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LEAD INDUCED EFFECTS ON RENAL ALKALINE PHOSPHATASE WITH ROLE OF ZINC IN ALBINO RATS

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  • DOW INTERNATIONAL MEDICAL COLLEGE KARACHI PAKISTAN

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Kidneys are adversely affected by a wide variety of therapeutic agents and chemicals including the environmental pollutants such as Lead. The nephrotoxic effects of lead have been widely studied. The proximal tubular cells are especially vulnerable to lead induced damage to membrane structure and function, characterized by enzymuria and inhibition of certain renal enzymes. Alkaline phosphatase activity is also known to be suppressed which has been evaluated in the present study by enzyme histochemistry. Moreover Zinc, an essential micronutrient has been used to minimize the effects of lead.
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Pakistan Journal of Pharmacology
Vol.28, No.2, July 2011, pp.39-44
LEAD INDUCED EFFECTS ON RENAL ALKALINE
PHOSPHATASE WITH ROLE OF ZINC IN ALBINO RATS
NAHEED KHAN, IMTIAZ WAGGAN,
FARRUKH MUSTAFA AND KHALIDA PERVEEN
Dow Medical College, DUHS, Karachi, Pakistan
ABSTRACT:
Kidneys are adversely affected by a wide variety of therapeutic agents and chemicals
including the environmental pollutants such as Lead. The nephrotoxic effects of lead
have been widely studied. The proximal tubular cells are especially vulnerable to lead
induced damage to membrane structure and function, characterized by enzymuria and
inhibition of certain renal enzymes. Alkaline phosphatase activity is also known to be
suppressed which has been evaluated in the present study by enzyme histochemistry.
Moreover Zinc, an essential micronutrient has been used to minimize the effects of lead.
Keywords: Lead, nephrotoxicity, alkaline phosphatase, zinc, proximal tubules.
INTRODUCTION
The increasing use of therapeutic agents
and chemicals for the last few decades has
considerably increased the possibility of
damage to the kidneys (WHO, 1991).
Nephrotoxic effects of analgesics, antibiotics,
anticancer agents, various household,
industrial and environmental chemicals have
been investigated.
Lead environmental pollution is a major
concern for public health (Oliveira et al.,
2009). Several sources of lead poisoning have
been identified in humans.The most common
are the leaded gasoline, batteries, paints,
ceramics, soldering, and building materials
(ATSDR, 1999),improperly glazed containers
(Klaasen, 2001), gunshot wounds with
retained lead pellets or particles, and a variety
of folk remedies and cosmetics( Meyer et al.,
2008; Woolf et al., 2007).
Besides having detrimental effect on
other organ systems it is also capable of
inducing nephrotoxicity (WHO, 1991) as
kidneys form major route of its excretion
(Noorafshan, 1998).Autopsy studies of lead
exposed humans showed that among soft
tissues, liver is the largest repository followed
by kidney (Sharma et al., 2010).
It is suggested that the mechanism
involved in lead induced toxicity is the metal-
induced reactive oxygen species (Ercal et al.,
2001) which are the initiators of peroxidative
damage to the membranes (Adegbesan and
Adenuga 2007; Sandhir et al., 1994) and cause
impaired membrane function, impaired
structural integrity and inactivation of a
number of membrane bound enzymes (Sidhu
et al., 2004). Lead-induced impairment of
proximal tubular function manifests as
enzymuria (ATSDR, 1999) and inhibition in
the activities of certain renal enzymes which
were also observed in lead administered rats.
The effects of lead were also studied on
isolated brush-border enzymes such as alkaline
phosphatase, that showed a decline upon its
administration (Sivaprasad et al., 2004). A
study by Flora et al (1983) showed that the
oral administration of lead acetate significantly
enhanced the urinary excretion and a
corresponding decrease in renal activities of
Alkaline Phosphatase. Alkaline phosphatase
helps in ionic movement across the cell
membrane and is also associated with
*Corres
p
ondence to: e-mail: drnkhan
@y
ahoo.com
Lead induced effects on renal alkaline phosphatase
40
secretory and absorption processes of the cell
(Bansal and Roy, 1997).
Adequate supply of essential
micronutrients in the diet is known to
minimize the effects of lead. Amongst them
zinc seems to have the maximal effects in
lowering the ill effects of lead (D’Souza et al.,
2003). Dose dependent effects of zinc
supplementation as a chelator in lead treated
rats was reported (Flora et al., 1994).
Zinc supplementation could significantly
compete for and effectively reduce the
availability of binding sites for lead uptake
(Batra et al., 1998). Zinc is an essential
mineral found in almost every cell (Office of
Dietary Supplement – National Institute of
Health, 2002), and plays a biochemical role by
stabilizing membrane structure, thus reducing
per oxidative damage to cell.
The pre-treatment with an essential metal
could prevent the appearance of signs of toxic
metal induced tissue injury (Afonne et al.,
2002) in experimental animals. A study of zinc
deficient patients receiving zinc
supplementation showed increases in alkaline
phosphatase activity that paralleled the degree
of zinc repletion. Important zinc containing
metalloenzymes in humans include alkaline
phosphatase (Milne, 2001).
MATERIALS AND METHODS
The study was carried out on a total of 36
active, young adult Albino rats in the
Department of Anatomy, Basic Medical
Sciences Institute (BMSI), Jinnah Post-
graduate Medical Centre (JPMC), Karachi
At the onset of experimental study, the
animals were divided into three groups
comprising 12 rats each; on the bases of drugs
they received. The drugs were injected
intraperitoneally to ensure uniform absorption.
Group-A rats served as control, received
injection normal saline 1 ml intra-
peritoneally daily for 6 weeks.
Group-B rats received Injection Lead
Acetate (Merck, Germany) at a dose of 8
mg/kg body weight intra-peritoneally
daily for 6 weeks.
Group-C rats received Injection Zinc
Chloride (Merck, Germany) at a dose of
0.21mg/kg body weight intra-peritoneally
two hours before administration of Lead
Acetate at a dose of 8 mg/kg body weight
intra-peritoneally daily for 6 weeks
The animals were sacrificed under ether
anesthesia at the end of experimental period.
The kidneys were obtained and were fixed in
10% formalin for 24 hours, after which
processing, sectioning and staining with
Gomori’s Calcium phosphatase methods were
done. The method was applied for the
histochemical study of enzyme Alkaline
Phosphatase.
OBSERVATIONS AND RESULTS
The present study was designed to
observe the lead induced nephrotoxicity with
role of zinc in albino rats. The histochemical
observations of renal Alkaline phosphatase
were based on the study of sections, stained
with Gomori’s Calcium Phosphate method.
The Gomori’s Calcium Phosphate stained
sections of group A rats showed the sites of
enzyme activity of alkaline phosphatase in the
renal proximal tubules in the form of brownish
black deposits. The deposits were seen
regularly and evenly arranged within the
tubules (Fig. 1).
The Gomori’s Calcium Phosphate stained
sections of group B rats for alkaline
phosphatase showed decreased enzyme
activity in tubules. The brownish black
deposits were decreased as few clumps,
irregularly distributed in renal tubules (Fig. 2).
The Gomori’s Calcium Phosphate stained
sections of group C rats for alkaline
phosphatase showed an increase activity of
enzyme in the tubules, which is comparable to
Khan et al. 41
control. The blackish brown deposits were
seen in the tubules quite regularly arranged
(Fig. 3).
DISCUSSION
It was thought worthwhile to carry out a
study using experimental induction of
nephrotoxicity in albino rats by administration
of lead. Moreover attempts have been made to
study the protective effects of zinc on lead
induced nephrotoxicity.
The histochemical study was done to
observe the effects of lead on activity of
enzyme alkaline phosphatase. The study of
Gomori’s Calcium Phosphatase stained
Fig. 1: Gomori’s Calcium Phosphate stained, 5 µm thick longitudinal section of kidney fro
m
group-A (control) rat showing regularly arranged brownish black deposits of alkaline
phosphatase (ALP) within proximal tubules. Photomicrograph × 1000.
Fig. 2: Gomori’s Calcium Phosphate stained, 5 µm thick, longitudinal section of kidney fro
m
group-B (lead treated) rat showing very few brownish black deposits of alkaline phosphatase
(ALP) irregularly distributed in a few tubules. Photomicrograph × 1000.
Lead induced effects on renal alkaline phosphatase
42
sections of group-B showed a decreased
amount of brownish black deposits in the
proximal tubules and hence a decrease activity
of enzyme alkaline phosphatase as compared
to corresponding controls. This could be
correlated with the study of Flora et al. (1983)
according to which the oral administration of
lead acetate enhanced the urinary excretion
and decrease the renal activities of alkaline
phosphatase. It is also in agreement with the
study of Wapnir et al. (1979) who observed
that administration of lead acetate
intraperitoneally for six weeks to rats
decreased the alkaline phosphatase activity in
kidney homogenates.A marked inhibition of
alkaline phosphatase in kidneys is also
observed in other species such as
Heteropneustes fossillis (Sastry and Agrawal,
1979).
These histochemical findings led us to
conclude that such changes in the activity of
phosphatases could be an adaptation to the
metabolic, structural, and functional alterations
in the organelles of the renal cells due to lead
intoxication (Sivaprasad et al., 2004).
The study of Gomori’s Calcium
Phosphate stained sections in group-C
revealed a greater number of deposits as
compared to group-B, thus showing an
increase in alkaline phosphatase activity. This
could be attributed to the fact that alkaline
phosphatase is a zinc-dependent enzyme and
zinc supplementation showed an increase in
alkaline phosphatase activity (Milne, 2001).
CONCLUSION
It is concluded from this study that higher
lead levels reduces the activities of renal
alkaline phosphatase in experimental rats, and
a pretreatment with zinc improves activity of
renal alkaline phosphatase.
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... Highest concentrations are found in the liver and mineralizing bone, but the enzyme is also present in the intestines, placenta, kidneys, and leukocytes (McComb et al. 1979;Weiss et al., 1989;Iba et al. 2004;Mota et al., 2008). Alkaline phosphatase helps in ionic movement across the cell membrane and is also associated with secretory and absorption processes of the cell ( Bansal and Roy, 1997;Khan et al., 2011). ALPase has role in bone mineralization (Van Hoof and De Broe, 1994;Hui and Tenenbaum, 1998;Mota et al., 2008). ...
Thesis
Full-text available
Summary Statins, such as atorvastatin (ATOR) and rosuvastatin (ROSU) are used as cholesterol-lowering drugs. Because statins widely used, commercially available and increasingly used day by day, with few studies and limited data existed on atorvastatin or rosuvastatin-induced histological, histochemical and ultrastructural changes, the present study was conducted to investigate the potential toxicity of the human equivalent therapeutic doses of ATOR and ROSU in Wistar albino rats. The study was conducted using apparently healthy adult male Wistar albino rats (Rattus norvegicus) obtained from the Laboratory Animal Center (College of Pharmacy, King Saud University, Saudi Arabia). The rats were nearly of the same age (8-10 weeks old) and weighing (220-250 g). All animals were kept in the laboratory conditions for a period of 7 days for acclimatization. Animals were maintained under standard management conditions (light, temperature and humidity) and were fed with commercial rat pellets and drinking water ad libitum. All experiments were conducted in accordance with the guidelines approved by Local Animal Care and Use Committee of King Saud University. A total of 120 adult Wistar male albino rats, were divided randomly into 6 groups of 20 animals each. All doses of treated groups were human equivalent therapeutic doses. Both drugs (ATOR and ROSU) were dissolved in 0.25% sodium carboxymethyle cellulose (CMC). ATOR-treated rats (5mg/kg/day), ATOR-treated rats (2.5mg/kg/day), ROSU-treated rats (2.5mg/kg/day), ROSU-treated rats (1.25mg/kg/day), (vehicle control) was intubated with (1mg/kg/day) (CMC 0.25%) and control rats was treated with (5mg/kg/day) physiological saline. All treatments were administered orally (gavage) for 90 consecutive days. At the end of the experimental period, blood samples were collected from 10 animals from each group. Relevant blood Summary v biochemical parameters (Alkaline phosphatase (ALP), Alanine aminotransferase (ALT), Aspartate aminotransferase (AST), creatinine, urea, uric acid, total cholesterol and total protein) were determined. Then animals were sacrificed and tissue samples from liver, kidney, heart, testes, brain and lung were processed for sectioning and examination by light and transmission electron microscope. The results of this study could be summarized as follows: First: Blood chemical alterations: Administration of statins (ATOR) or (ROSU) to all treated groups caused significant increases (P<0.05) in the levels of aspartate transaminase (AST), alanine transaminase (ALT) and alkaline phosphatase (ALP), creatinine (Cr), urea (Ur), uric acid levels compared with those of the control group after 90 days of exposure to statins. This treatment also induced significant decreases in the levels of cholesterol and total protein. The significant differences were clearly observed in high dose treated-groups [(ATOR 5 mg/kg) and (ROSU 2.5 mg/kg)] more than low dose treated-groups [(ATOR 2.5 mg/kg) and (ROSU 1.25 mg/kg)]. In (CMC, vehicle control) the results showed non-significant differences compared with those of the control group. Second: Gross examination: In terms of the anatomical appearance of organs of control animals during 90- day study period, all therapeutic doses of atorvastatin and rosuvastatin had no effect on gross pathological changes in all investigated organs of all members of treated groups. Third: Histological alterations All statin-treated groups [(ATOR 5 mg/kg), (ATOR 2.5 mg/kg), (ROSU 2.5 mg/kg) and (ROSU 1.25 mg/kg)] showed histological alterations in kidney, liver, heart, lung, brain and testes, especially at the high doses (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg). Renal alterations include the degeneration of the tissues up to the necrotic Summary vi patterns, as well as dilatation of blood capillaries and spacing between the renal tubules due to accumulation of fluid (edema). However, the cortex of kidney showed more damage especially in proximal convoluted tubules (PCT) than the medulla. The liver showed some necrotic and hemorrhagic foci especially in (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg). Hemorrhages and dilatation of the portal space and blood sinusoids of the liver were observed. ROSU had greater effects on the hepatic tissue than ATOR. The heart showed some sort of hemorrhages and wavy appearance of myofibers, as well as the sarcoplasm of some fibers was characterized by granular appearance. The lung tissue showed an increase in the thickness of alveolar walls associated with dilation or collapsing of some pulmonary alveoli. While the testicular tissue showed degenerative changes in some seminiferous tubules leading to partial arrest of spermatogenesis, as well as some necrotic cells and spermatid giant cells were shown in some seminiferous tubules of high dose groups. Moreover, The brain of statins-treated rats showed little changes characterized by slight dilatation of blood capillaries with little edema around the neurons in cerebral cortex. No histological changes were observed in (CMC, vehicle control). Fourth: Histochemical alterations Exposure to statins (ATOR) or (ROSU) caused alterations in content of chemical substances of different rat tissues. All treated groups, especially high doses (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg) manifested less content of proteins in the renal and hepatic tissues compared with control group. Liver tissues in (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg) showed reduction in glycogen content, as well as accumulation of glycogen in subsarcolemma of heart tissue of treated rats. 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The cardiac muscle of (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg), showed ultrastructural changes in their muscle fibers with clear rupture of some muscle fibers and separation of the fibers from each other together with mitochondria swelling and cristae destruction. Discontinuous of elongation of cardiac muscle fiber was observed which might be due to occurrence of partial decomposition in muscle fibers of some animals. Ultrastructural of cardiac muscle fiber exhibited almost normal structure Summary viii without any changes in muscle fibers and mitochondria in low dose (ATOR 2.5 mg/kg) and (ROSU 1.25 mg/kg). The ultrastructure of skeletal muscle of (ATOR 5 mg/kg) and (ROSU 2.5 mg/kg), showed ruptured muscle fibers and spacing from each other, also showing discontinuous of elongation of muscle fiber and swelling of the mitochondria and destruction of their cristae. 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Lead poisoning is an important environmental disease that can have life-long adverse health effects. Most susceptible are children, and most commonly exposed are those who are poor and live in developing countries. Studies of children's blood-lead levels (BLLs) are showing cognitive impairment at increasingly lower BLLs. Lead is dangerous at all levels in children. The sources of lead exposure vary among and within countries depending on past and current uses. Sources of lead may be from historic contamination, recycling old lead products, or from manufacturing new products. In all countries that have banned leaded gasoline, average population BLLs have declined rapidly. In many developing countries where leaded gasoline is no longer used, many children and workers are exposed to fugitive emissions and mining wastes. Unexpected lead threats, such as improper disposal of electronics and children's toys contaminated with lead, continue to emerge. The only medical treatment available is chelation, which can save lives of persons with very high BLLs. However, chelating drugs are not always available in developing countries and have limited value in reducing the sequelae of chronic low dose lead exposure. Therefore, the best approach is to prevent exposure to lead. Because a key strategy for preventing lead poisoning is to identify and control or eliminate lead sources, this article highlights several major sources of lead poisoning worldwide. In addition, we recommend three primary prevention strategies for lead poisoning: identify sources, eliminate or control sources, and monitor environmental exposures and hazards.
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