone and are more prone to illeffects of electromagnetic radiation. Four cases of cancer were found in three consecutive floors (6th, 7th, 8th) directly facing and at similar height as four mobile phone towers placed at the roof of the opposite building (Kumar, 2010). According to the Seletun Scientific Statement (2011), low-intensity (non-thermal) bioeffects and adverse health effects are demonstrated at levels significantly below existing exposure standards. ICNIRP/WHO and IEEE/FCC public safety limits are inadequate and obsolete with respect to prolonged, low-intensity exposures (New International EMF Alliance, 2011). New, biologically-based public exposure standards are urgently needed to protect public health world-wide. EMR exposures should be reduced now rather than waiting for proof of harm before acting (Fragopoulou et al., 2010). Electrohypersensitivity (EHS) and Electromagnetic Field Intolerance (EFI) Syndrome Electrosensitivity of people is now recognized as a physical impairment by government health authorities in the United Kingdom and Sweden. The UK Health Protection Agency (HPA) recognized that people can suffer nausea, headaches, and muscle pains when exposed to electromagnetic fields from mobile phones, electricity pylons, and computer screens. A case study in Sweden, one of the first countries were mobile technology was introduced approximately 15 years ago, shows that 250,000 Swedes are allergic to mobile phone radiation. Sweden has now recognized EHS as a physical degradation and EHS sufferers are entitled to have metal shielding installed in their homes free of charge from the local government (Kumar, 2010; Johansson, 2010). Belpomme (2011) in his presentation at the 8th National Congress on Electrosmog in Berne in 2011 elaborates on the dangers of wireless technology and the diagnostics and treatment of the electromagnetic field intolerance (EFI) Syndrome. In his study from 2008 to 2011, the patients with EHS were investigated with a pulse equilibrium brain scan, dosage of histamine in the blood, dosage of the heat shock proteins HSP70 and HSP27, and appearance and disappearance of symptoms on exposure to an electromagnetic field source. Diagnosis of fatigue and depression were noted. The physiological changes such as vitamin D deficiency, decrease in heat 210 Review Article shock proteins, increase in histamines, increase in biomarker of the opening of blood-brain barrier, protein S100P, decrease in urinary melatonin, and increase in blood anti-myelin proteins were noted in the electrosensitives. Around 50% of the patients in the study had used a mobile phone for more than one hour per day during several years and his findings were similar to the figures published by Hardell’s study (2007) dealing with the cancer occurrences and electromagnetic fields. Future Challenges and Solutions Research into the advantages of radio-frequency energies seen in tissue heating in benign prostatic hyperplasia (BPH), electrical therapy for cardiac arrhythmia, radio-frequency ablation, use of 41.5– 44.58C temperature to kill tumors, shortwave and microwave diathermy for musculoskeletal injuries, and microwave oven used in food preparation are all carried out under controlled conditions. But effects, if any, from RF-EMF radiations released into the environment over a long period of time in densely populated areas where people are continuously exposed to them will show in years to come. According to Osepchuk (1983), frequencies used in industrial, scientific, and medical heating processes are 27.12, 40.68, 433, 915, 2450, and 5800 MHz. Out of which, for diathermy, frequencies used are 27.12, 915, and 2450 MHz in US and 433 MHz is authorized in Europe. According to Kasevich (2000), “the physics of electromagnetic waves and their interactions with material and biological systems is based on the concept that the electromagnetic wave is a force field which exerts a mechanical torque, pressure or force on electrically changed molecules. All living things contain these dielectric properties. The thermal effects produced by absorption of electromagnetic energy are the direct result of water molecules acted upon by the oscillating electric field, rubbing against each other to produce electric heat (thermal effects)”. Research work on electromagnetic bioeffects in humans and animals in the non-thermal range is continuing where effects are noted even at intensities lower than 1 mW/m2 (0.001 W/m2 or 1000 µW/ m2, 0.0001 mW/cm2 or 0.1 µW/cm2). According to Levitt (2007), adverse outcomes of pregnancy can be mutagenic, teratogenic, oncogenic or carcinogenic, and ionizing radiations can cause all three. In animal studies, non-ionizing radiation was also found to be teratogenic and oncogenic, and likely mutagenic, but BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 it is unclear if these observations were due to heating affect, non-thermal affects or both. Trees, plants, soil, grass, and shrubs have the ability to absorb electromagnetic wave energy over a very broad range of wavelengths. According to the resonance concept, human beings can act as receiving antennas for some frequencies, where the absorbed energy is maximized in some areas of the body, like the brain (Levitt, 2007). In the Bioinitiative Report, a document prepared by 14 international experts in a ninemonth project, in which over 2000 scientific studies were reviewed, Sage (2007) came to a conclusion that there may be no lower limit that may be safe, and there was a need for biologically-based limits (1 mW/m2 or 0.001 W/m2) and children are at most risk. Safety limits suggested are 0.001 W/m2 for outdoor cumulative radio-frequency exposure and 0.0001 W/m2 for indoor, cumulative radiofrequency exposure. According to Blank (2012), there is a need for a realistic biological standard to replace the thermal (SAR) standard. The precautionary approaches includes prudence avoidance for public and ALARA, which stands for “as low as reasonably attainable” for regulatory agencies. According to Havas (2006), several disorders, including asthma, ADD/ADHD, diabetes, multiple sclerosis, chronic fatigue, fibromyalgia, are increasing at an alarming rate, as is electromagnetic pollution in the form of dirty electricity, ground current, and radio-frequency radiation from wireless devices and the connection between electromagnetic pollution and these disorders needs to be investigated and the percentage of people sensitive to this form of energy needs to be determined. According to Milham (2010), 20th century epidemic of the so-called diseases of civilization, including cardiovascular disease, cancer, diabetes, and also suicides, was caused by electrification and the unique biological responses we have to it and that our evolutionary balance, developed over the millennia has been severely disturbed and disrupted by man-made EMFs. Conclusion The Department of Telecommunication (DoT) in India has set new norms for cell phone towers with effect from September 1, 2012 (The Hindu, 2012). Exposure standards for RF-EMF radiation has been reduced to one-tenth of the existing level and SAR from 2 to 1.6 W/kg. This came after the ministry of environment and forest 211 Review Article Biology and Medicine, 4 (4): 202–216, 2012 Human Other animals Plants Wildlife Bees Birds 0% 10% 20% 30% Impact 40% 50% No impact 60% 70% 80% 90% 100% Inconclusive Figure 2: Percentage of studies that reported harmful effect of EMR in various groups of organisms (n 5 919), MOEF Report (2010). (MOEF) set up an Inter-ministerial Committee (IMC) to study the effects of RF-EMF radiations on wildlife (Figure 2) and concluded that out of the 919 research papers collected on birds, bees, plants, other animals, and humans, 593 showed impacts, 180 showed no impacts, and 196 were inconclusive studies. They conclude that there are no long-term data available on the environmental impacts of RF-EMF radiations in India. The population of India is increasing as well as the cell phone subscribers and the cell towers as supporting infrastructure. Hence, there is an urgent need to fill the gaps and do further research in this field with emphasis on the effects of early life and prenatal RF-EMF radiation exposure in animals, dosimetry studies, cellular studies using more sensitive methods, and human epidemiological studies, especially on children and young adults on behavioral and neurological disorders and cancer. Meanwhile, one can take the precautionary principle approach and reduce RF-EMF radiation effects of cell phone towers by relocating towers away from densely populated areas, increasing height of towers or changing the direction of the antenna. ARPANSA, 2011. Introduction to radiation basics. http://www.arpansa.gov.au/RadiationProtection/ basics/index.cfm Balmori A, 2003. The effects of microwave radiation on the wildlife. Preliminary results, Valladolid (Spain). http://www.whale.to/b/martinez.pdf Balmori A, 2005. Possible effects of electromagnetic fields from phone masts on a population of white stork (Ciconia ciconia). Electromagnetic Biology and Medicine, 24: 109–119. Balmori A, 2009. Electromagnetic pollution from phone masts. Effects on wildlife. Pathophysiology, 16(2): 191–199. DOI: 10.1016/j.pathophys.2009.01.007 Balmori A, 2010. Mobile phone masts effects on common frog (Rana temporaria) tadpoles: the city turned into a laboratory. Electromagnetic Biology and Medicine, 29: 31–35. Barnes FS, Greenebaum B, 2007. Handbook of biological effects of electromagnetic fields: bioengineering and biophysical aspects of electromagnetic fields. 3rd Edition, Boca Raton, FL: CRC Taylor and Francis Press, 440. References Beason RC, Semm P, 2002. Responses of neurons to an amplitude modulated microwave stimulus. Neuroscience Letters, 333: 175–178. Abdel-Rassoul G, El-Fateh OA, Salem MA, Michael A, Farahat F, EI-Batanouny M, et al., 2007. Neurobehavioral effects among inhabitants around mobile phone base stations. Neurotoxicology, 28(2): 434–440. Belpomme D, 2011. Presentation of Prof. Dominique Belpomme at 8th National Congress on Electrosmog, Berne. http://citizensforsafetechnology.org/uploads/ scribd/Presentation%20of%20Prof.pdf BMID: BM-8 212 Review Article Belyaev IY, Koch CB, Terenius O, Roxström-Lindquist K, Malmgren LO, Sommer W, et al., 2006. Exposure of rat brain to 915 MHz GSM microwaves induces changes in gene expression but not double stranded DNA breaks or effects on chromatin conformation. Bioelectromagnetics, 27(4): 295–306. Belyavskaya NA, 2004. Biological effects due to weak magnetic field on plants. Advances in Space Research, 34(7): 1566–1574. Birenbaum L, Grosof GM, Rosenthal SW, Zaret MM, 1969. Effect of microwaves on the eye. IEEE Transactions on Biomedical Engineering, 16(1): 7–14. Blank M, 2012. Cell Towers and Cancer – Bioinitiative Report. http://www.youtube.com/watch?v5a6wLFeIr CtU&feature5related; www.weepinitiative.org Business Standard, 2010. Cellular tower study debunks radiation myth by COAI, AUSPI. December 21, 2010. http://www.business-standard.com/india/ news/cellular-tower-study-debunks-radiation-mythby-coai-auspi/419036 Çam ST, Seyhan N, 2012. Single-strand DNA breaks in human hair root cells exposed to mobile phone radiation. International Journal of Radiation Biology, 88(5): 420–424. Cane JH, Tepedino VJ, 2001. Causes and extent of declines among native North American invertebrate pollinators: detection, evidence, and consequences. Conservation Ecology, 5(1): 1. Cherry N, 2001. Evidence that electromagnetic radiation is genotoxic: the implications for the epidemiology of cancer and cardiac, neurological, and reproductive effects. http://www.neilcherry.com/ documents/90_m2_EMR_Evidence_That_EMR-EMF_ is_genotoxic.pdf Davis D, 2010. Disconnect. USA: Dutton Penguin Group, 69–95. De Iuliis GN, Newey RJ, King BV, Aitken RJ, 2009. Mobile phone radiation induces reactive oxygen species production and DNA damage in human spermatozoa in vitro. PLoS ONE, 4(7): e6446. Biology and Medicine, 4 (4): 202–216, 2012 Favre D, 2011. Mobile phone-induced honeybee worker piping. Apidologie, 42(3): 270–279. DOI: 10.1007/ s13592-011-0016-x FCC, 1999. Questions and answers about biological effects and potential hazards of radiofrequency electromagnetic fields. OET Bulletin 56, 4th Edition. http://www.fcc.gov/encyclopedia/oetbulletins-line Fragopoulou A, Grigoriev Y, Johansson O, Margaritis LH, Morgan L, Richter E, et al., 2010. Scientific panel on electromagnetic field health risks: consensus points, recommendations, and rationales. Reviews on Environmental Health, 25(4): 307–317. Grefner NM, Yakovleva TL, Boreysha IK, 1998. Effects of electromagnetic radiation on tadpole development in the common frog (Rana temporaria L.). Russian Journal of Ecology, 29(2): 133–134. Hardell L, Carlberg M, Söderqvist F, Mild KH, Morgan LL, 2007. Long-term use of cellular phones and brain tumours: increased risk associated with use for . or 5 10 years. Occupational and Environmental Medicine, 64(9): 626–632. Hässig M, Jud F, Naegeli H, Kupper J, Spiess BM, 2009. Prevalence of nuclear cataract in Swiss veal calves and its possible association with mobile telephone antenna base stations. Schweizer Archiv fur Tierheilkde, 151(10): 471–478. Havas M, 2006. Electromagnetic hypersensitivity: biological effects of dirty electricity with emphasis on diabetes and multiple sclerosis. Electromagnetic Biology and Medicine, 25: 259–268. Hotary KB, Robinson KR, 1994. Endogenous electrical currents and voltage gradients in Xenopus embryos and the consequences of their disruption. Developmental Biology, 166: 789–800. Hyland GJ, 2000, Physics and biology of mobile telephony. The Lancet, 356: 1833–1836. ICNIRP SCI Review, 2011. Mobile phones, brain tumors, and the interphone study: Where are we now? Environmental Health Perspectives, 119(11): 1534–1538. DoT, 2010. Report of the Inter-Ministerial Committee (IMC) on EMF radiation. Ministry of Communication and Information Technology, Government of India. http://www.dot.gov.in/miscellaneous/IMC%20Report/ IMC%20Report.pdf ICNIRP, 1998. Guidelines for limiting exposure to time-varying electric, magnetic, and electromagnetic fields (up to 300 GHz). Health Physics, 74(4): 494–522. Doyon PR, 2008. Are the microwaves killing the insects, frogs, and birds? And are we next? http:// www.thenhf.com/article.php?id5480 Instituto Edumed, 2010. Latin American experts committee on high frequency electromagnetic fields and human health, Non-ionizing electromagnetic BMID: BM-8 213 Review Article radiation in the radio-frequency spectrum and its effects on human health. www.edumed.org.br/lasr2008/en/ Jing J, Yuhua Z, Xiao-qian Y, Rongping J, Dong-mei G, Xi C, 2012. The influence of microwave radiation from cellular phone on fetal rat brain. Electromagnetic Biology and Medicine, 31(1): 57–66. Johansson O, 2010. Aspects of studies on the functional impairment electrohypersensitivity. IOP Conference Series: Earth and Environmental Science, 10: 012005. DOI:10.1088/1755-1315/10/1/012005 Kane RC, 2001. Cellular telephone russian roulette – a historical and scientific perspective. New York: Vantage Press. Kasevich RS, 2000. Cell Towers, Wireless Convenience or Environmental Hazards? Proceedings of the “Cell Towers Forum” State of the Science/State of the Law. Chapter 11, Levitt BB (Ed.), Canada: New Century Publishing, pp. 170–175. Kesari KK, Kumar S, Behari J, 2011. Biomarkers inducing changes due to microwave exposure effect on rat brain, pp. 1–4. http://www.academia. edu/967270/Biomarkers_inducing_changes_due_to_ microwave_exposure_effect_on_rat_brain Kevan PG, Phillips TP, 2001. The economic impacts of pollinator declines: an approach to assessing the consequences. Ecology and Society, 5(1): 8. Kimmel S, Kuhn J, Harst W, Stever H, 2007. Effects of electromagnetic exposition on the behavior of the honeybee (Apis mellifera). Environmental Systems Research, 8: 1–8. Kirschvink JL, Walker MM, Diebel CE, 2001. Magnetite-based magnetoreception. Current Opinion in Neurobiology, 11: 462–467. Kumar G, 2010. Report on cell tower radiation, submitted to the Secretary, DoT, Delhi. http://www.ee.iitb.ac.in/~mwave/ GK-cell-tower-rad-report-DOT-Dec2010.pdf Kumar N, Kumar G, 2009. Biological effects of cell tower radiation on human body. Electrical engineering department, IIT Bombay. December 16–19, ISMOT, 2009, New Delhi, India. Lahijani MS, Ghafoori M, 2000. Teratogenic effects of sinusoidal extremely low frequency electromagnetic fields on morphology of 24 hr chick embryos. Indian Journal of Experimental Biology, 38(7): 692–699. Lai H, Singh NP, 1995. Acute low-intensity microwave exposure increases DNA single-strand breaks in rat brain cells. Bioelectromagnetics, 16: 207–210. BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 Lai H, Singh NP, 1996. Single- and double-strand DNA breaks in rat brain cells after acute exposure to radiofrequency electromagnetic radiation. International Journal of Radiation Biology, 69: 513–521. Lai H, Singh NP, 1997. Melatonin and a spin-trap compound block radio-frequency electromagnetic radiation-induced DNA strand breaks in rat brain cells. Bioelectromagnetics, 18: 446–454. Leszczynski D, Joenväärä S, Reivinen J, Kuokka R, 2002. Non-thermal activation of the hsp27/p38MAPK stress pathway by mobile phone radiation in human endothelial cells: molecular mechanism for cancerand blood-brain barrier–related effects. Differentiation, 70: 120–129. Levengood WC, 1969. A new teratogenic agent applied to amphibian embryos. Journal of Embryology and Experimental Morphology, 21(1): 23–31. Levitina NA, 1966. Non-thermal effect of microwaves on the rhythm of cardiac contractions in the frog. Bulletin of Experimental Biology and Medicine, 62(12): 64–66. Levitt BB, 2007. Electromagnetic fields: a consumer’s guide to the issues and how to protect ourselves. Authors Guild Backinprint.com Edition, iUniverse, Inc. ISBN: 978-0-595-47607-7. Levitt BB, 2010. The environmental effects of wireless technologies and other sources of non-ionizing radiation: an overview. http://www.croww.org/ environmental-effects.pdf Levitt BB, Lai H, 2010. Biological effects from exposure to electromagnetic radiation emitted by cell tower base stations and other antenna arrays. Canada: NRC Research Press, 369–395. Marino AA, Carrubba A, 2009. The effects of mobile phone electromagnetic fields on brain electrical activity: A critical review of literature. Electromagnetic Biology and Medicine, 28(3): 250-274. http://andrewamarino. com/PDFs/CellphoneEMFs-Review.pdf Milham S, 2010. Historical evidence that electrification caused the 20th century epidemic of disease of civilization. Medical Hypotheses, 74(2): 337–345. Mitra A, Bhattacharya D, 2008. Effects of melatonin in mild diabetics with dyslipidaemia. Journal of Human Ecology, 23(2): 109–114. MOEF, 2010. Report on possible impacts of commu nication towers on wildlife, including birds and bees, Government of India. http://www. indiaenvironmentportal.org.in/files/file/final_mobile_ towers_report.pdf 214 Review Article Biology and Medicine, 4 (4): 202–216, 2012 Mouritsen H, Ritz T, 2005. Magnetoreception and its use in bird navigation. Current Opinion in Neurobiology, 15(4): 406–414. Biological Effects and Hygienic Standardization”, Moscow. Geneva, Switzerland: World Health Organisation, 1999. http://www.who.int/iris/handle/10665/65976 Narayanan SN, Kumar RS, Potu BK, Nayak S, Bhat PG, Mailankot M, 2010. Effect of radio-frequency electromagnetic radiations (RF-EMR) on passive avoid ance behaviour and hippocampal morphology in Wistar rats. Uppsala Journal of Medical Sciences, 115: 91–96. Rogers KJ, 2002. Health effects from cell phone tower radiation. http://www.scribd.com/doc/3773284/ Health-Effects-from-Cell-Phone-Tower-Radiation New International EMF Alliance, 2011. Seletun Statement, Oslo, Norway. http://iemfa.org/index.php/ publications/seletun-resolution Nylund R, Leszczynski D, 2004. Proteomics analysis of human endothelial cell line EA.hy926 after exposure to GSM 900 radiation. Proteomics, 4: 1359–1365. Nylund R, Leszczynski D, 2006. Mobile phone radiation causes changes in gene and protein expression in human endothelial cell lines and the response seems to be genome- and proteome-dependent. Proteomics, 6: 4769–4780. Oberfeld G, Navarro E, Portoles M, Maestu C, GomezPerretta C, 2004. The microwave syndrome – further aspects of a Spanish study. EBEA Congres KosGreece, 1: 1–9. Osepchuk JM, 1983. Biological Effects of Electromagnetic Radiation. New York, USA: John Wiley and Sons, IEEE INC. Panagopoulos DJ, Karabarbounis A, Margaritis LH, 2004. Effect of GSM 900 MHz mobile phone radiation on the reproductive capacity of Drosophila melanogaster. Electromagnetic Biology and Medicine, 23(1): 29–43. Panagopoulos DJ, Karabarbounis A, Margaritis LH, 2008. Mobile Telephony Radiation Effects on Living Organisms. In: mobile telephones, Chapter 3, Harper AC, Buress RV (Eds.). New York: Nova Science Publishers, pp. 107–149. Panagopoulos DJ, Chavdoula ED, Nezis IP, Margaritis LH, 2007. Cell death induced by GSM 900 MHz and DCS 1800 MHz mobile telephony radiation. Mutation Research, 626(1–2): 69–78. Panagopoulos DJ, Chavdoula ED, Margaritis LH, 2010. Bioeffects of mobile telephony radiation in relation to its intensity or distance from the antenna. International Journal of Radiation Biology, 86(5): 345–357. Repacholi MH, Cardis E, 2002. Criteria for EMF health risk assessment. Radiation Protection Dosimetry, 72: 305–312. Repacholi MH, Rubtsova NB, Muc AM, 1998. Proceedings of the International Meeting on “Electromagnetic Fields: BMID: BM-8 Rubin EB, Shemesh Y, Cohen M, Elgavish S, Robertson HM, Bloch G, 2006. Molecular and phylogenetic analyses reveal mammalian-like clockwork in the honey bee (Apis mellifera) and shed new light on the molecular evolution of the circadian clock. Genome Research, 16(11): 1352–1365. Sage C, 2007.The Bioinitiative Report and Biologicallybased Exposure Standards. http://www.youtube.com/ watch?v5jC6Bzz25rzU&feature5relmfu Santini R, Santini P, Danze JM, Le Ruz P, Seigne M, 2002. Investigation on the health of people living near mobile telephone relay stations: incidence according to distance and sex. Pathological Biology (Paris), 50(6): 369–373. SCENIHR, 2007. Possible effects of electromagnetic fields (EMF) on human health. 16th Plenary on 21st March 2007. http://ec.europa.eu/health/ph_risk/committees/04_ scenihr/docs/scenihr_o_007.pdf Sharma VP, Kumar NR, 2010. Changes in honeybee behaviour and biology under the influence of cellphone radiations. Current Science, 98(10): 1376–1378. Tanwar VS, 2006. Living Dangerously in Indian cities: an RF radiation pollution perspective. ElectroMagnetic Interference and Compatibility (INCEMIC), 2006 Proceedings of the 9th International Conference, Cogent EMR Solutions, New Delhi, India, pp. 458–466. The Hindu, 2012. Mobile base station radiation limit will be cut from September 1. August 27, 2012. http://www.thehindu.com/news/national/ article3828735.ece The Hindu, 2012. No major health fallout from typical exposure, say studies. August 28, 2012. http://www.thehindu.com/todays-paper/tp-national/ article3829594.ece TRAI, 2012. Indian telecom services performance indicator report for the quarter ending December. Information note to the Press. Press release No. 74/2012, New Delhi. www.trai.gov.in US Fish & Wildlife Service, 2009. Public Press release on briefing paper on the need for research into the cumulative impacts of communication towers on migratory birds and other wildlife in 215 Review Article the United States, Division of Migratory Bird Management (DMBM). http://electromagnetichealth. org/pdf/CommTowerResearchNeedsPublicBriefing2-409.pdf Warnke U, 2007. Bees, birds, and mankind: destroying nature by “Electrosmog”. Effects of mobile radio and wireless communication. A series of papers by the competence initiative for the protection of mankind, environment, and democracy. Kempten. http://www. hese-project.org/hese-uk/en/papers/warnke_bbm.pdf BMID: BM-8 Biology and Medicine, 4 (4): 202–216, 2012 WHO Press Release, 2011. IARC classifies radiofrequency electromagnetic fields as possibly carcinogenic to humans. International Agency for Research on Cancer (IARC). http://www.who.int/ mediacentre/factsheets/fs193/en Xu S, Zhou Z, Zhang L, Yu Z, Zhang W, Wang Y, et al., 2010. Exposure to 1800 MHz radio-frequency radiation induces oxidative damage to mitochondrial DNA in primary cultured neurons. Brain Research, 1311: 189–196. 216 PATPHY-589; No. of Pages 9 ARTICLE IN PRESS Pathophysiology xxx (2009) xxx–xxx Electromagnetic pollution from phone masts. Effects on wildlife Alfonso Balmori Direccion General del Medio Natural, Consejería de Medio Ambiente, Junta de Castilla y Leon, C/Rigoberto Cortejoso, 14, 47014 Valladolid, Spain Received 10 August 2008; received in revised form 28 August 2008; accepted 30 January 2009 Abstract A review on the impact of radiofrequency radiation from wireless telecommunications on wildlife is presented. Electromagnetic radiation is a form of environmental pollution which may hurt wildlife. Phone masts located in their living areas are irradiating continuously some species that could suffer long-term effects, like reduction of their natural defenses, deterioration of their health, problems in reproduction and reduction of their useful territory through habitat deterioration. Electromagnetic radiation can exert an aversive behavioral response in rats, bats and birds such as sparrows. Therefore microwave and radiofrequency pollution constitutes a potential cause for the decline of animal populations and deterioration of health of plants living near phone masts. To measure these effects urgent specific studies are necessary. © 2009 Published by Elsevier Ireland Ltd. Keywords: Effects on wildlife; Effects on birds; Electromagnetic radiation; Mammals; Microwaves; Mobile telecommunications; Non-thermal effects; Phone masts; Radiofrequencies 1. Introduction Life has evolved under the influence of two omnipresent forces: gravity and electromagnetism. It should be expected that both play important roles in the functional activities of organisms [1]. Before the 1990’s radiofrequencies were mainly from a few radio and television transmitters, located in remote areas and/or very high places. Since the introduction of wireless telecommunication in the 1990’s the rollout of phone networks has caused a massive increase in electromagnetic pollution in cities and the countryside [2,3]. Multiple sources of mobile communication result in chronic exposure of a significant part of the wildlife (and man) to microwaves at non-thermal levels [4]. In recent years, wildlife has been chronically exposed to microwaves and RFR (Radiofrequency radiation) signals from various sources, including GSM and UMTS/3G wireless phones and base stations, WLAN (Wireless Local Area Networks), WPAN (Wireless Personal Area Networks such as Bluetooth), and DECT (Digital Enhanced (former European) Cordless Telecommunications) that are erected indiscriminately without studies of environmental impact measuring E-mail addresses: [email protected], [email protected]. long-term effects. These exposures are characterized by low intensities, varieties of signals, and long-term durations. The greater portion of this exposure is from mobile telecommunications (geometric mean in Vienna: 73% [5]). In Germany the GSM cellular phone tower radiation is the dominating high frequency source in residential areas [6]. Also GSM is the dominating high frequency source in the wilderness of Spain (personal observation). Numerous experimental data have provided strong evidence of athermal microwave effects and have also indicated several regularities in these effects: dependence of frequency within specific frequency windows of “resonance-type”; dependence on modulation and polarization; dependence on intensity within specific intensity windows, including superlow power density comparable with intensities from base stations/masts [4,7–9]. Some studies have demonstrated different microwave effects depending on wavelength in the range of mm, cm or m [10,11]. Duration of exposure may be as important as power density. Biological effects resulting from electromagnetic field radiation might depend on dose, which indicates long-term accumulative effects [3,9,12]. Modulated and pulsed radiofrequencies seem to be more effective in producing effects [4,9]. Pulsed waves (in blasts), as well as certain low frequency modulations exert greater 0928-4680/$ – see front matter © 2009 Published by Elsevier Ireland Ltd. doi:10.1016/j.pathophys.2009.01.007 Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 2 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx biological activity [11,13–15]. This observation is important because cell phone radiation is pulsed microwave radiation modulated at low frequencies [8,9]. Most of the attention on possible biological effects of electromagnetic radiation from phone masts has been focused on human health [5,16–21]. The effects of electromagnetic pollution on wildlife, have scarcely been studied [22–25]. The objective of this review is to detail advances in knowledge of radiofrequencies and microwave effects on wildlife. Future research may help provide a better understanding of electromagnetic field (EMF) effects on wildlife and plants and their conservation. 2. Effects on exposed wildlife 2.1. Effects on birds 2.1.1. Effects of phone mast microwaves on white stork In monitoring a white stork (Ciconia ciconia) population in Valladolid (Spain) in vicinity of Cellular Phone Base Stations, the total productivity in nests located within 200 m of antennae, was 0.86 ± 0.16. For those located further than 300 m, the result was practically doubled, with an average of 1.6 ± 0.14. Very significant differences among total productivity were found (U = 240; P = 0.001, Mann–Whitney test). Twelve nests (40%) located within 200 m of antennae never had chicks, while only one (3.3%) located further than 300 m had no chicks. The electric field intensity was higher on nests within 200 m (2.36 ± 0.82 V/m) than nests further than 300 m (0.53 ± 0.82 V/m). In nesting sites located within 100 m of one or several cellsite antennae with the main beam of radiation impacting directly (Electric field intensity >2 V/m) many young died from unknown causes. Couples frequently fought over nest construction sticks and failed to advance the construction of the nests. Some nests were never completed and the storks remained passively in front of cellsite antennae. These results indicate the possibility that microwaves are interfering with the reproduction of white stork [23]. (Fig. 1) Fig. 1. Average number of youngs and electric field intensity (V/m) in 60 nests of white storks (Ciconia ciconia) (Hallberg, Ö with data of Balmori, 2005 [23]). 2.1.2. Effects of phone mast microwaves on house sparrows A possible effect of long-term exposure to low-intensity electromagnetic radiation from mobile phone (GSM) base stations on the number of house sparrows during the breeding season was studied in Belgium. The study was carried out sampling 150 point locations within six areas to examine small-scale geographic variation in the number of house sparrow males and the strength of electromagnetic radiation from base stations. Spatial variation in the number of house sparrow males was negative and highly significantly related to the strength of electric fields from both the 900 and 1800 MHz downlink frequency bands and from the sum of these bands (Chi-square-tests and AIC-criteria, P < 0.001). This negative relationship was highly similar within each of the six study areas, despite differences among areas in both the number of birds and radiation levels. Fewer house sparrow males were seen at locations with relatively high electric field strength values of GSM base stations and therefore support the notion that long-term exposure to higher levels of radiation negatively affects the abundance or behavior of house sparrows in the wild [24]. In another study with point transect sampling performed at 30 points visited 40 times in Valladolid (Spain) between 2002 and 2006, counting the sparrows and measuring the mean electric field strength (radiofrequencies and microwaves: 1 MHz to 3 GHz range). Significant declines (P = 0.0037) were observed in mean bird density over time, and significantly low bird density was observed in areas with high electric field strength. The logarithmic regression of the mean bird density vs. field strength groups (considering field strength in 0.1 V/m increments) was R = −0.87; P = 0.0001 According to this calculation, no sparrows would be expected to be found in an area with field strength >4 V/m [25]. (Fig. 2) In the United Kingdom a decline of several species of urban birds, especially sparrows, has recently happened [26]. The sparrow population in England has decreased in the last 30 years from 24 million to less than 14. The more abrupt decline, with 75% descent has taken place from 1994 to 2002. In 2002, the house sparrow was added to the Red List of U.K. endangered species [27]. This coincides with the rollout of mobile telephony and the Fig. 2. Mean sparrow density as a function of electric field strength grouped in 0.1 V/m. (Balmori and Hallberg, 2007 [25]). Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx Fig. 3. Annual number of contacts (Mean) for 14 species studied in “Campo Grande” urban park (lack the information of the years 1999–2001). possible relationship of both circumstances should be investigated. In Brussels, many sparrows have disappeared recently [28]; similar declines have been reported in Dublin [29]. Van der Poel (cited in Ref. [27]) suggested that sparrows might be declining in Dutch urban centres also. 2.1.3. Effects on the bird community at an urban park Microwaves may be affecting bird populations in places with high electromagnetic pollution. Since several antennas were installed in proximities of “Campo Grande” urban park (Valladolid, Spain) the bird population has decreased and a reduction of the species and breeding couples has occurred. Between 1997 and 2007, of 14 species, 3 species have disappeared, 4 are in decline and 7 stay stable (Balmori, unpublished data) (Fig. 3). In this time the air pollution (SO2, NO2, CO and Benzene) has diminished. During the research some areas called “silence areas” contaminated with high microwave radiation (>2 V/m), where previously different couples usually bred and later disappeared, have been found. Several anomalies in magpies (Pica pica) were detected: plumage deterioration, locomotive problems (limps and deformations in the paws), partial albinism and melanism, especially in flanks [30]. Recently cities have increased cases of partial albinism and melanism in birds (Passer domesticus, Turdus merula and P. pica) (personal observation). 2.1.4. Possible physiological mechanisms of the effects found in birds Current scientific evidence indicates that prolonged exposure to EMFs, at levels that can be encountered in the environment, may affect immune system function by affecting biological processes [3,31,32]. A stressed immune system may increase the susceptibility of a bird to infectious diseases, bacteria, viruses, and parasites [33]. The plumage of the birds exposed to microwaves looked, in general, discolorated and lack of shine. This not only occurred in ornamental birds; such as peacocks, but also in wild birds; such as, tits, great tits, house sparrows, etc (personal observation). We must mention that plumage deterioration is the first sign of weakening or illnesses in birds since damaged feathers are a sure sign of stress. 3 Physiological conditions during exposure minimize microwave effects. Radical scavengers/antioxidants might be involved in effects of microwaves [4]. Microwaves used in cellphones produce an athermal response in several types of neurons of the birds nervous system [34]. Several studies addressed behavior and teratology in young birds exposed to electromagnetic fields [23,25,35–37]. Most studies indicate that electromagnetic field exposure of birds generally changes, but not always consistently in effect or in direction, their behavior, reproductive success, growth and development, physiology and endocrinology, and oxidative stress [37]. These results can be explained by electromagnetic fields affecting the birds’ response to the photoperiod as indicated by altered melatonin levels [38]. Prolonged mobile phone exposure may have negative effects on sperm motility characteristics and male fertility as has been demonstrated in many studies made in man and rats [39–46]. EMF and microwaves can affect reproductive success in birds [23,25,35,36,47]. EMF exposure affected reproductive success of kestrels (Falco sparverius), increasing fertility, egg size, embryonic development and fledging success but reducing hatching success [35,36]. The radiofrequency and microwaves from mobile telephony can cause genotoxic effects [48–55]. Increases in cytological abnormalities imply long-term detrimental effects since chromosomal damage is a mechanism relevant to causation of birth defects and cancer [55]. Long-term continuous, or daily repeated EMF exposure can induce cellular stress responses at non-thermal power levels that lead to an accumulation of DNA errors and to inhibition of cell apoptosis and cause increased permeability of blood–brain barrier due to stabilization of endothelial cell stress fibers. Repeated occurrence of these events over a long period of time (years) could become a health hazard due to a possible accumulation of brain tissue damage. These findings have important implications with regards to potential dangers from prolonged and repeated exposure to non-ionizing radiation [56,57]. Pulsed magnetic fields can have a significant influence on the development and incidence of abnormalities in chicken embryos. In five of six laboratories, exposed embryos exhibited more structural anomalies than controls. If the data from all six laboratories are pooled, the difference for the incidence of abnormalities in exposed embryos and controls is highly significant [58]. Malformations in the nervous system and heart, and delayed embryo growth are observed. The embryo is most sensitive to exposure in the first 24 h of incubation [58]. An increase in the mortality [59] and appearance of morphological abnormalities, especially of the neural tube [13,60,61] has been recorded in chicken embryos exposed to pulsed magnetic fields, with different susceptibility among individuals probably for genetic reasons. A statistically significant high mortality rate of chicken embryos subjected to radiation from a cellphone, compared to the control group exists [62,63]. In another study eggs exposed to a magnetic Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 4 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx field intensity of 0.07 T showed embryonic mortality during their incubation was higher. The negative effect of the magnetic field was manifested also by a lower weight of the hatched chicken [64]. Bioelectric fields have long been suspected to play a causal role in embryonic development. Alteration of the electrical field may disrupt the chemical gradient and signals received by embryo cells. It appears that in some manner, cells sense their position in an electrical field and respond appropriately. The disruption of this field alters their response. Endogenous current patterns are often correlated with specific morphogenetic events [65]. Available data suggests dependencies of genotype, gender, physiological and individual factors on athermal microwave effects [4,9]. Genomic differences can influence cellular responses to GSM Microwaves. Data analysis has highlighted a wide inter-individual variability in response, which was replicated in further experiments [4]. It is possible that each species and each individual, show different susceptibility to radiation, since vulnerability depends on genetic tendency, and physiologic and neurological state of the irradiated organism [15,35–37,61,66–68]. Different susceptibility of each species has also been proven in wild birds exposed to electromagnetic fields from high-voltage power lines [47]. 2.2. Effects on mammals 2.2.1. Alarm and aversion behavior Rats spent more time in the halves of shuttle boxes that were shielded from 1.2 GHz. Microwaves irradiation. The average power density was about 0.6 mW/cm2 . Data revealed that rats avoided the pulsed energy, but not the continuous energy, and less than 0.4 mW/cm2 average power density was needed to produce aversion [69]. Navakatikian & Tomashevskaya [70] described a complex series of experiments in which they observed disruption of rat behavior (active avoidance) from radiofrequency radiation. Behavioral disruption was observed at a power density as low as 0.1 mW/cm2 (0.027 W/kg). Mice in an experimental group exposed to microwave radiation expressed visible individual panic reaction, disorientation and a greater degree of anxiety. In the sham exposed group these deviations of behavior were not seen and all animals show collective defense reaction [71]. Microwave radiation at 1.5 GHz pulsing 16 ms. At 0.3 mW/cm2 power density, in sessions of 30 min/day over one month produced anxiety and alarm in rabbits [72]. Electromagnetic radiation can exert an aversive behavioral response in bats. Bat activity is significantly reduced in habitats exposed to an electromagnetic field strength greater than 2 V/m [73]. During a study in a free-tailed bat colony (Tadarida teniotis) the number of bats decreased when several phone masts were placed 80 m from the colony [74]. 2.2.2. Deterioration of health Animals exposed to electromagnetic fields can suffer a deterioration of health and changes in behavior [75,76]. There was proof of frequent death in domestic animals; such as, hamsters and guinea pigs, living near mobile telecommunication base stations (personal observation). The mice in an experimental group exposed to microwave radiation showed less weight gain compared to control, after two months. The amount of food used was similar in both groups [71]. A link between electromagnetic field exposure and higher levels of oxidative stress appears to be a major contributor to aging, neurodegenerative diseases, immune system disorders, and cancer in mammals [33]. The effects from GSM base transceiver station (BTS) frequency of 945 MHz on oxidative stress in rats were investigated. When EMF at a power density of 3.67 W/m2 , below current exposure limits, were applied, MDA (malondialdehyde) level was found to increase and GSH (reduced glutathione) concentration was found to decrease significantly (P < 0.0001). Additionally, there was a less significant (P = 0.0190) increase in SOD (superoxide dismutase) activity under EM exposure [77]. 2.2.3. Problems in reproduction In the town of Casavieja (Ávila, Spain) a telephony antenna was installed that had been in operation for about 5 years. Then some farmers began blaming the antenna for miscarriages in many pigs, 50–100 m from the antenna (on the outskirts of the town). Finally the topic became so bad that the town council decided to disassemble the antenna. It was removed in the spring 2005. From this moment onwards the problems stopped (C. Lumbreras personal communication). A Greek study reports a progressive drop in the number of rodent births exposed to radiofrequencies. The mice exposed to 0.168 W/cm2 become sterile after five generations, while those exposed to 1.053 W/cm2 became sterile after only three generations [22]. In pregnant rats exposed to 27.12 MHz continuous waves at 100 W/cm2 during different periods of pregnancy, half the pregnancies miscarried before the twentieth day of gestation, compared to only a 6% miscarriage rate in unexposed controls, and 38% of the viable foetuses had incomplete cranial ossification, compared to less than 6% of the controls. Findings included a considerable increase in the percentage of total reabsorptions (post-implantation losses consequent to RF radiation exposure in the first post-implantation stage). Reduced body weight in the exposed dams reflected a negative influence on their health. It seems that the irradiation time plays an important role in inducing specific effects consequent to radiofrequency radiation exposure [78]. There was also a change in the sex ratio, with more males born to rats that had been irradiated from the time of conception [2]. Moorhouse and Macdonald [79] find a substantial decline in female Water Vole numbers in the radio-collared population, apparently resulting from a male skew in the sex ratios of offspring born to this population. Recruits to the radio-tracked population were skewed heavily in favour of males (43:13). This suggests that radio-collaring of females caused male-skewed sex ratios. Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx Mobile phone exposure may have negative effects on sperm motility characteristics and male fertility in rats [46]. Other studies find a decrease of fertility, increase of deaths after birth and dystrophic changes in their reproductive organs [11]. Intermittent exposure showed a stronger effect than continuous exposure [4]. Brief, intermittent exposure to lowfrequency EM fields during the critical prenatal period for neurobehavioral sex differentiation can demasculinize male scent marking behavior and increase accessory sex organ weights in adulthood [80]. In humans, magnetic field exposures above 2.0 mG were positively associated with miscarriage risk [81]. Exposure of pregnant women to mobile phone significantly increased foetal and neonatal heart rate, and significantly decreased the cardiac output [82]. 2.2.4. Nervous system Microwaves may affect the blood brain barrier which lets toxic substances pass through from the blood to the brain [83]. Adang et al. [84] examined the effect of microwave exposure to a GSM-like frequency of 970 MHz pulsed waves on the memory in rats by means of an object recognition task. The rats that have been exposed for 2 months show normal exploratory behavior. The animals that have been exposed for 15 months show derogatory behavior. They do not make the distinction between a familiar and an unfamiliar object. In the area that received radiation directly from “Location Skrunda Radio Station” (Latvia), exposed children had less developed memory and attention, their reaction time was slower and neuromuscular apparatus endurance was decreased [85]. Exposure to cell phones prenatally and, to a lesser degree, postnatally was associated with behavioral difficulties such as emotional and hyperactivity problems around 7 years of age [86]. Electromagnetic radiation caused modification of sleep and alteration of cerebral electric response (EEG) [87–89]. Microwave radiation from phone masts may cause aggressiveness in people and animals (personal observation). 2.3. Effects on amphibians Disappearance of amphibians and other organisms is part of the global biodiversity crisis. An associated phenomenon is the appearance of large numbers of deformed amphibians. The problem has become more prevalent, with deformity rates up to 25% in some populations, which is significantly higher than previous decades [90]. Balmori [91] proposed that electromagnetic pollution (in the microwave and radiofrequency range) is a possible cause for deformations and decline of some wild amphibian populations. Two species of amphibians were exposed to magnetic fields at various stages of development. A brief treatment of early amphibian embryos produced several types of abnormalities [92]. Exposure to a pulsed electromagnetic field produced abnormal limb regeneration in adult Newts [93]. Frog tadpoles (Rana temporaria) developed under electro- 5 magnetic field (50 Hz, 260 A/m) have increased mortality. Exposed tadpoles developed more slowly and less synchronously than control tadpoles and remain at the early stages for longer. Tadpoles developed allergies and EMF caused changes in blood counts [94]. In a current study exposing eggs and tadpoles (n = 70) of common frog (R. temporaria) for two months, from the phase of eggs until an advanced phase of tadpole, to four telephone base stations located 140 m away: with GSM system 948.0–959.8 MHz; DCS system: 1830.2–1854.8; 1855.2–1879.8 MHz. and UMTS system: 1905–1910; 1950–1965; 2140–2155 MHz. (electric field intensity: 1.847–2.254 V/m). A low coordination of movements, an asynchronous growth, with big and small tadpoles, and a high mortality (90%) was observed. The control group (n = 70), under the same conditions but inside a Faraday cage (metallic shielding component: EMC-reinforcement fabrics 97442 Marburg Technic), the coordination of movements was normal, the development was synchronously and the mortality rate was only 4.2% [95]. 2.4. Effects on insects The microwaves may affect the insects. Insects are the basis and key species of ecosystems and they are especially sensitive to electromagnetic radiation that poses a threat to nature [96]. Carpenter and Livstone [97] irradiated pupae of Tenebrio molitor with 10 GHz microwaves at 80 mW for 20–30 min and 20 mW for 120 min obtained a rise in the proportion of insects with abnormalities or dead. In another study exposing fruit flies (Drosophila melanogaster) to mobile phone radiation, elevated stress protein levels (Hsp70) was obtained, which usually means that cells are exposed to adverse environmental conditions (’non-thermal shock’) [98]. Panagopoulos et al. [99] exposed fruit flies (D. melanogaster) to radiation from a mobile phone (900 MHz) during the 2–5 first days of adulthood. The reproductive capacity of the species reduced by 50–60% in modulated radiation conditions (emission while talking on the phone) and 15–20% with radiation nomodulated (with the phone silent). The results of this study indicate that this radiation affects the gonadal development of insects in an athermal way. The authors concluded that radio frequencies, specifically GSM, are highly bioactive and provoke significant changes in physiological functions of living organisms. Panagopoulos et al. [100] compare the biological activity between the two systems GSM 900 MHz and DCS 1800 MHz in the reproductive capacity of fruit flies. Both types of radiation were found to decrease significantly and non-thermally the insect’s reproductive capacity, but GSM 900 MHz seems to be even more bioactive than DCS 1800 MHz. The difference seems to be dependent mostly on field intensity and less on carrier frequency. A study in South Africa finds a strong correlation between decrease in ant and beetle diversity with the Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 6 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx electromagnetic radiation exposure (D. MacFadyen, personal communication.). A decrease of insects and arachnids near base stations was detected and corroborated by engineers and antenna’s maintenance staff [101]. In houses near antennas an absence of flies, even in summer, was found. In a recent study carried out with bees in Germany, only a few bees irradiated with DECT radiation returned to the beehive and they needed more time. The honeycomb weight was lower in irradiated bees [102]. In recent years a “colony collapse disorder” is occurring that some authors relate with pesticides and with increasing electromagnetic pollution [96]. The disappearance of insects could have an influence on bird’s weakening caused by a lack of food, especially at the first stages in a young bird’s life. 2.5. Effects on trees and plants The microwaves may affect vegetables. In the area that received radiation directly from “Location Skrunda Radio Station” (Latvia), pines (Pinus sylvestris) experienced a lower growth radio. This did not occur beyond the area of impact of electromagnetic waves. A statistically significant negative correlation between increase tree growth and intensity of electromagnetic field was found, and was confirmed that the beginning of this growth decline coincided in time with the start of radar emissions. Authors evaluated other possible environmental factors which might have intervened, but none had noticeable effects [103]. In another study investigating cell ultrastructure of pine needles irradiated by the same radar, there was an increase of resin production, and was interpreted as an effect of stress caused by radiation, which would explain the aging and declining growth and viability of trees subjected to pulsed microwaves. They also found a low germination of seeds of pine trees more exposed [104]. The effects of Latvian radar was also felt by aquatic plants. Spirodela polyrrhiza exposed to a power density between 0.1 and 1.8 W/cm2 had lower longevity, problems in reproduction and morphological and developmental abnormalities compared with a control group who grew up far from the radar [105]. Chlorophylls were quantitatively studied in leaves of black locust (Robinia pseudoacacia L.) seedlings exposed to high frequency electromagnetic fields of 400 MHz. It was revealed that the ratio of the two main types of chlorophyll was decreasing logarithmically to the increase of daily exposure time [106]. Exposed tomato plants (Lycopersicon esculentum) to low level (900 MHz, 5 V/m) electromagnetic fields for a short period (10 min) measured changes in abundance of three specific mRNA after exposure, strongly suggesting that they are the direct consequence of application of radio-frequency fields and their similarities to wound responses suggests that this radiation is perceived by plants as an injurious stimulus [107]. Non-thermal exposure to radiofrequency fields induced oxidative stress in duckweed (Lemna minor) as well as unespecific stress responses, especially of antioxidative enzymes [108]. For some years progressive deterioration of trees near phone masts have been observed in Valladolid (Spain). Trees located inside the main lobe (beam), look sad and feeble, possibly slow growth and a high susceptibility to illnesses and plagues. In places we have measured higher electric field intensity levels of radiation (>2 V/m) the trees show a more notable deterioration [109]. The tops of trees are dried up where the main beams are directed to, and they seem to be most vulnerable if they have their roots close to water. The trees don’t grow above the height of the other ones and, those that stand out far above, have dried tops (Hargreaves, personal communication and personal observation). White and black poplars (Populus sp.) and willows (Salix sp.) are more sensitive. There may be a special sensitivity of this family exists or it could be due to their ecological characteristics forcing them to live near water, and thus electric conductivity. Other species as Platanus sp. and Lygustrum japonicum, are more resistant (personal observation). Schorpp [110] presents abundant pictures and explanations of what happens to irradiated trees. 3. Conclusions This literature review shows that pulsed telephony microwave radiation can produce effects especially on nervous, cardiovascular, immune and reproductive systems [111]: - Damage to the nervous system by altering electroencephalogram, changes in neural response or changes of the blood–brain barrier. - Disruption of circadian rhythms (sleep–wake) by interfering with the pineal gland and hormonal imbalances. - Changes in heart rate and blood pressure. - Impairment of health and immunity towards pathogens, weakness, exhaustion, deterioration of plumage and growth problems. - Problems in building the nest or impaired fertility, number of eggs, embryonic development, hatching percentage and survival of chickens. - Genetic and developmental problems: problems of locomotion, partial albinism and melanism or promotion of tumors. In the light of current knowledge there is enough evidence of serious effects from this technology to wildlife. For this reason precautionary measures should be developed, alongside environmental impact assessments prior to installation, and a ban on installation of phone masts in protected natural areas and in places where endangered species are present. Surveys should take place to objectively assess the severity of effects. Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx Acknowledgment The author is grateful to Denise Ward and Örjan Hallberg. References [1] J.M.R. Delgado, Biological effects of extremely low frequency electromagnetic fields, J. Bioelectr. 4 (1985) 75–91. [2] A. Firstenberg, Microwaving Our Planet: The Environmental Impact of the Wireless Revolution, 11210, Cellular Phone Taskforce, Brooklyn, NY, 1997. [3] A.L. Galeev, The effects of microwave radiation from mobile telephones on humans and animals, Neurosci. Behav. Physiol. 30 (2000) 187–194. [4] I. Belyaev, Non-thermal biological effects of microwaves, Microw. Rev. 11 (2005) 13–29, http://www.mwr.medianis.net/pdf/Vol11No203-IBelyaev.pdf. [5] H.P. Hutter, H. Moshammer, P. Wallner, M. Kundi, Subjective symptoms, sleeping problems, and cognitive performance in subjects living near mobile phone base stations, Occup. Environ. Med. 63 (2006) 307–313. [6] T. Haumann, U. Munzenberg, W. Maes, P. Sierck, HF-radiation levels of GSM cellular phone towers in residential areas, in: 2nd International Workshop on Biological effects of EMFS, Rhodes, Greece, 2002. [7] W.R. Adey, Tissue interactions with non-ionizing electromagnetic fields, Physiol. Rev. 61 (1981) 435–514. [8] G.J. Hyland, Physics and biology of mobile telephony, Lancet 356 (2000) 1–8. [9] H. Lai, Biological effects of radiofrequency electromagnetic field, in: Encyclopaedia of Biomaterials and Biomedical Engineering, 2005, doi:10.1081/E-EBBE-120041846, pp. 1–8. [10] S. Kemerov, M. Marinkev, D. Getova, Effects of low-intensity electromagnetic fields on behavioral activity of rats, Folia Med. 41 (1999) 75–80. [11] N. Nikolaevich, A. Igorevna, and G. Vasil, Influence of highfrequency electromagnetic radiation at non-thermal intensities on the human body (A review of work by Russian and Ukrainian researchers), No place to hide, 3 (Supplement), 2001. [12] W.R. Adey, Bioeffects of mobile communications fields: possible mechanisms for cumulative dose. in: N. Kuster, Q. Balzano, J.C. Lin, (Eds.), Mobile communications safety, New York: Chapman & Hall, 1997, pp. 95–131. [13] A. Úbeda, M.A. Trillo, L. Chacón, M.J. Blanco, J. Leal, Chick embryo development can be irreversibly altered by early exposure to weak extremely-low-frequency magnetic fields, Bioelectromagnetics 15 (1994) 385–398. [14] I.U.G. Grigoriev, Role of modulation in biological effects of electromagnetic radiation, Radiats. Biol. Radioecol. 36 (1996) 659–670. [15] G.J. Hyland, The physiological and environmental effects of nonionising electromagnetic radiation, Working document for the STOA Panel, European Parliament, Directorate General for Research, 2001. [16] R. Santini, J.M. Santini, P. danze, M. Leruz, M. Seigne, Enquête sur la santé de riverains de stations relais: I. Incidences de la distance et du sexe, Pathol. Biol. 50 (2002) 369–373. [17] R. Santini, P. Santini, J.M. Le Ruz, M. Danze, M. Seigne, Survey study of people living in the vicinity of cellular phone base stations, Electromagn. Biol. Med. 22 (2003) 41–49. [18] R. Santini, P. Santini, J.M. Danze, P. Le Ruz, M. Seigne, Symptoms experienced by people in vicinity of base stations: II/Incidences of age, duration of exposure, location of subjects in relation to the antennas and other electromagnetic factors, Pathol. Biol. 51 (2003) 412–415. [19] E.A. Navarro, J. Segura, M. Portolés, C. Gómez Perretta, The microwave syndrome: a preliminary study in Spain, Electromagn. Biol. Med. 22 (2003) 161–169. 7 [20] G. Oberfeld, E. Navarro, M. Portoles, C. Maestu, C. Gomez-Perretta, The microwave syndrome—further aspects of a Spanish study, in: EBEA Congres Kos, Greece, 2004. [21] G. Abdel-Rassoul, M.A. Salem, A. Michael, F. Farahat, M. ElBatanouny, E. Salem, Neurobehavioral effects among inhabitants around mobile phone base stations, Neurotoxicology 28 (2007) 434–440. [22] I.N. Magras, T.D. Xenos, Radiation-induced changes in the prenatal development of mice, Bioelectromagnetics 18 (1997) 455–461. [23] A. Balmori, Possible effects of electromagnetic fields from phone masts on a population of white stork (Ciconia ciconia), Electromagn. Biol. Med. 24 (2005) 109–119. [24] J. Everaert, D. Bauwens, A possible effect of electromagnetic radiation from mobile phone base stations on the number of breeding House Sparrows (Passer domesticus), Electromagn. Biol. Med. 26 (2007) 63–72. [25] A. Balmori, Ö. Hallberg, The urban decline of the house sparrow (Passer domesticus): a possible link with electromagnetic radiation, Electromagn. Biol. Med. 26 (2007) 141–151. [26] M.J. Raven, D.G. Noble, S.R. Baillie, The breeding bird survey (2002), BTO Research Report 334, British Trust for Ornithology, Thetford, 2003. [27] J.D. Summers-Smith, The decline of the house sparrow: a review, Brit. Birds 96 (2003) 439–446. [28] J. De Laet, Ligue Royale Belgue pour la Protection des Oiseaux avec l’Université de Gand, 2004, <http://www.protectiondesoiseaux.be/ content/view/801/74/> (Accessed on May 20, 2008). [29] A. Prowse, The urban decline of the house sparrow, Brit. Birds 95 (2002) 143–146. [30] A. Balmori, Aves y telefonía móvil. Resultados preliminares de los efectos de las ondas electromagnéticas sobre la fauna urbana, El ecologista 36 (2003) 40–42. [31] C.K. Chou, A.W. Guy, L.L. Kunz, R.B. Johnson, J.J. Crowley, J.H. Krupp, Long-term, low-level microwave irradiation of rats, Bioelectromagnetics 13 (1992) 469–496. [32] E.T. Novoselova, E.E. Fesenko, Stimulation of production of tumour necrosis factor by murine macrophages when exposed in vivo and in vitro to weak electromagnetic waves in the centimeter range, Biofizika 43 (1998) 1132–1133. [33] K.J. Fernie, D.M. Bird, Evidence of oxidative stress in American kestrels exposed to electromagnetic fields, Environ. Res. A 86 (2001) 198–207. [34] R.C. Beasond, P. Semm, Responses of neurons to an amplitude modulated microwave stimulus, Neurosci. Lett. 33 (2002) 175–178. [35] K.J. Fernie, D.M. Bird, R.D. Dawson, P.C. Lague, Effects of electromagnetic fields on the reproductive success of American kestrels, Physiol. Biochem. Zool. 73 (2000) 60–65. [36] K.J. Fernie, N.J. Leonard, D.M. Bird, Behavior of free-ranging and captive American kestrels under electromagnetic fields, J. Toxicol. Environ. Health, Part A 59 (2000) 597–603. [37] K.J. Fernie, S.J. Reynolds, The effects of electromagnetic fields from power lines on avian reproductive biology and physiology: a review., J. Toxicol. Environ. Health, Part B 8 (2005) 127–140. [38] K.J. Fernie, D.M. Bird, Effects of electromagnetic fields on body mass and food-intake of American kestrels, Condor 101 (1999) 616–621. [39] S. Dasdag, M.A. Ketani, Z. Akdag, A.R. Ersay, I. Sar, Ö.C. Demirtas, M.S. Celik, Whole body microwave exposure emitted by cellular phones and testicular function of rats, Urol. Res. 27 (1999) 219–223. [40] M. Davoudi, C. Brössner, W. Kuber, Der Einfluss elektromagnetischer wellen auf die Spermienmotilität, J. für Urol. Urogynäkol. 9 (2002) 18–22. [41] I. Fejes, Z. Za Vaczki, J. Szollosi, R.S. Kolosza, J. Daru, L. Kova Cs, L.A. Pa, Is there a relationship between cell phone use and semen quality? Arch. Androl. 51 (2005) 385–393. [42] P. Stefanis, A. Drakeley, R. Gazvani, D.I. Lewis-Jones, Growing concern over the safety of using mobile phones and male fertility, Arch. Androl. 52 (2006) 9–14. Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; 8 No. of Pages 9 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx [43] O. Erogul, E. Oztas, I. Yildirim, T. Kir, E. Aydur, G. Komesli, H.C. Irkilata, M.K. Irmak, A.F. Peker, Effects of electromagnetic radiation from a cellular phone on human sperm motility: an in vitro study, Arch. Med. Res. 37 (2006) 840–843. [44] A. Agarwal, F. Deepinder, R.K. Sharma, G. Ranga, J. Li, Effect of cell phone usage on semen analysis in men attending infertility clinic: an observational study, Fertil. Steril. 89 (2008) 124–128. [45] A. Wdowiak, L. Wdowiak, H. Wiktor, Evaluation of the effect of using mobile phones on male fertility, Ann. Agric. Environ. Med. 14 (1) (2007) 169–172. [46] J.G. Yan, A.M. Gresti, T. Bruce, Y.H. Yan, A. Granlund, H.S. Matloub, Effects of cellular phone emissions on sperm motility in rats, Fertil. Steril. 88 (4) (2007) 957–964. [47] P.F. Doherty, T.C. Grubb, Effects of high-voltage power lines on birds breeding within the powerlines’ electromagnetic fields, Sialia 18 (1996) 129–134. [48] V. Garaj-Vrhovac, D. Horvat, Z. Koren, The relationship between colony-forming ability, chromosome aberrations and incidence of micronuclei in V79 Chinese hamster cells exposed to microwave radiation, Mutat. Res. 263 (1991) 143–149. [49] H. Lai, N.P. Singh, Acute low-intensity microwave exposure increases DNA single-strand breaks in rat brain cells, Bioelectromagnetics 16 (1995) 207–210. [50] S. Balode, Assessment of radio-frequency electromagnetic radiation by the micronucleus test in bovine peripheral erythrocytes, Sci. Total Environ. 180 (1996) 81–85. [51] I. Belyaev, L. Hillert, E. Markova, R. Sarimov, L. Malmgren, B. Persson, M. Harms-Ringdahl, Microwaves of mobile phones affect human lymphocytes from normal and hypersensitive subjects dependent on frequency, in: 26th Annual Meeting of the Bioelectromagnetics (BEMS), Washington, USA, 2004. [52] G. Demsia, D. Vlastos, D.P. Matthopoulos, Effect of 910-MHz electromagnetic field on rat bone marrow, Sci. World J. 4 (2004) 48–54. [53] Reflex, 2004, <http://www.verum-foundation.de/cgi-bin/content.cgi? id=euprojekte01>. [54] E. Diem, C. Schwarz, F. Adlkofer, O. Jahn, H. Rudiger, Non-thermal DNA breakage by mobile-phone radiation (1800 MHz) in human fibroblasts and in transformed GFSH-R17 rat granulosa cells in vitro, Mut. Res. 583 (2005) 178–183. [55] A.G. Gandhi, P. Singh, Cytogenetic damage in mobile phone users: preliminary data, Int. J. Hum. Genet. 5 (2005) 259–265. [56] A. Di Carlo, N. Wite, F. Guo, P. Garrett, T. Litovitz, Chronic electromagnetic field exposure decreases HSP70 levels and lowers cytoprotection, J. Cell. Biochem. 84 (2002) 447–454. [57] D. Leszczynski, S. Joenväärä, J. Reivinen, R. Kuokka, Non-thermal activation of the hsp27/p38MAPK stress pathway by mobile phone radiation in human endothelial cells: molecular mechanism for cancer- and blood-brain barrier-related effects, Differentiation 70 (2002) 120–129. [58] E. Berman, L. Chacon, D. House, B.A. Koch, W.E. Koch, J. Leal, S. Lovtrup, E. Mantiply, A.H. Martin, G.I. Martucci, K.H. Mild, J.C. Monahan, M. Sandstrom, K. Shamsaifar, R. Tell, M.A. Trillo, A. Ubeda, P. Wagner, Development of chicken embryos in a pulsed magnetic field, Bioelectromagnetics 11 (1990) 169–187. [59] B.J. Youbicier-Simo, M. Bastide, Pathological effects induced by embryonic and postnatal exposure to EMFs radiation by cellular mobile phones, Radiat. Protect. 1 (1999) 218–223. [60] A. Úbeda, J. Leal, M.A. Trillo, M.A. Jimenez, J.M.R. Delgado, Pulse shape of magnetic fields influences chick embryogenesis, J. Anat. 137 (1983) 513–536. [61] J.M. Farrel, T.L. Litovitz, M. Penafiel, The effect of pulsed and sinusoidal magnetic fields on the morphology of developing chick embryos, Bioelectromagnetics 18 (1997) 431–438. [62] Ju.G. Grigoriew, Influence of the electromagnetic field of the mobile phones on chickens embryo, to the evaluation of the dangerousness after the criterion of this mortality, J. Radiat. Biol. 5 (2003) 541–544. [63] F. Batellier, I. Couty, D. Picard, J.P. Brillard, Effects of exposing chicken eggs to a cell phone in “call” position over the entire incubation period, Theriogenology 69 (2008) 737–745. [64] L. Veterány, A. Veterányová, J. Jedlicka, Effect of magnetic field on embryonic mortality, Cesk. Fysiol. 50 (2001) 141–143. [65] K.B. Hotary, K.R. Robinson, Evidence of a role for endogenous electrical fields in chick embryo development, Development 114 (1992) 985–996. [66] M. Mevissen, M. Haübler, Acceleration of mammary tumorigenesis by exposure of 7,12-dimethylbenz(a)anthracene-treated female rats in a 50-Hz, 100-T magnetic field: replication study, J. Toxicol. Environ. Health, Part A 53 (1998) 401–418. [67] D. Flipo, M. Fournier, C. Benquet, P. Roux, C. Le Boulaire, Increased apoptosis, changes in intracellular Ca2+ , and functional alterations in lymphocytes and macrophages after in vitro exposure to static magnetic field, J. Toxicol. Environ. Health, Part A 54 (1998) 63–76. [68] M. Fedrowitz, K. Kamino, W. Löscher, Significant differences in the effects of magnetic field exposure on 7,12 dimethylbenz (a)anthracene-induced mammary carcinogenesis in two sub-strains of Sprague-Dawley rats, Cancer Res. 64 (2004) 243–251. [69] A.H. Frey, S.R. Feld, Avoidance by rats of illumination with low power nonionizing electromagnetic energy, J. Comp. Physiol. Psychol. 89 (1975) 183–188. [70] M.A. Navakatikian, L.A. Tomashevskaya, Phasic behavioral and endocrine effects of microwaves of nonthermal intensity, in: D.O. Carpenter (Ed.), Biological Effects of Electric and Magnetic Fields, 1, Academic Press, San Diego, CA, 1994. – D.T. Sokolović, V.V. Marković, D.M. [71] D.D. Krstić, B.J. Ðindić, Petković, S.B. Radić, The results of experimental exposition of mice by mobile telephones, in: TELSIKS Conference, Serbia and Montenegro, Microw. Rev. (2005) 34–37. [72] I.U.G. Grigoriev, S.N. Luk’ianova, V.P. Makarov, V.V. Rynskov, N.V. Moiseeva, Motor activity off rabbits in conditions of chronic lowintensity pulse microwave irradiation, Radiat. Biol. Radioecol. 35 (1995) 29–35. [73] B. Nicholls, P.A. Racey, Bats avoid radar installations: Could electromagnetic fields deter bats from colliding with wind turbines? PLOS One 3 (2007) e297. [74] A. Balmori Murciélago rabudo–Tadarida teniotis, En: Enciclopedia Virtual de los Vertebrados Españoles, Carrascal, L.M., Salvador, A. (Eds.), Museo Nacional de Ciencias Naturales, Madrid, 2004c, <http://www.vertebradosibericos.org/>. [75] T.A. Marks, C.C. Ratke, W.O. English, Strain voltage and developmental, reproductive and other toxicology problems in dogs, cats and cows: a discussion, Vet. Human Toxicol. 37 (1995) 163–172. [76] W. Löscher, G. Käs, Conspicuous behavioural abnormalities in a dairy cow herd near a TV and radio transmitting antenna, Pract. Vet. Surg. 29 (1998) 437–444. [77] A. Yurekli, M. Ozkan, T. Kalkan, H. Saybasili, H. Tuncel, P. Atukeren, K. Gumustas, S. Seker, GSM Base Station Electromagnetic Radiation and Oxidative Stress in Rats, Electromagn. Biol. Med. 25 (2006) 177–188. [78] S. Tofani, G. Agnesod, P. Ossola, S. Ferrini, R. Bussi, Effects of continuous low-level exposure to radio-frequency radiation on intrauterine development in rats, Health Phys. 51 (1986) 489– 499. [79] T.P. Moorhouse, D.W. Macdonald, Indirect negative impacts of radiocollaring: sex ratio variation in water voles, J. Appl. Ecol. 42 (2005) 91. [80] R.F. McGivern, R.Z. Sokol, W.R. Adey, Prenatal exposure to a lowfrequency electromagnetic field demasculinizes adult scent marking behavior and increases accessory sex organ weights in rats, Teratology 41 (1990) 1–8. [81] G.M. Lee, R.R. Neutra, L. Hristova, M. Yost, R.A. Hiatt, A Nested Case-Control Study of Residential and Personal Magnetic Field Measures and Miscarriages, Epidemiology 13 (2002) 21–31. Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007 PATPHY-589; No. of Pages 9 ARTICLE IN PRESS A. Balmori / Pathophysiology xxx (2009) xxx–xxx [82] A.Y. Rezk, K. Abdulqawi, R.M. Mustafa, T.M. Abo El-Azm, H. AlInany, Fetal and neonatal responses following maternal exposure to mobile phones, Saudi Med. J. 29 (2008) 218–223. [83] L.G. Salford, A.E. Brun, J.L. Eberhardt, L. Malmgren, B.R. Persson, Nerve cell damage in mammalian brain after exposure to microwaves from GSM mobile phones, Environ. Health Perspect. 111 (2003) 881–893. [84] D. Adang, B. Campo, A.V. Vorst, Has a 970 MHz Pulsed exposure an effect on the memory related behaviour of rats? in: The 9th European Conference onWireless Technology, September 2006, 2006, pp. [85] A.A. Kolodynski, V.V. Kolodynska, Motor and psychological functions of school children living in the area of the Skrunda Radio Location Station in Latvia, Sci. Total Environ. 180 (1996) 87–93. [86] H.A. Divan, L. Kheifets, C. Obel, J. Olsen, Prenatal and postnatal exposure to cell phone use and behavioral problems in children, Epidemiology 19 (2008) 523–529. [87] K. Mann, J. Roschkle, Effects of pulsed high-frequency electromagnetic fields on human sleep, Neuropsychobiology 33 (1996) 41–47. [88] A.V. Kramarenko, U. Tan, Effects of high-frequency electromagnetic fields on human EEG: a brain mapping study, Int. J. Neurosci. 113 (2003) 1007–1019. [89] A.A. Marino, E. Nilsen, C. Frilot, Nonlinear changes in brain electrical activity due to cell phone radiation, Bioelectromagnetics 24 (2003) 339–346. [90] A.R. Blaustein, P.T.J. Johnson, Explaining frog deformities, Sci. Am. 288 (2003) 60–65. [91] A. Balmori, The incidence of electromagnetic pollution on the amphibian decline: is this an important piece of the puzzle? Toxicol. Environ. Chem. 88 (2006) 287–299. [92] W.C. Levengood, A new teratogenic agent applied to amphibian embryos, J. Embryol. Exp. Morphol. 21 (1969) 23–31. [93] R.H. Landesman, W. Scott Douglas, Abnormal limb regeneration in adult newts exposed to a pulsed electromagnetic field, Teratology 42 (1990) 137–145. [94] N.M. Grefner, T.L. Yakovleva, I.K. Boreysha, Effects of electromagnetic radiation on tadpole development in the common frog (Rana temporaria L.), Russ. J. Ecol. 29 (1998) 133–134. [95] A. Balmori, in preparation: Phone masts effects on common frog (Rana temporaria) tadpoles: An experiment in the city. See the video clips in: http://www.hese-project.org/hese-uk/en/issues/nature. php?id=frogs. [96] U. Warnke, Bienen, vögel und menschen, Die Zerstörung der Natur durch “Elektrosmog”. Kompetenzinitiative, 2007 46 pp. [97] R.L. Carpenter, E.M. Livstone, Evidence for nonthermal effects of microwave radiation: Abnormal development of irradiated insect pupae, IEEE Trans. Microw. Theor. Tech. 19 (1971) 173–178. 9 [98] D. Weisbrot, H. Lin, L. Ye, M. Blank, R. Goodman, Effects of mobile phone radiation on reproduction and development in Drosophila melanogaster, J. Cell. Biochem. 89 (2003) 48–55. [99] D.J. Panagopoulos, A. Karabarbounis, L.H. Margaritis, Effect of GSM 900 MHz Mobile Phone Radiation on the Reproductive Capacity of Drosophila melanogaster, Electromagn. Biol. Med. 23 (2004) 29–43. [100] D.J. Panagopoulos, E.D. Chavdoula, A. Karabarbournis, L.H. Margaritis, Comparison of bioactivity between GSM 900 MHz and DCS 1800 MHz mobile telephony radiation, Electromagn. Biol. Med. 26 (2007) 33–44. [101] A. Balmori, Efectos de las radiaciones electromagnéticas de la telefonía móvil sobre los insectos, Ecosistemas (2006). [102] H. Stever, J. Kuhn, C.Otten, B.Wunder, W. Harst, Verhaltensanderung unter elektromagnetischer Exposition. Pilotstudie, Institut für mathematik. Arbeitsgruppe, Bildungsinformatik. Universität Koblenz-Landau, 2005. [103] V.G. Balodis, K. Brumelis, O. Kalviskis, D. Nikodemus, V.Z. y Tjarve, Does the Skrunda radio location station diminish the radial growth of pine trees? Sci. Total Environ. 180 (1996) 57–64. [104] T. Selga, M. Selga, Response of Pinus Sylvestris L. needles to electromagnetic fields. Cytological and ultraestructural aspects, Sci. Total Environ. 180 (1996) 65–73. [105] I. Magone, The effect of electromagnetic radiation from the Skrunda Radio Location Station on Spirodela polyrhiza (L.) Schleiden cultures, Sci. Total Environ. 180 (1996) 75–80. [106] D.D. Sandu, C. Goiceanu, A. Ispas, I. Creanga, S. Miclaus, D.E. Creanga, A preliminary study on ultra high frequency electromagnetic fields effect on black locust chlorophylls, Acta Biol. Hung. 56 (2005) 109–117. [107] D. Roux, Al. Vian, S. Girard, P. Bonnet, F. Paladian, E. Davies, G. Ledoigt, High frequency (900 MHz) low amplitude (5 V m−1 ) electromagnetic field: a genuine environmental stimulus that affects transcription, translation, calcium and energy charge in tomato, Planta 227 (2007) 883–891. [108] M. Tkalec, K. Malarik, B. Pevalek-Kozlina, Exposure to radiofrequency radiation induces oxidative stress in duckweed Lemna minor L., Sci. Total Environ. 388 (2007) 78–89. [109] A. Balmori, ¿Pueden afectar las microondas pulsadas emitidas por las antenas de telefonía a los árboles y otros vegetales? Ecosistemas (2004), http://www.revistaecosistemas.net/articulo.asp?Id= 29&Id Categoria=1&tipo=otros contenidos. [110] V. Schorpp, 2007, <http://www.puls-schlag.org/baumschaeden.htm# linden>. [111] A. Balmori, Posibles efectos de las ondas electromagnéticas utilizadas en la telefonía inalámbrica sobre los seres vivos, Ardeola 51 (2004) 477–490. Please cite this article in press as: A. Balmori, Electromagnetic pollution from phone masts. Effects on wildlife, Pathophysiology (2009), doi:10.1016/j.pathophys.2009.01.007
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