Effects in humans

Chromium deficiency symptoms have been clearly identified in patients receiving total parenteral nutrition (TPN) without chromium. One patient who had received TPN for 31/2 years developed symptoms of hyperglycemia, weight loss, ataxia and peripheral neuropathy. When chromium 

Because chromium potentiates the action of glucose, a poor chromium status might lead to impaired glucose tolerance and Type II diabetes (Anderson 1998). The prevalence of impaired glucose tolerance was 15.8% in adults aged 40-74 years in the Third National Health and Nutrition Examination Survey in the U.S. (Harris etal. 

Data on effects of chromium on accretion of lean body mass are also equivocal (Campbell etal. 1999 Lukaski 1999). 

The adequate intake (Al) for chromium established by the National Academy of Sciences is based on 13.4 pg Cr per 1000 kcal (Food and Nutrition Board 2001). This is expressed as an Al of 25 pg per day for women and 35 pg per day for adult men. 

The Al is somewhat lower for the elderly because of their lower energy expenditure (Briefel et al. 1995). Based on a report from Anderson and Kozlovsky in 1985, more than 50% of the 216 diets which they analyzed contained less chromium than the Al for adults. 

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Urethane [51-79-6] (ethyl carbamate) occurs as a natural by-product in fermented products such as wine, Hquors, yogurt, beer, bread, oHves, cheeses, and soy sauces. Whereas urethane has a known cancer etiology in experimental animals, no such relationship has yet been proven in humans (108,109). Alcohol may act by blocking the metaboHsm of urethane, and thus exert a protective effect in humans consuming alcohoHc beverages (110). 

Antituberculin Agents. Rifampin [13292-46-17, a semisynthetic derivative of rifamycin SV, is a most valuable dmg for treatment of tuberculosis, an infection caused by mycobacteria, leprosy, and an expanding range of other infections (23). Cycloserine [64-41-7] has been used to a limited extent for treatment of tuberculosis as a reserve dmg. Although cycloserine inhibits bacteria by interfering with their cell wall biosynthesis, it has toxic side effects in humans in the form of neurotoxicity. Capreomycin [11003-38-6] and to a much lesser extent viomycin [32988-50-4] both of which are peptides, have also been used for treatment of this disease. 

Value is toxic dose low. TD q, the lowest dose of a substance introduced by any route other than inhalation, over any given period of time to which humans or animals have been exposed and reported to produce any nonsignificant toxic effect in humans or to produce nonsignificant tiimorigenic or reproductive effects in animals or humans. 

Effects in Humans. In chlorophenol production, irritation symptoms of the nose, eyes, respiratory tract, and skin resulting ia chloroacne have been observed. The results of epidemiology studies on the long-term effects of chlorophenols are quite contradictory and have not allowed the experts to reach any firm conclusions (54). 

Table 7. Ethanol Vapor Concentration and Its Effects in Humans ...

Effects in humans for which links with exposure to endocrine disrupters have been suggested include the following. 

Of all the uncertainties surrounding the hypothesis that environmental chemicals with endocrine disrupting properties are responsible for the observed effects in humans and wildlife, one of the major unknowns relates to exposure. Humans and wildlife can be, and sometimes are, exposed to these substances in the environment but our knowledge of the levels, routes and timing of exposure is poor. 

Health Hazards Information - Recommended Personal Protective Equipment Dust mask goggles or face shield protective gloves Symptoms Following Exposure Inhalation of dust irritates nose and throat. Contact with eyes causes irritation General Treatment for Exposure INHALATION move to fresh air. EYES flush immediately with physiological saline or water get medical care if irritation persists. SKIN flush with water Toxicity by Inhalation (Thresholdlimit Value) Data not available Short-Term Exposure Limits Data not available Toxicity by Ingestion Grade 1 oral LDjq 11.7 g/kg (rat) Late Toxicity Chronic effects in humans are unknown Vapor (Gas) Irritant Characteristics Not pertinent liqidd or Solid Irritant Characteristics Data not available Odor Threshold Data not available. 

The analysis of the consequences of nuclear accidents began with physical concepts of core melt, discussed the mathematical and code models of radionuclide release and transport within the plant to its release into the environment, models for atmospheric transport and the calculation of health effects in humans. After the probabilities and consequences of the accidents have been determined, they must be assembled and the results studied and presented to convey the meanings. 

Exposure assessment to reveal the exposure of different groups of people, and to compare their exposure levels to the doses that cause harmful effects in humans as shown in epidemiological studies, or to doses that cause toxic effects in experimental animals... 

Hazard identification, step one, means identification of new chemicals or other factors that may cause harmful health effects. Previously, novel hazards were usually observed in case studies or after accidents or other excessive exposures, usually in occupational environments. Today, thorough toxicity studies are required on all pesticides, food additives, and drugs. New chemicals also have to be studied for their potential toxic effects. Thus, earlier hazards were in most cases identified after they had caused harmful effects in humans. Today, most chemical products have been evaluated for their toxicity with experimental animals. Therefore, hazard identification has become a preventive procedure based on safety studies conducted before a chemical compound or product reaches the market, and before individuals are exposed to it. ... 

Using dose-response information from animal studies to predict effects in humans... 

Both disodium cromoglycate and nedocromil sodium have antitussive effects in humans. In this instance, their activity occurs by increasing the depolarisation of sensory nerves, which increases the threshold for an action potential and therefore inhibits the activity of these neurons. 

Taking into account the low oral toxicity and the low intestinal and percutaneous absorption of alcohol sulfates and alcohol ether sulfates, the possibility of systemic toxic effects in humans is extremely unlikely [344]. 

The overall objective of clinical trials is to establish a drug therapy that is safe and effective in humans, to the extent that the risk-benefit relationship is acceptable. The ICH process has developed an internationally accepted definition of a clinical trial as Any investigation in human subjects intended to discover or verify the clinical, pharmacological and/or other pharmacodynamic effects of one or more investigational medicinal product(s), and/or to identify any adverse reactions to one or more investigational medicinal product(s) and/or to study absorption, distribution, metabolism and excretion of one or more investigational medicinal product(s) with the object of ascertaining its (their) safety and/or efficacy. ... 

What are the reported carbon and nitrogen effects in humans Not much data has been published regarding herbivore-human carbon shifts. We will discuss our data in a later section. 

Table 3.2 shows the 5 Cu and 5 Cc values of herbivores, omnivores, carnivores and humans. The (climate-corrected) trophic level effect between herbivores and carnivores is 0.90%o. Human values are closer to carnivore and omnivore values than to herbivore 5 Cc values. The human 5 Cc values are on average 0.66%o more positive than the herbivore 5 Cc values, a good estimate for a carnivore effect in humans (see section on trophic level effects, below). The average human 5 Cc value is -19.92 1.28%o,which would indicate that Holocene humans in Europe had a diet that consisted of C3 terrestrial foods, whieh is as might be expected. By looking at the humans separate from the total bone data set, we notice potential human food selection (Fig. 3.3) we can see a non-climatic pattern, which is much less uniform than in the total bone data set (Fig. 3.2b). Italy (6 Cc = -21.3%o) has a much more negative 8 Cc value than the Czech Republic (8 Cc =-18.7%o), Spain (8 Cc = -19.3%o) and Greece (-18.9%o but the 8 N of 9.0%odoes not indicate marine food), while the northern European coimtries are closer to a 5 Cc value of-20%o. What the actual causes are for this pattern in the human samples is not clear to better understand these variations it is best to consider, where possible, the 8 N values with the 8 Cc values. 

Hematological Effects. No information was found regarding hematological effects in humans following exposure to methyl parathion. Repeated oral exposure to methyl parathion resulted in decreased mean corpuseular volume in one study and decreased hematocrit and erythrocyte count in another study in rats. Chronic ingestion of methyl parathion induced reduction of mean hemoglobin, hematocrit, and erythrocyte eounts in rats. 

The significance of the exposure levels shown in the Levels of Significant Exposure (LSE) tables and figures may differ depending on the user s perspective. Public health officials and others concerned with appropriate actions to take at hazardous waste sites may want information on levels of exposure associated with more subtle effects in humans or animals (LOAELs) or exposure levels below which no adverse effects (NOAELs) have been observed. Estimates of levels posing minimal risk to humans (minimal risk levels or MRLs) may be of interest to health professionals and citizens alike. 

No studies were located regarding gastrointestinal, hematological, musculoskeletal, or dermal effects in humans or animals after inhalation exposure to methyl parathion. Dean et al. (1984) reported that seven children exposed to methyl parathion by many routes exhibited pinpoint pupils, abdominal pain, and diarrhea. The respiratory, cardiovascular, hepatic, and renal effects reported by Fazekas (1971) that were found in humans acutely exposed to methyl parathion intoxication resulted from exposure by all three routes however, the results did not distinguish between the routes. 

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