palacios, román, cifuentes biol trace element res (2012)
TRANSCRIPT
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Biological Trace Element Research
ISSN 0163-4984
Biol Trace Elem Res
DOI 10.1007/s12011-012-9355-3
Exposure to Low Level of Arsenic and Leadin Drinking Water from Antofagasta City
Induces Gender Differences in GlucoseHomeostasis in Rats
Javier Palacios, Domingo Roman &
Fredi Cifuentes
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Exposure to Low Level of Arsenic and Lead in Drinking
Water from Antofagasta City Induces Gender
Differences in Glucose Homeostasis in Rats
Javier Palacios & Domingo Roman & Fredi Cifuentes
Received: 8 December 2011 /Accepted: 2 February 2012# Springer Science+Business Media, LLC 2012
Abstract Populations chronically exposed to arsenic in
drinking water often have increased prevalence of diabetes
mellitus. The purpose of this study was to compare the glu-
cose homeostasis of male and female rats exposed to low
levels of heavy metals in drinking water. Treated groups were
SpragueDawley male and female rats exposed to drinking
water from Antofagasta city, with total arsenic of 30 ppb and
lead of 53 ppb for 3 months; control groups were exposed to
purified water by reverse osmosis. The two treated groups in
both males and females showed arsenic and lead in the hair of
rats. The -aminolevulinic acid dehydratase was used as a
sensitive biomarker of arsenic toxicity and lead. The activity
of -aminolevulinic acid dehydratase was reduced only in
treated male rats, compared to the control group. Treated
males showed a significantly sustained increase in blood
glucose and plasma insulin levels during oral glucose toler-
ance test compared to control group. The oral glucose toler-
ance test and the homeostasis model assessment of insulin
resistance demonstrated that male rats were insulin resistant,
and females remained sensitive to insulin after treatment. The
total cholesterol and LDL cholesterol increased in treated male
rats vs. the control, and triglyceride increased in treated female
rats vs. the control. The activity of intestinal Na+/glucose
cotransporter in male rats increased compared to female rats,
suggesting a significant increase in intestinal glucose absorp-
tion. The findings indicate that exposure to low levels of
arsenic and lead in drinking water could cause gender differ-
ences in insulin resistance.
Keywords Gender differences . Arsenic . Lead . Drinking
water. Insulin resistance . Rat
Introduction
The prevalence of diabetes mellitus is increasing in Chilean
population, similar to the USA, Canada, Argentina, and
Uruguay [1]. The association between chronic exposure to
inorganic arsenic at high levels (>100 ppb) and diabetes
mellitus was confirmed by several epidemiological studies
in Taiwan, Bangladesh, and Mexico [24]. The low-level
lead exposure is associated with hypertension, cognitive
dysfunction, neurobehavioral disorders, and renal impair-
ment [5], but not with type 2 diabetes mellitus.
Chronic arsenic exposure via drinking water has been
reported in population of Antofagasta (latitude 23 38 S,
longitude 70 24 W). Since September 2004, the total
arsenic level in drinking water from Antofagasta City has
approximately 40 [6] and 20 ppb [7]. The World Health
Organization set 10 ppb as the recommended limit for
arsenic in drinking water [8]. Unfortunately, there are no
studies that show the toxic effects of lead in drinking water
from Antofagasta city, only a few studies on the toxic effect
of lead in salt rivers and in soil [9, 10].
J. Palacios (*)
Departamento de Qumica, Universidad Catlica del Norte,
Angamos 0610,
Antofagasta, Chile
e-mail: [email protected]
D. Roman
Laboratorio de Qumica Bio-Inorgnica y Analtica Ambiental,
Departamento de Qumica, Universidad de Antofagasta,
Angamos 601,
Antofagasta, Chile
F. Cifuentes
Experimental Physiology Laboratory (EPhyL),
Departamento Biomdico, Universidad de Antofagasta,
Angamos 601,
Antofagasta, Chile
Biol Trace Elem Res
DOI 10.1007/s12011-012-9355-3
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Arsenic exposure can potentially induce type 2 diabetes
mellitus by: homeostasis alteration of glucose, inhibition of
glucose uptake by adipocytes and skeletal muscle [11, 12],
or interference with the glucose metabolism in the liver [13,
14]. Other mechanisms that could be involved in glucose
homeostasis are the Na+/glucose cotransporter and the ac-
tivity of incretin in the small intestine. It is known that the
Na+/glucose cotransporter activity is increased by diabetesmellitus and is regulated by insulin [15], but there are few
studies on the effect of heavy metals on Na+/glucose
cotransporter.
Because Na+/glucose cotransporter (SGLT1; SLC5A1) is
the primary glucose transporter involved in intestinal ab-
sorption of mammals [16], we studied this in rats. This
cotransporter is located in the apical membrane of small
intestinal brush, which has a 2:1 stoichiometry (sodium/
glucose; Km01050 M), and is inhibited by phloridzin,
Ki0510 M [17].
The purpose of this study was to compare the insulin
sensitivity and glucose homeostasis of male and female ratsexposed to low levels of arsenic and lead in drinking water.
Materials and Methods
Drugs
The following drugs were used in this study: thiopental
sodium (Sigma, St. Louis, MO), -aminolevulinic acid
(Merck, Germany), HgCl2 (Merck, Germany), 4-(dimethy-
lamino) benzaldehyde (Merck, Germany), sodium arsenite
(Merck, Germany), and phloridzin (Sigma, USA). The
drugs were dissolved in distilled deionized water.
Animals
SpragueDawley rats, male and female (1516 weeks of
age, 300450 g), from the breeding colony at the Anto-
fagasta University were used. All rats were housed in
groups of two or three in a temperature-controlled, light-
cycled (08002000 hours) room with ad libitum access
to drinking water and standard rat chow (Champion,
Santiago). The investigation conformed to the Guide for
the Care and Use of Laboratory Animals published by
the U.S. National Institutes of Health (NIH Publication
No. 8523, revised 1996), and the local animal research
committee approved the experimental procedure used in
the present study.
Male and female rats were randomized into four groups
(six to ten animals each): treated male rats, control male
rats, treated female rats, and control female rats. Treated
groups drank drinking water from Antofagasta city
(30 ppb As and 53 ppb Pb), or control groups drank
purified water by reverse osmosis (3 ppb As and
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The Oral Glucose Tolerance Test and Plasma Insulin
Animals were fasted 12 h prior to administration of the oral
glucose tolerance test (OGTT). Samples of whole blood
were collected from a lateral tail incision in male and female
rats slightly anesthetized (dose of 20 mg/kg body weight
with thiopental), as recommended by some authors [20, 21].
A level of glucose (2 g/kg body weight) via oral was used aspreviously described [12]. Glycemia was measured in the
tail of rats every 15 min and for 90 min using OneTouch
Ultra Blood Glucose System; in the same blood sample was
also determined plasma insulin level by RIA.
Blood -Aminolevulinic Acid Dehydratase
The -aminolevulinic acid dehydratase (ALA-D) activity of
erythrocyte is a sensitive biomarker for arsenic and lead
toxicity [22, 23]. The method is based on the conversion
of-aminolevulinic acid by the enzyme to porphobilinogen.
The activity of blood ALA-D was assayed according toBerlin and Schaller procedure [24]. Total volume of
0.2 mL of heparinized blood was mixed with 1.3 mL of
distilled water and incubated for 10 min at 37C until
complete hemolysis. The standard -aminolevulinic acid
(0.01 M; 1 mL) was added to the samples, and then, the
tubes were incubated for 60 min at 37C. Porphobilinogen
formation is linear for at least 2 h at 37C.
The enzyme activity was stopped after 1 h by adding
1 mL of HgCl2 (1.35 g per 100 mL of 10% trichloroacetic
acid). The reaction mixture was centrifuged (3,000 rpm
10 min). An equal volume of Ehrlich reagent was added to
the supernatant, and the absorbance was recorded at 555 nm
after 5 min. The ALA-D activity was calculated by absor-
bance and hematocrit according to this relationship: ALA Dactivity Abs 100 2 35=Ht 60 0:062; where 20conversion factor from -aminolevulinic acid to porphobili-
nogen, 350dilution factor, 60 min0incubation time, and
0.062 L mol1 cm1 is the extinction coefficient of
porphobilinogen.
Activity of Intestinal Na+/Glucose Cotransporter
(SGLT1; SLC5A1)
The rats were anesthetized by intraperitoneal administration
of thiopental at a dose of 60 mg/kg body weight followed by
a midline laparotomy. Briefly, the protocol used was from
Diez et al. [25]. A segment of about 20 cm of proximal
duodenum was perfused using two catheters. The intestinal
content was washed out with physiological solution at 37C.
After a period of equilibrium (10 min), a bolus of 1 g
glucose in 1.5 ml 0.9% NaCl was infused within 1 min.
Cotransporter SGLT1 activity was calculated as the differ-
ence between the concentration of glucose eluated, in the
presence or absence of 0.5 mM phloridzin (a specific com-
petitive inhibitor of SGLT1), regarding the length of the
segment of the small intestine and 10 min of absorption.
Statistical Analysis
All results were evaluated by ANOVA with Dunnett test to
detect significant differences. Area under the curve (AUC)glucose and insulin values were calculated using the trapezoi-
dal rule. All data are expressed as the meansstandard error of
the mean, and p
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the treated female rats (0.540.03; p
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significant gender difference in the insulin AUC. The insulin
AUC was significantly higher in the treated male rats
(80.3 ngmL1min1 control group versus 231.4 ng
mL1min1 treated group;p
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control group, whereas there were no significant differences
in ALA-D activity of the female rats. These data suggest that
the toxic effect was mainly in the male rats than in the
females.
It has been proposed that men may be more affected by
the toxic effects of arsenic than women [33]. This hypoth-
esis is supported by the methylation of inorganic arsenic
which is considered a detoxification pathway [34]. Actually,women have a greater proportion of methylated metabolites
of arsenic compared to men, which would decrease arsenic
toxicity in the body [35, 36]. However, the theory of the
methylation of inorganic arsenic as a detoxification process
has been revised [37]; in fact, it was demonstrated that other
trivalent methylated species have high toxicity [38]. There-
fore, further investigation is required to get a deeper knowl-
edge of detoxification mechanisms in gender differences.
An important finding was that exposure to drinking water
from Antofagasta city caused gender differences in glucose
homeostasis. Indeed, in the treated groups only the male rats
were insulin resistant, as indicated by measurements ofglucose and insulin levels in blood during OGTT. The male
rats showed a significantly sustained increase in blood glu-
cose and plasma insulin levels during OGTT compared to
the control group. In addition, HOMA-IR confirmed that
insulin resistance was presented only in the male rats. In
contrast to insulin resistance observed above, the treated
female rats were more sensitive to insulin during OGTT.
The lipid profile was associated with insulin resistance in
male rats. In fact, total cholesterol and LDL cholesterol
increased in the treated males vs. the control rats, while
glucose tolerance and insulin sensitivity decreased. These
results suggest that lipid intake or lipogenesis exceeds the
storage capacity of the tissues, leading to glucose intolerance
and insulin resistance in the treated male rats. However, in the
treated female rats, triglyceride level increased, and glucose
tolerance and insulin sensitivity did not change. This is con-
sistent with improved glucose tolerance and insulin sensitivity
in the female rats under excessive lipid metabolism compared
with the male rats [39].
Another gender difference between the two groups after
treatment was in the intestinal absorption of glucose. The
activity of intestinal SGLT1 in the male rats increased com-
pared with the females. In addition, the slope of the curve of
glycemia during the first 30 min of OGTT was significantly
higher in the treated male rats vs. the treated females.
Therefore, the increase in intestinal glucose absorption
may be another factor that enhances the postprandial blood
glucose level in treated male rats.
It is known that intestinal SGLT1 activity is inhibited by
insulin in normal rats [15]. However, Fujica et al. showed that
an increase in intestinal glucose absorption by SGLT1 cotrans-
porter is associated with postprandial hyperglycemia before
the onset of insulin resistance and hyperinsulinemia in obese
type 2 diabetic rats [40, 41]. Actually, we may hypothesize
that intestinal SGLT1 activity was not inhibited by the high
level of plasma insulin observed in the treated groups during
OGTT. In fact, preincubation with insulin in a segment of
intestine did not inhibit the SGLT1 activity in the treated male
rats compared to the control group (data not shown).
Although the purpose of this paper was not to examine
whether insulin resistance was due to arsenic or lead, orboth, we repeated OGTT in the male rats treated with 30 ppb
sodium arsenite in purified water. The data indicated that
arsenic (sodium arsenite) produced insulin resistance but
less than in male rats exposed to drinking water. Izquierdo-
Vega showed that exposure to 1.7 ppm sodium arsenite pro-
duced insulin resistance in the male rats [42]; Paul et al. found
that 50 ppm sodium arsenite caused insulin resistance in mice
[43]; glucose metabolism is altered by exposure to 50 ppb
sodium arsenite in drinking water in mice [44]. Lin et al.
showed that exposure to low levels of lead accelerates pro-
gressive renal insufficiency in patients with chronic renal
disease (without diabetes) [28]. We think the lead could en-hance resistance to insulin, but more experiments are required
to fully understand this point.
In conclusion, exposure to low level of arsenic and lead
in drinking water of Antofagasta city alters the sensitivity to
insulin in a gender-dependent way. The role of intestinal
SGLT1 activity in the insulin resistance of male rats is
relevant probably because it contributes to the increase of
intestinal glucose absorption [45].
Acknowledgments We would like to thank Blanca Alvarez Carvajal
from Laboratorio Clnico Hormonal RadioLab, Laboratorio Clnico
Blanco for the technical assistance in this study. This work was in part
supported by grants from Fondo Interno de Investigacin Cientfica de
la Universidad Catlica del Norte (DGIP 220203-10301206) and
Direccin General de Investigacin (DIRINV 1339-2007) de la Uni-
versidad de Antofagasta.
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