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Biotechnic & Histochemistry

ISSN: 1052-0295 (Print) 1473-7760 (Online) Journal homepage: https://www.tandfonline.com/loi/ibih20

A histopathological and stereological study of liver

damage in female rats caused by mercury vapor

A Yahyazedeh, BZ Altunkaynak, N Akgül & HM Akgül

To cite this article:

A Yahyazedeh, BZ Altunkaynak, N Akgül & HM Akgül (2017) A

histopathological and stereological study of liver damage in female rats caused by mercury vapor,

Biotechnic & Histochemistry, 92:5, 338-346, DOI: 10.1080/10520295.2017.1312527

To link to this article: https://doi.org/10.1080/10520295.2017.1312527

Published online: 09 Jun 2017.

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A histopathological and stereological study of liver

damage in female rats caused by mercury vapor

A Yahyazedeh

1

, BZ Altunkaynak

1

, N Akgül

2

, HM Akgül

3

1

Department of Histology and Embryology, Faculty of Medicine, Ondokuz Mayıs University, Samsun, and, Departments of 2

Restorative Dentistry, and3Oral Diagnosis and Radiology, Faculty of Dentistry, Atatürk University, Erzurum, Turkey Accepted March 25, 2017

Abstract

We examined the possible effects of elemental mercury vapor on the liver of the female rats. We

divided the animals into an untreated control group and an experimental group that was

exposed to mercury vapor for 45 days. Liver samples were obtained for histological and

stereo-logical analysis. The total liver, parenchyma and sinusoid volumes were increased signi

ficantly

in the mercury vapor treated group compared to controls. Also, the mean density, total number

and mean nuclear diameter of hepatocytes, except for binucleated hepatocytes, was decreased in

the experimental group compared to controls. Light and electron microscopy revealed alterations

of liver structure of the experimental animals compared to controls.

Key words: electron microscopy, histology, liver, mercury vapor, rat, stereology, toxicity

Mercury (Hg) is an environmental pollutant that

is toxic to humans (Selin

2009

). Mercury vapor is

the inhaled form of elemental Hg (Björkman

et al.

2007

, WHO

2003

). The vapor can be formed

from dental amalgam, liquid metallic Hg, Hg

compounds, and mines. Hg is lipophilic and is

absorbed easily by the oral mucosa, skin and

lungs. After entering the blood, mercury vapor

is oxidized to toxic divalent inorganic Hg

(Clarkson

1997

), which accumulates in various

tissues (Björkman et al.

2007

, Iranmanesh et al.

2013

, Yasutake et al.

2010

). Divalent inorganic Hg

stimulates production of reactive oxygen species

(ROS) and ROS reduce the level of antioxidant

enzymes (Goering et al.

2002

, Zhao et al.

2009

).

Also, after absorption by the body, mercury

vapor causes tissue damage by increasing

intra-cellular calcium storage and in

flux of calcium

from the extracellular

fluid. The deleterious

effects of ROS on mitochondrial membrane lipids

and proteins initiate the apoptotic cascade (Sunja

et al.

2010

).

Mercury vapor can cause neurological and

behavioral disorders with symptoms including

tremors, memory loss, neuromuscular effects,

and cognitive and motor dysfunction (WHO

1991

). It has been reported that Hg vapor

released from amalgam for

filling teeth

predis-poses people to Alzheimer’s disease (Pendergrass

et al.

1997

). Mercury exposure exerts adverse

effects on genes (Liu et al.

2003

), kidney

(Tanaka et al.

1998

, Akgül et al.

2016

),

cardiovas-cular system (Fernandes Azevedo et al.

2012

),

beta cells of the pancreas (Chen et al.

2010

),

female

reproductive

system

(Apostoli

and

Catalani

2011

, Altunkaynak et al.

2016

) male

reproductive systems (Boujbiha et al.

2009

,

Altunkaynak et al.

2015

) and neurons (Tang and

Li

2006

). Accumulation of Hg decreases

hepato-cyte viability in the liver (Ashour et al.

1993

, Cao

et al.

2012

, Endo et al.

2013

, Karapehlivan et al.

2014

). To clarify the toxicity of mercury vapor

further, we investigated its effects on hepatic

architecture using quantitative methods.

Correspondence: B. Zuhal Altunkaynak, Faculty of Medicine, Department of Histology and Embryology, Ondokuz Mayıs University, Samsun, Turkey. E-mail:berrinzuhal@gmail.com

Color versions of one or more of thefigures in the article can be found online atwww.tandfonline.com/ibih

© 2017 The Biological Stain Commission

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Material and methods

Experimental animals and procedure

Our investigation was conducted with the approval of

the

Experimental

Research

and

Application

Committee of the Ataturk University, Erzurum,

Turkey. We used 10

−12-week-old 200 g female

Wistar albino rats. Rats were obtained from the

Experimental Animal Research and Application

Center of Atatürk University. The animals were kept

at 22 ± 2° C with optimal humidity and a 12 h light:12

h dark cycle. The rats had access to food and water ad

libitum. We divided the animals into control and

experimental groups, each with six rats. The

experi-mental group was exposed to 1 mg/m

3

/day mercury

vapor by inhalation for 45 days within a special

cham-ber as described in our earlier report (Altunkaynak

et al.

2015

). The untreated controls were housed for 45

days in an identical chamber without exposure to Hg

vapor. After exposure to Hg, all rats were

anesthe-tized by inhalation of 2

−3% sevoflurane (Sevorane®

Liquid 250 ml; Abbott, Istanbul, Turkey) in 100%

oxy-gen. After sacri

fice and perfusion with 4%

parafor-maldehyde, the liver was removed from each rat.

Histology

After removal, the livers were cut into small pieces

by systematic random sampling (Altunkaynak and

Ozbek

2009

) and

fixed in 10% formaldehyde. Also,

some pieces were placed in glutaraldehyde for

elec-tron microscopy. For light microscopy, liver samples

were dehydrated through an ascending series of

alcohols, cleared three times in xylene, then

embedded in fresh paraf

fin. Light microscopy

sec-tions were cut at 5

μm using a rotary microtome

(Leica RM 2225; Leica Instruments, Nussloch,

Germany). The sections were placed on glass slides

and stained with hematoxylin and eosin for light

microscopy (Kiernan

2008

, Guven et al.

2013

). These

slides also were used for stereological analyses.

Stereology

Volumes of total liver, sinusoids and parenchyma

We used the Cavalieri method (Dursun et al.

2010

,

Altunkaynak et al.

2012a

) to estimate liver volume

(Altunkaynak et al.

2012a

, Arslan et al.

2016

). A pilot

study was performed to determine the suitable point

density for the point counting grid. Selecting the

appropriate grid size provides an acceptable coef

fi-cient of error (CE) for the area of interest in each

section (Bulut et al.

2014

, Khoshvakhti et al.

2015

).

The CE and coef

ficient of variation (CV) were

estimated to determine whether the point density of

the point counting grid and sectioning intervals were

appropriate (Göçer et al.

2016

). According to

pre-vious studies, CE values <0.05 are sufficient to ensure

reliability of the stereological studies. CE and CV

values were estimated using the formulas below.

The volumetric values [V(total)] of interest were

esti-mated using the formula (Uyanık et al.

2009

):

V total

ð

Þ ¼ t  a p

 

 P

where t is the thickness of the section, a(p) is the

interval point area and

ΣP is the total number of

points that touch appropriate areas in the sections.

Mean numerical density, and number of

hepatocytes and binucleated hepatocytes

We used the physical disector method (Altunkaynak

et al.

2011a

) to obtain unbiased numerical data.

Selection of the physical dissector pairs was

per-formed as described by Sterio (

1984

). The

first section

selected (reference section) and its adjacent section

(look up section) are de

fined as a dissector pair.

These sections were separated by 20

μm, which was

the thickness of four sections as a rule of the physical

disector. According to this rule, the distance between

the section pairs must be approximately 30–40% of

the average projected height of the interested object

to be estimated. In this way, approximately 15

–20

section pairs were obtained for evaluation.

For selection, the

first section was selected

ran-domly from the

first four sections, e.g., we selected

the third section. We then systematically continued

sampling by selecting each consecutive fourth section,

i.e., the

first pair = third section and seventh (3 + 4)

sections, the second pair = 11th and 15th (11 + 4)

sections etc. Digital photographs were taken at 4, 10

and 40 × magni

fications for each section. An unbiased

20 × 20 cm

2

counting frame (Altunkaynak et al.

2011b

)

was superimposed on the sampled regions of the

digital photographs of the sections for calculation of

the number of hepatocytes. According to the rule of

physical disector, hepatocytes that were observed in

the reference section, but not in the look-up section,

were countable. Initially, the numerical frequency of

both hepatocytes and binucleated hepatocytes were

computed; later the numerical density of only

binu-cleated hepatocytes was counted in similar areas of

the section pairs (Fig. 1c, d).

The mean numerical density of hepatocytes/cm

3

was calculated as:

Nv

¼

P

Q



P

Vdisector

(4)

where

P

Q



is the total number of hepatocytes and

P

V disector is the total volume of disector frames.

The total number of hepatocytes then was estimated

by multiplying NV in total volume of liver (Vref) as:

Total number of hepatocytes = Nv

∙Vref

We estimated the mean numerical density of

cleated hepatocytes and total number of

binu-cleated hepatocytes using the same approach.

Finally, we estimated the mean diameter of

hepa-tocytes using the equation:

Diameter

¼

P

Q

P

Q



xt

where

∑Q is the total number of nuclei observed in

the reference section,

P

Q



is total number of nuclei

observed in the reference section, but not in the

look-up section, and t is the mean thickness of sections. CE

and CV indicate reliability of the counted cells and

biological variability, respectively (Altunkaynak

et al.

2012b

).

Electron microscopy

Blocks of livers were

fixed in 3% buffered

glutaralde-hyde for 1 h, post

fixed in 1% osmium tetroxide for 90

min, then passed through acetone and propylene

oxide. Samples were embedded in Araldite CY 212

(Agar Chemicals, Tekser Ltd. Sti,

İstanbul, Turkey)

(Harorli et al.

2009

). Semithin sections were cut at 1

µm by an ultramicrotome (LKB NOVA, Bromma,

Sweden) and stained with toluidine blue. These

sections were used to examine the general

organiza-tion of the liver at the light microscopic level. Thin

sections were cut from the same tissue blocks and

stained with uranyl acetate and lead citrate, and used

for ultrastructural examination (Ayranci et al.

2013

,

Çolakoglu et al.

2014

). Sections were viewed using a

Jeol 100 SX electron microscope (Jeol, Tokyo, Japan).

Statistical analysis

We analyzed our data using Mann Whitney-U

statis-tical test (SPSS software, version15.0; IBM Corp,

İstanbul, Turkey). Data are expressed as medians ±

SEM. Values for p

≤ 0.05 were considered significant.

Results

Stereology

The stereology results are summarized in

Table 1

.

The total volume of the liver was increased signi

fi-cantly in the Hg treated group compared to controls.

The volume of the parenchyma was decreased

sig-ni

ficantly, but the volume of the sinusoids was

increased in the Hg treated group compared to

con-trols. In the experimental group, the mean numerical

density and total number of hepatocytes were

reduced signi

ficantly, but the mean numerical

den-sity and total number of binucleated hepatocytes

were increased signi

ficantly in the Hg treated

group compared to controls. The nuclear diameter

Table 1. Morphometric evaluations of control and experimental groups with CE values

Estimation Control CE Hg CE p LV via CM (cm3) 9.98 ± 1.21 0.002 11.095 ± 3.11 0.002 < 0.01 Volume of parenchyma (cm3) 6.70 ± 1.34 0.012 5.840 ± 1.17 0.023 < 0.05 Volume of 3.73 ± 0.87 0.03 5.48 ± 1.7 0.029 < 0.01 sinusoids (cm3) ND of hepatocytes 211.65 × 103± 1428 0.01 169.86 × 103± 1297 0.017 < 0.01 (cell/cm3) MND of 29.93 × 103± 832 0.04 38.79 × 103± 644 0.038 < 0.05 binucleated hepatocytes (cell/cm3) TN of 2.11 × 106± 105613 0.01 1.88 × 106± 94229 0.01 < 0.05 hepatocytes TN of binucleated 298.73 × 103± 14936 0.02 430.43 × 103± 23180 0.032 < 0.01 hepatocytes NH of hepatocytes (μm) 7.90 ± 0.81 0.04 5.16 ± 0.44 0.043 < 0.01

Means ± SEM. LV, liver volume; CM, Cavalieri method; MND, mean numerical density; TN, total number; NH, nuclear diameter; CE, coefficient of error.

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of the hepatocytes was decreased significantly in the

group exposed to Hg compared to controls.

Light microscopy

We observed enlarged blood vessels and dilated

sinusoids with increased perivascular connective

tissue in the Hg treated group (

Fig. 2

). We also

found extensive degeneration of hepatocytes in

sec-tions from the experimental group (

Fig. 3

). The

degenerated hepatocyte cytoplasm was stained

darkly and no nucleolus could be found (

Fig. 3

).

The livers of the control group appeared normal

(

Figs. 1a

,

2a

).

Electron microscopy

Electron microscopy of the experimental group

showed mildly to moderately pyknotic nuclei.

Irregular cellular borders, edematous and expanded

spaces of Disse, enlarged bile canaliculi and

sepa-rated adhesion complexes indicated degeneration in

the experimental group. We also observed dilated

rough endoplasmic reticulum and sinusoids,

degen-erated mitochondria and accumulation of electron

dense material. Vacuoles also were evident in some

hepatocytes of the experimental group compared to

normal appearing controls (

Figs. 4

,

5

).

Discussion

The liver degrades or eliminates toxic materials

including Hg, which is a common pollutant in the

environment. Liver tissue is susceptible to injury

from environmental and industrial mercury (Lee

et al.

2014

, Garcia-Niñoand Pedraza-Chaverrí

2014

). Exposure to Hg increases products of lipid

oxidation (Huang et al.

1996

), impairs the function

of mitochondria (Belyaeva et al.

2011

), reduces the

activity of metabolic enzymes, decreases synthesis

of hepatic coagulation factors (Chang et al.

1973

),

interferes with antioxidant enzymes (Pal and Ghosh

2012

) and causes vascular injury (Kanluen and

Gottlieb

1991

). Hg exposure increases oxidative

Fig. 1. a, b) Point counting grid for the Cavalieri principle. c, d) Consecutive pair sections for applying the physical dissector. Images in c) and d) are reference and look-up sections, respectively. *, countable profiles of hepatocytes as disector particle; X, uncountable profiles according to the rule of unbiased counting frame.

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Fig. 2. Sections of liver from control (a) and experimental (b, d) groups.−, increased perivascular connective tissue; arrow, dilated sinusoid; +, enlarged blood vessel.

Fig. 3. Semithin sections from liver of control (a, b) and experimental (c−f) groups. −, abnormal intracellular accumula-tions; +, enlarged blood vessel; arrow, degenerated hepatocytes.

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stress (Gutierrez et al.

2006

), which may contribute

to its histopathology.

We used stereological methods to estimate the

number of hepatocytes and to measure the volumes

of the parenchyma and sinusoids (Altunkaynak and

Altunkaynak

2007

). Our stereological and

histo-pathological

findings were consistent with each

other. We found that the total volume of the liver

in the Hg treated group was increased signi

ficantly

compared to controls. The increase may be due to

enlarged blood vessels, increased perivascular

con-nective tissue and increased sinusoid volume.

Moderate hyperaemia in the sections of the

experi-mental group re

flected alteration of sinusoid

volume. Exposure to Hg vapor also caused dilation

of the blood vessels. On the other hand, the mean

numerical density and total number of hepatocytes

were reduced in the group exposed to Hg vapor.

The reduced number of hepatocytes was caused by

degeneration and death of these cells. The mean

numerical density and total number of binucleated

hepatocytes were increased signi

ficantly in the Hg

treated group compared to untreated controls. We

concluded that Hg vapor inhalation caused the

pro-liferation of binucleated hepatocytes. Nuclear

height

of

the

hepatocytes

was

signi

ficantly

decreased in the Hg exposed group and the nuclear

diameter

of

hepatocytes

was

signi

ficantly

decreased. We believe that the decrease might be

due to alteration of the genetic material including

pyknotic or heterochromatic changes

(Cebulska-Wasilewska et al.

2005

, Chen et al.

2005

). Further

investigation is required to clarify the impact of Hg

vapor on human health.

Fig. 4. Electron micrographs of liver sections. a−d) Control group. c) Canaliculi; white arrow, smooth endoplasmic reticulum; asterisk, nucleus; black arrow, rough endoplasmic reticulum; double black arrowheads, border between hepatocytes; single black arrowhead, lysosome; single white arrowhead, mitochondria; x, hepatocyte microvillus; plus, endothelial cell; minus, Disse space; arrow with double heads, sinusoid; black circle, erythrocyte. e, f) Hg vapor treated group. Plus with circle, pyknotic nucleus; ce, irregular borders and enlarged bile canaliculi; double black arrowheads, dilated rough endoplasmic reticulum; white triangle, degeneration of mitochondria; white circle, cytoplasmic edema; hexagon, swollen nucleus; circle with black arrowhead, separated adhesion complex. Scale bars = 0.5 µm.

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Declaration of interest: The authors report no

con-flicts of interest. The authors alone are responsible

for the content and writing of this paper.

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