Neonicotinoid Analysis in Sunflower (Helianthus annuus) Honey Samples Collected around Tekirdag in Turkey.

In recent years, the widespread use of neonicotinoids in agricultural areas has caused environmental pollution due to its lower toxicity to mammals. Honey bees, which are considered as biological indicators of environmental pollution, can carry these pollutants to the hives. Forager bees returning from sunflower crops that have been treated with neonicotinoids treated sunflower fields cause residue accumulation in the hives, which reason colony-level adverse effects. This study analyses neonicotinoid residues in sunflower (Helianthus annuus) honey sampled by beekeepers from Tekirdag province. Honey samples have been subjected to liquid-liquid extraction methods before liquid chromatography-mass spectrometry (LC-MS/MS). The method validation was carried out to fulfill all the necessary requirements of procedures SANCO/12571/2013. Accuracy was in the range of 93.63-108.56%, for recovery in the range of 63.04-103.19%, and for precision in the range 6.03-12.77%. Detection and quantification limits were determined according to the maximum residue limits of each analyte. No neonicotinoid residues were found above the maximum residue limit in the sunflower honey samples analysed.

Blood concentrations of potentially toxic trace elements (PTEs) and correlation with biochemical and hematological parameters in dogs from thrace region, Turkey.

Environmental exposure to potentially toxic trace elements (PTEs) leads to health problems in animals as well as in humans. Dogs can be used as bioindicators for health status of both environment, animals and humans. The study material consisted of a total of 140 dogs from Thrace region in Turkey. Essential (Co, Cr, Cu, Fe, Zn) and non-essential (As, Cd, Hg, Ni, Pb) PTEs concentrations of blood samples were determined by ICP-MS. In addition, hemogram (RBC, MCV, MCH, MCHC, HCT, WBC, HGB, PLT) and biochemical parameters (Glucose, total protein, albumin, globulin, total bilirubin, triglyceride, cholesterol, BUN, AST, ALT, ALP, GGT) levels were determined. The possible correlations between PTEs and blood parameters were investigated. The results were compared according to gender, age (<2, 2-5, >5 years), sampled location with hemogram and biochemistry data. Essential element concentrations (ppb) were sorted as Zn > Fe > Cu > Cr > Co, and non-essentials were As > Ni > Pb > Hg > Cd. There were statistically important negative or positive correlations between elements and hematological (except Fe and Cd), and biochemical parameters (except Ni) (p < 0.05, p < 0.01). It was determined that Pb concentrations (9.34-23.30 ng ml-1) were below the concentrations considered to be toxic in all locations, Cu concentrations (475.35-521.98 ng ml-1) were within the normal reference range, Zn (3229.65-4.265.00 ng ml-1) were higher than the reference values in all locations. Since the concentrations of elements and correlations between hematological, biochemical parameters as well as gender, age, and location in an area with heavy urban and industrial activity; indicate that the situation may be similar for other living things in the region, it constitutes a starting point for studies to be carried out in this direction.

Rapid confirmatory analysis of avermectin residues in milk by liquid chromatography tandem mass spectrometry.

Our study developed a quick method for confirmatory analysis of avermectins (abamectin B1a, doramectin, ivermectin B1a, eprinomectin B1a, and moxidectin) in bovine milk according to the European Commission Decision 2002/657/EC requirements. Avermectins were liquid-liquid extracted with acetonitrile, followed by an evaporation step, and then analyzed by liquid chromatography/electrospray ionization tandem mass spectrometry in the negative ion mode. An in-house method validation was performed and the data reported on specificity, linearity, recovery, limit of detection, limit of quantitation, decision limit, and detection capability. The advantage of this method is that low levels of avermectins are detectable and quantitatively confirmed at a rapid rate in milk.

Influence of ovariectomy and flutamide treatment on vaginal tissue and body weight.

OBJECTIVE: To determine the effect of flutamide on vaginal histology, and to ascertain whether flutamide regulates body weight gain in the ovariectomized rat model. METHODS: We chose 36 sexually mature female Wistar-Albino rats in this study. The study took placed in the Department of Medical Science Application and Research Center of Dicle University, Diyarbakir, Turkey, in 2002. We divided the model rats into 3 groups: group 1--control group, group 2--sham-operated group and group 3--bilaterally ovariectomized group. In addition, we gave flutamide to group 3. RESULTS: We found that the body weight was higher in the ovariectomized rats than the control rats. Furthermore, the body weight decreased a little after flutamide therapy. The thickness in the vaginal epithelium of the control group decreased, moreover, the appearance of stromal tissue was rather loose. After flutamide applications, infiltration of the stromal cells increased, the vaginal epithelial layer thickened and became keratinized. Microscopic papillae and anatomical processes appeared in the flutamide treated group. CONCLUSION: We observed that the antiandrogen drug flutamide is hormonally active and may exhibit estrogenic-antiestrogenic activity in rats. Our study may be a source for further research examining the relationship between the androgen receptor antagonist flutamide and reproductive function in female rats.

Effect of ovariectomy and of estrogen treatment on the adrenal gland and body weight in rats.

OBJECTIVE: To determine the effect of estrogen on adrenal gland histology, and to ascertain whether or not estrogen regulates body and adrenal gland wet weight gain in the ovariectomized rat model. Two experiments investigated the effects of ovariectomy and estrogen replacement on the body and adrenal gland weight. METHODS: We used 36 female Wistar Albino rats in this study. The study took placed in the Department of Medical Science Application and Research Center of Dicle University, Diyarbakir, Turkey, in 2002. Group 1 (control group) received no ovariectomy; all animals in the other groups were bilaterally ovariectomized and kept for 60 days. We designated group 2 and 3 as sham-operated group and bilaterally ovariectomized then in addition, group 3 received estradiol. We then cut the paraffin sections, which we obtained by routine histologic methods, into 5 mm and stained them with hematoxylin-eosin. We later evaluated the stained sections under a light microscope. RESULTS: The body weight was higher in the ovariectomized rats compared to the control groups. Ovariectomy did not result in significant changes in the wet weight of the adrenal gland. Furthermore, body weight increased after estrogen therapy, and the wet weight of the adrenal gland increased in the estrogen group. It was obtained in the sham-operated group that ovariectomy resulted in a decrease in the activity of the adrenal cortex. In the sham-operated and estrogen group, we observed a prominent capsule, expanded zona glomerulosa cells, regular parallel columns in zona fasciculata and there was an increased vascularization in the medulla, after the estrogen treatment. CONCLUSION: We determined that bilateral ovariectomy can result in a decrease in the activity of the adrenal cortex. In contrast, estradiol injection can cause a significant increase in the activity of the adrenal cortex and medulla.

Investigation of the accumulation of 2,4-dichlorophenoxyacetic acid (2,4-D) in rat kidneys.

The accumulation of 2,4-dichlorophenoxyacetic acid (2,4-D) and its metabolite 2,4-dichlorophenol (2,4-DCP) in the kidneys of rats was investigated. Male and female Sprague-Dawley rats were given 2,4-D in drinking water and food for 30 days. Group A (control group) was fed a normal diet, Group B was fed 50 ppm 2,4-D in 15 g food, Group C received 100 ppm 2,4-D in 15 g food, Group D received 25 ppm 2,4-D in 15 ml drinking water and Group E was given 50 ppm 2,4-D in 15 ml of drinking water. Levels of 2,4-D and 2,4-DCP in kidneys were determined using high performance liquid chromatography (HPLC). It was observed that at low doses of 2,4-D, the metabolite, 2,4-DCP found in the kidneys.