Structural changes in femoral bone tissue of rats after subchronic peroral exposure to selenium
- Monika Martiniaková†1,
- Ivana Boboňová†1,
- Radoslav Omelka†2,
- Birgit Grosskopf3Email author,
- Robert Stawarz4 and
- Róbert Toman†5
© Martiniaková et al.; licensee BioMed Central Ltd. 2013
Received: 24 September 2012
Accepted: 29 January 2013
Published: 1 February 2013
The role of selenium (Se) on bone microarchitecture is still poorly understood. The present study aims to investigate the macroscopic and microscopic structures of femoral bone tissue in adult male rats after subchronic peroral administration of Se.
Twenty one-month-old male Wistar rats were randomly divided into two experimental groups. In the first group (Se group) young males were exposed to 5 mg Na2SeO3/L in drinking water, for 90 days. Ten one-month-old males without Se administration served as a control group. At the end of the experiment, macroscopic and microscopic structures of the femurs were analysed using analytical scales, sliding instrument, and polarized light microscopy.
The body weight, femoral length and cortical bone thickness were significantly decreased in Se group rats. These rats also displayed different microstructure in the middle part of the femur, both in medial and lateral views, where vascular canals expanded into the central area of the bone while, in control rats, these canals occurred only near the endosteal surfaces. Additionally, a smaller number of primary and secondary osteons was identified in Se group rats. Histomorphometric analyses revealed significant increases for area, perimeter, maximum and minimum diameters of primary osteons’ vascular canals but significant reductions for all measured variables of Haversian canals and secondary osteons.
Se negatively affected the macroscopic and microscopic structures of femoral bone tissue in adult male rats. The results contribute to the knowledge on damaging impact of Se on bone.
Bone is a specialized connective tissue, which forms the framework of the body. Its metabolic activities may be immediate targets for xenobiotics and various physiological conditions can adversely affect bone metabolism leading to skeletal deformities and diseases. Excess or deficiency of certain essential elements may also affect bone maturation [1, 2].
Selenium (Se), an essential trace element, plays an important role in mammalian biology . It is known that humans and animals require Se for the normal function of a number of Se-dependent biological processes [4, 5]. At low concentration (≤ 0.3 mg/L), Se exerts its various effects through its incorporation into selenoproteins. According to Ebert and Jakob  several selenoproteins are expressed in bone and play important roles in bone metabolism. Se deficiency may induce retardation of bone formation  or may be a possible risk factor for osteoporosis . At higher concentrations (≥ 4 mg/L), however, Se is cytotoxic. It is widely known that high concentrations of Se trigger the opening of the mitochondrial permeability transition pore by inducing the synthesis of the superoxide anion and the oxidation of protein thiol groups [8–10]. Chung et al. found that sodium selenite induced apoptosis in mature osteoclasts mediated by mitochondria. Excess of Se also causes the death of osteoblast-like cells , leads to abnormal bone and cartilage development and is reported to be teratogenic .
Studies of the effects of Se on bone structure contribute to the knowledge on the mechanisms of Se activity in the organism and relations between changes found in different organs. Generally, the effects of Se on bone tissue are studied mainly in relation to the deficiency of Se in the food, but it is also interesting if and how Se can impact on bone structure and function after subchronic intoxication. Administration of subchronic toxic doses allows for the high probability that the toxic effect will be observable and defined at the structural level. In our study the subchronic peroral dose was used to study toxic effects of Se on macroscopic and microscopic structures of femoral bone tissue in rats.
Twenty one-month-old male Wistar rats were obtained from the accredited experimental laboratory (number SK PC 50004) of the Slovak University of Agriculture in Nitra (Slovakia). These clinically healthty rats were randomly divided into two experimental groups of 10 individuals. Male rats were used, as they are less susceptible than females to Se toxicity. The rats were housed individually in plastic cages in an environment maintained at 20-24°C, 55 ± 10% humidity. They had access to water and food (feed mixture M3, Bonargo, Czech Republic) ad libitum. The first group (Se group, n=10 rats) was exposed daily to 5 mg Na2SeO3/L in their drinking water for a total of 90 days. The water consumption was monitored daily during the whole experiment. The selenium intake was calculated from the water consumption and expressed as total amount of consumed Se. The average amount of consumed Se was 9.7 mg per animal. The dose was high enough to reach toxicity but also safe enough to prevent animal mortality. The second group (n=10 rats), without Se exposure, served as the control group. This study was approved by the Animal Experimental Committee of the Slovak Republic.
At the end of the 90 days, all the rats were killed and their femurs were used for macroscopic and microscopic analyses. The left femurs were weighed on analytical scales with an accuracy of 0.0001 g and the length was measured with a sliding instrument.
For histomorphometric analysis, the right femurs were sectioned at the midshaft of the diaphysis and the segments fixed in HistoChoice fixative (Amresco, USA). The segments were then dehydrated in increasing grades (40 to 100%) of ethanol and embedded in Biodur epoxy resin (Günter von Hagens, Heidelberg, Germany) according to the method described by Martiniaková et al.. Transverse thin sections (70–80 μm) were prepared with a sawing microtome (Leitz 1600, Leica, Wetzlar, Germany) and fixed onto glass slides by Eukitt (Merck, Darmstadt, Germany) as previously described . The qualitative histological characteristics of the compact bone tissue were determined according to the internationally accepted classification systems of Enlow and Brown  and Ricqlés et al., who classified bone into three main categories: primary vascular tissue, non-vascular tissue and Haversian bone tissue. Various patterns of vascularization can occur in primary vascular bone: longitudinal, radial, reticular, plexiform, laminar, lepidosteoid, acellular, fibriform and protohaversian. There are three subcategories indentified in Haversian bone tissue: irregular, endosteal and dense.
The quantitative (histomorphometric) variables in the anterior, posterior, medial and lateral views of thin section(s) were assessed using the software Motic Images Plus 2.0 ML (Motic China Group Co., Ltd.). We measured area, perimeter and the minimum and maximum diameters of the primary osteons’ vascular canals, Haversian canals and secondary osteons in all views of the thin sections in order to minimize inter-animal differences.
Diaphyseal cortical bone thickness was also measured by Motic Images Plus 2.0 ML software. Twenty random areas were selected, and average thickness was calculated for each femur.
Statistical analysis was performed using SPSS 8.0 software. All data were expressed as mean ± standard deviation (SD). The unpaired Student’s t-test was used for establishing statistical significance (P < 0.05) between experimental groups.
Body weight, femoral weight, femoral length and cortical bone thickness in adult male rats subchronic exposed to 5 mg of Na 2 SeO 3 /L in drinking water for 90 days (Se group) and control rats
Body weight (g)
Femoral weight (g)
Femoral length (cm)
Cortical bone thickness (mm)
405.0 ± 52.7
1.05 ± 0.17
3.94 ± 0.09
352.5 ± 37.1
1.07 ± 0.11
3.74 ± 0.07
P < 0.05
P < 0.05
P < 0.05
Data of the primary osteons’ vascular canals, Haversian canals and secondary osteons in adult male rats subchronic exposed to 5 mg of Na 2 SeO 3 /L in drinking water for 90 days (Se group) and control rats
Max. diameter (μm)
Min. diameter (μm)
Primary osteons’ vascular canals
397.3 ± 98.1
72.29 ± 8.95
12.89 ± 2.08
9.83 ± 1.58
459.6 ± 127.5
77.93 ± 11.11
14.08 ± 2.58
10.36 ± 1.51
P < 0.05
P < 0.05
P < 0.05
P < 0.05
426.9 ± 119.2
74.47 ± 10.25
13.21 ± 2.16
10.24 ± 1.73
375.5 ± 67.4
70.29 ± 6.58
12.49 ± 1.68
9.64 ± 1.28
P < 0.05
P < 0.05
P < 0.05
P < 0.05
6541.0 ± 2012.6
291.79 ± 43.09
52.21 ± 8.61
39.38 ± 7.52
5766.7 ± 1539.2
272.16 ± 35.81
47.80 ± 7.06
37.99 ± 6.24
P < 0.05
P < 0.05
P < 0.05
P < 0.05
Subchronic peroral exposure to 5 mg Na2SeO3/L in drinking water for 90 days resulted in a significant decrease in body weight and femoral length in adult male rats. Ip  similarly reported a reduction in growth in rats after 12 weeks of dietary exposure to 5 mg/kg Na2SeO3. Selenium is known to accumulate in the anterior part of the pituitary gland. Thorlacius-Ussing et al. mention decreased secretion of growth hormone (GH) and somatomedin C in rats after receiving 15 mg/L Na2SeO3 in their drinking water, suggesting that growth retardation could be mediated by reduced GH and somatomedin C production. Next Gronbaek et al. showed that a Se dose of 3.3 mg Na2SeO3/L in drinking water for 35 days induced a significant reduction in circulating insulin-like growth factor I (IGF-I). These rats also displayed a significantly shorter tibia.
The thickness of cortical bone is generally accepted as an important parameter in the evaluation of cortical bone quality and strength. We observed significantly decreased cortical bone thickness in Se-exposed rats. Studies of cortical bone thickness in Se-exposed rats has not been published previously. The value of cortical bone thickness in control group rats differed from values reported by Comelekoglu et al. and Chovancová et al., who analysed rats of different age.
The results of the qualitative histological analysis of the control rats corresponded to those of previous works [23–26]. We identified non-vascular and primary vascular radial tissues and irregular Haversian bone tissue. However, there was no evidence of true Haversian intracortical bone remodelling. It is generally known that aged rats and mice lack true Haversian cortical bone remodelling but not cancellous bone remodelling [25, 27]. Therefore, some secondary osteons can be observed in the long bones near the endosteal border. In our study, the newly formed remodelling units within compact bone originated from the endocortical surface and extended deep into the underlying compact bone. The same findings have also been documented in 13 month-old male rats .
Prolonged intake of a high dose of Se induced changes in the middle part of compact bone where primary vascular radial bone tissue was present. We propose that the formation of this type of bone, in the central area of the femur, could be explained as an adaptive response to Se toxicity to protect bone tissue against cell death. It is generally known that Se at high doses induces apoptosis in mature osteoclasts  and death of osteoblast-like cells . In a study by Turan et al. osteocyte loss was identified because of the destruction of the bone tissue and its replacement with a large uncalcified mass of new bone matrix in rabbits fed excess Se (10 mg Na2SeO3/kg of diet for a period of 12 weeks). These authors also reported decreased biomechanical strength of the femur in the Se-exposed animals.
Data obtained from the histomorphometric analysis showed a significant increase in area, perimeter, maximum and minimum diameters of the primary osteons’ vascular canals and on the other hand a significant decrease of the Haversian canals’ variables in the Se-exposed rats. In general, the vascular system is a critical target for toxic substances and their effects on the vascular system may play an important role in mediating the pathophysiological effects of these substances in specific target organs . Blood vessels readily adapt structurally in response to sustained functional changes, particularly those related to chronic pressure alterations or changes in the nutritional demands of the tissue [30, 31]. Results obtained by Ruseva et al. demonstrate that rats exposed to increased amount of dietary Se had higher glutathione peroxidase 1 (GPx-1) activity and a lower level of anti-elastin antibodies (AEABs) than those of control group, and the aortic wall histology showed degenerative changes associated with reduced thickness of the wall of the left coronary artery. Our results indicate that an excess of Se had a different impact on the primary osteons’ vascular canals and Haversian canals. The main difference between these structures is the presence of a cement line in Haversian canals (cement line delimits the canals) and its absence in primary osteons. We surmise that the cement line could be the main reason for the different results in the histomorpometry of both canals.
We found significantly lower values of all variables of secondary osteons in Se-exposed rats. According to Jowsey , the values of secondary osteons are higher in individuals with longer bones. Our results correspond with those found by Jowsey , as the femurs were longer in the control rats, which also displayed higher values for osteons. Moreover we propose that the observed differences in histomorphometry between the Se-exposed and control rats could be associated with changes in bone remodelling, which is mediated by osteoblasts and osteoclasts and subsequent calcification of bone tissue. The results of Boyar  showed that an excess of Se increased the amount of carbonate content in bones of Wistar rats injected intraperitoneally with 5 μmol Na2SeO3/kg for 4 weeks. The incorporation of carbonate ions into the crystal structure of hydroxyapatite (HA) results in changes in the physical and chemical properties of HA . HA crystals, as a major mineral component of bones, are aligned with their long axis parallel to the collagen fibre axis  creating concentric lamellae of secondary osteons. Another factor that could have contributed to the minimization of secondary osteons could be Se intoxication, which induces apoptosis in mature osteoclasts . Decreased osteoclast activity is associated with smaller osteon size . Therefore, significantly decreased secondary osteons may be present in Se-exposed rats.
The paper is the first report of femoral bone structure in rats after subchronic peroral administration of Se. Our results contribute to the insight into the complexity of Se toxicology in rats. Moreover, since the microstructural changes in the bone typically follow biochemical action of Se in the tissue, the results of the study can highlight the physiological implications and possible mechanisms of Se effects.
Our results demonstrate the effect of Se on bone microstructure of rats; however, possible extrapolation of the results to humans may be an interesting topic for discussion. Although Se poisoning is not reported frequently in humans and human toxicity from environmental exposure to Se is rare, incidents include industrial accidents, accidental ingestions, suicides, and attempted murder . In humans, the minimum lethal dose seems to be similar to that for animals. The chronic toxic dose for human beings is about 2.4 to 3 mg of Se per day . Although there are some differences in bone microstructure between humans and rats we suppose that observed changes in the variables of Haversian canals and secondary osteons in our rats will correspond to those of humans. Human femur in adult individuals is namely composed of many secondary osteons, which contain Haversian canals (dense Haversian bone tissue). Additional research dealing with the influence of Se on human bone structure is required to obtain more information on comparative aspects.
This study demonstrates that subchronic peroral administration of 5 mg Na2SeO3/L in drinking water affects the body weight, femoral length, cortical bone thickness and both the qualitative and quantitative microscopic structures of femoral bone tissue in adult male rats. The results can be applied in experimental studies focusing on the effects of various trace elements on bone structure.
The study was supported by the grant KEGA 025UKF-4/2012 (Ministry of Education, Slovakia). This article was written during realization of the project LAGEZ No.26220120051 supported by the Operational Programme Research and Development funded from the European Regional Development Fund.
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