Mortarity due to pesticide poisoning for prefectures in Japan is examined according to the vital statistics in 1979-1981. The atlases of pesticide poisoning mortality for prefectures in Japan are presented.
There is a wide range in mortality among prefectures and the highest mortality is 17.8 times as high as that observed in the prefecture which showed the lowest mortality. Regional characteristic is observed in the mortality. Northern part of Kanto Area and the southern part of Kyusyu Island show high mortality and low mortality is observed in Hokuriku Area.
The ratio of the deaths due to pesticide poisoning to those due to automobile accident also show wide range among prefectures. The highest ratio is 38.3% and the lowest is 2.4%. The ratio shows similar regional characteristic to that observed in mortality.

Objectives: Progressive and generalized loss of skeletal muscle mass (SMM) and strength are characteristics of sarcopenia. However, the impact of appendicular and trunk SMM and back extensor strength (BES) on spinal sagittal alignment remains unclear. Herein, we investigate the relationship between these factors and spinal sagittal alignment. Methods: In total, 202 women without vertebral fractures (median age, 66.9 years; interquartile range, 61.4–71.9 years) were analyzed at an orthopedic outpatient clinic. Pelvic incidence (PI), lumbar lordosis (LL), sagittal vertical axis (SVA), and pelvic tilt (PT) were measured on whole spine radiographs. Body mass index (BMI), appendicular and trunk relative SMM index, and BES were also evaluated. These measurements were compared between spinal sagittal alignment groups using the Mann–Whitney U test. Finally, the factors contributing to abnormal alignment were analyzed using multiple logistic regression analysis. Results: BES was significantly lower in all abnormal sagittal alignment groups, as defined by PI-LL (≥ 10°), SVA (≥4 cm), and PT (≥20°) (all P < 0.001). On multivariate analysis, BES was a contributing factor for abnormal PI-LL (P < 0.001), SVA (P = 0.001), and PT (P < 0.001). Conversely, a decrease in appendicular and trunk relative SMM index did not statistically affect abnormal spinal sagittal alignment. Conclusions BES was associated with changes in spinal sagittal alignment; however, SMM, which is often used for diagnosing sarcopenia, did not affect spinal sagittal alignment.

Objectives: Progressive and generalized loss of skeletal muscle mass (SMM) and strength are characteristics of sarcopenia. However, the impact of appendicular and trunk SMM and back extensor strength (BES) on spinal sagittal alignment remains unclear. Herein, we investigate the relationship between these factors and spinal sagittal alignment. Methods: In total, 202 women without vertebral fractures (median age, 66.9 years; interquartile range, 61.4–71.9 years) were analyzed at an orthopedic outpatient clinic. Pelvic incidence (PI), lumbar lordosis (LL), sagittal vertical axis (SVA), and pelvic tilt (PT) were measured on whole spine radiographs. Body mass index (BMI), appendicular and trunk relative SMM index, and BES were also evaluated. These measurements were compared between spinal sagittal alignment groups using the Mann–Whitney U test. Finally, the factors contributing to abnormal alignment were analyzed using multiple logistic regression analysis. Results: BES was significantly lower in all abnormal sagittal alignment groups, as defined by PI-LL (≥ 10°), SVA (≥4 cm), and PT (≥20°) (all P < 0.001). On multivariate analysis, BES was a contributing factor for abnormal PI-LL (P < 0.001), SVA (P = 0.001), and PT (P < 0.001). Conversely, a decrease in appendicular and trunk relative SMM index did not statistically affect abnormal spinal sagittal alignment. Conclusions BES was associated with changes in spinal sagittal alignment; however, SMM, which is often used for diagnosing sarcopenia, did not affect spinal sagittal alignment.

  The purpose of this study was to clarify the effects of ingesting chloridquellen and bicarbonate spring waters on electrogastrography and heart rate variability in humans. The subjects were ten young adults (average age 21.9 years old). Three and six cycles per minute (cpm) frequency of electrogastrography (EGG) were measured, as well as the high-frequency (HF: 0.15-0.40Hz) components, and the ratio of low-frequency (LF: 0.04-0.15Hz) components to HF components in heart rate variability (HRV) during 90 minutes. The taste of the water and pain or abnormalities in the stomach were also assessed by having the subjects answer a questionnaire. The subjects ingested the spa water or purified water and were asked to respond to the questionnaire after thirty minutes, and they also ingested no water on a different day and were questioned. The EGG-6 cpm frequency, presumably reflecting intestinal activity, did not change under any conditions. The EGG-3 cpm frequency, presumably reflecting stomach activity, significantly increased with bicarbonate spring waters immediately after ingestion and decreased after 30 min. Additionally, the 3 cpm frequency significantly increased with ingestion of purified water over the course of 30 min. The HF components in HRV, presumably reflecting cardiac parasympathetic activity, did not change under any conditions. The ratio of LF to HF components in HRV, presumably reflecting cardiac sympathetic activity, significantly increased with ingestion of purified water immediately and after 15 min, and bicarbonate spring waters after 30 min. There was a difference between ingestion of chloridquellen and purified water in the answers concerning the taste of the water in the questionnaire. These findings suggest that the constituent parts of chloridquellen water and other factors activate stomach and autonomic nervous activities in humans.

  Foot and hand baths are used well in partial baths. It is thought that a warm temperature effect varies according to the size of warmed part in a partial bath, but it is not clear. The purpose of this study is to examine the thermal response on the size of warming area and position during foot and hand baths. The subjects were ten young individuals (all men, average age 23.2 ± 1.3 years), and these individuals partook in a 15-min foot and hand bath. Subjects submerged themselves up to the lower thigh and forearm in a bath at 42°C, in a seated position, rested in the position for five min, and then rested for an additional five min after bathing. There are five styles for baths (single thigh, both thighs, single forearm, both forearms, and no bath). Tympanic temperature was taken with a thermistor, skin blood flow with a laser Doppler flowmeter, and sweat rate with capsule method on the right side. We measured whether the subjects felt warm and comfortable. Tympanic temperature was significantly increased in both the foot and hand baths. Skin blood flow and sweat rate showed no change under any condition. Warm temperature and subjects’ feelings of comfort varied for all bathing conditions, in comparison with no bath. Warm temperature feeling was significant for both the foot and hand baths, in comparison with single baths. The change in these temperatures depended on the surface area warmth in the bath, and the response of the warming at different parts of body was suggested by various factors.

  In Japan, the Hot Springs Law and the Guideline of Analytical Methods of Mineral Springs (revised) classify springs containing 74 Bq/kg of radon as “hot springs” and those with radon levels exceeding 111 Bq/kg as “medical springs” called “radioactive spring”. Radon is a noble gas that easily diffuses in air.   This study evaluates exposure dose due to radon when using a radioactive spring at a spa in the Toriido area, Komono town, Mie district, Mie prefecture.   After bath water was supplied through a pipe from hot spring storage tanks to bathtubs, only 5.3-18.0% of radon remained in the water. Two days later, only 0.3-0.4% of the radon remained in the bath water due to radioactive decay and diffusion into air being increased by bathing and recirculation filtering.   The calculated effective dose from bathing in radioactive hot spring was 2.8-12.0 nSv, and that from drinking radioactive hot spring water was 5.1-23.3 nSv. To determine the total effective dose from use of the hot spring facility that may effects on human health, it is necessary to analyze radon concentrations not only in the water but also the surrounding air.

Objectives: Radon (222Rn) is a noble gas and a component of water in many hot spring spas. The Hot Springs Law and the Guideline of Analytical Methods of Mineral Springs (revised edition) of Japan classify springs containing 74 Bq/kg or more of radon as “hot springs” and those with radon levels exceeding 111 Bq/kg as “medical springs”, also called “radioactive springs”. Komono Town, one of the foremost spa and health resort destinations in Mie Prefecture, is the site of many radioactive springs. For the purpose of regional vitalization of this area through radioactive springs, it is necessary to confirm the safety and effectiveness of their use. To evaluate the exposure dose due to radioactive spring usage, it is important to measure radon concentration in air, especially in high-humidity air such as in bathing rooms. Methods: The concentration of radon in air was analyzed using an activated charcoal detector (PICO-RAD; AccuStar Labs) with a desiccant (Drierite; 8-mesh anhydrous calcium sulfate; W.A. Hammond Drierite Company, Ltd.) and a liquid scintillation counter (LSC LB-5; Hitachi Aloka Medical, Ltd.). A DPO (2,5-diphenyloxazole) + POPOP (1,4-bis- (5-phenyl-2-oxazolyl)-benzene) toluene solution (Wako Pure Chemical Industries, Ltd.) was used as a liquid scintillator. Activated charcoal detectors were set up in and around the radioactive spring facilities. Results and Discussion: In a radioactive spring facility, radon concentration in air in the bathing room and changing room were relatively high at about 50 Bq/m3. In the corridor on all floors and at the entrance, these values were approximately 10-30 Bq/m3, indicating that radon in hot spring water diffuses into the air and spreads within the facility. Outdoors, radon concentration was 12.5 Bq/m3 at a campsite near the discharge point of the radioactive spring.   Exposure dose is calculated under the assumption of a two-day stay, during which the visitor will use the bath for several hours. The results obtained show that the exposure dose at the hot spring facility is lower than the exposure dose from daily environmental radiation or medical devices. These conclusions are considered sufficient to confirm the safety of the hot spring facility.

Objectives: Radon (222Rn) is a noble gas found in the water of hot spring spas (“onsen”). In Japan, the Hot Springs Law and the Guideline of Analytical Methods of Mineral Springs (revised) classify springs containing 74 Bq/kg of radon as “hot springs” and those with levels exceeding 111 Bq/kg as “medical springs”, also called “radioactive springs”. According to the notification article (the Nature Conservation Bureau of the Ministry of the Environment in Japan), bathing in a radioactive springs may alleviate the effects of gout, arteriosclerosis, and hypertension as well as chronic conditions such as cholecystitis, gallstones, and skin and gynecological diseases. Drinking water from these springs may treat gout, chronic digestive disorders, chronic cholecystitis, gallstones, neuralgia, muscle pain, and arthralgia. To determine exposure doses from radioactive springs, it is important to establish an easy and accurate method of measuring radon concentration in water and humid air in bathing areas. Methods: This study measured the concentration of airborne radon using an activated charcoal detector (PICO-RAD: AccuStar Labs), desiccant (Drierite; 8 mesh of anhydrous calcium sulfate: W.A. Hammond Drierite Company, Ltd.), a liquid scintillation counter (LSC LB-5: Hitachi Aloka Medical, Ltd.), and 2,5-diphenyloxazole(DPO) + 1,4-bis (5-phenyl-2-oxazolyl) benzene(POPOP) toluene solution (Wako Pure Chemical Industries, Ltd.) were used as the liquid scintillator. Results and Conclusions: This study evaluated radon exposure doses due to radioactive spring at a spa in Komono town, Mie prefecture. After water was piped from hot spring storage tanks into bathtubs, only 5.3-18.0% of the radon remained in the water. Two days later, only 0.25% remained, likely due to radioactive decay and increased diffusion into the air from bathing and recirculating filters. Thus, we investigated radon levels in the humid bathroom air around the radioactive hot spring and determined the total radon exposure from spa water and air. The total exposure dose was calculated assuming a two-day stay, during which customers used the bath for some number of hours. Our findings confirm the safety and efficacy of the hot spring facility. This study was supported in part by a grant from the Daido Life Welfare Foundation.