ras oncoproteins in human plasma from lung cancer patients and healthy controls

Zinc oxide nanoparticles affect the expression of p53, Ras p21 and JNKs: an ex vivo/in vitro exposure study in respiratory disease patients

Zinc oxide (ZnO) nanoparticles are the mostly used engineered metal oxide nanoparticles in consumer products. This has increased the likelihood of human exposure to this engineered nanoparticle (ENPs) through different routes. At present, the majority of the studies concerning ZnO ENPs toxicity have been conducted using in vitro and in vivo systems. In this study, for the first time we assessed the effect of ZnO ENPs on the major cellular pathways in the lymphocytes of healthy individuals as well as in susceptible patients suffering from lung cancer, chronic obstructive pulmonary disease (COPD) and asthma. Using the differential expression analysis, we observed a significant (P < 0.05) dose-dependent (10, 20 and 40 µg/ml for 6h) increase in the expression of tumour suppressor protein p53 (40, 60 and 110%); Ras p21 (30, 52 and 80%); c-Jun N-terminal kinases; JNKs) (28, 47 and 78%) in lung cancer patient samples treated with ZnO ENPs compared to healthy controls. A similar trend was also seen in COPD patient samples where a significant (P < 0.05) dose-dependent increase in the expression of tumour suppressor protein p53 (26, 45 and 84%), Ras p21 (21, 40 and 77%), JNKs (17, 32 and 69%) was observed after 6h of ZnO ENPs treatment at the aforesaid concentrations. However, the increase in the expression profile of tested protein was not significant in the asthma patients as compared to controls. Our results reiterate the concern about the safety of ZnO ENPs in consumer products and suggest the need for a complete risk assessment of any new ENPs before its use.

Expression of ras (p21) protein in plasma from exposed workers and from patients with lung disease

Oncogenes are involved with the regulation of cellular proliferation and thus could be important in the development of many cancers. Cells transformed in culture by ras genes can be activated either by the introduction of specific point mutations or by overexpression of the normal proto-oncogene. The ras genes encode a protein of 189 amino acids (molecular mass 21 kDa) designated as p21. ras p21 proteins are contained in all eukaryotic cells on the inner surface of the plasma membrane. We measured ras p21 proteins in lung cancer patients, patients with chronic obstructive pulmonary disease (COPD) and workers exposed to emissions from petrochemical plants and 1,3-butadiene and 1,3-butadiene/styrene. Proteins were separated by gel electrophoresis, transferred to a nitrocellulose membrane by Western blotting and detected by chemiluminescence. A monoclonal pan-ras antibody was used as the primary antibody. Optical densities of the peak area of the protein bands were calculated and values which were two standard deviations above negative control means were considered positive. Many of the cancer patients and some of the COPD patients gave positive responses, whilst exposed worker groups did not show statistically significant increases by comparison with the controls. Thus, an increase in ras oncoproteins could be a biomarker for cancer or the disease state in general, but it cannot be ruled out that it is a biomarker for exposure since many of the individuals examined were smokers exposed to cigarette smoke.

Serum ras (p21) as a marker for occupationally derived lung cancer?

Certain subsets of the population are especially sensitive to carcinogens, and this can be determined using molecular biological methods. In the literature there has been evidence presented for the use of p21ras (ras) as a tumor marker for human carcinogenic substances such as asbestos, polycyclic aromatic hydrocarbons, and vinyl chloride in the workplace. In this study we have examined whether serum ras could serve as a biomarker for the early detection of occupationally derived lung cancer, with an emphasis on Schneeberger (radon-induced) lung cancer. Sera were taken from 65 male tumor patients. Fifty-nine patients suffered from primary lung cancer (including 18 patients with Schneeberger lung cancer and 12 patients with asbestos-related lung cancer). Additionally, 29 patients with non-malignant lung disease, and a healthy control group (44) including 32 former uranium miners of SDAG Wismut exposed to ionizing radiation (radon and its decay products) were examined. Ras protein was determined via three different methods: 1) immunoprecipitation followed by SDS-polyacrylamide gel electrophoresis (SDS-PAGE) and Western blotting; 2) SDS-PAGE using 5-17% gradient gels followed by Western blotting; 3) pre-incubation with Blue Sepharose, SDS-PAGE on 5-17% gradient gels, and Western blotting. The results show that 1 ng ras protein was measurable in serum standards. This protein could not be detected in patient sera or in sera from any of the study groups. Thus, ras cannot be considered useful as a marker for the early detection of asbestos-induced or Schneeberger lung cancer.

Examination of ras oncoproteins in human plasma from healthy controls and workers exposed to petroleum emissions, including benzene-related compounds

Ras oncoproteins in blood plasma from workers exposed to petroleum emissions and unexposed controls were examined from Polish and Estonian samples. Twenty-four workers and 35 unexposed controls were examined from Poland and 97 exposed and 40 unexposed controls from Estonia. Of the Estonian workers, 50 were exposed to benzene in a benzene production plant and 47 to polyaromatic hydrocarbons and benzene in a cokery. Blood plasma proteins were separated by gel electrophoresis, transferred to a nitrocellulose membrane by Western blotting and detected by chemiluminescence using a monoclonal antibody as the primary antibody. There were no statistically significant differences between the exposed and the control groups in either the Polish or the Estonian samples.

Biomarker responses in human populations: towards a worldwide map

The discipline of epidemiology studies the determinants of diseases in human populations, identifies causes, determines outcomes and develops prevention strategies. Traditional epidemiology is most useful for studies of acute, relatively common diseases with short incubation periods but less so for studies of chronic low incidence diseases with long incubation periods. Molecular epidemiology, which employs biological responses or biomarkers as surrogates of exposures or effects, can help with the latter. For this reason, there is a great interest in developing and validating biomarkers. DNA damage underlies an important group of chronic diseases with long incubation periods, i.e., cancer. Biomarkers may measure the exposures that induce the DNA damage, the damage itself, or individual susceptibility to damage. Before they can be used for human population research, however, these measures must be validated. Biomarker validation critically depends on field studies. This is accomplished through transitional epidemiological studies that 'bridge the gap' between laboratory and field. Transitional epidemiological studies are of three varieties: (i) Developmental, (ii) Characterization, and (iii) Applied. Biomarkers are the dependent variables in transitional studies. An international network of laboratories for human population monitoring requires yet another dimension for validation, i.e., the comparability of results among laboratories must be determined. This will be achieved by sample sharing projects, with workshops to compare results. Only then can results in one population be compared with results in another. Interlaboratory standardization of assays for biomarkers validated by transitional studies will have far-reaching benefits. It will allow development of worldwide databases of background values for the various biomarkers-or biomarker maps. This, in turn, will facilitate problem identification and eventually constitute the baselines for area-specific population monitoring. Biomarker databases so developed can be compared with worldwide databases for cancer and heritable diseases, validating the former as statistical surrogates of the latter.

Examination of various biomarkers measuring genotoxic endpoints from Barcelona airport personnel

Three different biomarkers: sister-chromatid exchanges (SCE), micronuclei (MN), and the Comet assay, were used to evaluate different kinds of genetic damage in peripheral blood lymphocytes from 34 male workers at Barcelona airport, exposed to low levels of hydrocarbons and jet fuel derivatives. The control group consisted of 11 unexposed men. We also investigated the ras p21 protein levels in plasma, in order to evaluate whether the ras gene could serve as a suitable potential marker of carcinogenic pollution in occupationally exposed cohorts. SCE and MN analyses failed to detect any statistically significant increase in the airport workers when compared with the controls, and in fact, the frequency of binucleated cells with MN in the exposed group was significantly lower than that obtained in the control. However, slight but significant differences in the mean comet length and genetic damage index were observed between the exposed and control groups when using the Comet assay. There were no statistically significant differences between both groups in p21 plasma levels. Smoking was shown to affect significantly both SCE and high frequency cells (HFC) in the exposed group.

Ras p21 protein levels in human plasma from patients with chronic obstructive pulmonary disease (COPD) compared with lung cancer patients and healthy controls

To explore the value of an increase in ras p21 proteins in plasma as a biomarker for the carcinogenic process or for the general disease state, we have directly analysed for ras p21 proteins, plasma samples from Polish human patients with chronic obstructive pulmonary disease (COPD). They were compared with appropriate controls and also with the Polish lung cancer patients previously examined before treatment [D. Anderson, J.A. Hughes, A. Cebulska-Wasilewska, E. Nizankowska, B. Graca, Ras oncoproteins in human plasma from lung cancer patients and healthy controls, Mutat. Res. 349 (1996) 121-126]. An elevated level of ras p21 proteins was considered to be greater than 2 standard deviations (SD) above the mean negative control values. Nine out of 20 COPD patients (mean age = 65.9 years) had increased ras p21 protein levels when compared with 20 age-matched (mean age = 62.4 years) controls of the present study with a mean + 2 SD of 0.70. Eighteen out of 40 lung cancer patients (mean age = 60.1 years) had increased ras p21 protein levels compared with their concurrent controls (mean age = 40.2 years) with a mean + 2 SD of 2.53. However when compared with the age-matched controls of this present study, there were 35 out of 40 (87.5%) with increased levels. When the COPD patients and lung cancer patients were compared with 101 historical controls (age range 25-76 years, of those whose age was recorded) from unexposed healthy populations from Poland, Estonia and Spain with a mean + 2 SD of 1.83, then 4 out of 20 (20%) COPD patients and 30 out of 40 (75%) lung cancer patients had increased levels. Whether using concurrent controls, age-matched controls or historical controls, the data would suggest that an increase in ras p21 protein levels in plasma from lung cancer patients could be a possible prognostic marker or biomarker for lung cancer. COPD patients when compared with historical controls or age-matched controls had lower ras p21 protein values than cancer patients. Their ras p21 protein values might also be a biomarker for cancer. It is possible that some of these COPD patients were in the process of developing cancer or perhaps would die from COPD before cancer develops. It cannot be ruled out that the increases could be a biomarker of exposure since many of the lung cancer patients and most of the COPD patients were smokers.

Examination of ras (P21) proteins in plasma from workers exposed to benzene emissions from petrochemical plants and healthy controls

Exposure of workers to benzene and polyaromatic hydrocarbons has been documented to be at relatively high levels in the production of benzene and in the coking process at a petrochemical plant in the oil shale area in Estonia. Altogether 97 plasma samples from workers and 40 from unexposed matched referents from two samplings in different seasons were analyzed for the presence of ras (P21) proteins; of the workers 50 were exposed to benzene in the benzene production plant and 47 to polyaromatic hydrocarbons and benzene in a cokery. Proteins were separated by gel electrophoresis, transferred to a nitrocellulose membrane by Western blotting and detected by chemiluminescence, using a monoclonal antibody as the primary antibody. There were no statistically significant differences between the exposed and the referent groups. The results are thus in keeping with the lack of exposure related cytogenetic effects for this same workforce.

Factors affecting various biomarkers in untreated lung cancer patients and healthy donors

The purpose of the present communication was to determine in lung cancer patients and healthy donors if there was a possible association between cancer and biomarkers of cytogenetic damage and ras p21 oncoprotein levels, and if various exogenous confounding factors (such as smoking habit) and endogenous ones (age, sex, etc.) could affect these biomarkers. Peripheral blood and plasma were collected from 31 lung cancer patients prior to treatment and 35 healthy donors of a similar socioeconomic status and from the same region in Poland. Chromosomal aberrations (CA), sister chromatid exchanges (SCE), high frequency cells (HFC), and proliferative rate index (PRI) were examined from the blood and ras p21 oncoproteins from the plasma. These parameters were used as biomarkers of genotoxic anomalies. All the biomarkers were examined for their relationship to confounding factors of age, sex, smoking habit, and immediate family cancer history. Results were analyzed by a t-test, analysis of variance (ANOVA), and stepwise multivariate regression analysis. All types of CA (including and excluding gaps), percent aberrant cells, SCE, and ras p21 oncoproteins were statistically significantly higher in cancer patients than in the healthy donors. Although there were smaller numbers of females in the cancer patients group who were older than the males, there was a difference due to sex (gender) with statistically significant increases in females for CA, SCE, and HFC, but there was no increase for ras p21 oncoproteins. Cytogenetic damage was not related to other cancers in the immediate families of the groups. All major CA parameters differed significantly between smokers and non-smokers in the cancer patients group, and SCE and HFC differed in the healthy donors group. Such parameters also showed a significant variability with the number of cigarettes smoked and the years of smoking habit. Multivariate regression analyses showed a significant association between cytogenetic damage, ras p21 oncoproteins, and cancer. In conclusion, cytogenetic damage and ras p21 oncoproteins in this study appear to be biomarkers associated with cancer, but have not been proved causally, and confounding factors such as age, sex (gender), and smoking can have an impact on them.

Monitoring of occupational exposure to cytostatic anticancer agents

Many anticancer agents have been shown to be carcinogenic, mutagenic and teratogenic in experimental animals and in in vitro test systems. Epidemiological data on the association of second neoplasms with a specific chemotherapy treatment is available on some 30 agents, and in the case of 10 compounds the overall evidence on human carcinogenicity has been evaluated to be conclusive (Group 1: IARC, 1987 and 1990). The primary source of human exposure to anticancer drugs is from their use in therapy of cancer. However, persons employed in the manufacture, preparation and administration of the drugs to patients and in nursing patients may also be exposed. Safe handling of anticancer drugs, since the introduction of various general handling guidelines, is now good practice in hospitals, pharmacies and drug manufacturing companies of most developed countries. Careless handling of cancer chemotherapeutic agents may lead to exposure of the personnel in amounts detectable with chemical or biological methods in the body fluids or cell samples of the subjects. The exposure is typically to mixed compounds over long-term and to low exposure levels with accidental peaks. Therefore, the use of biological exposure markers is appropriate for the monitoring of such exposure patterns. The biological markers/methods for exposure assessment are either non-specific (e.g., cytogenetic damage, point mutations or 32P-post-labelling adducts in peripheral blood lymphocytes, urinary mutagenicity) or specific for a given compound (immunological methods for DNA adducts, specific analytical methods). Studies have revealed minor amounts of cyclophosphamide in the urine of pharmacy technicians and nurses handling the drug even when taking special safety precautions (Sessink et al. (1994a) J. Occup. Med., 36, 79; Sessink et al. (1994b) Arch. Env. Health, 49, 165). Another study showed surface wipe samples with measurable cyclophosphamide even away from the handling site (McDevitt et al. (1993) J. Occup. Med., 5, 57). These studies strongly implicate the importance of skin absorption as an exposure route. Also accidental spillage is never completely avoidable (Sorsa et al. (1988) Mutation Res., 204, 465-479). The potential confounders (smoking etc.), toxicokinetics of the agent(s) to be assessed and individual working practices should be carefully considered in any exposure assessment studies using human body fluid samples. Environmental monitoring on indicator cytostatics should be combined into studies designed to identify potential occupational exposure situations to anticancer agents. A properly performed study should also include dissemination of information to the workers to create a psychologically positive atmosphere for this important work.