Cisplatin. Documentation of proposed values of occupational exposure limits (OELs)

Journal Title: Podstawy i Metody Oceny Środowiska Pracy - Year 2018, Vol 34, Issue 1

Abstract

Cisplatin is a cytostatic used in the treatment of testicular, ovarian, cervix and bladder cancers, squamous cell carcinoma of a head and a neck, small cell and non-small cell lung cancer. For medical staff, it is available in ampoules of 10 or 50 mg with a concentrate for solution for infusion (1 mg cisplatin/ml). Occupational exposure to cisplatin may occur during production and drug use in hospital wards. Exposure during production is a minor problem because it concerns a relatively narrow group of employees of pharmaceutical companies, that are subjected to requirements of good manufacturing practice and restrictive exposure control. A much larger group of workers exposed to cisplatin are health professionals (nurses, doctors, pharmacists, cleaning service, laundry workers) who care for and have contact with treated patients. The source of exposure for medical and auxiliary personnel may be preparation and administration of drug and excretions and secretions of patients. The main routes of occupational exposure during cisplatin production processes are respiratory and skin. In hospitals, skin is the main route of exposure, although inhalation exposure cannot be excluded, mainly on cisplatin aerosols. The highest concentrations of cisplatin in the occupational environment air were < 5.3 ng/m3, while on different surfaces of pharmacy and hospital rooms, surgical equipment and gloves, concentrations did not exceed 110 ng/cm2. There are no quantitative data on the absorption of cisplatin through the skin or through the respiratory tract in humans, but it is known that the compound can absorb these routes, as demonstrated by studies conducted among pharmacists and medical personnel with significantly higher concentrations of platinum (Pt) in urine compared to the control group. There is little information on the health effects of occupational exposure to cisplatin. Only cases of occupational allergy manifesting by urticaria have been described. The data available in the literature refer mainly to adverse reactions in patients treated with cisplatin. The most commonly reported adverse effects of cisplatin are renal, haematological, hearing, gastrointestinal and neuropathic disorders. In about one third of patients, after the administration of a single dose of cisplatin (50 mg/m2), the toxic effects of the compound were observed on kidneys, bone marrow and hearing. The nephrotoxic, ototoxic and neurotoxic effects of cisplatin can be long-term and permanent. In animal toxicity studies with cisplatin, the compound was administered intraperitoneally or intravenously. Cisplatin affects mainly kidneys of animals, causing biochemical changes (including an increase creatinine and urea nitrogen levels in serum), and histopathological abnormalities, necrosis in the proximal renal tubules. Moreover, there were changes in liver enzymes activities, numerous inflammation and liver necrosis, and disorders in secretory cell distribution, intestinal barrier enzymes activities, and histopathological changes in the small intestine, which disturbed digestive processes and led to appetite disturbances in animals. Cisplatin is also ototoxic, leading to hearing loss in rodents. Changes in the blood parameters and disorders in the hematopoietic system have also been observed. Leukopenia, decreased number of neutrophils, lymphocytes and platelets, and bone marrow suppression occurred in exposed animals. In neurobehavioral tests in animals, cisplatin caused a decrease in physical activity. Cisplatin was mutagenic in tests on bacteria and on mammalian cells, including human lymphocytes. It evoked an increase in the frequency of sister chromatid exchanges and chromosomal aberrations. There were positive comet and micronucleus test results. One of the reported side effects of cisplatin therapy is its carcinogenic effect. The literature describes cases of acute non-lymphoblastic leukemia in patients treated with cisplatin only and carboplatin 6 years after chemotherapy. In the available literature, there are no data on the incidence of cancer of workers professionally exposed only to cisplatin. The existing reports concern simultaneous exposure to various cytostatics. Cisplatin has been shown to be carcinogenic to mice and rats after intraperitoneal administration. In mice exposed to cisplatin an increased number and incidence of lung adenomas were observed. After exposure of animals to cisplatin intraperitoneally, and additionally to epidermal croton oil, skin papillomas were noticed. In the exposed rats, cisplatin induced leukemia. The cisplatin was classified by IARC experts as probably carcinogenic to humans (Group 2A). In DECOS, it was considered as genotoxic carcinogen, NTP also classifies it as a potentially carcinogenic substance for humans. Although cisplatin has not been officially classified in the EU and there is lack of its harmonized classification, most manufacturers classify this compound as a carcinogen 1B category. There is no data available in the literature on clinical cases and results of epidemiological studies on the effect of cisplatin on the fetus and reproduction due to occupational exposure to this compound. Based on the described cases of pregnant patients treated with cisplatin, this compound is known to cross the placenta and into breast milk. Serious malformations were observed in 20% of children of patients treated with cisplatin in the first trimester of pregnancy and 1% of children in patients treated in the second and/or third trimester of pregnancy. In men, chronic administration of cisplatin induced reversible azoospermia and Leydig cell dysfunction. Of the 61 women with ovarian cancer undergoing conservative surgery and cisplatin chemotherapy at reproductive age, 47% gave birth to children after treatment, and 87% of those trying to get pregnant, became pregnant. In laboratory animal studies, cisplatin was highly embryotoxic. Teratogenic changes were less frequently observed. Cisplatin also affected ovarian activity. Based on the cisplatin toxicity data available in humans and animals, it is not possible to determine the dose-response relationship. The analysis of the classification of drugs used by ASHP, NIOSH, IACP and IPCS shows that the cisplatin should have a permissible occupational exposure value within 0.001–0.01 mg/m3. Considering the quantitative carcinogenicity assessment of cisplatin performed by DECOS experts and the acceptable level of occupational risk set by the Interdepartmental Commission on MAC (10-3–10-4) for carcinogens, acceptable concentrations of cisplatin in the work environment should be within 0.005 mg/m3–0.0005 mg/m3. In most countries (in the USA, Belgium, Switzerland and Hungary), the occupational exposure limits for this compound were set at 0.002 mg/m3. The maximum admissible concentration (MAC) value for cisplatin was proposed at 0.002 mg/m3. It was proposed to label the substance as “Carc. 1B” – carcinogenic substance of category 1B, “Ft” – toxic to the fetus and “skin”, because absorption through the skin may be as important as inhalation. There are no substantive basis to establish the value of the short--term (STEL) and permissible concentrations in biological material (DSB) for cisplatin.<br/><br/>

Authors and Affiliations

Anna Pałaszewska-Tkacz, Sławomir Czerczak

Keywords

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  • EP ID EP274624
  • DOI 10.5604/01.3001.0011.5845
  • Views 110
  • Downloads 0

How To Cite

Anna Pałaszewska-Tkacz, Sławomir Czerczak (2018). Cisplatin. Documentation of proposed values of occupational exposure limits (OELs). Podstawy i Metody Oceny Środowiska Pracy, 34(1), 13-52. https://europub.co.uk/articles/-A-274624