Impact Factor 2.483 | CiteScore 2
More on impact ›

Perspective ARTICLE

Front. Public Health, 12 November 2020 | https://doi.org/10.3389/fpubh.2020.582114

Human Biomonitoring in the Oil Shale Industry Area in Estonia—Overview of Earlier Programmes and Future Perspectives

Hans Orru1,2*, Anu Viitak3, Koit Herodes4, Triin Veber2 and Märten Lukk5
  • 1Department of Public Health and Clinical Medicine, Umeå University, Umeå, Sweden
  • 2Institute of Family Medicine and Public Health, University of Tartu, Tartu, Estonia
  • 3Department of Chemistry, Tallinn University of Technology, Tallinn, Estonia
  • 4Institute of Chemistry, University of Tartu, Tartu, Estonia
  • 5Estonian Health Board, Tallinn, Estonia

Ida-Viru County, in Eastern Estonia, features industrially contaminated sites–where oil shale has been mined and used for electricity generation, and shale oil extraction. Higher prevalence of respiratory and cardiovascular disease has been found in the region due to high quantities of air pollution. Within the framework of “Studies of the health impact of the oil shale sector—SOHOS,” this analysis aimed to map earlier human biomonitoring (HBM) studies and identify the suitable biomarkers for upcoming HBM in Estonia. Altogether, three studies have been conducted among residents: first, among adults in the 1980's; second, among children in the 1990's; and third, among employees, with a focus on workers and miners in the oil shale chemistry industry in the late 1990's and 2000's. In some of those studies, increased levels of biomarkers in blood and urine (heavy metals, 1-OHP) have appeared; nevertheless, in last 20 years, there has been no population-wide HBM in Estonia. According to air pollution monitoring and emission analysis, the pollutants of concern are benzene, PM10, PM2.5, and PAHs. In general, there is a decreasing trend in air pollutant levels, with the exception of a slight increase in 2018. One of the aims of HBM is to be analyzed if this trend can be identified in HBM, using similar biomarkers as applied earlier. The future perspective HBM could be divided into two Tiers. Tier 1 should focus on exposure biomarkers as heavy metals, PAH, and BTEX metabolites and Tier 2, in later stage, on effect biomarkers as Ox LDL, TBARS, etc.

Introduction

In Estonia, mining, and use of mineral resource oil shale for generating electricity generation and producing shale oil, is concentrated in Ida-Viru County– a large-scale industrial area in Eastern-Estonia. Oil shale is a fine-grained sedimentary rock containing organic matter, in the form of kerogen, which yields substantial amounts of oil and combustible gas. Oil shale industry activities have led to various environmental problems in the region, the most important of which is ambient air pollution. Frequently, those industry affected areas are called industrially contaminated sites (1), defined as “areas hosting or having hosted human activities which have produced or might produce environmental contamination of soil, surface or groundwater, air, food-chain, resulting or being able to result in human health impacts” (2).

Ambient air quality affects health, as toxic substances entering the respiratory tract can also reach other organs through the bloodstream, and cause various health problems and diseases (3). Health effects, related to the oil shale sector, have been studied in Estonia; studies suggest poorer health indicators, including increased respiratory and cardiovascular disease prevalence and a decrease in life expectancy (4). In addition, children living in the area have a higher risk of developing asthma (5, 6). Also a recent study has found the lung cancer age-standardized incidence rate being higher in Ida-Viru County compared to Estonia overall (7). One of the weaknesses in epidemiological studies has been poor exposure data, as discussed by Orru et al. (4, 6). We believe the implementation of human biomonitoring (HBM), would help to specify data on exposures in the population and advantage to refine the results.

Within the framework of “Studies of the health impact of the oil shale sector—SOHOS,” the current analysis aims to map the earlier HBM studies in the oil shale sector area, as well as elsewhere in Estonia, and identify the suitable biomarkers with an appropriate analysis methodology for the upcoming HBM program in Estonia.

Human Biomonitoring

The Human Biomonitoring Methodology

HBM is a methodology for assessing human exposure to natural and man-made compounds from living or working environments. Typically, specific substances or their degradation products, called metabolites, are measured in blood, urine, breast milk, and other body fluids or human tissues. The most commonly used and preferred biological matrix for HBM is blood, as it is in contact with organs and tissues where many chemicals are deposited (8, 9). However, there is a growing interest in non-invasive biomarkers, e.g., urine, that allow more routine sampling in human studies and reduce the number of blood sample refusers (9). Accordingly, previous studies of the health effects of the oil shale sector have used fractional exhaled nitric oxide (FeNO), which is a biomarker of airway inflammation (5, 6).

Compared to environmental monitoring, HBM has several advantages. For example, biological samples can characterize repeated exposure and the interaction of different exposures. HBM directly describes contaminants that have entered the body from all routes of exposure—inhalation, dermal absorption, and ingestion– and reflects individual differences due to different exposure levels, metabolism, and excretion rates. HBM data also refers to human physiological variations such as bioavailability, bioaccumulation, and persistence, which may increase the levels of some environmental chemicals (e.g., persistent organic pollutants) (911). Nevertheless, different matrixes (blood, urine, hair, breast milk, etc.) and different chemical physicochemical characteristics might characterize different exposures. If chemical substances, or their metabolites, are released rapidly from the human organism, repeated sampling at the individual level– to indicate a long-term exposure pattern– is needed (12).

The generally accepted classification of biomarkers divides them into two main categories: (1) exposure biomarkers and (2) effect biomarkers. Exposure biomarkers detect and measure chemical residues, or metabolites, in tissues or body fluids. It has been found that the advantage of utilizing exposure biomarkers is the so-called integrated measurement exposure, which is especially important in the case of substances with large differences in absorption depending on the time and location of exposure (9).

Effect biomarkers measure the processes that are considered to be “early events” associated with disease-related changes (13). An important group of effect biomarkers is genotoxicity biomarkers in workers or, to a lesser extent, in the population exposed to mutagens or genotoxic carcinogens. Many tests are used for the detection of DNA damage, such as micronucleus counting, Comet Assays (single cell gel electrophoresis), chromosomal aberrations, DNA adducts, etc (14).

However, effect biomarkers have been found to be effective only when people exposed to high levels of contaminants (e.g., working with mutagenic agents), and they are difficult to use to differentiate the effects of individuals. Toxicological studies have shown that individuals' responses to chemical exposure can often vary significantly (15). Ladeira and Viegas (14) consider that such differences between individuals may be genetically mediated or caused by some environmental stressor, disease process, or other epigenetic factor. Thus, effect biomarkers are currently recommended to be used as group indicators—they are sensitive, but not contaminant-specific and often difficult to interpret. Effect biomarkers have been used in earlier studies among oil shale sector workers (see chapter HBM Among Employees in the Oil Shale Sector for details).

National HBM Programs and HBM4EU Network

Many countries have established national HBM programs. The main objectives of these programs are to develop and validate biomarkers based on certain exposures and to predict the risk of disease for both populations and/or, under certain conditions, individuals (16). HBM can also identify spatial and temporal trends in human exposure as well as provide information on risk assessment. On the basis of risk assessments, decision-makers can be informed about chemical risks and policy measures can be initiated in order to protect population with the special focus on susceptible groups such as children and pregnant women (9, 11, 17). Successful examples of the impact of HBM include the banning of lead in petrol, avoiding mercury-containing amalgam teeth fillings, restricting the use of phthalates in plastics, and several other initiatives (18).

Within the Horizon2020 European HBM project HBM4EU has been established. It is now a joint project of 30 countries (Estonia joined in 2020), the European Environment Agency, and the European Commission for the period of 2017–2021 (19). The aim of this initiative is to promote and harmonize HBM activities in Europe, with the special focus to develop European HBM indicators (20). The harmonization of biomarkers collection and analysis– as well as the selection of which biomarkers to use– should make studies more comparable and give valuable reference material. Besides this, several other tools, such as questionnaires, have been developed which can be used in further HBM studies, i.e., in an Estonian HBM program that includes oil shale area (19).

Air Quality in Oil Shale Industry Area

Previous studies have shown that the most important oil shale sector pollutants– that cause toxic and allergic reactions– are benzene, formaldehyde, phenol, particulate matter (PM10), fine particles (PM2.5), and polycyclic aromatic hydrocarbons (PAHs), including benzo(a)pyrene (B(a)P) (46). In Ida-Viru County, the air quality has been monitored in the cities of Kohtla-Järve, Narva, and Sillamäe, and in the Sinimäe region (Figure 1). In general, the air quality currently is said to be “good,” with few exceedances of pollutants' limit values in recent years (21, 22). However, several studies have indicated that the health effects of PM10 and PM2.5 also occur at concentrations below the set limit values (3), so health risks associated with air pollution still remain (46).

FIGURE 1
www.frontiersin.org

Figure 1. Annual average concentrations of benzene, particulate matter (PM10), fine particles (PM2.5) and benzo(a)pyrene (BaP) in monitoring stations in Ida-Viru County.

If we look at the long-term trends of pollutant concentrations, a slight decrease can be seen in the case of benzene in Narva, while in Kohtla-Järve the concentration has remained the same and in Sillamäe fluctuated from year to year (Figure 1). In the case of PM10 and PM2.5, the concentrations have decreased somewhat over time, but spiked in 2018 (Figure 1). Concentrations of B(a)P have been on a slight upward trend in 2011–2014, then decreased sharply in 2015, and then started to increase again (Figure 1). In the analysis of concentrations of heavy metals and PAHs, bound to PM2.5, we noted arsenic and cadmium remain at the same level in 2018–2019, whereas lead and nickel increased in 2018 in Narva and Kohtla-Järve, while both decreased again in 2019.

Earlier HBM Studies in Estonia

In our analysis, we conducted three larger HBM studies among residents and three among employees. The residents' studies were country-wide (incl. oil-shale area) with focus on adults and children; occupational studies focused on oil-shale sector employees.

HBM Among Residents

The largest HBM program took place in 1982–1985, where the content of heavy metals in the blood and hair of adults was studied in nine different regions in Estonia (Table 1). The study included residents aged 20–60 who had lived in the area for at least 5 years and were born, or lived, in Estonia for at least 20 years (23). In addition, later the data of residents from Maardu and Kostivere was analyzed (24).

TABLE 1
www.frontiersin.org

Table 1. Average content of heavy metals in blood (μg/100 ml) and hair (μg/g) [based on (2326)].

The other two surveys were conducted among children in 1989–1990 and 1991–1994. In the first study (25), an increase in the concentration of some microelements in blood of oil shale region children was found according to the contamination of the external environment. The blood lead levels found in the children from Kohtla-Järve, Narva, and Sillamäe were on average three times higher than in Tartu (reference area). The cadmium concentration was 1.6 times higher in Kohtla-Järve compared to Tartu. The lead and cadmium levels in the blood of children from Kohtla-Järve were significantly higher compared to children from other two studied cities in Ida-Viru County. Compared to Tartu, the blood heavy metal concentrations were higher in all three Ida-Viru County cities. The second study (26) showed higher levels of lead and cadmium in children's hair in North-Eastern Estonia and higher levels of mercury in Western Estonia (in the hair of island and coastal residents). The higher levels of mercury are most likely related to the consumption of fish caught in the Baltic Sea. In that study, the values were also compared to limit values at that time. The lead values in blood were exceeded allowable limit of that time (27) in almost all regions, whereas cadmium levels were exceeded only in Kohtla-Järve and mercury levels in Western-Estonia and Lahemaa (affected by cement factory pollution).

HBM Among Employees in the Oil Shale Sector

The occupational studies have focused on miners and coke oven, and benzene plant workers. Due to weak ventilation systems and diesel-powered machinery, miners had a significantly higher exposure to benzene than oil shale sector's surface workers. In 2000, the concentration of benzene in the oil shale mine was 190 μg/m3, while in the urban air of Kohtla-Järve the concentration of benzene was 29 μg/m3 (28). Furthermore, mine workers are exposed to elevated levels of PM2.5 and PAHs, which has resulted in 7.5 times higher levels of 1-nitropyrene (1-OHP) compared to ground workers (29, 30).

Of these studies, the first HBM looked at the exposure of coke oven workers to PAHs (31, 32). The workers were highly exposed, as the average amount of B(a)P in the air inhaled by workers was 5.7 μg/m3 (32). The study also measured the urinary concentrations of 1-OHP and white blood cell DNA adducts. Though 1-OHP levels correlated with the number of DNA adducts, coke oven workers did not differ significantly compared to the controls from nearby Iisaku village (33). The subsequent analysis found that genotype might have played an important role regarding both biomarkers (1-OHP and DNA adducts), as evidenced by significant differences in number of adducts by genotypes among coke oven workers (34).

The second study compared benzene plant and coke oven workers. Higher benzene concentrations were observed at the benzene plant, which was confirmed with personal monitoring of benzene in the exhaled air (35). The same study also found higher levels of benzene in the workers' blood and elevated levels of the metabolite t,t-muconic acid (MA) in the workers' urine. The later analysis of effect biomarkers did not indicate an increase in the number of micronuclei in buccal cells (36) or increased cancer-specific ras (p21) proteins in plasma (37). A subsequent study of chromosomal aberrations did not show significant differences between the serum albumin levels of the controls from nearby countryside residents and the people working at the Kohtla-Järve chemical plant; nevertheless, the levels of S-phenylcysteine adducts were considered relatively high in both groups (38).

The third study compared 50 underground mine workers exposed to diesel exhaust with 50 above-ground oil shale sector workers. It was found that miners had a higher degree of DNA damage (Comet assay data) compared to the control group (39). They had also several changes in the levels of biomarkers such as S-phenylmercapturic acid (S-PMA) and MA (28) and increased 5-aminolevulinic acid (ALA) activity (40). Muzyka et al. (40, 41) have claimed that exposure to diesel exhaust has caused changes in heme synthesis, resulting in the accumulation of ALA and protoporphyrin in miners' lymphocytes.

Selection of Biomarkers for Estonian HBM

Based on the analysis of pollutants, emission and monitoring, the pollutants characterizing the environmental pollution of the oil shale sector would be PM10, and PM2.5 (as well as heavy metals bound to particles), benzene and PAHs such as B(a)P.

Elvidge et al. (42) have reviewed >20 biomarkers used as PM2.5 biomarkers. The most common of these are the markers of inflammation: C-reactive protein (CRP), interleukin 6 (IL-6), and fibrinogen. However, more than half of the studies using these markers have shown no effect. Less commonly used, but more robust biomarkers have been oxidized low-density lipoprotein (ox LDL), lipoprotein receptor-1, TBARS, which characterize lipid hyperperoxidation, and malondialdehyde (MDA), a marker of oxidative stress. However, the limitation is that these biomarkers are also elevated with cardiovascular diseases, so they are not specific for the contamination. Even more robust biomarkers are heavy metals bound to particles (43). The update of the temporal and spatial trends, should be encompassed. This should certainly include heavy metals from the earlier HBM in Estonia (lead, cadmium, mercury, copper, zinc), as well as arsenic and chromium.

In the case of benzene, we recommend to determine it as the BTEX (benzene, toluene, ethylbenzene, and xylene) metabolite complex, which has been used as a biomarker found in urine in petroleum distribution facilities (44). To assess exposure to PAH, it is valuable to use 1-OHP, which is the most commonly used PAHs biomarker in both work and living environments (45). It has been earlier used among oil shale sector workers (32).

Chemical Analysis of Biomarkers

If the earlier studies mainly used different (AAS) techniques for heavy metal detection in blood and plasma, recently the Inductively Coupled Plasma Mass Spectrometry (ICP-MS) and Inductively Coupled Plasma—Optical Emission Spectrometry (ICP-OES) have been preferred due to much lower detection limits (46). ICP-MS and ICP-OES have been applied in several studies of populations living near industrially contaminated sites (4749).

For 1-OHP determination HPLC with fluorescence detection (50), gas chromatography with mass spectrometry (GC/MS) (51), and more recently liquid chromatography tandem mass spectrometry (LC-MS/MS) (52) have been applied using isotopically labeled standard for 1-OHP detection (53). Another important metabolite would be 1-hydroxypyrene glucuronide (1-OHP-G), which allows better determination of low exposure to PAH (54). Due to low 1-OHP-G levels, more accurate ultra-high performance liquid chromatography–tandem mass spectrometry (UHPLC-MS/MS) should be applied (55).

For the determination of BTEX, several new studies have used headspace solid-phase microextraction (HS-SPME) coupled with gas chromatography-mass spectrometry (GC-MS) (56, 57). It is a sensitive methodology that can be used to determine low levels biomarkers. This is especially crucial among those less exposed, such as children (58).

Discussion and Conclusions

HBM is valuable tool in indicating exposures as well as early effects in a large number of studies (9, 12). The information on human exposure can then be linked to data on sources and epidemiological surveys in order to inform research on exposure-response relationships in humans (19).

However, there are also several limitations in the interpretation of HBM results. One of the main limitations is that in many cases it may be difficult to confirm from which source the measured effects have been induced. This can be refined by using HBM and environmental monitoring data in parallel, where we can ultimately identify the sources of the pollutants.

Other major limitations are the confounding factors that could induce similar effects, e.g., in case possible biomarkers of PM2.5 health effects, existing cardiovascular disease might have a similar effect (42). One of the possibilities to collect data on confounding factors is through questionnaires.

Often, HBM is very costly and resource intensive. Tan et al. (59) have suggested that an HBM program could be divided into different tiers. We propose that Tier 1 could focus on exposure biomarkers as heavy metals, PAH, and BTEX metabolites. Tier 2, in a later stage, could focus on effect biomarkers, e.g., particle exposure biomarkers. Collecting blood samples in Tier 1 for Tier 2 could be beneficial.

Applying the described approached and taking into account the limitations, would warrant the solid ground for HBM in Estonia. Though, besides the exposed population, e.g., people living near oil shale industry or industry workers, the data from reference areas is needed in order to get good basis for spatial comparison. We support including the areas that have been analyzed earlier: Tallinn as capital area, Southern-Estonia as reference area and Western-Estonian coastal areas with somewhat different dietary habits like higher consumption of Baltic-Sea fish.

In the current analysis we could identify several HBM studies in the oil shale industry area in Estonia; however, all of those have been made in 1980, 1990, and 2000's. During the last two decades there has been change in environmental quality, so the update of HBM data is essential. As Estonia is recently joined HBM4EU network, this information would also be important from that perspective.

Data Availability Statement

Publicly available datasets were analyzed in this study. This data can be found here: Data is available in the reports referred in the article.

Ethics Statement

Ethical approval was not provided for this study on human participants because the current study only reviews earlier studies. The original studies had been approved by local ethics committees. Written informed consent to participate in this study was provided by the participants' legal guardian/next of kin.

Author Contributions

HO and ML contributed conception of the study. HO and TV compiled the database of earlier studies. HO and AV contributed interpretation of the study findings. AV and KH reviewed the methodology used for chemical analysis in human biomonitoring. All authors contributed to writing the manuscript.

Funding

The study was supported by the Estonian Environmental Research Center with the project: Implementation of biomonitoring among population exposed to the oil shale sector (workers and residents), preliminary study—Identification of biomarkers. HO's work was supported by the Estonian Ministry of Education and Research, grant IUT34-17. The open access publication was supported by Umea University. This initiative has also been part of the EU-Cost Action, CA 15129 (DiMoPEx). The Cost action was supported by the EU Framework Program Horizon 2020.

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

We would like to express the gratitude to the family of Prof. R. Silla for bringing his original, largely unpublished, materials to Estonian Health Board.

References

1. Martuzzi M, Pasetto R, Martin-Olmedo P. Industrially contaminated sites and health. J Environ Public Health. (2014) 2014:198574. doi: 10.1155/2014/198574

PubMed Abstract | CrossRef Full Text | Google Scholar

2. WHO. Contaminated Sites and Health. Copenhagen: WHO Regional Office for Europe (2012).

Google Scholar

3. WHO. Review of Evidence on Health Aspects of Air Pollution-REVIHAAP Project: Technical Report. Copenhagen: WHO Regional Office for Europe (2013).

PubMed Abstract | Google Scholar

4. Orru H, Idavain J, Pindus M, Orru K, Kesanurm K, Lang A, et al. Residents' self-reported health effects and annoyance in relation to air pollution exposure in an industrial area in Eastern-Estonia. Int J Environ Res Public Health. (2018) 15:252. doi: 10.3390/ijerph15020252

PubMed Abstract | CrossRef Full Text | Google Scholar

5. Idavain J, Julge K, Rebane T, Lang A, Orru H. Respiratory symptoms, asthma and levels of fractional exhaled nitric oxide in schoolchildren in the industrial areas of Estonia. Sci Total Environ. (2019) 650(Pt 1):65–72. doi: 10.1016/j.scitotenv.2018.08.391

PubMed Abstract | CrossRef Full Text | Google Scholar

6. Orru H, Triin V, Julge K, Aidla K, Albrecht L, Idavain J, et al. Metoodika Väljatöötamine ja Rakendamine Välisõhuseisundi Ning Lapseea Astma ja Teiste Allergiahaiguste Vaheliste Seoste Leidmiseks Põlevkivitööstusest Mõjutatud Aladel–METRAK. Tartu; Tallinn: Tartu Ülikool, Eesti Keskkonnauuringute Keskus, Terviseamet (2019).

7. Idavain J, Lang K, Tomasova J, Lang A, Orru H. Cancer incidence trends in the oil shale industrial region in Estonia. Int J Environ Res Public Health. (2020) 17:3833. doi: 10.3390/ijerph17113833

PubMed Abstract | CrossRef Full Text | Google Scholar

8. Barrett JC, Vainio H, Peakall D, Goldstein BD. 12th meeting of the scientific group on methodologies for the safety evaluation of chemicals: susceptibility to environmental hazards. Environ Health Perspect. (1997) 105(Suppl. 4):699–737. doi: 10.1289/ehp.97105s4699

PubMed Abstract | CrossRef Full Text | Google Scholar

9. WHO. Human Biomonitoring: Facts and Figures. Copenhagen: WHO Regional Office for Europe (2005).

Google Scholar

10. Sexton K, Needham L, Pirkle J. Human biomonitoring of environmental chemicals: measuring chemicals in human tissues is the “gold standard” for assessing people's exposure to pollution. Am Sci. (2004) 92:38–45. doi: 10.1511/2004.45.921

CrossRef Full Text | Google Scholar

11. Angerer J, Ewers U, Wilhelm M. Human biomonitoring: state of the art. Int J Hyg Environ Health. (2007) 210:201–28. doi: 10.1016/j.ijheh.2007.01.024

PubMed Abstract | CrossRef Full Text | Google Scholar

12. WHO. Biomonitoring-Based Indicators of Exposure to Chemical Pollutants. Copenhagen: WHO Regional Office for Europe (2012).

PubMed Abstract | Google Scholar

13. Bonassi S, Coskun E, Ceppi M, Lando C, Bolognesi C, Burgaz S, et al. The HUman MicroNucleus project on eXfoLiated buccal cells (HUMN(XL)): the role of life-style, host factors, occupational exposures, health status, assay protocol. Mutat Res. (2011) 728:88–97. doi: 10.1016/j.mrrev.2011.06.005

PubMed Abstract | CrossRef Full Text | Google Scholar

14. Ladeira C, Viegas S. Human biomonitoring–an overview on biomarkers and their application in occupational and environmental health. Biomonitoring. (2016) 3:15–24. doi: 10.1515/bimo-2016-0003

CrossRef Full Text

15. Dorne JL, Amzal B, Bois F, Crépet A, Tressou J, Verger P. Population effects and variability. Methods Mol Biol. (2012) 929:521–81. doi: 10.1007/978-1-62703-050-2_20

PubMed Abstract | CrossRef Full Text | Google Scholar

16. Watson WP, Mutti A. Role of biomarkers in monitoring exposures to chemicals: present position, future prospects. Biomarkers. (2004) 9:211–42. doi: 10.1080/13547500400015642

PubMed Abstract | CrossRef Full Text | Google Scholar

17. Den Hond E, Govarts E, Willems H, Smolders R, Casteleyn L, Kolossa-Gehring M, et al. First steps toward harmonized human biomonitoring in Europe: demonstration project to perform human biomonitoring on a European scale. Environ Health Perspect. (2015) 123:255–63. doi: 10.1289/ehp.1408616

PubMed Abstract | CrossRef Full Text | Google Scholar

18. Manno M, Viau C, Cocker J, Colosio C, Lowry L, Mutti A, et al. Biomonitoring for occupational health risk assessment (BOHRA). Toxicol Lett. (2010) 192:3–16. doi: 10.1016/j.toxlet.2009.05.001

PubMed Abstract | CrossRef Full Text | Google Scholar

19. HBM4EU. Available online at: https://www.hbm4eu.eu/about-hbm4eu/ (accessed July 7, 2020).

Google Scholar

20. Buekers J, David M, Koppen G, Bessems J, Scheringer M, Lebret E, et al. Development of policy relevant human biomonitoring indicators for chemical exposure in the European population. Int J Environ Res Public Health. (2018) 15:2085. doi: 10.3390/ijerph15102085

PubMed Abstract | CrossRef Full Text | Google Scholar

21. Saare K, Kabral N, Maasikmets M, Teinemaa E. Välisõhu Kvaliteedi Seire 2018. Tallinn: Eesti Keskkonnauuringute Keskus (2019).

22. Saare K, Kabral N, Maasikmets M, Teinemaa E. Välisõhu Kvaliteedi Seire 2019. Tallinn: Eesti Keskkonnauuringute Keskus (2020).

23. Viitak A. Изучение содержания некоторых металлов в крови и волосах у жителей Эстонско˘u CCP. University of Tartu (1987).

24. Viitak A, Kahn H, Vilkis A, Hödrejärv H. Pb ja Cd in the blood and hair of the inhabitants of Estonian insdutrial regions. In: Abstracts of the Republican IV Conference in Ecology, MArch 23-25, 1988. Tartu (1998).

25. Silla R. Laste Tervislikus Seisundis Toimunud Muutuste Hinnang, Mis on Seotud Väliskeskkonna Kahjulike Tegurite Mõjuga Sillamäel, KOHTLA-Järvel, Narvas ja Tartus ning Väliskeskkonna Kahjulike Faktorite Uurimine Nendes. Tallinn: EV TM Profülaktilise Meditsiini TU Instituut (1991).

26. Silla R, Teoste M, Ostrat A, Võžull D, Salijeva K, Haas L. Eesti Elanikkonna Tervise ja Elutingimuste Valikuline Uurimine. Tallinn: EV Sostsiaalministeerium Profülaktilise Meditsiini Instituut (1994).

27. Lazarev NV. Вредные вещества в промышленности. Справочник для химиков, инженеров и врачей. Изд. 7-е, пер. и доп. В трех томах.. Moscow: Химия (1977).

28. Sørensen M, Poole J, Autrup H, Muzyka V, Jensen A, Loft S, et al. Benzene exposure assessed by metabolite excretion in Estonian oil shale mineworkers: influence of glutathione s-transferase polymorphisms. Cancer Epidemiol Biomarkers Prev. (2004) 13(11 Pt 1):1729–35. Available online at: https://cebp.aacrjournals.org/content/13/11/1729.short

PubMed Abstract | Google Scholar

29. Scheepers PT, Coggon D, Knudsen LE, Anzion R, Autrup H, Bogovski S, et al. BIOMarkers for occupational diesel exhaust exposure monitoring (BIOMODEM)–a study in underground mining. Toxicol Lett. (2002) 134:305–17. doi: 10.1016/S0378-4274(02)00195-9

PubMed Abstract | CrossRef Full Text | Google Scholar

30. Scheepers PT, Micka V, Muzyka V, Anzion R, Dahmann D, Poole J, et al. Exposure to dust and particle-associated 1-nitropyrene of drivers of diesel-powered equipment in underground mining. Ann Occup Hyg. (2003) 47:379–88. doi: 10.1093/annhyg/meg036

PubMed Abstract | CrossRef Full Text | Google Scholar

31. Kuljukka T, Vaaranrinta R, Veidebaum T, Sorsa M, Peltonen K. Exposure to PAH compounds among cokery workers in the oil shale industry. Environ Health Perspect. (1996) 104(Suppl 3):539–41. doi: 10.1289/ehp.96104s3539

PubMed Abstract | CrossRef Full Text | Google Scholar

32. Kuljukka T, Vaaranrinta R, Mutanen P, Veidebaum T, Sorsa M, Kalliokoski P, et al. Assessment of occupational exposure to PAHs in an Estonian coke oven plant- correlation of total external exposure to internal dose measured as 1-hydroxypyrene concentration. Biomarkers. (1997) 2:87–94. doi: 10.1080/135475097231805

PubMed Abstract | CrossRef Full Text | Google Scholar

33. Kuljukka T, Savela K, Vaaranrinta R, Mutanen P, Veidebaum T, Sorsa M, et al. Low response in white blood cell DNA adducts among workers in a highly polluted cokery environment. J Occup Environ Med. (1998) 40:529–37. doi: 10.1097/00043764-199806000-00005

PubMed Abstract | CrossRef Full Text | Google Scholar

34. Kuljukka-Rabb T, Nylund L, Vaaranrinta R, Savela K, Mutanen P, Veidebaum T, et al. The effect of relevant genotypes on PAH exposure-related biomarkers. J Expo Anal Environ Epidemiol. (2002) 12:81–91. doi: 10.1038/sj.jea.7500204

PubMed Abstract | CrossRef Full Text | Google Scholar

35. Kivistö H, Pekari K, Peltonen K, Svinhufvud J, Veidebaum T, Sorsa M, et al. Biological monitoring of exposure to benzene in the production of benzene and in a cokery. Sci Total Environ. (1997) 199:49–63. doi: 10.1016/S0048-9697(97)05481-8

PubMed Abstract | CrossRef Full Text | Google Scholar

36. Surrallés J, Autio K, Nylund L, Järventaus H, Norppa H, Veidebaum T, et al. Molecular cytogenetic analysis of buccal cells and lymphocytes from benzene-exposed workers. Carcinogenesis. (1997) 18:817–23. doi: 10.1093/carcin/18.4.817

PubMed Abstract | CrossRef Full Text | Google Scholar

37. Anderson D, Hughes JA, Brinkworth MH, Cebulska-Wasilewska A, Nizankowska E, Graca B, et al. Examination of ras oncoproteins in human plasma from healthy controls and workers exposed to petroleum emissions, including benzene-related compounds. Mutat Res. (1999) 445:167–73. doi: 10.1016/S1383-5718(99)00123-0

PubMed Abstract | CrossRef Full Text | Google Scholar

38. Rynö M, Anttinen-Klemetti T, Vaaranrinta R, Veidebaum T, Farmer PB, Peltonen K. S-phenylcysteine adduct concentration in serum albumin of countryside residents and factory workers in Estonia. Toxicol Environ Chem. (2003) 85:243–52. doi: 10.1080/02772240410001665544

CrossRef Full Text | Google Scholar

39. Knudsen LE, Gaskell M, Martin EA, Poole J, Scheepers PT, Jensen A, et al. Genotoxic damage in mine workers exposed to diesel exhaust, and the effects of glutathione transferase genotypes. Mutat Res. (2005) 583:120–32. doi: 10.1016/j.mrgentox.2005.03.004

PubMed Abstract | CrossRef Full Text | Google Scholar

40. Muzyka V, Scheepers PTJ, Bogovski S, Lang I, Schmidt N, Ryazanov V, et al. Porphyrin metabolism in lymphocytes of miners exposed to diesel exhaust at oil shale mine. Sci Total Environ. (2004) 322:41–50. doi: 10.1016/S0048-9697(03)00404-2

PubMed Abstract | CrossRef Full Text | Google Scholar

41. Muzyka V, Bogovski S, Scheepers P, Volf J, Kusova J. Effects of occupational exposure to diesel exhaust on porphyrin metabolism in lymphocytes of workers employed at black coal and oil-shale mines. Am J Ind Med. (2003) 44:70–4. doi: 10.1002/ajim.10239

PubMed Abstract | CrossRef Full Text | Google Scholar

42. Elvidge T, Matthews IP, Gregory C, Hoogendoorn B. Feasibility of using biomarkers in blood serum as markers of effect following exposure of the lungs to particulate matter air pollution. J Environ Sci Health C Environ Carcinog Ecotoxicol Rev. (2013) 31:1–44. doi: 10.1080/10590501.2013.763575

PubMed Abstract | CrossRef Full Text | Google Scholar

43. Flora SJS. Chapter 29-Metals. In: Gupta RC, editor. Biomarkers in Toxicology. Boston: Academic Press (2014). p. 485–519. doi: 10.1016/B978-0-12-404630-6.00029-4

CrossRef Full Text

44. Heibati B, Godri Pollitt K, Charati J, Ducatman A, Shokrzade M, Karimi A, et al. Biomonitoring-based exposure assessment of benzene, toluene, ethylbenzene and xylene among workers at petroleum distribution facilities. Ecotoxicol Environ Saf. (2017) 149:19–25. doi: 10.1016/j.ecoenv.2017.10.070

PubMed Abstract | CrossRef Full Text | Google Scholar

45. Hansen AM, Mathiesen L, Pedersen M, Knudsen LE. Urinary 1-hydroxypyrene (1-HP) in environmental and occupational studies–a review. Int J Hyg Environ Health. (2008) 211:471–503. doi: 10.1016/j.ijheh.2007.09.012

PubMed Abstract | CrossRef Full Text | Google Scholar

46. Heitland P, Köster H. Applications of ICP-MS in human biomonitoring studies. In: Caroli S, Záray G, editors. Analytical Techniques for Clinical Chemistry. Hoboken, NJ: John Wiley & Sons, Inc (2012). p. 367–95. doi: 10.1002/9781118271858.ch13

CrossRef Full Text | Google Scholar

47. Coelho P, Costa S, Costa C, Silva S, Walter A, Ranville J, et al. Biomonitoring of several toxic metal(loid)s in different biological matrices from environmentally and occupationally exposed populations from Panasqueira mine area, Portugal. Environ Geochem Health. (2013) 36:255–69. doi: 10.1007/s10653-013-9562-7

PubMed Abstract | CrossRef Full Text | Google Scholar

48. Li J, Cen D, Huang D, Li X, Xu J, Fu S, et al. Detection and analysis of 12 heavy metals in blood and hair sample from a general population of Pearl River Delta Area. Cell Biochem Biophys. (2014) 70:1663–9. doi: 10.1007/s12013-014-0110-6

PubMed Abstract | CrossRef Full Text | Google Scholar

49. Queiroz TKL, Naka KS, Mendes LCDS, Costa BNS, Jesus IM, Câmara VM, et al. Human blood lead levels and the first evidence of environmental exposure to industrial pollutants in the Amazon. Int J Environ Res Public Health. (2019) 16:3047. doi: 10.3390/ijerph16173047

PubMed Abstract | CrossRef Full Text | Google Scholar

50. Wang Y, Zhang W, Dong Y, Fan R, Sheng G, Fu J. Quantification of several monohydroxylated metabolites of polycyclic aromatic hydrocarbons in urine by high-performance liquid chromatography with fluorescence detection. Anal Bioanal Chem. (2005) 383:804–9. doi: 10.1007/s00216-005-0066-x

PubMed Abstract | CrossRef Full Text | Google Scholar

51. Xu X, Zhang J, Zhang L, Liu W, Weisel CP. Selective detection of monohydroxy metabolites of polycyclic aromatic hydrocarbons in urine using liquid chromatography/triple quadrupole tandem mass spectrometry. Rapid Commun Mass Spectrom. (2004) 18:2299–308. doi: 10.1002/rcm.1625

PubMed Abstract | CrossRef Full Text | Google Scholar

52. Gill B, Mell A, Shanmuganathan M, Jobst K, Zhang X, Kinniburgh D, et al. Urinary hydroxypyrene determination for biomonitoring of firefighters deployed at the Fort McMurray wildfire: an inter-laboratory method comparison. Anal Bioanal Chem. (2019) 411:1397–407. doi: 10.1007/s00216-018-01569-1

PubMed Abstract | CrossRef Full Text | Google Scholar

53. Zhang X, Hou H, Xiong W, Hu Q. Development of a method to detect three monohydroxylated polycyclic aromatic hydrocarbons in human urine by liquid chromatographic tandem mass spectrometry. J Anal Methods Chem. (2015) 2015:514320. doi: 10.1155/2015/514320

PubMed Abstract | CrossRef Full Text | Google Scholar

54. Strickland P, Kang D. Urinary 1-hydroxypyrene and other PAH metabolites as biomarkers of exposure to environmental PAH in air particulate matter. Toxicol Lett. (1999) 108:191–9. doi: 10.1016/S0378-4274(99)00089-2

PubMed Abstract | CrossRef Full Text | Google Scholar

55. Li M, Wang Q, Zhu J, Li N, Zou X. A simple analytical method of determining 1-hydroxypyrene glucuronide in human urine by isotope dilution with ultra performance liquid chromatography-tandem mass spectrometry. Anal Bioanal Chem. (2017) 409:1513–8. doi: 10.1007/s00216-016-0083-y

PubMed Abstract | CrossRef Full Text | Google Scholar

56. Barros N, Carvalho M, Silva C, Fontes T, Prata JC, Sousa A, et al. Environmental and biological monitoring of benzene, toluene, ethylbenzene and xylene (BTEX) exposure in residents living near gas stations. J Toxicol Environ Health A. (2019) 82:550–63. doi: 10.1080/15287394.2019.1634380

PubMed Abstract | CrossRef Full Text | Google Scholar

57. Moradi M, Hopke P, Hadei M, Eslami A, Rastkari N, Naghdali Z, et al. Exposure to BTEX in beauty salons: biomonitoring, urinary excretion, clinical symptoms, and health risk assessments. Environ Monit Assess. (2019) 191:286. doi: 10.1007/s10661-019-7455-7

PubMed Abstract | CrossRef Full Text | Google Scholar

58. Antonucci A, Vitali M, Avino P, Manigrasso M, Protano C. Sensitive multiresidue method by HS-SPME/GC-MS for 10 volatile organic compounds in urine matrix: a new tool for biomonitoring studies on children. Anal Bioanal Chem. (2016) 408:5789–800. doi: 10.1007/s00216-016-9682-x

PubMed Abstract | CrossRef Full Text | Google Scholar

59. Tan C, Dary C, Chang D, Ulrich E, Van Emon J, Xue J, et al. Biomonitoring—An Exposure ScienceTool for Exposure and Risk Assessment. US Environmental Protection Agency (2013).

PubMed Abstract | Google Scholar

Keywords: industrially affected lands, heavy metal, air pollution, PAH, HBM

Citation: Orru H, Viitak A, Herodes K, Veber T and Lukk M (2020) Human Biomonitoring in the Oil Shale Industry Area in Estonia—Overview of Earlier Programmes and Future Perspectives. Front. Public Health 8:582114. doi: 10.3389/fpubh.2020.582114

Received: 10 July 2020; Accepted: 22 September 2020;
Published: 12 November 2020.

Edited by:

Radu Corneliu Duca, Laboratoire National de Santé (LNS), Luxembourg

Reviewed by:

Gulnihal Ozbay, Delaware State University, United States
Özlem Göksel, Ege University, Turkey

Copyright © 2020 Orru, Viitak, Herodes, Veber and Lukk. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Hans Orru, hans.orru@umu.se