ABSTRACT
Organophosphates are highly neurotoxic to aquatic fauna if they enter the water bodies as runoff, thus affecting the nervous system of the fishes. The present study was undertaken to investigate the vision changes, especially on the photoreceptor layer of the retina, of Cyprinus carpio communis L. when exposed to monocrotophos, an organophosphate. Fish were exposed to three sub-lethal concentrations of LC50, i.e. 0.038 ppm (1/10 LC50), 0.062 ppm (1/6 LC50), and 0.126 ppm (1/3 LC50), to observe the changes in the photoreceptor cells at the behavioral, histopathological and ultrastructural levels. Further, acetylcholinesterase activity was also evaluated. Behavioral changes, such as long resting period, inactivity, increase in air gulps and decrease in opercular and fin movements, were observed. A semi-quantitative analysis of the histological sections showed shrinkage in retinal layers at 0.038 ppm concentration of monocrotophos. At 0.062 ppm, the disappearance of the outer nuclear layer was observed and at the highest concentration of 0.126 ppm, damage in all retinal layers involving necrosis of the outer segment of the photoreceptor cells was observed. Further, at the ultrastructural level, detachment of photoreceptor cells and damage in the inner and outer segments of the photoreceptors were observed in an increasing dose-dependent manner. A reduction in the acetylcholinesterase level was observed in the treated groups. The treated fish were then transferred to toxicant-free water for 60 days to study self-regeneration, but no regeneration was observed in photoreceptor cells of the fish retina. This study shows that exposure to of monocrotophos effectively damages and disturbs the functioning of photoreceptor cells of retina of C. carpio communis L., thus affecting its vision.
Subject(s)
Carps , Monocrotophos , Acetylcholinesterase , Animals , Monocrotophos/toxicity , Organophosphates , Photoreceptor CellsABSTRACT
BACKGROUND: Virtual surgical planning (VSP) is increasingly used in maxillomandibular osseous free flap reconstruction. Non-commercial ('in-house') VSP may offer the same level of accuracy and other benefits, without the inflated costs and time delays inherent in using commercial providers. Comparisons between commercial and in-house methods are lacking. This study aims to determine the accuracy of VSP, compare in-house and commercially planned cases, and explore predictors of the reconstruction error. METHODS: Seventy-six patients who had a virtually planned maxillomandibular reconstruction between January 2012 and July 2020 were retrospectively identified. The preoperative digital plan was compared to the postoperative CT scan in terms of length of bone segments, angle between adjacent segments and intercondylar, and intergonial angle distances (mandibular reconstructions only). RESULTS: Forty-four patients fulfilled the inclusion criteria. The mean intergonial and intercondylar distances error was 1.7 ± 1.01 mm, mean segment length error was 1.3 ± 1.40 mm, and mean angles error was 1.9 ± 2.32°. The difference in error of in-house VSP compared to commercial VSP was not statistically significant for intercondylar and intergonial distance (p = 0.76), segment length (p = 0.15), or angle between segments (p = 0.92). The increased error was associated with osteoradionecrosis as the indication for surgery, greater number of segments, and secondary reconstructions. CONCLUSION: VSP is an accurate method of maxillary and mandibular reconstruction. In-house VSP may be similar in accuracy to commercial VSP options. Higher levels of inaccuracy are likely to occur in more complex reconstructions, particularly secondary reconstructions, and in the setting of osteoradionecrosis.
Subject(s)
Free Tissue Flaps , Mandibular Reconstruction , Osteoradionecrosis , Surgery, Computer-Assisted , Free Tissue Flaps/surgery , Humans , Mandibular Reconstruction/methods , Retrospective Studies , Surgery, Computer-Assisted/methodsABSTRACT
The Sydney Modification of the Alberta Mandibular Reconstruction technique (SM-ART) is a hybrid of the Rohner method and the Alberta Reconstructive Technique (ART). SM-ART differs from ART in three ways, notably the use of custom plates, intraoral placement of implants via three-dimensionally printed guides and a skin graft buried deep into the skin paddle of the fibula flap in the first stage of the reconstruction.
Subject(s)
Dental Implants , Free Tissue Flaps , Mandibular Reconstruction , Plastic Surgery Procedures , Alberta , Bone Transplantation , Fibula/surgery , Mandibular OsteotomyABSTRACT
The present studies are based on the feedback provided by fish farmers practicing composite fish culture of carps. According to them, fish habitats are affected by pesticides draining from agricultural fields into their catchments, especially during the rainy season. The lenses of most of the cultured fish became opaque, resulting in poor overall growth. In the literature, there was mounting evidence of pesticide toxicity involving multiple tissues. However, the fish visual system has never been investigated particularly from the toxicological perspective. In this regard, we carried out comparative toxicological studies on the lens of Cyprinus carpio communis using three different sublethal concentrations (0.038, 0.062 and 0.126 p.p.m.) of monocrotophos along with untreated controls for 30 days. Lenses from all the groups were extracted and preserved in gluteraldehyde and osmium tetraoxide and dehydrated in increasing grades of acetone. After dehydration, tissues were conducted with gold to observe under SEM. The fish exposed to monocrotophos developed cataract. Furthermore, when fish from the monocrotophos-treated tanks were transferred to normal environmental conditions for the next 60 days, progressive lens degeneration was noted. To conclude, monocrotophos induces irreversible cataractous changes in the lens of C. carpio communis. The fish visual system has many similarities to mammals and may serve as a good model for comparative toxicologic and ophthalmologic studies.
Subject(s)
Eye Diseases/veterinary , Fish Diseases/chemically induced , Insecticides/adverse effects , Monocrotophos/adverse effects , Animals , Carps , Eye Diseases/chemically induced , Lens, Crystalline/pathology , Lens, Crystalline/ultrastructureABSTRACT
BACKGROUND: Studies have shown that weight loss can have a favourable effect upon non-alcoholic fatty liver disease (NAFLD). However, the most effective means of achieving weight loss and safety profile of lipid-lowering drugs in the presence of NAFLD is unknown. AIM: To investigate the effect of dietary advice and lipid-lowering drugs, particularly statins, on patients with NAFLD and dyslipidaemia. DESIGN: Observational records based study. METHODS: We studied 71 patients with NAFLD and dyslipidaemia diagnosed and treated between 1996 and 2002 at University Hospital Lewisham. Some were referred to a dietician for weight loss advice as part of their management. After treatment all patients were assessed for changes in weight, serum alanine transaminase (ALT) and serum lipids including serum cholesterol, serum high density lipoprotein (HDL) and serum triglycerides. RESULTS: Thirty-seven male and 34 female patients with NAFLD and dyslipidaemia were followed up for a mean period of 440 +/- 374 days (median 335). Regression analysis revealed a significant association between changes in weight and changes in serum ALT (p < 0.039). Dietary advice failed to reduce body weight but significantly lowered the serum cholesterol to HDL ratio (p = 0.05). Only 15.4% of patients taking statins experienced a rise in serum ALT > or = 40 U/l, and in each case the rise was transient, returning near baseline or below without discontinuation of statin treatment. CONCLUSIONS: Weight loss appears to improve NAFLD, and dietary advice and lipid-lowering drugs may be beneficial for patients with NAFLD and dyslipidaemia even if weight loss is not achieved. Statins appear to be safe and efficacious in this group.
Subject(s)
Dyslipidemias/diet therapy , Dyslipidemias/drug therapy , Fatty Liver/diet therapy , Fatty Liver/drug therapy , Hydroxymethylglutaryl-CoA Reductase Inhibitors/therapeutic use , Alanine Transaminase/blood , Cohort Studies , Female , Humans , Hydroxymethylglutaryl-CoA Reductase Inhibitors/adverse effects , Life Style , Lipids/blood , Male , Middle Aged , Regression Analysis , Retrospective Studies , Treatment Outcome , Weight Loss/physiologyABSTRACT
The paper deals with the deleterious changes at ultrastructural level of the epithelial cells of gills of Cyprinus carpio communis Linn. upon exposure to 1/10th of LC50 of monocrotophos which is considered to be insignificant concentration from toxicological point of view. The gills of the fish are the primary corridor formolecularexchange between the internal milieu of a fish and its environment. Gills perform numerous functions such as oxygen uptake and CO2 excretion, osmoregulation, acid-basic balance, excretion of nitrogenous compounds and taste. Hazardous chemicals present in water may alter the morphology of the epithelial cells of gills of the fish, which may affect the process of diffusion of gases and ultimately the overall health of the fish. To prove this fact Cyprinus carpio communis Linn. was kept in water for 30 days having low concentration of 0.038 ppm (1\10th of LC50) of monocrotophos and an attempt was made to study the different types of degenerations produced in the epithelial cells of gills as compared to the normal epithelial cells of gills of this culturable fish using Scanning Electron Microscope (SEM) technique. The ultrastructural changes due to the toxic exposure at finer scale were thinning of microridges, upliftment of epithelial cells, development of hyperplasia, decrease in the density of mucous cells which are considered to be the first line of defence and total dystrophy of epithelial tissue. Thus, it is opined that a low concentration of monocrotophos has the potential to bring different type of degenerations at finer scale hence affecting the fish's health drastically and altering the fitness of the fish in water even having insignificant amount of this toxicant in the ambient water