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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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    13

    Your article is protected by copyright and

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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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