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. Author manuscript; available in PMC: 2021 Nov 20.
Published before final editing as: J Trace Elem Med Biol. 2020 May 20;61:126554. doi: 10.1016/j.jtemb.2020.126554

The Impact of Manganese on Neurotransmitter Systems

Ana Thalita Gonçalves Soares 1, Aline Castro da Silva 1, Alexey A Tinkov 4,5,6, Haroon Khan 2, Abel Santamaría 3, Margarita G Skalnaya 5, Anatoly V Skalny 5,6, Aristidis Tsatsakis 7, Aaron B Bowman 9, Michael Aschner 5,8,*, Daiana Silva Ávila 1
PMCID: PMC7677177  NIHMSID: NIHMS1599448  PMID: 32480053

Abstract

BACKGROUND

Manganese (Mn) is a metal ubiquitously present in nature and essential for many living organisms. As a trace element, it is required in small amounts for the proper functioning of several important enzymes, and reports of Mn deficiency are indeed rare.

METHODS

This mini-review will cover aspects of Mn toxicokinetics and its impact on brain neurotransmission, as well as its Janus-faced effects on humans and other animal’s health.

RESULTS

The estimated safe upper limit of intracellular Mn for physiological function is in anarrow range of 20 to 53μM.Therefore, intake of higher levels of Mn and the outcomes have been well documented.

CONCLUSION

The metal affects mostly the brain by accumulating in specific brain areas, altering cognitive functions and locomotion, thus severely impacting the health of the exposed organisms.

Keywords: Manganese, Trace elements, Manganism, Neurotoxicity

1. Introduction

Manganese (Mn) is a naturally occurring element, present in rocks and soils, air, water and food. It is an essential nutrient, needed for a variety of functions ranging from bone mineralization, protein and energy metabolism, and metabolic regulation to cellular protection[1, 2]. Mn serves as a co-factor for several enzymes that control the above cited functions and is easily obtained from the diet, as is present in several foods[3]. Although rare, Mn deficiency is severe and affects several organs [2].

On the other hand, Mn overexposure is a public health concern due to its widespread industrial usage and the risk for environmental contamination[4]. Anthropogenic activities as iron and stainless-steel production, formation of aluminumalloys, use of antiknock additive in gasoline, and application of fungicides, are a few sources that increase Mn levels in the environment[5, 6]. Mn is mainly absorbed by the gastrointestinal and respiratory tracts and uptake by cells through many transporters, some of them recently reported. Notably, Mn can easily cross de blood brain barrier and has a tropism by brain areas that contain dopamine, such as the basal ganglia. In these areas, Mn accumulates and causes neurotoxic effects by several mechanisms that are still being undercovered [7]. Manganism, or locura manganica, is characterized by Parkinson’s disease (PD)-like symptoms such as gait difficulties and tremors, which are not responsive to levodopa as the PD symptoms[810]. In addition, cognitive problems have been reported in children using milk formulas and patients using total parenteral nutrition, which then were found to have Mn levels above the recommended [1113]. The damage caused by Mn neurotoxicity has been widely studied, thus providing impetus for reducing Mn levels in milk and nutrition formulas, prohibition of Mn-containing antiknock additives in some countries, and for more strict occupational risk assessments[14]. Studying and understanding Mn health effects is indispensable as to prevent exposure to high levels and also for the development of therapeutic strategies against poisoning.

2. Manganese toxicokinetics

When Mn in ingested from sources as water and diet, this metal is readily absorbed in the intestine through passive diffusion or active transport via the divalent metal transporter 1 (DMT1), which also transports other divalent metals such as iron (Fe) [12, 15]. Adult humans absorb approximately 3–5% of ingested Mn [1], but this rate can be modified by age [16, 17], carbohydrate source in the diet [18], presence of phytate [19] and animal protein [20], besides the content of manganese [21] and other mineral elements in diet, especially Fe, which deficiency can increase Mn absorption [18, 21]. Interestingly, high Mn intake, either through dietary or environmental exposure, causes the gastrointestinal tract to absorb less Mn while liver increases metabolism for biliary and pancreatic excretion [22, 23]. This regulation is important in preventing dyshomeostasis of Fe, since it has been reported that Mn interferes with Fe s absorption and distribution as both trace metals are known to compete for the same transporters [24, 25].

Inhalation is the primary route of entry in most occupational exposure settings, such as mining, Mn alloy production, smelting, welding, application of pesticides containing Mn and dry alkaline battery production. Mn is easily absorbed by lungs and enters the circulation,crossing to the nervous system by two zinc transporters, ZIP8 and ZIP14, bypassing the liver and BBB [26]. Since this route delivers a great amount of Mn to the brain, manganism, or locuramanganica, was primarily described and studied in workers that inhaled Mn for a long time during occupational activities [5, 27]. Because is an irritant to the pulmonary tract, it can also cause bronchitis and decrease lung function[28].

Another exposure route is intravenous, thus bypassing the gastrointestinal regulation mentioned above and therefore promoting 100% Mn absorption. Patients under total parenteral nutrition, especially infants, may receive amounts of Mn that overcome the nutritional requirements, thus leading to poisoning [12, 13]. A recent source of intravenous exposure is by the use of methcathinone (ephedrone), a synthetic drug that contains Mn dioxide and has been associated to cognitive deficits and development of parkisonism in abusers, essentially young people [2931]. Other possible routes of exposure include in utero and dermal, which are still poorly reported.

Once in the bloodstream, Mn distribution to tissues is fast. The estimated half-life for Mn to leave plasma is 1 min [1,32], Mn is distributed from plasma to the liver (30% of total Mn), kidney (5%), pancreas (5%), colon (1%), urinary system (0.2%), bone (0.5%), brain (0.1%), erythrocytes (0.02%), and the remaining 58.18% to other soft tissues [1, 32]. Liver, pancreas, bone, kidney, and brain retain Mn more than other tissues and have the highest Mn concentrations due to the essential nature of Mn in energy production and the high energy demands of these tissues [12].

Mn transport to these tissues has been ascribed to high affinity metal transporters of Ca and Fe. In fact some of these transporters include DMT-1, ZIP8, a member of the solute carrier-39, transferrin receptor (TfR), voltageregulated and store-operated Ca2+ channels and the ionotropic glutamate receptoi Ca2+ channels [1, 12, 33]. In relation to mechanisms of cellular Mn efflux, SPCA 1 [34], ferroportin [35] and SLC30A10 [36] have been reported by playing arole. Previous data demonstrated that mutations in SPCA1 and ferroportin are known to occur in humans but do not cause a Mn toxicity phenotype [37], whereas mutations in SLC30A10 are associated to a familiar form of Parkinson’s disease [38]. This suggests that SLC30A10 is the primary Mn exporter, particularly in the digestive system, though it does not appear to be the key cellular exporter from brain.

Indeed, several studies have demonstrated that Mn can cross the blood-brain barrier (BBB). A major route of Mn influx may be mediated by TfR, the ironcarrying plasma protein [39]. In addition, Mn citrate, Mn ion and the Mn-Tf complex cross the BBB, most likely via carrier-mediated transport [40]. However, this facility in Mn across the BBB could contribute to its own toxic effect [41, 42].

Because little Mn is required to maintain physiological functions, extra Mn needs to be eliminated. The turnover of ingested Mn is relatively fast, with an average retention of 10 days [43]. Most of excess Mn is conjugated to bile by the liver and get eliminated via fecal excretion [44]. The liver plays a critical role in this process and is the main organ responsible for Mn excretion [2]. When damaged, Mn elimination is altered, resulting in its accumulation in hepatic cells and consequently increased Mn levels in the brain consistent with hepatic encephalopathy [45, 46]. Furthermore, small amounts of bile-Mn conjugates could be reabsorbed in entero-hepatic circulation and can also be detected in urine, sweat, and breast milk [15, 47].

3. Health effects of Mn

3.1. Essentiality and Deficiency

Mn is an essential nutrient for growth and development in animals, including humans, and along with other trace metals and nutrients is needed for optimal physiology. Some pathways are responsive to Mn, as those controlled by the Ataxia Telangiectasia Mutated (ATM) kinase [48], responsible for regulating immune system and the response against DNA double strand breaks. In addition, proinflammatory cytokines such as IL-6, IL-1β, and tumor necrosis factor-alpha production have been shown to be potentiated by Mn [49, 50]. In addition, metalloproteins as oxidoreductases, transferases, hydrolases, lyases, isomerases, and ligases are dependent or activated by Mn [8]. [1, 33, 51]. Particularly, the major Mn containing enzyme in mammalian brain is glutamine synthetase, which is predominantly present in astrocytes and responsible for converting the amino acid glutamate to glutamine for nitrogen clearance (Figure 1) [7, 52]. In table 1 we present the main Mn-dependent enzymes.

Figure 1. Summary of the main biological effects of Mn at recommended vs elevated levels:

Figure 1.

Mn2+-alteration of Glu transporters (EAAT), especially GLAST and GLT1 [122], impairs glutamate uptake by astrocytes resulting in an increase in extracellular glutamate concentrations [95]. The net glutamine uptake is also inhibited due to down-regulation of of SNAT1, SNAT2, and SNAT3 expression in astrocytes [90, 96]. The overall effect of manganese on GABAergic synapses is characterized by increased extracellular GABA (GABAEC) levels that is expected to be mediated through inhibition of GAT1 [103]. However, inhibition of astrocytic GAT3 was not supported by the laboratory data [110].

AMPAR - α-amino-3-hydroxy-5-methyl-4-isoxazolepropionic acid receptor; EAAT - Excitatory amino acid transporter; GABA - Gamma-aminobutyric acid; GABA-T - GABA-transaminase; GAD - Glutamate decarboxylase; GAT - GABA transporter; GLAST1 - Glutamate aspartate transporter 1; GLT1 - Glutamate transporter 1; GluR - Glutamate receptor; GOT - Glutamate:oxaloacetate transaminase; NMDAR - N-methyl-D-aspartate receptor; SNAT - Sodium-coupled neutral amino acid transporter; SSADH - Succinic semialdehyde dehydrogenase; VGLUT - Vesicular glutamate transporter

Table 1:

Mn- dependent and Mn activated enzymes

Enzyme Localization Sub-localization Function
Arginases I [130] Hepatocytes Citoplasm Amino acid metabolism
Arginases II [130] Mostly in kidneys Mitochondria Amino acid metabolism
Pyruvate Carboxylase [131] Liver, kidney and adipose tissue Mitochondria Gluconeogenesis and lipogenesis
Mn-superoxide dismutase [132] ubiquitous Mitochondria Antioxidant activity
Glutamine Synthetase [133] Brain, kidneys, and liver Both Amino acid metabolism
Protein serine/threonine phosphatase-1 (PP1) [134] ubiquitous cytosol cell survival and differentiation

To prevent Mn deficiency, small daily doses are necessary. The Institute of Medicine’s diary recommended intake for Mn suggests 2 mg/day as an adequate intake for adults and 1.2–1.5 mg/day for children. However, Mn essentiality in humans varies according of the life-stage and of the sex [1, 33]. Inadequate dietary intake of manganese results in impaired growth, poor bone formation and skeletal defects, abnormal glucose tolerance, and altered lipid and carbohydrate metabolism, and these changes probably occur by decreased MnSOD and glutamine synthetase (GS) activities [53].

Due to its ubiquity, dietary Mn deficiency is uncommon. Mn is easily found in animal and plant foods, with vegetables being the most abundant variety. Whole grains (wheat germ, oats, and bran), rice, and nuts (hazelnuts, almonds, and pecans), chocolate, tea, mussels, clams, legumes, fruit, leafy vegetables (spinach), seeds (flax, sesame, pumpkin, sunflower, and pine nuts), and spices (chili powder, cloves, and saffron) are all good examples of Mn-enriched foods[1, 26].

Although genetic changes in the uptake and export of Mn are rare, they may have severe consequences. Recent studies show that mutations in SLC39A8, a Mn transporter,decreased blood Mn levels causing reduced activity of Mn-dependent enzymes such as the β-1,4-galactosyltransferase and MnSOD, leading to dysglycosylation. This congenital disorder of glycosylation type lln (CDG2N) causes impaired mitochondrial function that leads to developmental delay, short statue, dwarfism, seizures, hypotonia, and dystonia. Suggested therapy is based on oral Mn and galactose supplementation [26, 54].

Two other genetic diseases are characterized by changes in Mn transport in cells: hypermanganesaemia with dystonia 1 (SLC30A10 deficiency) and hypermanganesaemia with dystonia 2 (SLC39A14 deficiency). In the first typethesystemic Mn accumulation (levels raised as ten times that of normal) leads to a distinct syndrome of hypermanganesaemia, polycythaemia, dystonia, chronic liver disease and depletion of iron stores. Although blood Mn levels do not reduce the treatment with chelation with EDTA-CaNa2 is effective for reducing the accumulation of Mn and treat neurological symptoms and prevent liver disease progression. In the second case, distinctfrom the type 1, the affected individuals mainly exhibit neurotoxic effects of Mn accumulation, such as progressive dystonia with signs of parkinsonism variables and, in general,hypermanganesaemia does not lead to systemic symptoms also seen in type 1 as liver disease or polycythaemia. In addition, chelation with EDTA-CaNa2 treatment is generally not effective to minimize neurological effects [26, 54].

Considering the set of factors that guarantee the essentiality of Mn in health, the imbalance in homeostasis, either due to its deficiency in the diet or genetic factors can be rare but with serious consequences. Furthermore, there is no effective treatment for type 2 genetic disorders yet and Mn supplementation in cases of deficiency may lead to toxicity. This underscores the importance of the search for new therapies and treatments.

3.2. Side and Toxic effects

Humans are easily exposed to Mn through air, soil and, consequently, water, being the main source of intoxication identified due to occupational exposure [9, 55]. Industry professionals in battery production, welding and mining operations are constantly exposed to Mn by inhalation, with reported neurotoxicity in these workers [27, 5659]. Neurological damage with Mn accumulation in various areas of the midbrain such as globus pallidus, substantia nigra, subthalamic nucleus, putamen, caudate nucleus and dentate nucleus has been described [31, 60, 61]. Notably, low-level occupational exposure with airborne Mn concentrations within or below these occupational standards may also be detrimental [9, 62].

As already mentioned. Mn is necessary to control numerous metabolic functions. However, exacerbated exposure to this metal affects several biological activities, depending on the levels, routes of exposure, as well as gender and age of the exposed subject [3]. Although the main focus of toxicity is the CNS, high Mn concentrations can cause hepatic, cardiac, endocrine, male reproductive disorders and nephrotoxicity [36, 63, 64]. Symptoms of Mn intoxication consist of limb stiffness, reduced response speed, intellectual deficits, mood swings, hallucinations, tremors and balance disorders, symptoms that characterize manganism, a condition that causes neurological disorders characterized by cognitive and motor abnormalities which resemble Parkinson’s disease (PD) [65,67].

The mechanisms of toxicity of Mn are not yet fully understood [6, 68]; however, some of its actions on the CNS are well-known, such as the effects on catecholamines (mainly dopamine), acetylcholine, glutamate and aminobutyric gamma acid (GABA), besides triggering mitochondrial dysfunctions by inhibiting the electron transport chain even before affecting neurons and astrocytes [6, 63, 68, 69]. Mn intoxication ordyshomeostasis is also suspected as an environmental modifier or risk factor in several neurodegenerative diseases, such as PD, amyotrophic lateral sclerosis (ALS), Huntington’s disease (HD), and Alzheimer’s disease (AD) [70]. Of note, it has been reported that excess Mn can replace copper and stabilize the prion protein (PrP), initiating its aggregation and converting it to a neurotoxic form [71, 72]. Mn can render PrP in a proteaseresistant form [71], and this has been associated with increased disease progress. Next, we will briefly discuss the main neuronal systems affected by Mn exposure.

3.2.1. Dopaminergic System

In the brain, Mn accumulates in areas rich in dopaminergic neurons, which are directly involved in motor emotional and endocrine control. Mn’spropensityto oxidize catecholamines, including dopamine (DA), decreases its concentration in the substantia nigra, leading to the onset of PD-like symptoms [73].Therefore, in the early stages of manganism, after cessation of exposure to Mn, symptoms may be reversed, whereas in patients with motor disorders, manganism is irreversible [73].

Mn-induced DA oxidation is a complex process that involves several steps in which semiquinone, aminochrome intermediates, L-cysteine, copper and NADH are involved, in its oxidation states Mn2+ and Mn3+, Mn reacts with DA through the Fenton reaction, catalyzing the auto-oxidation of the neurotransmitter, which generates reactive oxygen species (ROS) and DA-oquinone, thus leading to oxidative damage and DAergic neuronal death [73, 74].

The literature suggests that neurodegeneration caused by Mn, in addition to presenting symptoms and areas common to PD or that PD-mimicking drugs (6-hydroxydopamine / 6-OHDA, 1-methyl-4-phenylpyridide / MPP +, rotenone, paraquat), also shares multiple common effector mechanisms, causing mitochondrial dysfunction, therefore ATP depletion, oxidative stress, protein aggregation and activation of apoptotic cells [62, 73]. In C. elegans, orthologs to PD-associated genes play a role in α-synuclein toxicity and DAergic neurodegeneration, and a link between mutated α-synuclein and Mn toxicity has also been demonstrated in the worm [75, 76]. The NRAMP / DMT family of metal transporters already described in vertebrates, involving the Mn uptake pathways and toxicity, leads to developmental defects and excretory systems in C. elegans [77]. In addition, it has been shown that acute exposure to Mn leads to specific neurodegeneration in DAergic neurons sparing other neuronal systems and that this dose-dependent toxicity confirms th specificity seen in vertebrate models[78]. This same study shows that the cause of this specific neurodegeneration of DAergic neurons in the worm is the exogenous DA that potentiates Mn toxicity and its neurodegeneration and that this mechanism of toxicity requires the DAergic neuron-specific dopamine reuptake transporter, DAT-1 [78]. A summary of Mn effects on the DAergic system is illustrated in Figure 2.

Figure 2. General effects of Mn2+ exposure in dopaminergic neurons.

Figure 2.

The net effects of Mn exposure in dopaminergic neurons are characterized by reduced dopamine levels resulting from various mechanisms [2]. Particularly, dopamine transporters, VMAT2 and DAT, are significantly down-regulated by manganese exposure leading to impaired dopamine handling in dopaminergic synapse [123]. In addition, decreased DAT activity may also occur due to DAT internalization [124]. Manganese exposure also results in increased dopamine oxidation involving Fenton chemistry, also resulting in reduced dopamine availability [125]. Recent findings also demonstrate that Mn2+ may reduce activity of tyrosine hydroxylase, a rate-limiting enzyme of dopamine synthesis [126], although the effect is shown to be dose-, time- [127], and age-dependent [6]. These data corroborate the observation of a significant reduction in tyrosine hydroxylasepositive neurons in substantia nigra pars compacta in response to manganese treatment [128]. In addition to modulation of dopamine levels, manganese exposure was also shown to modulate dopamine receptor expression and function [129].

3-MT - 3-Methoxytyramine; COMT - Catechol-O-methyltransferase; D1/2R - Dopamine receptor ½; DAT2 - Dopamine transporter; DOPA - 3,4-Dihydroxy-L-phenylalanine; DOPAC - 3,4-Dihydroxyphenylacetic acid; MAO - Monoamine oxidase; VMAT2 Vesicular monoamine transporter 2

3.2.2. Cholinergic System

Mn at neurotoxic levels also affects the cholinergic system. Acetylcholine (ACh) is an important excitatory neurotransmitter in the central and peripheral nervous systems, modulating essential cognitive functions such as learning, memory and locomotion [6, 79, 80]. Although the cholinergic system is not a primary target in Mn toxicity and several symptoms of PD and manganism are largely related to effects on the dopaminergic system, studies suggest that the cholinergic system may play an important role in both diseases, however many of these mechanisms are not well understood [6, 79, 80].

Mn alters choline uptake, Ach transferase (ChAT) activity, ACh release and postsynaptic ACh binding to clearance receptors [8183].Studies in rats show that brain choline uptake was inhibited in the presence of Mn2+. Mn caused significant regional inhibition of choline uptake in the hippocampus, frontal and parietal cortices, caudate and putamen suggesting that choline uptake through the brain blood barrier is probably inhibited by Mn2+[81]. Different Mn exposure have shown different effects, indicating that toxic effects on cholinergic neurons occur only at specific stages of Mn poisoning [84].

The effects of Mn on ChAT in rats after life-long exposure showed that this enzyme decreased only in 2-month-old rats [39]. Since ChAT serves as a specific marker of cholinergic activity, these observations may point to a greater neurotoxic effect of manganese and greater vulnerability of cholinergic neurons in the developing brain [85]. Oxidative stress induced by Mn may mediate the decrease in ChAT activity through the denaturation of part of the enzymatic pool [86].

AChE is the degrading enzyme of ACh and therefore responsible for terminating cholinergic response in muscarinic and nicotinic ACh receptors in the brain [80]. Effects of short-term Mn exposure on adult rats have demonstrated a controversial effect on AChE activity, as both inhibition or activation have been reported [6]. Focusing on AChE inhibition, it is known that additive or synergistic mechanisms of cellular disruption caused by Mn leads to mitochondrial dysfunction and neuronal degeneration [80]. Several studies have shown that the deleterious effect of Mn on AChE and ChAT may be mediated through the induction of oxidative stress as treatment with antioxidants has been shown efficacious in reversing these inhibitions [87, 88]. The implications of Mn effects on cholinergic signaling are impairments in emotional and environmentl stimuli responses, in learning tasks and disruption of anti-inflammatory reactions. Mn-induced cortical cholinergic dysfunction is compatible with these cognitive deficits as well as those observed in dementia [79].

3.2.3. Glutamatergic System

Glutamate (Glu) is the most abundant excitatory neurotransmitter in the brain and plays several major roles in normal brain function [89]. Glu is synthesized at the nerve endings through the Krebs cycle using glucose or can also be converted from glutamine by astrocytes. Glu is highly sensitive to changes in energy supply, thus Mn-induced mitochondrial dysfunction could cause an imbalance in this neurotransmitter’s homeostasis[7, 69, 9092]. In addition, Mn-induced ROS generation can directly inhibit Glu uptake, effectively increasing its extracellular concentrations. Studies indicate that Mn exposure may decrease the ability of astrocytes to absorb Glu, thereby increasing its excitatory potential in the synaptic cleft.This may explain the decrease in glutamate-aspartate transporter’s (GLAST) gene expression in astrocytes exposed to Mn, which would lead to a decrease in glutamate uptake, thus accumulating in the synaptic cleft and causing excitotoxicity[7, 69, 90].In nonhuman primates prolonged exposure to Mn has been associated with negative regulation of GLAST and GLT-1 transporter expression [93].

PKC stimulation significantly decreases Mn-induced astrocytic Glu uptake [91]. Studies show that increased PKC signaling by decreasing Mn-induced Glu transport has also been reported for Gin transport systems [94], The inhibitory effect of Mn on GLT-1 was reversed with the GLT-1 transcription factor mutant YY1 in astrocytes. Further studies have shown that an increase in YY1 expression upon Mn exposure was induced by NF-κB activation [95].

In addition, glutamate (Glu) and γ-aminobutyric acid (GABA) homeostasis is dependent on the metabolic interaction between neurons and astrocytes. The interaction, characterized by the glutamine (Gin)/Glu cycle (GGC) involves the synthesis of Gin by specific astrocytes and their subsequent release from the astrocytes into the extracellular space (Figure 1) [89, 90]. Impairment of the GGC has been previously described in response to Mn exposure [96, 97], since astrocytes accumulate Mn and show mitochondrial dysfunction [98]. As a consequence of the breakdown in their function and supportive role of neurons, increased glutamate levels in the synaptic cleft has been shown to cause excitotoxicity [99]. Disruption of GGC has been reported in numerous pathological conditions, such as epilepsy, cerebral ischemia, AD, PD and manganism [89].

3.2.4. GABAergic System

GABA (γ-aminobutyric acid) is known to be the major inhibitory neurotransmitter and this GABAergic system is affected by Mn; however the exact mechanisms underlying this effect are not well-known [69, 100, 101]. Several studies have suggesteda possible increase in GABA release upon exposure to Mn [102]. In contrast, it has been proposed that GABA uptake isinhibited by Mn exposure [103]. The mechanisms of Mn toxicity in the GABAergic system are poorly understood, but most likely factors such as concentration, time and exposure conditions are related to the toxic effects of Mn[100, 101, 104, 105].

GABA plays a key rolemediating the direct and indirect pathway of the basal ganglia, both with GABAergic thalamus, which then propagate to cortical regions [106, 107]. The ganglion-thalamus-cortical pathway is mainly involved in voluntary movement, fine motor control as well as in emotions, motivation and cognition that drive the movement [108]. Studies show high levels of thalamic GABA in a group of foundry workers with high Mn exposure levels [102]; however, data may vary depending on the animal model used [101, 109]. These discrepancies suggest that the effects of Mn on the GABAergic system are complex and that species differences, duration of exposure and routeof exposure may play a role in the effect of Mn neurotoxicity [6]. GABA clearance is partially performed by astrocytes, whichexpress the GABA transporter GAT3 isoform that is required to eliminate excess GABA from the synapse. The relatively high Km of GATS suggests that it plays a critical role in eliminating GABA from the synaptic cleft during Mn neurotoxicity [110]; however, with increasing Mn concentrations, the protective function of astrocytes may be compromised [110].

It is know that GABA biosynthesis depends strictly on the adequate supply of Glu within GABAergic neurons and subsequent conversion of Glu to GABA by Glu decarboxylase (GAD) [111]. Therefore, the mechanisms responsible for GGC between astrocytes and neurons are fundamental to brain physiology [7]. There are still many questions regarding the exact mechanism of Mn toxicity on the GABAergic system; however the dependence that exists between Glu and GABA suggests they are intertwined.

4. Perspectives and Concluding Remarks

The research on Mn’s effects in different animals has provided scientific basis for the understanding of its role in several biochemical and physiological processes. Research in this field has also enabled the understanding of the effects caused by Mn exposure and its putative mechanisms. These opposing biological effects are summarized in Figure 1.

The interaction between Mn exposure and genetic models for neurodegenerative diseases has been a subject of recent attention. In a C. elegans model, it has been demonstrated that wildtype human α-synuclein has a neuroprotective effect when mutants for PD genes were exposed to Mn [112]. On the other hano, evidence from human neuroblastoma cell lines SH-SY5Y and SKN-MC demonstrated that Mn exposure resulted in synergistic exacerbation of cellular toxicity with concomitant overexpression of a-synuclein [113, 114]. In addition, in vitro and in vivo models for Huntington’s disease (HD) have demonstrated that mutated huntingtin may affect Mn homeostasis by reducing its levels, impairing urea cycle (contributing to HD striatal urea-cycle pathophysiology) [115], and inhibiting autophagy (which increases protein aggregation and cell death) [116]. Striatal cells expressing mutant huntingtin appeared to be more resistant to Mn than wildtype cells secondary to reduced Mn accumulation, a finding that was also reproduced in vivo [117, 118]. In addition, Mn supplementation has been shown to restore autophagic function and promote aggregate clearance[116].

Other focus areas that have been subject to recent studies are the molecular targets of Mn, in hope of developing new pharmaceutical modalities to counteract the neurotoxic effects of Mn. Such mechanisms include transporters [119], transcriptional factors and modulating proteins [120, 121]. In addition, neuroprotective small molecules which might be effective in attenuating intracellular Mn levels, have been studied and recently reviewed by Peres et al [6].

There remain many gaps to be filled regarding Mn kinetics, additional mechanisms of toxicity and its role in triggering and propagating neurodegenerative diseases. The impacts of this metal needs to be further explored and elucidated since its deficiency or excessive levels can cause serious health conditions.

Acknowledgements

MA and ABB were supported in part by grants from the National Institute of Environmental Health Sciences, NIEHS, R01ES07331, R01ES10563. MA was also supported in part bygrant #R01ES020852. DSA is recipient of CNPq researcher scholarship and supported by CNPq (Universal Grant) 453963/2014-5, FAPERGS/PqG # 18/2551-0000434-0, CNPq/FAPERGS/DECIT/SCTIE-MS/PRONEM #16/25510000248-7 and PROPPI/UNIPAMPA. ATGS is recipiente of schollarship from Coordenaçäo de Aperfeiçoamento de Pessoal de Nivel Superior - Brasil (CAPES) Finance Code 001.

Footnotes

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