PubMed HealthSearch

SEARCH · PubMed Health

Results for “Bathing Beaches”

Explore indexed PubMed citations for clinical trials, systematic reviews and public health research. Read source abstracts and follow each citation to its original PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 19 recordsLinked to original sources

A probabilistic model of bathing beach safety.

An improved mathematical model for bathing beach safety is proposed. It is derived by joining the probability of infection from a given dose (Poisson distribution and the probability of acquiring such a dose (lognormal distribution). Even in the absence of better clinical and epidemiological data, the model permits an assessment of relative risk from certain hazards and the design of more meaningful bacteriological standards for individual beaches.

Bacteria

The occurrence of Candida Albicans in Lake Ontario bathing beaches.

There are inherent weaknesses associated with currently used bacterial fecal pollution indicator systems. Fecal pollution indicator data would be more meaningful if supplemented with information relating to the occurrence of pathogens in recreational water. Through surveys of four bathing beaches on Lake Ontario, it was established that the opportunistically pathogenic yeast Candida albicans occurs in near shore waters. The beaches surveyed could be differentiated on the basis of bacterial fecal pollution indicator levels and numbers of the pathogens C. albicans and Pseudomonas aeruginosa. The occurrence of C. albicans and P. aeruginosa appeared to be related to elevated fecal pollution indicator levels. Maximum numbers of all parameters were observed in July and August in association with peak bather loads at the beaches. In only one instance does the data suggest that a beach was subjected to human fecal contamination.

Bathing Beaches

Relationship of microbial indicators to health effects at marine bathing beaches.

Findings are described from the second year of an epidemiological-microbiological study conducted at New York City beaches as part of the U.S. Environmental Protection Agency program to develop health effects-recreational water quality criteria. Symptomatology rates among swimmers (defined as immersion of the head in the water) relative to nonswimming but beach-going controls at a "barely acceptable" (BA) beach and a "relatively unpolluted" (RU) beach were examined. Data were collected by contacting family groups at the beach on weekends, obtaining information on bathing activity, and then questioning them by phone some 8--10 days later. In addition measurements were made for a number of potential water quality indicators. It was observed that the symptom rates, categorized as gastrointestinal (GI), respiratory, "other", and "disabling" (stayed home, stayed in bed, consulted a physician), were higher among swimmers than nonswimmers. As in the pretest conducted the previous year, the rate of GI symptoms was significantly higher among swimmers relative to nonswimmers at the BA but not the RU beach. Children, Hispanic Americans, and the low-middle socioeconomic groups were identified as the most susceptible portions of the population.

Adolescent

Tumors and amyloidosis in mice painted with crude oil found on bathing beaches.

Oil lumps collected on the beaches of Israel in 1970, 1971 and 1973 were extracted with pure acetone and the extracts were used to paint the skin of mice twice weekly for 12 months. The oil lumps originated from crude oil spilled from tankers. The less recently collected oils induced papillomata and lymphomata in some animals. They were also more active than the recent oil in the induction of generalized amyloidosis. Mice painted for 12 months with acetone alone developed amyloidosis to a similar extent as those painted with the oldest oil. In previously reported experiments, however, acetone was much less active than the oil in producing amyloidosis after 5 months of painting. The possibility that acetone and oil might act both synergistically or to be antagonistic at different phases of amyloidogenesis is discussed.

Amyloidosis

Respiratory colonization with Pseudomonas putrefaciens after near-drowning in salt water.

Pseudomonas putrefaciens, a marine organism infrequently found in human culture material, was repeatedly isolated from the sputum of a patient with pneumonia during a three-week period following a salt-water drowning accident. Similar organisms were found in the water at the site of the accident in Boston, and at ocean bathing beaches on nearby Martha's Vineyard.

Drowning

Rapid seven-hour fecal coliform test.

A rapid 7-h fecal coliform (FC) test for the detection of FC in water has been developed. This membrane filter test utilizes a lightly buffered lactose-based medium (m-7-h FC medium) combined with a sensitive pH indicator system. FC colonies appeared yellow against a light purple background after incubation at 41.5 degrees C for 7 to 7.25 h. Comparison of FC test results showed that the mean verified FC count ratio (7-h FC count/24-h FC count) for surface water samples was 1.08. The mean FC count ratio (7-h FC count/24-h FC count) for unchlorinater wastewater ranged from 1.95 to 5.05. Verification of yellow FC colonies from m-7-h FC medium averaged 97%. Data from field tests on Lake Michigan bathing beach water samples showed that unverified 7-h FC counts averaged 96% of the 24-h FC counts. The 7-h FC test was found to be suitable for the examination of surface waters and unchlorinated sewage and could serve as an emergency test for detection of sewage or fecal contamination of potable water.

Culture Media

[Research, education and environmental health related to pollution in the Gulf].

At Italian-Russian International Conference on "Rôle of the University on ecological education and training", was illustrate six topics of 30 years of our scientific and didactic activity on Environmental Hygiene, here below summarized: I. At first time, sludges of biological treatment plants and domestic sewage were frequently utilized under bacteriological control as economical and ecological fertilizers of land and waters. At present such a custom is very rare owing the chemical pollution of sewage continuously increasing; but in some countries it is still in use, and is our opinion and experience that organic waste material must be reused as fertilizer of land, more and more devoid of humus and subject to erosion of winds and waters. Some treatment plants are shown, and related plankton pyramid's. II. Pilot sewage treatment plants are frequently used in our experiments and training, for study and control of the biological degradation of organic matter, for evaluate the disappearance rate of bacteria and viruses, for investigate the foric action and behaviour of chemical and radioactive pollutants, for quantify their accumulation in the sludges of sewage treatment plants, and so forth. Different pilot plants are used, located both in our laboratories both in industries; in nuclear power plant are tested at the same time 3 models of 3 different plants (biodiscs, activated sludges, biofiltering channels), working with prevalent algal growth. III. Many species of microorganisms (metazoa, protozoa, algae, fungi, bacteria, viruses and new species like Bdellovibrio) are present in aerobic sewage treatment plants (activated sludge, bacterial bed, biodiscs, lagooning, etc.); in anaerobic treatment (digesters) prevail only methane-producing bacteria. Some of these organisms are very abundant and very active as consumers of organic matter; others are characteristic indicators of well balanced purification or of bad purification owing acute variation of organic load or presence of toxic substances in sewage. Many strains are antibiotic-producing, or Vit. B12 producing; others explain a strong lytic activity or are neuraminidase-formers. Production of great amount of biofloculant polysaccharides useful on sedimentation of organic matter is enhanced by adding particular organic pollutants like distillery wastes and others. Sewage treatment plants are good means for scientific research of particular biota continuously available and for food microbiological training for students and technicians on pathogens present in treated and untreated sewage and in sludges. IV. Big fecal pollution of coastal waters is clearly dangerous because of bathing beaches, shellfish farming, bacterial aerosols, damage to marine biota, eutrofication, aesthetic problems.(ABSTRACT TRUNCATED AT 400 WORDS)

Biodegradation, Environmental

Microbial classification of seawaters. The case against arbitrary health standards.

Various microbial health standards for recreational bathing waters obtain in many parts of the world, including Europe and America. These criteria appear to be a product of water laboratory scientists and legislators, bypassing the person most concerned--the local medical officer with his experience and knowledge of parochial epidemiology. In Natal we have a sophisticated and stringent system of grading bathing beaches which includes pathogenic microorganisms. The system functions as a measuring device for assessing changes in water quality, not as an arbitrary health standard. It is hoped that the practice of setting capricious so-called health standards for marine recreational waters does not spread to this country.

Escherichia coli

Variations in microbial indicator densities in beach waters and health-related assessment of bathing water quality.

Daily and hourly variations in microbial indicators densities in the beach-waters of Hong Kong have been described. The levels of Escherichia coli at a number of beaches was observed to be influenced by tide, and for staphylococci, by bather numbers. The tidal influence was most obvious during spring tides; and for the effect of bathers, during neap tides. Both organisms are present in high densities in external sources of faecal pollution of bathing beaches, with the average staphylococci to E. coli ratios being 0.04-3. Staphylococci may serve as an indicator of bather density and the risk of cross-infection amongst bathers (rather than as another indicator of faecal contamination) when the average staphylococci to E. coli ratio for a bathing beach is considerably higher than 3. The variability of microbial indicator densities means the routine sampling of bathing beaches should be carried out on weekend days with maximum numbers of swimmers exposed to the water, and spread throughout the bathing season.

Colony Count, Microbial

[Results of hardening in children with bronchial asthma].

In 40 girls between 10 and 16 years, 28 of them asthmatics, spirometry and body plethysmography was carried out before and after an air bath from the end of december at outside temperatures of -10 degrees C up to april at temperatures of +10 degrees C. In 50% of the asthmatic girls a bronchospasm occurred, which depended nearly linearly (r = 0.68) from the outside temperature. After the usual air bath at the beach in bathing suits in three quarters of these girls a regression of the bronchospasm nearly or completely to the initial values was observed. This change is interpreted as a sympathicotonic stimulation by the cutaneous system with bronchospasmolytic effect.

Adolescent