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The Journal of Neuroscience, September 1, 2002, 22(17):7408-7416
In Vitro Neurotoxicity of Methylisothiazolinone, a
Commonly Used Industrial and Household Biocide, Proceeds via a Zinc and
Extracellular Signal-Regulated Kinase Mitogen-Activated Protein
Kinase-Dependent Pathway
Shen
Du,
BethAnn
McLaughlin,
Sumon
Pal, and
Elias
Aizenman
Department of Neurobiology, University of Pittsburgh School of
Medicine, Pittsburgh, Pennsylvania 15261
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ABSTRACT |
Neurodegenerative disorders in humans may be triggered or
exacerbated by exposure to occupational or environmental agents. Here,
we show that a brief exposure to methylisothiazolinone, a widely used
industrial and household biocide, is highly toxic to cultured neurons
but not to glia. We also show that the toxic actions of this biocide
are zinc dependent and require the activation of p44/42 extracellular
signal-regulated kinase (ERK) via a 12-lipoxygenase-mediated pathway. The cell death process also involves activation of NADPH oxidase, generation of reactive oxygen species, DNA damage, and overactivation of poly(ADP-ribose) polymerase, all occurring downstream from ERK phosphorylation. The toxic effects of methylisothiazolinone and related biocides on neurons have not been reported previously. Because of their widespread use, the neurotoxic consequences of both
acute and chronic human exposure to these toxins need to be evaluated.
Key words:
neurotoxicity; isothiazolone; biocide; oxidation; necrosis; zinc; glutathione; ERK; lipoxygenase; NADPH oxidase; PARP
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INTRODUCTION |
There is mounting evidence that a
number of neurodegenerative disorders may be triggered or exacerbated
by exposure to occupational or environmental agents (Lohmann et al.,
1996 ; Gorell et al., 1999 ; Andersen et al., 2000 ; Betarbet et al.,
2000 ; Olden and Guthrie, 2001 ). Unfortunately, we have little or no
information about the potential negative impact on the brain for many
commonly used substances. In this study, we have focused on
2-methyl-4-isothiazolin-3-one (MIT), a cyclic, sulfur-containing
biocide for which there are no published data available regarding its
neurotoxic properties, although we have found it to be highly toxic to
neurons in vitro.
Isothiazolinone (or isothiazolone)-derived biocides, such as Kathon CG
[a 3:1 mixture of 5-chloro-2-methyl-4-isothiazolin-3-one (CMIT) and
MIT], are widely used for controlling microbial growth in
water-containing solutions (Collier et al., 1990 ). The biocidal applications of these agents range from industrial water storage tanks
to cooling units, in processes as varied as mining to energy production. Their widespread use has resulted in a large number of
reported cases of human occupational exposure. This occurs primarily,
but not exclusively, when workers come into contact with stock
solutions (containing 15 gm/l or 0.1 M of the active ingredients) during the dilution process, usually resulting in caustic
burns, contact dermatitis, and allergic sensitization (Ng and Tay,
1996 ; Primka and Taylor, 1997 ). Nonoccupational exposure to
isothiazolinones by the general population also occurs, albeit at much
lower concentrations. Because of their use in dehumidifiers, these
compounds can be detected in air-conditioned indoor air (Nagorka et
al., 1990 ) and are also present in a very large number of commonly used
cosmetics (Rastogi, 1990 ). The long-term consequences of low-level
chronic exposure to isothiazolinones on the CNS have not been investigated.
Isothiazolinones kill microorganisms by interacting and oxidizing
accessible cellular thiols (Collier et al., 1990 ). We have shown
previously that another thiol oxidant, 2,2'-dithiodipyridine (DTDP),
induces neuronal cell death by liberating zinc from intracellular, thiol-containing stores, such as metal-binding proteins (Aizenman et
al., 2000 ). The intracellular release of
Zn2+ can lead to activation of p38
mitogen-activated protein (MAP) kinase (MAPK), subsequent enhancement
of voltage-gated potassium currents, and caspase-dependent cell death
(McLaughlin et al., 2001 ). A similar zinc-p38-K channel pathway can be
activated by nitric oxide-derived species (Pal et al., 2001 ). We
hypothesized that isothiazolinone biocides would be neurotoxic by
activating similar signaling molecules. In this study, we describe the
neurotoxic cascade induced by MIT, which, contrary to our expectations,
proceeds via the activation of p44/42 extracellular signal-regulated
kinase (ERK) MAPK, rather than p38, and culminates in the demise of
neurons via a caspase-independent pathway.
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MATERIALS AND METHODS |
Materials.
Bis[amino([1-aminophenyl]thio)methylene]butanedinitrile
(U0126), 2'-amino-3'-methoxyflavone (PD98059),
8-hydroxy-2-methylquinazoline-4-one (NU1025), and
N-(5-(3-dimethylaminobenzamido)-2-methylphenyl)-4-hydroxybenzamide (ZM336372) were purchased from Calbiochem (La Jolla, CA).
trans-1-(4-hydroxycyclohexyl)-4-(fluorophenyl)-5-(2-methoxy-pyrimidin-4-yl)imidazole (SB239063) was a gift from GlaxoSmithKline Pharmaceuticals (King of Prussia, PA). ERK and p38 antibodies were from Cell Signaling Technology (Beverly, MA); 12-lipoxygenase (12-LOX) antibody was from Cayman Chemical Co. (Ann Arbor, MI). Unless specified, all other chemicals were purchased from Sigma (St. Louis, MO).
Cell culture and toxicity assay. Mixed cultures of rat
cortical neurons and glia were prepared as described previously
(Hartnett et al., 1997 ). In brief, cortices from embryonic day 16 Sprague Dawley rat fetuses were isolated and incubated in trypsin for 2 hr at 37°C. Cortices were dissociated in 10 ml of plating medium containing DMEM (Invitrogen, Gaithersburg, MD), 10% F12 nutrients, and
10% bovine calf serum (Hyclone, Logan, UT). Astrocyte cultures were
prepared from postnatal day 5 Swiss-Webster mice as described by Noble
and Mayer-Proschel (1998) and were a kind gift from C. Lagenaur
(University of Pittsburgh). A few toxicity experiments were performed
on neuron-enriched cultures (Aizenman et al., 2000 ; McLaughlin et al.,
2001 ), but we found that in this system, MIT toxicity had a moderate
excitotoxic component, likely because of the inability of these
cultures to effectively take up glutamate released by injured or dying
cells (Rosenberg and Aizenman, 1989 ). As such, proteins for immunoblots
(see below) were generally harvested from MIT-treated, neuron-enriched
cultures that had also been exposed to the NMDA receptor antagonist
(+)-5-methyl-10,11-dihydro-5H-dibenzo [a,d] cyclohepten-5,10-imine
maleate (MK-801; 10 µM). We found, however, that the expression profile of proteins of interest was unaffected by the presence of MK-801, suggesting that the excitotoxic component was a late event in cell death and did not impact on the
upstream signaling pathways reported here. All toxicity experiments shown were performed on mixed 4-week-old cultures in which the excitotoxic component was absent and would not confound the
interpretation of the results. Cells were exposed to MIT for 10 min in
MEM (plus 0.01% BSA and 25 mM HEPES). Unless
otherwise noted, cells were normally exposed to neuroprotective
compounds 10 min before, during, and in the 18-20 hr after MIT
exposure. In addition to the pre-exposure and coexposure period,
N,N,N',N'-tetrakis (2-pyridylmethyl) ethylenediamine (TPEN)
was included for 10 min in the postexposure period. Cell viability was
determined 18-20 hr after MIT exposure using a lactate dehydrogenase
(LDH)-based in vitro toxicity assay kit (Sigma). Toxicity
data were either represented as averaged raw LDH values or normalized
to the toxicity induced by 100 µM MIT alone
(100% toxicity) (Fig. 1). In the former
case, an ANOVA followed by post hoc Bonferroni tests were
used to assess a significant deviation from control, whereas in the
latter case, one-sample tests (vs 100%) were performed.

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Figure 1.
MIT is neurotoxic in vitro.
A-D, Phase-contrast micrographs of rat cortical
cultures 24 hr after being treated for 10 min with either vehicle
(A), 100 µM MIT
(B), 10 µM TPEN
(C), or 100 µM MIT plus 10 µM TPEN (D). Note the relative
absence of phase-bright (live) neurons in B and the
neuroprotective actions of TPEN in D. E,
Concentration-toxicity relationship for MIT in control mixed cultures
(Neurons/Glia) and in sister cultures that had been
treated 72 hr earlier with kainic acid (1 mM, 24 hr) to
remove the neuronal component (Glia). MIT results in a
large increase in LDH release (an index of cell death) in the mixed but
not in the glial cultures. LDH release induced by a 1 hr exposure to
200 µM NMDA (a selective neuronal toxin) is included for
comparison. Values represent the mean ± SD for a total of six
experiments in the mixed cultures and three experiments in the
kainate-treated cells; **p < 0.01;
***p < 0.001. The inset shows
a representative experiment, in triplicate (mean ± SD), performed
on primary mouse astrocytes. A 10 min exposure to 100 µM
MIT was not toxic to the cells. Total LDH in the culture was measured
after cell lysis; ***p < 0.001. F, LDH activity measured with known concentrations of
the enzyme alone or in the continuous presence of 100 µM
MIT. No differences were observed between the two standard curves.
Values represent the mean ± SD of three independent
measurements.
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Western blot assessment of MAPK activation. Proteins were
harvested from neuron-enriched cultures to prevent a potential glial contamination of the signal. All results were confirmed with
immunostaining and with immunoblots using proteins harvested from mixed
cultures. Total protein extract was prepared as described previously
(McLaughlin et al., 2001 ). Equal protein concentrations were separated
using 7.5% Criterion gels (Bio-Rad, Hercules, CA). Proteins were then transferred to polyvinylidene difluoride membranes (Amersham
Biosciences, Piscataway, NJ) and blocked for 1 hr at room temperature
with 5% milk in PBS/0.1% Tween 20. Membranes were then incubated
overnight in primary antibodies against ERK and p38 MAPK diluted 1:1000 in blocking solution. Membranes were then treated with an
HRP-conjugated anti-rabbit secondary antibody (Santa Cruz
Biotechnology, Santa Cruz, CA) for 1 hr at room temperature, placed in
2 ml of ECL substrate (Amersham Biosciences) for 1 min at room
temperature, and exposed to X-OMAT film (VWR Scientific, West Chester, PA).
Immunostaining. Cultures were fixed in 10% formaldehyde and
then permeabilized with 0.3% Triton X-100. Cells were blocked with 1%
BSA diluted in PBS and incubated in 12-LOX primary antibody (1:100)
overnight. Cultures were then washed in PBS for a total of 20 min and
incubated in cy-2 anti-rabbit secondary antibody for 60 min. After
additional washes, coverslips were mounted, and fluorescence was
visualized with an Olympus AX70 confocal microscope system. Olympus
Fluoview software was used to scan and view the resulting images.
Glutathione assay. Cultures were exposed to 100 µM MIT for 10 min and rinsed with MEM. Five
minutes later, cells were rinsed, scraped off the dish, and resuspended
in a lysis buffer on ice. The supernatant was collected and incubated
with a solution containing monochlorobimane (MCB), a dye that has a
high affinity for glutathione (GSH) (Biovision, Mountain View,
CA). Free MCB is nonfluorescent, whereas the GSH-MCB adduct emits at
461 nm after excitation at 380 nm. Fluorescence measurements were
performed in a fluorimetric plate reader and normalized to protein
content (BCA; Pierce, Rockford, IL).
Terminal deoxynucleotidyl transferase-mediated dUTP nick-end
labeling staining. Cells were fixed in 4% paraformaldehyde for terminal deoxynucleotidyl transferase-mediated dUTP nick-end labeling (TUNEL) staining as per the manufacturer's specifications (Promega, Madison, WI). Briefly, cells were washed twice in PBS and permeabilized in 0.1% sodium citrate with 0.1% Triton X-100. Biotinylated
nucleotide was incorporated at the 3'-OH DNA. Positive control slides
were generated by incubating cells with DNase I, whereas adding
labeling mix without terminal transferase to DNase-treated cells
generated negative control slides. Horseradish peroxidase-labeled
streptavidin was then bound to biotinylated nucleotides and reacted
with diaminobenzidine. Cells were counterstained with 0.25% thionin.
Electrophysiological measurements of K+
currents. Electrophysiological recordings were performed
using the whole-cell configuration of the patch-clamp technique as
described previously (McLaughlin et al., 2001 ). The extracellular
solution contained (in mM): 115 NaCl, 2.5 KCl, 2 MgCl2, 10 HEPES, 0.1 1,2-bis(2-aminophenoxy)ethane-N,N,N,N-tetraacetic acid, and
10 D-glucose, pH 7.2; 0.1 µM tetrodotoxin was added to inhibit
voltage-gated sodium channels. The intracellular (electrode) solution
contained (in mM): 120 KCl, 1.5 MgCl2, 1 CaCl2, 2 Na2ATP, 1 BAPTA, and 10 HEPES, pH 7.2. Measurements were obtained under voltage clamp with an Axopatch 200 amplifier (Axon Instruments, Foster City, CA) and pClamp software (Axon
Instruments) using 2 M electrodes. Partial compensation ( 80%) for
series resistance was performed in all cases. Currents were filtered at
2 kHz and digitized at 10 kHz (Digidata; Axon Instruments). Potassium
currents were evoked with a series of incremental 80 msec voltage steps to 35 mV from a holding potential of 70 mV. Steady-state current amplitudes were measured relative to baseline 70 msec after the initiation of each voltage step and normalized to cell capacitance.
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RESULTS |
MIT is neurotoxic to neurons in culture
Rat cortical cultures exposed for 10 min to 100 µM
MIT underwent widespread neuronal cell death within 24 hr. MIT toxicity spared the underlying glial cell layer (Fig. 1A,B).
Exposure to increasing concentrations of MIT augmented the number of
injured neurons, as measured by the release of LDH from the cultures
(Fig. 1E). Sister cultures that had been exposed
previously to 1 mM kainate overnight to remove
the neuronal component of the cultures (Aizenman et al., 2000 ) showed a
much less pronounced increase in LDH release on MIT exposure (Fig.
1E), suggesting that gliotoxicity was relatively low
even at high concentrations of this agent. This observation was
confirmed in primary astrocyte cultures (Fig. 1E,
inset). This argues that neurons are appreciably more
sensitive than glial cells to the toxic actions of MIT. Although cells
are exposed to MIT for only 10 min, and the LDH is assayed 24 hr after the MIT exposure, we confirmed that MIT (100 µM) does not interfere with the cell death
assay itself by using known concentrations of the enzyme (Fig.
1F). We also evaluated whether NMDA receptor-mediated excitotoxicity was indirectly responsible for the effects of MIT. Inclusion of 10 µM MK-801 during and after MIT
exposure did not afford any neuroprotection to the cultures (data not
shown). NMDA receptors are solely responsible for the induction of
glutamate excitotoxicity in our system (Aizenman and Hartnett, 1992 ;
Sinor et al., 2000 ).
A role for Zn2+ in MIT toxicity
Previous studies in our laboratory reported that thiol-oxidizing
agents, such as DTDP, triggered neuronal cell death by inducing intracellular zinc release (Aizenman et al., 2000 ; McLaughlin et al.,
2001 ). Thus, we sought to investigate whether MIT toxicity might also
involve zinc. We observed that TPEN, a cell-permeable, metal-chelating
agent with very high affinity for zinc and iron and only moderate
affinity for calcium (Arslan et al., 1985 ), rescued MIT-induced
neuronal death in a concentration-dependent manner (Figs.
1C,D, 2A).
The protective effects of 10 µM TPEN were
confirmed with cell counts (Fig. 2A,
inset). Pretreatment of 1 µM TPEN
with equal molar zinc chloride abolished its neuroprotective properties
(Fig. 2B). In contrast, TPEN pretreated with equal molar iron was still able to protect neurons from MIT toxicity (Fig.
2B). A similar paradigm was used against DTDP
toxicity where an identical outcome was observed (Fig. 2C).
These results strongly suggest that zinc contributes to MIT
neurotoxicity.

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Figure 2.
Role of Zn2+ in MIT toxicity.
A, Cortical cultures were exposed to 100 µM MIT (10 min) in the absence or presence of various
concentrations of TPEN. LDH release for each experimental group was
normalized to that generated by MIT alone (100% relative toxicity) in
this and subsequent figures. Note that the toxicity after MIT exposure
decreases as a function of TPEN concentration. Values represent the
mean ± SEM (n = 4);
**p < 0.01; ***p < 0.001; significantly different from MIT alone. The inset
confirms the neuroprotective actions of 1 µM TPEN, as
determined by cell counting; ***p < 0.001. B, The neuroprotective action of 1 µM TPEN
was eliminated by preincubating the chelating agent with equimolar zinc
(ZnCl2) but not iron (FeSO4);
*p < 0.05; **p < 0.01 (n = 4). C, Similar to
B above, except that neurons were killed by 100 µM DTDP instead of MIT (Aizenman et al., 2000 ; McLaughlin
et al., 2001 ) (n = 3).
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MIT-induced cell death is triggered by ERK activation
Because zinc appears to play a critical role in both DTDP and MIT
toxicity, we anticipated that downstream-signaling pathways leading to cell death would be similar. In our
previous study with DTDP, we observed that intracellularly liberated
zinc activated p38 MAPK within 30 min, which in turn induced an
enhancement of voltage-dependent K+
currents and caspase cleavage, measured 3-6 hr later (McLaughlin et
al., 2001 ). Therefore, we investigated whether p38 MAPK activation and
K+ channel enhancement would follow MIT
exposure. In contrast to our results with DTDP, phosphorylation of p38
was completely absent in cells treated with MIT (Fig.
3A, top panels). In
addition, SB239063, a specific p38 MAPK inhibitor that is effective in
protecting neurons against DTDP toxicity (McLaughlin et al., 2001 ), did
not afford any neuroprotection against MIT (Fig. 3B).
Moreover, whole-cell patch-clamp recordings did not reveal any delayed
enhancement of voltage-gated K+ currents
after MIT treatment (Fig. 3C). Consistent with this finding,
neither tetraethylammonium (TEA) nor high extracellular K+ concentrations (25 mM) had any significant effects on MIT-induced cell death (Fig. 3D), suggesting that
K+ efflux (Yu et al., 1997 ) was not
involved in the MIT-induced death pathway.

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Figure 3.
MIT toxicity involves ERK activation.
A, Immunoblots of cell extracts from cortical cultures
harvested at various time points after a 10 min exposure to 100 µM MIT. Proteins were separated by SDS-PAGE and probed
with antibodies specific to the phosphorylated and nonphosphorylated
forms of both p38 and p44/42 ERK. Note the absence of phosphorylated
p38 (Ph-p38) at all time points and the early increase
in phosphorylated ERK (Ph-ERK) after MIT
exposure. The MEK inhibitor U0126 (10 µM) and the zinc
chelator TPEN (1 µM) completely blocked ERK
phosphorylation (30 min). Similar results were obtained in three
additional experiments. Aniso, Anisomycin;
Con, control. B, MIT toxicity was
not blocked by the p38 inhibitor SB239063 (20 µM) but was
significantly inhibited by the MEK inhibitors U0126 (10 µM) and PD98059 (40 µM). Results represent
the mean ± SEM of three to four independent experiments;
*p < 0.05. C, A lack of p38
involvement in MIT toxicity was confirmed by a lack of enhancement in
potassium channel currents 3-4 hr after a 10 min MIT (100 µM) exposure (compare with McLaughlin et al., 2001 ).
Results represent the mean ± SD current density
(n = 6, 11) for potassium currents evoked in
voltage-clamped cortical neurons by stepping the voltage to 10 mV
from a holding voltage of 70 mV. Con, Control.
Insets, Examples of whole-cell potassium currents
obtained in two separate cortical neurons ~3 hr after a 10 min
exposure to vehicle or MIT. Currents were evoked by a series of steps
to 35 mV from a holding voltage of 70 mV. D, Lack of
neuroprotection against MIT by the following agents: TEA (10 mM), high extracellular potassium (25 mM),
cyclohexamide (CHX, 3.5 µM), and BAF (20 µM); data represent the mean ± SEM
(n = 4-9).
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Although generally associated with cell survival and proliferation
pathways (Xia et al., 1995 ; Derkinderen et al., 1999 ), activation of
ERK, another member of the MAPK family, has been reported to be
responsible for neuronal cell death after oxidative stimuli (Stanciu et
al., 2000 ). ERK activation has also been implicated in neuronal cell
death after focal cerebral ischemia (Alessandrini et al., 1999 ),
seizures (Murray et al., 1998 ), and zinc exposure (Seo et al., 2001 ).
Therefore, we examined whether ERK activation was present after MIT
treatment and tested whether such activation was responsible for the
ensuing neurotoxicity. A time course study of ERK phosphorylation
revealed a transient activation of p44/42 ERK within 30 min of MIT
exposure (Fig. 3A, middle panels). The levels of
phosphorylated p44/42 ERK quickly returned to baseline 1 hr after
treatment. U0126, a specific inhibitor of the ERK kinases MAP kinase
kinase (MEK) 1/2, blocked MIT-induced ERK phosphorylation (Fig.
3A) as well as MIT toxicity (Fig. 3B). PD98059, a
structurally unrelated MEK 1/2 inhibitor, exhibited similar levels of
protection against MIT toxicity (Fig. 3B). ERK activation
was also prevented by TPEN (Fig. 3A, bottom
panels), suggesting that the neuroprotective actions of the metal
chelator occurred upstream from the phosphorylation of the MAPK.
ERK-mediated cell death after MIT exposure was not affected by the
protein synthesis inhibitor cycloheximide or by butoxy-carbonyl-aspartate-fluoromethyl ketone (BAF), a broad-spectrum cysteine protease inhibitor (Fig. 3D). This indicates that
MIT neurotoxicity proceeds without the synthesis of new proteins and is
independent of caspase activation.
MIT-induced ERK phosphorylation is mediated via activation
of 12-lipoxygenase
It has been suggested that lipoxygenase metabolites of arachidonic
acid (AA) can activate the ERK cascade (Rao et al., 1994 ; Chakraborti
and Chakraborti, 1998 ; Alexander et al., 2001 ; Chang and Wang, 2001 ).
Indeed, zinc can bind to and stimulate phospholipase A2
(PLA2) (Lindahl and Tagesson, 1996 ), an enzyme
that releases arachidonic acid from lipids, and lipoxygenases have been
widely associated with activation of cell death pathways (Maccarrone et
al., 2001 ). Furthermore, 12-LOX, the predominant LOX present in the
brain (Bendani et al., 1995 ), has been implicated in neuronal oxidative
injury (Li et al., 1997 ; Stanciu et al., 2000 ). Based on this
information, we tested whether a 12-LOX inhibitor could prevent MIT
toxicity and block MIT-induced ERK activation. We used
5,6,7-trihydroxyflavone (baicalein) (Cho et al., 1991 ), a 12-LOX
inhibitor that inhibits oxidative stress-induced ERK activation (Stanciu et al., 2000 ) and has been shown to be neuroprotective (Li et
al., 1997 ). This drug effectively abrogated both MIT neurotoxicity (Fig. 4A) and
MIT-initiated ERK activation (Fig. 4B). Similar protective effects were obtained with the broad-spectrum LOX inhibitor 2,3,5-trimethyl-6-(12-hydroxy-5-10-dodecadiynyl)-1, 4-benzoquinone (AA861) (Li et al., 1997 ) (Fig. 4A). The
neuroprotective actions of two PLA2 inhibitors,
bromoenol lactone (20 µM) and quinacrine (20 µM), could not be properly evaluated, because
these substances were toxic to neurons on their own.

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Figure 4.
MIT toxicity and MIT-induced ERK activation
requires 12-LOX activity. A, MIT (100 µM)
toxicity was significantly inhibited by the 12-LOX inhibitor baicalein
(20 µM) and by the less-specific LOX inhibitor AA861 (1 µM). Results represent the mean ± SEM
(n = 3); ***p < 0.001. B, Immunoblots demonstrate that MIT-induced ERK
activation is blocked by baicalein. Baicalein had no effect on ERK
activation when added alone (data not shown). Similar results were
observed in a total of three independent experiments.
Phospho-ERK, Phosphorylated ERK.
C-F, 12-LOX immunostaining in control cultures
(C) and 5 min after a 10 min exposure to 100 µM MIT alone (D) or in the presence
of either 20 µM baicalein (E) or 1 µM TPEN (F). LOX activation is
usually accompanied by its translocation to the cell membrane.
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LOX activation has been associated with its translocation to the cell
membrane (Hagmann et al., 1993 ). As such, activation of 12-LOX was
confirmed by detecting said translocation MIT exposure (Hagmann et al.,
1993 ; Li et al., 1997 ). We observed a dramatic redistribution of 12-LOX
antibody staining to the cell membrane within 5 min after a 10 min
exposure to MIT (Fig. 4A,B). Coexposure of the cells
to MIT with either TPEN or baicalein completely prevented the
translocation of 12-LOX to the cell membrane (Fig.
4C,D).
MIT-induced decrease in GSH levels
Decreases in intracellular GSH can be directly correlated with
increased 12-LOX activity, possibly as a consequence of eliminating the
tonic inhibition of the enzyme by GSH itself (Hagmann et al., 1993 ;
Shornick and Holtzman, 1993 ; Li et al., 1997 ). We speculated that MIT
induction of 12-LOX activity could be partly attributable to the
oxidation of GSH to oxidized glutathione (GSSG). Indeed, Fuller et al.
(1985) reported that the interaction of benzothiazolone (BIT, a
structural analog of MIT) with GSH resulted in the formation of GSSG
and thiol dimers of the ring-opened form of BIT (mercaptobenzamide). Thus, we tested whether MIT exposure would result in a decrease in GSH
levels in our cultures. Cells were exposed for 10 min to MIT, and cell
lysates were collected 5 min later and assayed for GSH activity. MIT
was able to rapidly decrease cellular GSH levels by ~40% (Fig.
5). This suggests that MIT-induced
activation of 12-LOX activity might be mediated in part by a direct
oxidation of GSH. However, TPEN did not block the MIT-induced effects
on GSH levels, suggesting that the
Zn2+-mediated component of 12-LOX
activation occurs independently of this process. This result also
suggests that GSH depletion is necessary but not sufficient for the MIT
toxicity pathway to be activated.

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Figure 5.
MIT induces a decrease in GSH activity. Cultures
were exposed to 100 µM MIT for 10 min and assayed for
cellular GSH activity 5 min later. MIT induces a decrease in GSH
levels, which can be prevented by coexposure to the cysteine reagent
NAC (1 mM) but not by the antioxidant trolox (100 µM) or by TPEN (1 µM) (mean ± SEM;
n = 3-4); **p < 0.01.
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MIT-induced ERK activation and reactive oxygen species
Li et al. (1997) suggested that neuronal oxidative injury requires
a 12-LOX-dependent production of reactive oxygen species (ROS). Because
several reports have indicated that ROS are involved in ERK activation,
including those that are generated after
Zn2+ exposure (Seo et al., 2001 ), we
tested whether ROS production downstream from 12-LOX was responsible
for ERK activation and contributed to the MIT toxicity. We observed
that two antioxidants, N-acetylcysteine (NAC) and trolox,
almost completely abrogated MIT-induced cell death in our cultures
(Fig. 6A). In initial
experiments, the antioxidants were applied before, during, and after
MIT exposure to ensure full neuroprotection. Surprisingly, NAC but not
trolox prevented ERK activation (Fig. 6B). The
simplest explanation to account for this observation is that ROS
production occurs downstream from ERK phosphorylation. NAC, being a
thiol-containing agent like GSH, can directly interact with MIT,
whereas trolox, being a true radical scavenger, must be working at a
point subsequent to GSH depletion. Indeed, exogenous GSH mimicked the
effects of NAC in blocking MIT toxicity (Fig. 6A). To
further test this hypothesis, we applied NAC and trolox during the
post-MIT exposure period only. Under these circumstances, NAC was no
longer neuroprotective (Fig. 6A), nor did it prevent
MIT-induced ERK activation (Fig. 6B). Trolox,
however, continued to effectively protect neurons when applied only
after the MIT treatment (Fig. 6A). Finally, we
observed that NAC, but not trolox, could block the effects of MIT on
GSH depletion (Fig. 5). A glutathione peroxidase analog, ebselen (10 µM) (Mueller at al., 1984 ; Wendel et al.,
1984 ), mimicked the actions of trolox. Together, these results strongly
suggest that the injurious production of ROS occurs downstream from ERK activation.

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Figure 6.
Effect of antioxidants and PARP inhibitors on
MIT-induced toxicity. A, MIT toxicity was abrogated by
including NAC (1 mM), trolox (100 µM), and
GSH (1 mM) before, in conjunction with, and after a 10 min
MIT (100 µM) treatment. NAC, but not trolox, lost its
neuroprotective properties when included in the postexposure period
only (post). The PARP inhibitors NU1025 (5 µM) and DPQ (1 µM) were also protective.
Results represent the mean ± SEM for three to four experiments;
**p < 0.01; ***p < 0.001. B, Immunoblots demonstrating that ERK
phosphorylation after MIT exposure could be abolished by the NAC
treatment but not by trolox (before exposure, during exposure, and
after exposure). The effect of NAC was absent when the antioxidant was
included in the postexposure period only. Trolox, NAC, and NU1025 had
no effect on ERK activation when added alone (data not shown). Similar
results were obtained in a total of three independent experiments.
These results suggest that ROS production and PARP activation occur
downstream from ERK phosphorylation. Phospho-ERK,
Phosphorylated ERK.
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Poly(ADP-ribose) polymerase activation is required for
MIT toxicity
DNA is vulnerable to ROS attack during oxidative stress.
Single-stranded DNA breaks activate the repair enzyme poly(ADP-ribose) polymerase (PARP) (de Murcia and Menissier de Murcia, 1994 ). Excessive DNA damage and PARP activation can deplete nicotine adenine
dinucleotide (NAD+) and impair ATP
production (Schraufstatter et al., 1986 ), a process that can lead to
neuronal cell death (Szabo and Dawson, 1998 ; Pieper et al., 1999 ).
Indeed, pharmacological and genetic disruption of PARP function has
been shown to be neuroprotective in models of cerebral ischemia
(Eliasson et al., 1997 ; Endres et al., 1997 ; Lo et al., 1998 ; Takahashi
et al., 1999 ; Moroni et al., 2001 ). Thus, we sought to determine
whether MIT-induced toxicity is accompanied by DNA damage and whether
overactivation of PARP contributes to the cell death process. The
appearance of DNA strand breaks was apparent in our cultures 4 hr after
MIT exposure (Fig. 7). Virtually no
TUNEL-positive cells were present when cells were exposed to MIT in
conjunction with the MEK inhibitor U0126 or with trolox (Fig. 7). The
importance of PARP overactivation in MIT toxicity was
evident, because two inhibitors on this enzyme, NU1025 and 3,4-dihydro-5-[4-(1-piperidinyl)butoxy]-1(2H)-isoquinolinone
(DPQ), substantially abrogated cell death (Fig. 6A).
Moreover, ROS production, DNA damage, and PARP overactivation occur
downstream from ERK activation, because NU1025 did not prevent
MIT-induced ERK phosphorylation (Fig. 6B).

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|
Figure 7.
NADPH oxidase inhibitors are protective against
MIT toxicity. A, MIT (100 µM) toxicity was
significantly inhibited by the NADPH inhibitors AEBSF (100 µM) and DPI (100 nM). Results represent the
mean ± SEM (n = 3); *p < 0.05. B, Immunoblots demonstrating that MIT-induced
ERK activation was not blocked by AEBSF or DPI. Neither of these
compounds had an effect on ERK phosphorylation when added alone (data
not shown). Similar results were observed in a total of three
independent experiments. Phospho-ERK, Phosphorylated
ERK.
|
|
NADPH oxidase inhibitors prevent MIT toxicity by acting downstream
from ERK activation
NADPH oxidase is a superoxide-generating enzyme system that is
responsible for generating the respiratory burst in phagocytic cells
(Babior, 1999 ) and has been shown recently to be present in neurons
(Tammariello et al., 2000 ). NADPH oxidase has also been implicated in
Zn2+ neuronal toxicity (Noh and Koh, 2000 )
and linked to ERK activity in several systems (Lu et al., 1993 ; Cui et
al., 2000 ; Dewas et al., 2000 ; Karlsson et al., 2000 ). We hypothesized
that MIT-induced production of ROS occurred downstream from ERK via
activation of this NADPH oxidase. Therefore, we investigated whether
NADPH oxidase inhibitors could block MIT toxicity without preventing MIT-induced ERK activation. Cultures were exposed to MIT in the presence and absence of the NADPH oxidase inhibitors
4-(2-aminoethyl)-benzenesulfonyl fluoride (AEBSF) and
diphenyleneiodonium (DPI) (Diatchuk et al., 1997 ; Li and Trush,
1998 ; Holland et al., 2000 ). Both of these substances proved to be
effective neuroprotective agents against MIT toxicity (Fig.
8A). Moreover, neither
compound blocked ERK activation (Fig. 8B), suggesting
that NADPH oxidase is a probable source of ROS production in the MIT
toxicity pathway and that its activation occurs downstream from ERK
phosphorylation.

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|
Figure 8.
MIT induces ERK-dependent DNA damage. Four hours
after a 10 min exposure to 100 µM MIT, cultures were
stained for TUNEL and counterstained with thionin. Using this
procedure, nuclei with damaged DNA are stained dark
brown (arrowheads in B),
and cells are stained purple. A, Control.
B, MIT-treated cultures. C, MIT-treated
cultures in the presence of the MEK inhibitor U0126 (10 µM). D, MIT-treated cultures in the
presence of the antioxidant trolox (100 µM). Note the
absence of TUNEL staining in A, C, and
D.
|
|
 |
DISCUSSION |
Molecular mechanism of MIT neurotoxicity
Neurons acutely exposed in vitro to MIT undergo
caspase-independent cell death. We hypothesize that a molecular cascade
that involves GSH depletion, zinc-dependent 12-LOX enzymatic activity, ERK phosphorylation, NADPH oxidase-dependent ROS production, DNA damage, and PARP overactivation mediates this process:
|
(1)
|
The temporal ordering and interdependence of these events are
strongly suggested by the fact that: (1) MIT induces a decrease in GSH
levels, (2) TPEN can block translocation of 12-LOX to the membrane, (3)
TPEN, thiol-containing agents, and a 12-LOX inhibitor can block ERK
activation and cell death, (4) inhibition of ERK activation is
neuroprotective and prevents DNA damage, and (5) inhibitors of NADPH
oxidase and PARP, as well as a nonthiol-containing antioxidant, can
block cell death without preventing ERK activation. We do not yet know,
however, how these various components are linked or whether other
cellular events are involved in this process.
The neurotoxic cascade of MIT is reminiscent, at least in part, of the
proposed pathway mediating oxidative glutamate toxicity, a process
whereby high concentrations of extracellular glutamate lead to a slow
and relatively large depletion of glutathione (GSH) via inhibition of
the cysteine transporter (Murphy et al., 1989 ). Based on results
reported by Li et al. (1997) and Stanciu et al. (2000) , the putative
mechanism mediating oxidative glutamate toxicity can be summarized as
follows:
|
(2)
|
The term
([Ca2+]i/ERK/ROS)
is listed in parentheses because the temporal ordering of these three
events has not been established. Glutamate-induced decreases in
intracellular GSH have been directly correlated with increased 12-LOX
activity, perhaps as a consequence of eliminating the tonic inhibition
of the enzyme by GSH itself (Hagmann et al., 1993 ; Shornick and
Holtzman, 1993 ; Li et al., 1997 ). An examination of equations 1 and 2 reveals that several key components are shared by both cell death
pathways, namely GSH depletion, 12-LOX activation, phosphorylation of
ERK, and the production of ROS. There are, however, some important
differences. In particular, MIT toxicity proceeds in a protein
synthesis and caspase-independent manner, whereas oxidative glutamate
toxicity depends on protein synthesis (Ratan et al., 1994a ,b ) and has
several hallmark features of apoptosis (Ratan et al., 1994b ). One
possible reason for this difference may be that MIT and oxidative
glutamate toxicity actually represent two ends of a necrotic-apoptotic
spectrum that has an initial common cellular trigger (e.g., 12-LOX
activity) but lead to activation of diverse downstream death effectors
because of differences in the severity of the overall insult. Because MIT can theoretically oxidize GSH directly, one would expect the neurotoxic cascade be triggered very rapidly, and indeed, we do see GSH
depletion and ERK activation occurring rather suddenly after MIT
exposure. Oxidative glutamate toxicity requires prolonged applications
of the amino acid, because GSH depletion occurs as a result of the
inhibition of its synthesis (Murphy et al., 1989 ; Li et al., 1997 ).
Our neuroprotection, immunoblots, and immunostaining experiments with
TPEN suggest that zinc is involved upstream from 12-LOX in the
neurotoxic cascade of MIT. We do not believe that TPEN is protective by
binding cellular iron and inhibiting Fenton generation of hydroxyl
radicals, because the pretreatment of the chelating agent with this
metal did not abolish MIT toxicity. Interestingly, Zn2+ can bind to and stimulate
PLA2 and enzymes that lead to AA release from the
membrane (Lindahl and Tagesson, 1996 ). Therefore, it is possible that
an additional pathway may be activated by MIT that is concurrent with
GSH depletion and leads to increased levels of AA. An increase in
12-LOX activity coupled with an increase in the availability of
substrate for 12-LOX (i.e., AA) may also help explain the increased
severity of the MIT insult when compared with oxidative glutamate
toxicity. It is noteworthy, however, that very low concentrations of
MIT have been shown to trigger apoptosis in HL60 cells after prolonged
exposures (Anselmi et al., 2002 ); thus, we may indeed find a similar
outcome in future chronic toxicity studies in neurons.
Our previous studies on the mechanism of DTDP toxicity, a
disulfide-containing oxidizing agent, clearly demonstrate that a rise
in intracellular Zn2+ was an early and
critical signal for induction of neuronal apoptosis (Aizenman et al.,
2000 ; McLaughlin et al., 2001 ). Activation of p38 rapidly followed
Zn2+ liberation in this system. Nitric
oxide-derived species can also effectively activate this pathway (Pal
et al., 2001 ). In those studies, however, we observed that although ERK
was phosphorylated, p38 inhibition but not MEK inhibition more
effectively blocked cell death. In addition, we noted that caspase
inhibitors were neuroprotective against DTDP toxicity, which is not the
case for MIT. We have yet to fully characterize the point of divergence for the toxic actions of DTDP and MIT, but it is likely to be intimately dependent on the activation of p38, which in the case of
DTDP appears to be also entirely Zn2+
dependent (McLaughlin et al., 2001 ).
Environmental and occupational exposure concerns regarding
MIT exposure
MIT and related biocides currently are being used in a large
number of industrial settings (Collier et al., 1990 ). In addition, many
cosmetics contain these compounds. The concentration of Kathon CG in
these household products ranges from 15 to 30 ppm, which corresponds to
~100-200 µM (for the combined CMIT and MIT) (Rastogi, 1990 ). There is no question that in addition to the many known cases of
occupational exposure to these compounds (Ng and Tay, 1996 ; Primka and
Taylor, 1997 ), a significant portion of the general population is being
constantly exposed to low levels of these compounds, which are potent
neurotoxins. Use of these substances has only escalated relatively
recently. Therefore, it may be some time before potential adverse
neurological consequences may surface in humans as a result of
occupational or environmental exposure to these biocides. Our results
suggest that the neurotoxic consequences of both acute and chronic
exposure to MIT and related biocides in humans need to be investigated.
 |
FOOTNOTES |
Received May 2, 2002; revised June 21, 2002; accepted June 21, 2002.
This work was supported in part by National Institutes of Health Grant
NS29365 and by an American Heart Association grant-in-aid. We thank
Drs. Paul Rosenberg, Ian Reynolds, and Don DeFranco and Daniel
Leszkiewicz and Kirk Dineley for helpful comments and suggestions, Dr.
Frank Barone for SB239063, Dr. Carl Lagenaur for the astrocyte cultures, and Karen Hartnett for assistance with some of the experiments.
Correspondence should be addressed to Dr. Elias Aizenman, Department of
Neurobiology, University of Pittsburgh School of Medicine, E1456
Biomedical Science Tower, Pittsburgh, PA 15261. E-mail: redox{at}pitt.edu.
 |
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