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Epidemiological studies have demonstrated the relationship between exposure to ambient particulate matter (PM) and health effects in those with cardiopulmonary diseases. The free radical generating activity of particles has been suggested as a unifying factor in the biological activity of PM in toxicological studies but so far has not been applied as a method for environmental monitoring of PM. The purpose of this study was to characterize hydroxyl radical (OH*) production by different size fractions of PM, to use as an alternative method for monitoring of PM composition and activity. We have developed a method, using electron paramagnetic resonance (EPR), to measure OH* radical formation in suspensions of particles in the presence of hydrogen peroxide and 5,5-dimethyl-1-pyrroline-N-oxide (DMPO) as a specific spin-trap. Samples of ambient particulate matter (PM) of different size fractions were collected from various sites on various filters. PM deposited on filters as well as suspensions in water retain its ability to generate OH* and this generation is determined by concentration of hydrogen peroxide and soluble metals. However, large variations in OH* radical formation and kinetics were found with different soluble metals and within metals (Fe, V) with different valencies. The method was applied to environmental monitoring in Hettstedt-Zerbst, situated in South-Eastern Germany, where it showed a relation to Cu-content of PM. The method was also applied in Duisburg, where the PMI fraction showed the highest DMPO-OH* generation but was not linked to particle counts. The method integrates metal bioavailability and reactivity and can provide a better understanding of the effect of small variations in mass concentrations on health.
OBJECTIVES: This study evaluates by comet assay the induction of early DNA damage in healthcare workers of an oncology hospital regularly handling antineoplastic drug mixtures. The aim was to identify a suitable biomarker of DNA damage by exposure to low levels of such drugs. METHODS: We studied 12 day hospital nurses and 13 oncology ward nurses who performed up to 300 and up to 35 drug administrations per week, respectively, and five pharmacy employees who regularly prepared mixtures of antineoplastic agents. Thirty healthy subjects were selected as controls. For exposure evaluation, we performed environmental monitoring of 5-fluorouracil, cytarabine, gemcitabine, cyclophosphamide, and ifosfamide in selected work areas of pharmacy and day hospital units and biological monitoring of urine for the 5-fluorouracile metabolite, alpha-fluoro-beta-alanine. We evaluated early DNA damage in lymphocytes and exfoliated buccal cells by comet assay measuring tail moment (TM) parameter that indirectly indicates the presence of DNA damage. RESULTS: Environmental monitoring detected cyclophosphamide, 5-fluorouracil and ifosfamide, with higher levels of contamination in day hospital unit. The biological monitoring measured detectable levels of alpha-fluoro-beta-alanine only in three nurses. Comet assay showed an increase on exfoliated buccal cells, even if not statistically significant, of mean TM with respect to controls in day hospital nurses (43.2 vs. 28.6, respectively) while ward nurses and pharmacy technicians did not show differences. Comet assay performed on lymphocytes did not show appreciable differences between exposed and controls. CONCLUSIONS: The employment of the sensitive comet assay, which is able to detect early the effects of a recent exposure to genotoxic substances, allowed us to find a slight DNA damage, only on exfoliated buccal cells of day hospital nurses, the group handling the highest amount of drugs during the administration process. This finding suggests that comet assay on exfoliated buccal cells could represent a useful tool to evaluate early and still repairable genotoxic effects of exposure to antineoplastic drug mixtures and then contribute to the improvement of the hospital safety practices.
A review of thermistor-based calorimetric measurement is presented. The principles of thermometric measurements are highlighted in the introduction followed by the instrumentation, materials and methods. Various applications relating to enzyme activity measurements, clinical monitoring, process monitoring, multianalyte determination, hybrid sensing, environmental monitoring, non-aqueous measurements and other miscellaneous applications are described. A brief note on future developments and a detailed reference list is also included.
Biological monitoring or, simply, biomonitoring (BM), refers to the periodic measurement of biological markers, or biomarkers (BMKs), in human fluids and tissues to assess the interaction (absorption, early health effects, susceptibility) between physical, chemical or biological agents and the human organism. The primary aim of BM in the workplace is to integrate environmental monitoring data and detect early, reversible biochemical or functional changes in workers exposed to chemicals before they become clinically relevant. BM also contributes to the assessment of chemical risk to workers, as individuals or as a group. Biomarkers are generally divided into three main types: biomarkers of exposure (BME), response/effect (BMR), and susceptibility (BMS). Other, more specific types of biomarkers are those of internal dose (BID), those of biologically effective dose (BED) and early biomarkers of disease (EBD). It is not always easy, however, to allocate a given BMK--such as the measurement of cytochrome P450 phenotype in subjects exposed to organic solvents--to one or the other type. Biomonitoring provides several advantages over environmental monitoring or health surveillance. For example, it allows an estimate of inter- and intra-individual variability in the absorption, distribution and excretion of chemicals. It also allows the detection of reversible changes before the appearance of a clinically relevant occupational impairment or disease. For these reasons, BM has become a routine procedure in occupational health practice throughout the world. Even the widely acknowledged, recently updated Code of Ethics for Occupational Health Professionals, a milestone in occupational health practice, only provides the basic ethical principles associated with biological monitoring. The aim of the present paper is to survey the various types of BMK available today with two main objectives: to discuss their toxicological significance and highlight the substantial differences that exist between their use in the practice of occupational health and in medical research. The development of new, more valid and reliable BMKs is strongly dependent on the understanding not only of the toxicokinetic and toxicodinamic mechanisms of chemicals, but also of the various susceptibility factors involved, whether genetic or environmental. It is hoped that the concurrent use of BMKs of different types may improve chemical risk assessment in workers, both individually and as a group.
This article reviews developments in the sampling and analysis of volatile organic compounds (VOCs) in ambient air since the 1970s, particularly in the field of environmental monitoring. Global monitoring of biogenic and anthropogenic VOC emissions is briefly described. Approaches used for environmental monitoring of VOCs and industrial hygiene VOC exposure assessments are compared. The historical development of the sampling and analytical methods used is discussed, and the relative advantages and disadvantages of sorbent and canister methods are identified. Overall, there is considerable variability in the reliability of VOC estimates and inventories. In general, canister methods provide superior precision and accuracy and are particulary useful for the analysis of complex mixtures of VOCs. Details of canister methods are reviewed in a companion paper.
More and more evidence from both laboratory and field experiments suggested that soil microbes were more sensitive to heavy metal stress than soil animals or plants living in the same soil. This understanding has been gradually accepted as a common point in this field. The history and the latest advances in soil microorganisms and its mediated processes under heavy metal stresses in soils were reviewed in this paper. It is difficult to do any comparison among the results from laboratory, field toxicological experiment and environmental monitoring. So far, a relevantly 'accurate' control soil was rarely available in the environmental monitoring. Much of evidence has indicated that not only microbial population/biomass was changed under heavy metal stress, but also its structure was varied. Although many molecular methods, such as PLFA, BIOLOG and DNA, have been developed to detect this microbial structural change, they always need many expensive instruments and accessories, and only could be done in laboratory. Therefore, some rapid and easy methods are expected to develop to substitute the traditional plate count. The speciation in the solution phase, ion effect and rhizospheric effect of heavy metal on the toxicity to soil microorganisms and its mediated processes need extent studies and discussion. Finally, the microbial indicator system of assessing heavy metal toxicity to soil microorganisms and its mediated processes need to be established.
The latest version of the Environmental Symptoms Questionnaire (ESQ-III) contains 67 symptoms designed to allow researchers to evaluate a broad range of environmental stresses. We have developed an interactive computer software package that administers and monitors the ESQ-III. This package, written in a format maximizing clarity, provides consistency of administration from one test or day to another, checks for response inconsistencies, maintains subject motivation, provides feedback to the subject and allows an investigator to quickly inspect raw and computed results. Further, because there is no interaction between investigators and subjects, no experimenter bias can be introduced. This package can be adapted to almost any computer system having a CRT and at least one disc drive.
The Sørfjord (Western Norway) has a long history of industry and pollution, and has been monitored for several decades. The environmental monitoring has comprised analyses of different contaminants in sea water, mussel, fish, seaweed and sediments. Measurements of polychlorinated biphenyls (PCBs) in blue mussels (Mytilus edulis) some 17 years ago indicated a local source. In 2001 severe concentrations were measured in blue mussels and further investigations disclosed the primary source of PCBs in the Sørfjord. In 2002, extreme PCB-concentrations were found in cod (Gadus morhua) from the same area. However, no induction of EROD activity was detected, indicating the limitations of this assay as marker for PCB contamination. A future scientific challenge will be to understand the specific mechanisms and effects of such PCB accumulation in fish.
Tissue doses of cancer initiators/mutagens are suitably monitored through hemoglobin adducts formed in vivo, but the use of this method has been hampered by a lack of sufficiently simple and fast procedures. It was previously observed that when the N-terminal amino acid in hemoglobin, valine, is alkylated it is cleaved off by the Edman sequencing reagent, phenyl isothiocyanate, in the neutral-alkaline coupling medium, as opposed to the acidic medium required by normal amino acids. Based on this principle, conditions for a functioning procedure for gas chromatography/mass spectrometry (GC/MS) determination of N-terminal alkylvalines in hemoglobin were worked out. Derivatizing the protein in formamide solution with pentafluorophenyl isothiocyanate, using a 2H-alkylated protein as internal standard, and applying on-column injection during analysis, permit reproducible determination of hydroxyethylvaline and other adducts down into the dose range where cancer risks may be considered acceptably low.
The literature on metallothioneins (MT) and metallothionein-like proteins (MTLP) in aquatic invertebrates is large and increasing, and yet inconsistencies and confusion remain, not least over the physiological role of MT and their use as biomarkers in environmental monitoring programmes. We have collated published information on MT in three important groups of aquatic invertebrates-the molluscs, crustaceans and annelid worms, and attempted to seek explanations for some of the apparent inconsistencies present in the dataset. MTs can be induced by the essential metals Cu and Zn and the non-essential metals Cd, Ag and Hg in both vertebrates and invertebrates, but their induction is variable. Such variation is intraspecific and interspecific, and is down to a variety of reasons environmental and physiological explored here. Against this background of variability MTs do appear to play roles both in the routine metabolic handling of essential Cu and Zn, but also in the detoxification of excess amounts intracellularly of these metals and of non-essential Cd, Ag and Hg. Different isoforms of MT probably play different physiological roles, and the dependence on MT in detoxification processes varies environmentally and between zoological groups. MTs can be used as biomarkers if used wisely in well-designed environmental monitoring programmes.
Many hazardous chemicals have polluted the environment of the earth. Among them, organochlorine compounds and heavy metals have dispersed worldwide. I reviewed the results of cooperative research based on specimens shared with colleagues at Ehime University, Japan: (1) bioaccumulation of organochlorine compounds (DDT, PCB, HHC, etc.) and heavy metals (Hg, Cd, Pb, etc.) from sea water to marine mammals through the food chain, (2) placental transfer of contaminants, (3) transfer of contaminants through lactation, (4) biological impacts of contaminants to marine mammals, and (5) the global movement of contaminants. This work was based on about 1200 specimens of marine mammals obtained from scientific research over 17 years during 1976-1992. Soft tissues were banked at -20 degrees C at Ehime University while related materials and information were deposited in the National Science Museum, Tokyo. These and other materials should be preserved in good condition in an international specimen bank for future global environmental monitoring studies, the examination of hazardous chemicals which are currently unknown, the reexamination of the same samples in future using more advanced equipment by different scientists, and the reaction to unknown environmental questions, etc. The need for the establishment of an International Environmental Specimen Bank for marine mammals and other marine organisms are recommended.
Parasites are attracting increasing interest from parasite ecologists as potential indicators of environmental quality because of the variety of ways in which they respond to anthropogenic pollution. However, until recently, little was known about the accumulation of toxins within parasites. Certain parasites, particularly intestinal acanthocephalans and cestodes of fish, can accumulate heavy metals at concentrations that are orders of magnitude higher than those in the host tissues or the environment. In this review, Bernd Sures, Roy Siddall and Horst Taraschewski discuss the recently described phenomenon of conspicuous metal accumulation by parasites and how this might be applied to environmental monitoring. They also suggest how environmental science and parasitology might profit from each other in the near future.
These guidelines mainly deal with prevention of carcinogenic effects following occupational exposure to polycyclic aromatic hydrocarbons (PAH). After some toxicological remarks, the guidelines define a possible method to demonstrate and evaluate occupational exposure to PAH. In particular, it is illustrated the strategy of environmental monitoring and indicated which PAH should be measured, with suggestion about the most appropriate analytical techniques. As regards biological monitoring, the 1-OH-pyreneseems to be currently the most useful indicator since it reflects the recent and global exposure to PAH. The guidelines also give elements to interpret monitoring data, taking into account environmental and biological reference and limit values suggested by some authors, Associations, or current regulations. The most important health effects are carcinogenic and excess risks have been described mainly for lung, bladder and skin cancer in some PAH exposed workers. The studies on cytogenetic effects showed contradictory results. On the basis of such information and current regulations, the guidelines show how to perform health surveillance in preventive and periodical examinations and how to proceed for the information and formation of exposed workers. It is not advisable, on the basis of the current scientific data, to screen asymptomatic PAH exposed workers for early diagnosis of lung or bladder cancer, nor it is opportune the use of tumor markers for health surveillance nor is genetic screening applicable for individual susceptibility evaluation outside research programs.
Although formaldehyde has recently been classified by the IARC as "carcinogenic in humans" (class 1), it is still widely used in pathology departments for the fixing and conservation of biological tissues. Its use therefore raises the question of occupational exposure. The present paper reports the results of an environmental monitoring campaign to evaluate pollution by formaldehyde in various areas of three pathology departments. Chemi-adsorbent cartridges able to adsorb airborne formaldehyde were used to detect the substance. Quantitative determination of the formaldehyde was carried out by means of liquid chromatography (HPLC). The concentrations of airborne formaldehyde in the areas monitored were fairly modest, being below the limits of indoor concentration proposed by the OSHA. In one of the three departments, however these limits were exceeded in 40% of the samples taken in the room used for the storage of containers. As yet, in spite of the recent class 1 classification by the IARC, no provisions have been made to ban the use of formaldehyde. It is therefore essential to draw up environmental monitoring programmes in order to evaluate occupational exposure and to assess the efficacy of any preventive measures adopted.
Luciferase-based biosensors are becoming increasingly used for environmental monitoring. A transcriptional fusion of the Vibrio harveyi luxAB genes (encoding bacterial luciferase) to the fliC gene of Escherichia coli was constructed and luminescence shown to be induced (in liquid media) in the presence of 1-10 micrograms/ml aluminum, but not copper, iron or nickel. Moreover, luminescence is markedly increased at pH 5.5, where aluminum is more soluble than at pH 7.0. However, aluminum also stimulated luciferase activity when the luxAB genes were located in the xyl operon. This suggests that aluminum stimulates luciferase enzyme activity in vivo. These results are specific to E. coli, as no such aluminum stimulation was observed in the luminescent bacterium V. harveyi. These results have important implications in the generalized use of these clones for environmental monitoring, where aluminum can be present at elevated concentrations.
Liquid chromatography with time-of-flight mass spectrometry (TOF-MS) and quadrupole-time-of-flight (Q-TOF) mass spectrometry/mass spectrometry (MS/MS) were used for the accurate mass analysis of sulfadimethoxine in pond water of a fish hatchery. Sulfadimethoxine is the most important sulfa antimicrobial used in aquaculture to treat bacterial disease in a wide variety of fish. Because correct identification is essential to environmental monitoring of antimicrobial pharmaceuticals, accurate mass analyses (TOF and Q-TOF-MS/MS) were compared to nominal mass measurement (quadrupole ion trap). It was known that all six members of the sulfa antimicrobial family gave a common 6-sulfanilamido ion at a nominal mass of m/z 156; thus, this ion was the focus of TOF confirmation (exact mass 156.0119 u) along with the protonated molecule (exact mass 311.0814 u). In the process of accurate mass confirmation of the 156 m/z fragment ion, a second isobaric ion (exact mass m/z 156.0773), was discovered at the same nominal mass, which was not differentiated by quadrupole ion trap. The structure was assigned as 2-4-dimethoxypyridine and is exactly the other protonated half of the sulfadimethoxine molecule. This discovery led to the subsequent use of Q-TOF-MS/MS and high-resolution identification of five other important ion fragments for the identification of sulfadimethoxine in pond water at environmental concentrations. The caveats of using low-resolution mass spectrometry without MS/MS for environmental monitoring are discussed in the light of high profile monitoring of sulfa antimicrobial pharmaceuticals in the aquatic environment.
Workers at a toluene-diisocyanate manufacturing plant were studied longitudinally to determine the effects of the chemical on their health. Studies included health questionnaire, pulmonary function, environmental monitoring, and immunologic testing. Workers reporting increased lower respiratory symptoms were from the nonsmoker group. Environmental monitoring showed frequent excursions of toluene-diisocyanate concentrations above the threshold limiting value. There was poor correlation between area and personal exposure levels. No exposure-related decline of pulmonary function was demonstrable. Immunologic studies showed development of a positive skin test to a toluene-diisocyanate-human serum albumin conjugate by some persons and an increasing incidence of toluene-diisocyanate-specific IgE antibodies as measured by a radioallergosorbent test. Toluene-diisocyanate did not induce histamine release from leukocytes in vitro but did diminish the in vitro stimulation of cyclic adenosine monophosphate by isoproterenol. Most of the clinically sensitive persons demonstrated adverse bronchial response when challenged by inhalation of toluene-diisocyanate. This response was dose dependent in some persons. When challenged with Mecholyl, clinically sensitive persons showed greater reactivity of airways than nonsensitive persons.