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Biomedical subjects

J Hartung

Publications and source records attributed to J Hartung.

12 recordsLinked to original sources

[Environmental hygiene tasks of the veterinarian in practice].

Apart from his direct tasks like treating diseased animals, preservation of animal health, recognition of mal-feeding and failures, recognition of unsuitable keeping systems and acknowledgement of animal welfare the veterinary practitioner can be the environmental-hygienic consultant of the farmer in following areas in particular: management and technique of feeding; management and technique of water supply; management and technique of air quality and ventilation; management and technique of manure handling and hygiene; cleaning and disinfection; deratting and pest control. The aim of these tasks is to diminish the risks/hazards for food products (food control act), the air (emission control act), surface water (law on the water household), ground water (waste control act, law on the water household) and vegetation and soil (waste control act, nature conservation act). Some examples will be given and comments are made on how to run a practice in an environmentally friendly way.

Air Pollution, Indoor

[Emission and control of gases and odorous substances from animal housing and manure depots].

Agricultural animal production in increasingly regarded as a source of gases which are both aggravating and ecologically harmful. An overview of the origin, number and quantity of trace gases emitted from animal housing and from manure stores is presented and possible means of preventing or reducing them are discussed. Of the 136 trace gases in the air of animal houses, odorous substances, ammonia and methane are most relevant to the environment. The role played by the remaining gases is largely unknown. Quantitative information is available for 23 gases. The gases are emitted principally from freshly deposited and stored faeces, from animal feed and from the animals themselves. Future work should determine sources and quantities of the gases emitted from animal housing more precisely and should aim to investigate the potential of these gases to cause damage in man, animals and environment. Odorous substances have an effect on the area immediately surrounding the animal housing. They can lead to considerable aggravation in humans. For years, VDI1 guidelines (3471/72), which prescribe distances between residential buildings and animal housing, have been valuable in preventing odour problems of this kind. Coverings are suitable for outside stores. The intensity of the odour from animal housing waste air increases from cattle through to hens and pigs; it is also further affected by the type of housing, the age of the animals and the purpose for which they are being kept. Methods of cleaning waste air (scrubbers/biofilters) are available for problematic cases. The need for guidelines to limit emissions from individual outside manure stores (lagoons) is recognised. Total ammonia emissions from animal production in the Federal Republic of Germany (up to 1989) are estimated at approximately 300,000 to 600,000 t/year. There is a shortage of satisfactory and precise research on the extent of emissions, in particular on those from naturally ventilated housing. It is calculated that between 12 and 21 kg/ha of nitrogen a year enter the soil via the air, the average of which is higher than the average "critical loads" for most natural habitats. Ammonia has a direct effect on the trees in the area surrounding animal housing and is transported long distances through the air causing eutrophication and acidification of water and vegetation. This frequently results in changes in plant sociology. Reduction measures must begin with the housing and manure removal systems and with feeding and management.(ABSTRACT TRUNCATED AT 400 WORDS)

Air Pollution

[Emissions of airborne substances from stalls of domestic animals].

There is concern on recent reports indicating an increase of respiratory affections in humans in areas with high livestock production. A survey is presented on airborne emissions from livestock buildings. About 136 gaseous compounds are analysed in animal house air of which 22 are quantified, only. The most environment-related compounds are ammonia and methane. It is assumed that German animal husbandry emits more than 350,000 t ammonia per year. The content of airborne microorganisms in livestock buildings is between some 100 and several 1000 per liter. The greatest part, more than 80%, are Staphylococcae and Streptococcae. Fungi, moulds and yeasts can form more than 1%, and coli-like bacteria about 0.5% of the total amount. Moulds like Penicillium, Aspergillus, Cladosporium and Alternaria were identified which are known to have allergic properties. The average concentrations of dust in animal barns vary between 0.5 and 20 mg/m3. The dust contains high amounts of protein and carries endotoxins which both have an allergic potential. Preliminary results show that the germ content of the surrounding air in areas with high animal densities seems to be distinctly higher than in non-livestock regions.

Agricultural Workers' Diseases

Paraben preservatives do not increase intracranial pressure in cats.

It has been hypothesized recently that succinylcholine-associated increases in intracranial pressure (ICP) are caused by the paraben preservatives contained in multidose vials. We tested that hypothesis in a standard feline model to determine the effects on ICP of equal-volume injections of preservative-free succinylcholine, succinylcholine with preservatives from multi-dose vials that contain both propylparaben and methylparaben, these preservatives alone at five times the dose contained in the succinylcholine, and normal saline. The preservatives alone increased ICP by 0.08 +/- 0.08 mmHg (+/- standard error; not significant). Normal saline had no effect on ICP. Preservative-free succinylcholine and succinylcholine with preservatives increased ICP by 4.2 +/- 0.10 and 3.8 +/- 0.07 mmHg respectively (P less than 0.01 compared to the preservatives alone and normal saline). The 99% upper confidence limit for the increase in ICP induced by the preservatives alone was 0.42 mmHg. This result suggests that parabens do not cause or substantially augment the ICP increase associated with succinylcholine administration.

Animals

[Anxiety and stress in dental practice. 2. Results of studies in children].

The stressor effects of various dental procedures were studied in 85 children. In the group of children undergoing extractions, the highest average values for pulse rate and blood pressure were observed right before anaesthesia. Stress reactions occurring in filling therapy were, on an average, almost as frequent and as severe than those due to extractions. "Anxious" children responded to dental procedures more frequently with increased 11-OHCS excretion in the urine than "indifferent" children, but there was no significant difference in adrenocortical activity.

11-Hydroxycorticosteroids

[Anxiety and stress in dental practice. 3. Results of studies in adults].

By means of clinical appreciation and determination of the adrenocortical function, the stressor effects of various dental procedures were evaluated in 110 patients aged from 18 to 77 years. The stress of stomatological treatment (extraction, filling therapy, prosthodontic procedures) may vary with age, the patient's psychic condition being of particular importance. Apart from premedication, psychic conditioning seems to be beneficial in case of tooth extraction.

Adolescent