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R Kroes

Publications and source records attributed to R Kroes.

At least 19 recordsLinked to original sources
PubMed2000

Pan-European research challenges in toxicology and epidemiology: twinning for the better.

At the Third Ministerial Conference on Environment and Health held in London in June 1999, a document on environment and health research for Europe was discussed and endorsed. This initiative - developed by the European Science Foundation, the European Commission and the WHO European Region - will be one of the largest of its kind in Europe. The programme described in particular an analysis of the more than 80 research recommendations which served as the basis for the high priority research questions presented in London. The need for an integrated multi-disciplinary approach is emphasised. The ultimate aim is to provide risk managers with tools to implement remediation and prevention effectively and efficiently in a prioritised fashion. Related research challenges in toxicology for the new millennium are described.

Congresses as Topic↗
PubMed2000

Safety evaluation and risk assessment of the herbicide Roundup and its active ingredient, glyphosate, for humans.

Reviews on the safety of glyphosate and Roundup herbicide that have been conducted by several regulatory agencies and scientific institutions worldwide have concluded that there is no indication of any human health concern. Nevertheless, questions regarding their safety are periodically raised. This review was undertaken to produce a current and comprehensive safety evaluation and risk assessment for humans. It includes assessments of glyphosate, its major breakdown product [aminomethylphosphonic acid (AMPA)], its Roundup formulations, and the predominant surfactant [polyethoxylated tallow amine (POEA)] used in Roundup formulations worldwide. The studies evaluated in this review included those performed for regulatory purposes as well as published research reports. The oral absorption of glyphosate and AMPA is low, and both materials are eliminated essentially unmetabolized. Dermal penetration studies with Roundup showed very low absorption. Experimental evidence has shown that neither glyphosate nor AMPA bioaccumulates in any animal tissue. No significant toxicity occurred in acute, subchronic, and chronic studies. Direct ocular exposure to the concentrated Roundup formulation can result in transient irritation, while normal spray dilutions cause, at most, only minimal effects. The genotoxicity data for glyphosate and Roundup were assessed using a weight-of-evidence approach and standard evaluation criteria. There was no convincing evidence for direct DNA damage in vitro or in vivo, and it was concluded that Roundup and its components do not pose a risk for the production of heritable/somatic mutations in humans. Multiple lifetime feeding studies have failed to demonstrate any tumorigenic potential for glyphosate. Accordingly, it was concluded that glyphosate is noncarcinogenic. Glyphosate, AMPA, and POEA were not teratogenic or developmentally toxic. There were no effects on fertility or reproductive parameters in two multigeneration reproduction studies with glyphosate. Likewise there were no adverse effects in reproductive tissues from animals treated with glyphosate, AMPA, or POEA in chronic and/or subchronic studies. Results from standard studies with these materials also failed to show any effects indicative of endocrine modulation. Therefore, it is concluded that the use of Roundup herbicide does not result in adverse effects on development, reproduction, or endocrine systems in humans and other mammals. For purposes of risk assessment, no-observed-adverse-effect levels (NOAELs) were identified for all subchronic, chronic, developmental, and reproduction studies with glyphosate, AMPA, and POEA. Margins-of-exposure for chronic risk were calculated for each compound by dividing the lowest applicable NOAEL by worst-case estimates of chronic exposure. Acute risks were assessed by comparison of oral LD50 values to estimated maximum acute human exposure. It was concluded that, under present and expected conditions of use, Roundup herbicide does not pose a health risk to humans.

Abnormalities, Drug-Induced↗
PubMed1999

Sialidase gene transfection enhances epidermal growth factor receptor activity in an epidermoid carcinoma cell line, A431.

Glycosphingolipids expressed in cancer cells have been implicated in the modulation of tumor cell growth through their interaction with transmembrane signaling molecules such as growth factor receptors. For glycosphingolipids to interact with growth factor receptors, the presence of sialic acid seems to be essential. Stable transfection of a gene encoding a soluble Mr 42,000 sialidase into a human epidermoid carcinoma cell line (A431) provided an approach by which the level of terminal lipid-bound sialic acid on the cell surface could be altered. In the sialidase-positive clones, the level of ganglioside GM3 was diminished, and little change was observed in protein sialylation. Sialidase-transfected cells grew faster than control cells. Sialidase expression did not modify the binding of epidermal growth factor (EGF) to its receptor but enhanced EGF receptor (EGFR) tyrosine autophosphorylation as compared to that of parental cells or cells transfected with the vector (pcDNA3) alone. Moreover, the phosphorylation of the EGFR, as well as other protein substrates, was observed at low EGF concentrations, suggesting an increase in the receptor kinase sensitivity. These data provided evidence that changes in ganglioside expression in cancer cells by appropriate gene transfection can dramatically affect EGFR kinase activity. Hence, the modulation of ganglioside expression may represent an approach to alter tumor cell growth.

Carcinoma, Squamous Cell↗
PubMed1995

European School of Oncology Advisory report to the European Commission for the "Europe Against Cancer Programme" European Code Against Cancer.

A European School of Oncology Advisory Group has reviewed the European Code Against Cancer after its initial use over a 6-year period. With minor modifications, the original ten recommendations were found to be adequate, although it was agreed that an Annex was necessary to explain the scientific evidence supporting each point, and is presented herewith. Tobacco smoking clearly remains the most important cause of cancer, and now it can be quantified better than ever before. It is also clear that it is never too late to stop smoking: stopping even in middle age, prior to the onset of serious illness has a beneficial effect on life expectancy. Alcohol drinking is an important cause of cancer, and yet modest consumption levels protect against cardiovascular disease mortality. The optimal strategy seems to be a consumption not exceeding 2-3 drinks per day, although this limit may be lower for women. Increased consumption of fruits and vegetables, reduction in consumption of fatty foods, reduction of obesity and increased physical activity can all be recommended to reduce cancer risk. Exposure to excessive sunlight remains a problem which should be limited. Control of occupational cancer is a three-way partnership: legislation identifies and limits exposure to known carcinogens, employers enact the legislation and workers should respect the measures introduced. There are a number of signs and symptoms which may lead to cancer being diagnosed earlier, and patients with these should be referred to a doctor. For women, participation in organised programmes of cervical cancer and breast cancer (after 50 years of age) should lead to a reduction in mortality from these forms of cancer. The key element is organised programmes, where quality control and quality assurance are in force. These revised recommendations are the result of an agreement following advice, review and dialogue with cancer experts throughout Europe. They were approved by the European Community Cancer Experts at their meeting in Bonn on 28-29 November 1994. Their implementation by the European population should greatly reduce cancer incidence and mortality.

Alcohol Drinking↗
PubMed1994

The intake of chemicals related to age in long-term toxicity studies--considerations for risk assessment.

The estimation of acceptable daily intake (ADI) is generally based on results from long-term toxicity studies. Long-term exposure of rodent and nonrodent species is extrapolated to lifetime exposure in humans, using uncertainty factors to compensate inter- and intraspecies differences. Special consideration can be given to groups of humans at increased risk, such as children, due to higher susceptibility or higher predicted intake. A retrospective study of long-term carcinogenesis studies was performed at the National Toxicology Program of the National Institute of Environmental Health Sciences to gain insight into the relationship between age and intake of test compounds. In these long-term studies, average intake of feed and drinking water, and consequently chemicals dosed in these, was approximately two times higher on a body weight basis in young animals (postweaning) than in adults. Thus, estimating an ADI from the NOEL of this type of studies already includes a higher dose for the young. When maximum levels for food additives are being set using the already established ADI, it may not be necessary to add an additional uncertainty factor for different ages, unless there are other specific reasons to do so, such as unduly high exposure and toxicity at a certain age. Compared to intake per kilogram of body weight at the end of the study, the ADI already includes an extra uncertainty factor of approximately 2 for young individuals.

Aging↗
PubMed1993

The no-effect level of sodium bromide in healthy volunteers.

1. A total of 0, 4 and 9 mg kg-1 body weight sodium bromide was administered orally to 45 healthy female volunteers. 2. The experiment lasted for six menstrual cycles: only during the first three cycles was bromide administered; 3. At the start, at the end of the administration period and at the end of the experiment a physical examination and haematological and routine clinical chemistry tests were performed. Except for nausea in relation to the intake of bromide, no adverse effects were observed. 4. The bromide concentration in plasma rose to 3.22 +/- 0.93 mmol kg-1 in the 4 mg kg-1 group and to 7.99 +/- 1.89 in the 9 mg kg-1 group by the end of the administration period. 5. Before and at the end of the experiment the thyroid hormones (T4, FT4, TBG, T3 and TSH) were analysed. No significant differences were observed between the groups. 6. Before, after three menstrual cycles and at the end of the experiment an EEG with a Visual Evoked Response was recorded. At the 4 and 9 mg kg-1 dose level in the alpha 1-band and the beta-bands significant changes were found (P < 0.1 and P < 0.05, respectively). The Visual Evoked Response showed no significant differences between the three groups. 7. From this experiment and previous experiments a no-effect level in humans for sodium bromide of 4 mg kg-1 body weight is proposed.

Adult↗
PubMed1992

Induction of proliferative lesions of ventral prostate, seminal vesicle, and other accessory sex glands in rats by N-methyl-N-nitrosourea: effect of castration, pretreatment with cyproterone acetate and testosterone propionate and rat strain.

Wistar (Cpb:WU), F344 or Sprague-Dawley rats were sequentially treated with cyproterone acetate (CA) for 21 days, testosterone propionate (TP) for 3 days, followed by a single i.v. injection of N-methyl-N-nitrosourea (MNU). One group of Wistar rats was castrated 4 weeks after MNU injection, and another group 58 weeks after MNU, when the first prostatic carcinoma was detected. Control groups received only CA + TP, CA, MNU, or they remained untreated. Early or late castration inhibited the development of atypical hyperplasia of the ventral prostate in Wistar rats. This lesion was induced by the CA + TP + MNU treatment in F344 rats, but not Sprague-Dawley rats; in Wistar rats, it was induced by CA + TP treatment, irrespective of whether MNU was given. Hypertrophic-hyperplastic lesions of the seminal vesicle were induced by MNU, irrespective of pretreatment, and their development was prevented by early castration and inhibited by late orchiectomy. Dorsolateral prostate carcinomas and preneoplasia occurred only in low incidence in Wistar and Sprague-Dawley rats. These lesions were absent in F344 rats that had received treatment with CA + TP + MNU. No dorsolateral prostate (pre)neoplasia was found in Wistar rats subjected to early orchiectomy, but rats castrated at 58 weeks had an incidence similar to that for the intact group treated with CA + TP + MNU. This finding supports the contention that androgens are required for the development of MNU-induced prostatic cancer in rats but that advanced carcinomas are androgen insensitive. Differences in incidence and localization of prostatic proliferative lesions between F344 and Wistar rats and between dorsolateral and ventral prostate could not be explained by differences in epithelial cell proliferative responses to CA + TP treatment at the time of MNU injection, since they were similar in ventral and dorsolateral prostate and were more prominent in F344 rats than in Wistar rats. DNA damage as estimated by MNU-induced unscheduled DNA synthesis also did not differ between dorsolateral and ventral prostate.

Androgens↗
PubMed1991

[Environment, chemicals and public health].

It is obvious that, to the general public, environmental pollution determines the state of public health to a considerable extent. Scientifically, however, this relationship is less readily detectable, particularly when the environment polluted by chemicals is the polluted human environment. It is more correct to define 'environment' to include both the 'external' and the 'local' environment. The external environment includes a part which is directly affected by man, for instance when man-made chemicals are involved as well as the natural environment. The local or personal environment particularly concerns matters which may be comprised in the term 'lifestyle'. The above forms of environment may all affect health, although effects may differ in quality and quantity. These relationships are discussed, with special reference to the occurrence of cancer.

Carcinogens↗