The resistance of parathyroid cells to 1,25-dihydroxyvitamin D3 (1,25(OH)2D3) in uremic hyperparathyroidism is thought to be caused, in part, by a 1,25(OH)2D3 receptor (VDR) deficiency in the parathyroids. However, results of biochemical studies addressing VDR numbers in the parathyroids are controversial. Several studies have found VDR content to be decreased in the parathyroids of uremic patients and animals, while others have found no such decrease in the parathyroids of uremic animals.To clarify the role of VDR, we investigated VDR distribution in surgically-excised parathyroids obtained from chronic dialysis patients by immunohistochemistry. We classified the parathyroids as exhibiting nodular or diffuse hyperplasia. Our studies demonstrated a lower density of VDR in the parathyroids showing nodular hyperplasia than in those showing diffuse hyperplasia. Even in the parathyroids showing diffuse hyperplasia, nodule-forming areas were present; these areas were virtually negative for VDR staining. A significant negative correlation was found between VDR density and the weight of the parathyroids. These findings indicate that the conflicting results of biochemical studies may be caused by the heterogeneous distribution of VDR; the decreased VDR density in parathyroids may contribute to the progression of secondary hyperparathyroidism and to the proliferation of parathyroid cells that is seen in uremia. (J. Clin.

To clarify whether the changes of parathyroid size have any correlations with the long-term prognosis of calcitriol pulse therapy, we examined the time course of serum levels of parathyroid hormone (PTH) and size of parathyroid glands in 14 chronic dialysis patients during and after the oral calcitriol pulse therapy. In 5 patients without any detectable glands, secondary hyperparathyroidism was easily controlled by calcitriol pulse therapy and then by conventional oral active vitamin D therapy. In 2 patients with detectable gland(s) in whom size of all parathyroid glands as well as PTH hypersecretion regressed to normal by calcitriol pulse therapy, secondary hyperparathyroidism could then remain controlled at least for 12 months after switching to conventional oral active vitamin D therapy. In contrast, in 7 patients in whom size of all parathyroid glands did not regress to normal by calcitriol pulse therapy, secondary hyperparathyroidism relapsed after switching to the conventional therapy, even if PTH hypersecretion could be controlled temporarily. Our findings suggest that the time course of parathyroid hyperplasia detected by ultrasonography is an important determinant of the efficacy and the prognosis of calcitriol pulse therapy. Thus, the change of parathyroid gland size as well as PTH hypersecretion should be taken into account for the management of secondary hyperparathyroidism.

The distribution of all larval stages of the Japanese eel, Anguilla japonica, were examined using historical catch records and original data in the western North Pacific (WNP) to evaluate existing information about the larval distribution and migration of this species. A total of 148 preleptocephali, 2547 leptocephali, 6 metamorphosing larvae, and 21 glass eels were collected during 37 cruises over a 52-year period . Sampling effort was spatio-temporally biased in latitude/longitude among seasons with sampling effort being concentrated near the western margin of the subtropical gyre near Taiwan in the winter season and extensive effort occurring near the spawning area to the east near the seamount chain of the West Mariana Ridge in summer during the spawning season. The distribution of preleptocephali (4.2-8.7 mm) was limited to a narrow area around 14°N, 142°E just west of the southern part of the seamount chain, while leptocephali (7.7-62.0 mm) were widely distributed at increasing size westward in the North Equatorial Current (NEC) to the region east of Taiwan. Metamorphosing larvae (52.7-61.2 mm) were collected only in the area 21-26°N, 121-129°E to the east of Taiwan, while glass eels (51.3-61.2 mm) occurred only within or west of the Kuroshio. These distributions suggest that leptocephali begin to

Anguillid eels are found globally in fresh, transitional and saline waters and have played an important role in human life for centuries. The population status of several species is now of significant concern. The threats to populations include direct exploitation at different life stages, blockages to migratory routes by dams and other structures, changes in river basin management that impact habitat carrying capacity and suitability, pollution, climate change, diseases and parasites. While much has been done to understand eel biology and ecology, a major challenge is to identify the key research and management questions so that effective and targeted studies can be designed to inform conservation, management and policy. We gathered 30 experts in the field of eel biology and management to review the current state of knowledge for anguillid eel species and to identify the main topics for research. The identified research topics fell into three themes: (a) Lifecycle and Biology; (b) Impacts and (c) Management. Although tropical anguillid eels are by far the least well understood, significant knowledge gaps exist for all species. Considerable progress has been made in the last 20 years, but the status of many species remains of great concern, particularly for northern temperate species. Without improved engagement and coordination at the regional, national and international level, the situation is unlikely to improve. Further, adaptive management mechanisms to respond to developments in science, policy and our knowledge of potential threats are required to ensure the future of these important and enigmatic species.

The influences of water temperature and feeding regime on otolith growth in Anguilla japonica glass eels and elvers were investigated using individuals reared at 5, 10, 15, 20, 25 and 30 degrees C and in fed or unfed conditions at salinity 32 after their otoliths were marked with alizarin complexone (ALC). To eliminate the difficulty of observing the edges of otoliths with optical (OM) or scanning electron (SEM) microscopes, three to 10 individuals were sampled from each tank at 10, 20 and 30 days during the experiment and reared for an additional 10 days at 25 degrees C after their otoliths were marked a second time. Otolith growth and the number of increments were measured using both OM and SEM. Most A. japonica commenced feeding after 10 days at 20-30 degrees C or after 20 days at 15 degrees C, but no feeding occurred at 5 and 10 degrees C. No otolith growth occurred at 5 and 10 degrees C except in two individuals with minimal increment deposition at 10 degrees C. Otolith growth was proportional to water temperature within 15-25 degrees C and not different between 25 and 30 degrees C. At 15, 25 and 30 degrees C, the mean otolith growth rate in fed conditions was higher than in unfed conditions. The number of increments per day was significantly different among water temperatures (0.00-0.01 day(-1) at 5 and 10 degrees C, 0.43-0.48 day(-1) at 15 degrees C and 0.94-1.07 day(-1) at 20-30 degrees C). These results indicated that otolith growth in A. japonica glass eels and elvers was affected by temperature and ceased at< or =10 degrees C under experimental conditions. Hence, future studies analysing the otoliths of wild-caught A. japonica glass eels and elvers need to carefully consider the water temperatures potentially experienced by the juveniles in the wild.