Public health and landfill sites

Landfill management is a complex discipline, requiring very high levels of organisation, and considerable investment. Until the early 1990’s most Irish landfill sites were not managed to modern standards. Illegal landfill sites are, of course, usually not managed at all. Landfills are very active. The traditional idea of ‘put it in the ground and forget about it’ is entirely misleading. There is a lot of chemical and biological activity underground. This produces complex changes in the chemistry of the landfill, and of the emissions from the site. The main emissions of concern are landfill gases and contaminated water (which is known as leachate). Both of these emissions have complex and changing chemical compositions, and both depend critically on what has been put into the landfill. The gases spread mainly through the atmosphere, but also through the soil, while the leachate (the water) spreads through surface waters and the local groundwater. Essentially all unmanaged landfills will discharge large volumes of leachate into the local groundwater. In sites where the waste accepted has been properly regulated, and where no hazardous wastes are present, there is a lot known about the likely composition of this leachate and there is some knowledge of its likely biological and health effects. This is not the case for poorly regulated sites, where the composition of the waste accepted is unknown. It is possible to monitor the emissions from landfills, and to reduce some of the adverse health and environmental effects of these. These emissions, and hence the possible health effects, depend greatly on the content of the landfill, and on the details of the local geology and landscape. There is insufficient evidence to demonstrate a clear link between cancers and exposure to landfill, however, it is noted that there may be an association with adverse birth outcomes such as low birth weight and birth defects. It should be noted, however, that modern landfills, run in strict accordance with standard operation procedures, would have much less impact on the health of residents living in proximity to the site

Frequency of micronuclei and of other nuclear abnormalities in erythrocytes of the grey mullet from the Mondego, Douro and Ave estuaries—Portugal

Fish are bioindicators of water pollution, and an increased rate of their erythrocyte nuclear morphological abnormalities (ENMAs)—and particularly of erythrocyte micronuclei (EMN)—is used as a genotoxicity biomarker. Despite the potential value of ENMAs andMN, there is scarce information about fish captured in Iberian estuaries. This is the case of the Portuguese estuaries of the Mondego, Douro and Ave, suffering from different levels of environmental stress and where chemical surveys have been disclosing significant amounts of certain pollutants. So, the aim of this study was to evaluate genotoxicants impacts and infer about the exposure at those ecosystems, using the greymullet (Mugil cephalus) as bioindicator and considering the type and frequency of nuclear abnormalities of erythrocytes as proxies of genotoxicity. Sampling of mullets was done throughout the year in the important Mondego, Douro and Ave River estuaries (centre and north-western Portugal). The fish (total n=242) were caught in campaigns made in spring–summer and autumn– winter, using nets or fishing rods. The sampled mullets were comparable between locations in terms of the basic biometric parameters. Blood smears were stained with Diff-Quik to assess the frequencies of six types of ENMAs and MN (given per 1,000 erythrocytes). Some basic water physicochemical parameters were recorded to search for fluctuations matching the ENMAs. Overall, the most frequent nucleus abnormality was the polymorphic type, sequentially followed by the blebbed/ lobed/notched, segmented, kidney shaped, vacuolated,MNand binucleated. The total average frequency of the ENMAs ranged from 73‰in the Mondego to 108‰in the Ave. The polymorphic type was typically ≥50 % of the total ENMAs, averaging about 51‰, when considering all three estuaries. The most serious lesion—the MN—in fish from Mondego and Douro had a similar frequency (≈0.38‰), which was significantly lower than that in the Ave (0.75‰). No significant seasonal differences existed as to the MN rates and seasonal differences existed almost only in the Douro, with the higher values in AW. In general, the pattern of ENMAs frequencies was unrelated with the water physicochemical parameters. Considering the data for both the total ENMAs and for each specific abnormality, and bearing in mind that values of MN in fish erythrocytes >0.3‰ usually reflect pollution by genotoxicants, it is suggested that mullets were likely being chronically exposed to such compounds, even in the allegedly less polluted ecosystem (Mondego). Moreover, data supported the following pollution exposure gradient: Mondego<Douro<Ave. The scenario and inferences nicely agree with the published data from chemical monitoring.This work was partially supported by the European Regional Development Fund (ERDF) funds through the Competitiveness and Trade Expansion Program (COMPETE), and by National Funds provided by Fundação para a Ciência e a Tecnologia (FCT), via the research projects PTDC/MAR/70436/2006, PEst-C/MAR/LA0015/ 2011, PEst-C/MAR/LA0015/2013, and also by the PhD grant SFRH/BD/25746/2005

Challenges to water quality assessment in Europe – Is there scope for improvement of the current Water Framework Directive bioassessment scheme in rivers?

The EU Water Framework Directive (WFD) assessment scheme has been putting in force the evaluation of freshwater ecosystems in Europe, including a new paradigm of ecological status. After almost 20 years since the WFD implementation, it is imperative to evaluate the efficiency of its standard assessment scheme and to explore the possibility of learning how to improve its effectiveness. That is the spirit of this review, aiming (i) to explore the existing literature on the WFD bioassessment scheme for assessing freshwater ecosystem health, particularly in lotic ecosystems (where the WFD scheme is most consolidated); (ii) to document which paths are suggested by the scientific community to improve the efficiency of the bioassessment in tackling current challenges. In the specific arena of bioassessment, we first identify the major constraints to the WFD full implementation in rivers. Second, we analyse retrospective Ecological Risk Assessment (ERA) as an evaluation approach supporting management actions that could inspire improvements in the WFD bioassessment scheme. Third, we review the advances and debate on complementary metrics to improve WFD evaluation protocols and/or the feasibility of the evaluation outcome. Fourth, a conceptual scheme for an improved evaluation strategy is presented. Our proposal essentially merges the WFD bioassessment scheme with the ERA philosophy, proposing a tiered approach of increasing complexity and spatial resolution, where expert judgement is included surgically at all decision stages. This scheme requires true integration of chemical, ecological and ecotoxicological LoE for a quantitative estimation of risks, and provides a comprehensive framework that accommodates tools and perspectives already suggested by other authors. Besides providing a literature review on the strengths and weaknesses of the current WFD bioassessment scheme, we wish to open way for the scientific discussion towards an improved conceptual scheme for the evaluation of ecosystem health.CESAM - Centro de Estudos Ambientais e Marinhos, Universidade de Aveiro(UIDP/50017/2020 + UIDB/50017/2020

Environmental effects of offshore produced water discharges: A review focused on the Norwegian continental shelf

Produced water (PW), a large byproduct of offshore oil and gas extraction, is reinjected to formations or discharged to the sea after treatment. The discharges contain dispersed crude oil, polycyclic aromatic hydrocarbons (PAHs), alkylphenols (APs), metals, and many other constituents of environmental relevance. Risk-based regulation, greener offshore chemicals and improved cleaning systems have reduced environmental risks of PW discharges, but PW is still the largest operational source of oil pollution to the sea from the offshore petroleum industry. Monitoring surveys find detectable exposures in caged mussel and fish several km downstream from PW outfalls, but biomarkers indicate only mild acute effects in these sentinels. On the other hand, increased concentrations of DNA adducts are found repeatedly in benthic fish populations, especially in haddock. It is uncertain whether increased adducts could be a long-term effect of sediment contamination due to ongoing PW discharges, or earlier discharges of oil-containing drilling waste. Another concern is uncertainty regarding the possible effect of PW discharges in the sub-Arctic Southern Barents Sea. So far, research suggests that sub-arctic species are largely comparable to temperate species in their sensitivity to PW exposure. Larval deformities and cardiac toxicity in fish early life stages are among the biomarkers and adverse outcome pathways that currently receive much attention in PW effect research. Herein, we summarize the accumulated ecotoxicological knowledge of offshore PW discharges and highlight some key remaining knowledge needs.publishedVersio

Évaluation du 4,5-dihydrodiol-benzo[a]pyrène et du 7,8-dihydrodiol-benzo[a]pyrène en tant que biomarqueurs spécifiques alternatifs d’exposition au benzo[a]pyrène

Reconnu par le Centre international de recherche sur le cancer (CIRC) comme cancérigène chez l’être humain, le benzo[a]pyrène (BaP) est un des hydrocarbures aromatiques polycycliques (HAP) les plus étudiés. Souvent rencontrés dans de nombreux milieux de travail, les HAP sont un groupe de polluants omniprésents dans l’environnement, formé par des processus de combustion incomplets. Bien que le BaP présente un risque élevé pour la santé des travailleurs, il n’existe aucun biomarqueur spécifique au composé permettant le suivi et la surveillance d’exposition au BaP dans un lieu de travail. Le 3-hydroxybenzo[a]pyrène (3-OHBaP) est le métabolite du BaP le plus développé comme biomarqueur. Ce métabolite est principalement excrété dans les fèces, ainsi qu’une quantité infime dans l’urine, ce qui le rend difficile à mesurer. De plus, le 3-OHBaP montre une certaine rétention rénale, un facteur qui rend plus compliqué son utilisation en tant que biomarqueur car il oblige de prendre plusieurs critères en compte dans l’analyse de sa cinétique temporelle. Par ailleurs, le 1-hydroxypyrène (1-OHP) est un métabolite urinaire du pyrène souvent utilisé comme biomarqueur d’exposition aux HAP. Neanmoins, il s’agit du métabolite d’un HAP non-cancérigène et par conséquent sa capacité de démontrer le risque de cancer associé à une exposition donnée est faible. Ce mémoire visait à détecter et à évaluer l'exposition au BaP en suivant ses métabolites urinaires: le 4,5-dihydrodiol-benzo[a]pyrène et le 7,8-dihydrodiol-benzo[a]pyrène (le 4,5-diolBaP et le 7,8-diolBaP; les diolBaP). L’évaluation du 4,5-diolBaP et du 7,8-diolBaP s’est déroulée dans deux études: La première étude, surnommée « l’expérience du shampooing », portait sur un volontaire qui s’est exposé aux HAP dans un environnement contrôlé en utilisant un shampooing à base de goudron de houille. Cette étude a été conçue afin d’évaluer l'évolution temporelle du 7,8-diolBaP chez l'homme et de vérifier son potentiel en tant que biomarqueur d'exposition par comparaison avec le 1-OHP dans le même cadre expérimental. Elle a été réalisée avec deux expériences. La première portait sur une seule exposition et la seconde sur une exposition multiple. La deuxième étude, surnommée « l’étude des travailleurs », reposait sur une analyse comparative du 4,5-diolBaP, du 7,8-diolBaP, du 1-OHP et du 3-OHBaP dans un milieu de travail. Cette étude avait pour objectif d’évaluer les compétences des diolBaP dans un contexte réel à côté des biomarqueurs établis d'exposition au BaP et aux HAP. Cinq travailleurs d'une usine de production d'anodes en carbone ont accepté de participer à cette étude. Dans le cadre de ces deux études, les échantillons d'urine étaient analysés par la chromatographie en phase liquide à ultra-haute performance (UHPLC) couplée à la fluorescence. « L’expérience du shampooing » : L’expérience de l’exposition unique et celle de l’exposition multiple ont révélé une élimination de façon mono-exponentielle du 7,8-diolBaP, identique à celle du 1-OHP, avec des concentrations dans le même ordre de grandeur. Nous avons également confirmé un taux d’élimination plus rapide pour le 1-OHP en regardant ses pics. Le 7,8-diolBaP augmente en valeur maximale après chaque exposition, et cette découverte a mis en évidence une accumulation tout au long de la semaine, alors que pour le 1-OHP, le deuxième pic est plus grand, mais le troisième est plus petit, montrant ainsi moins d'accumulation pendant la même période temporelle. « L’étude des travailleurs »: Selon les résultats, la méthode analytique utilisée était incapable de discerner correctement le 4,5-diolBaP des autres contaminants urinaires éluant pendant le même temps de rétention. Le 7,8-diolBaP, quant à lui, élue à des concentrations urinaires d'un ordre de grandeur similaire au 1-OHP tel que vu chez tous les travailleurs évalués. Chez certains travailleurs, la concentration urinaire du 7,8-diolBaP était toujours plus élevée avant le début d'un quart de travail avec l'élimination qui avait lieu pendant le quart de travail pour fournir une valeur de concentration inférieure à la fin du quart de travail. Cependant, la concentration du 1-OHP a eu une hausse immédiate avec l'exposition, culminant à la fin de chaque quart de travail. Pour les autres travailleurs, les concentrations du 7,8-diolBaP et du 1-OHP étaient systématiquement plus élevées à la fin du quart de travail. Il est probable que ces variations indiquent les différentes voies d'exposition. Le présent mémoire a montré le potentiel du 7,8-diolBaP en tant que biomarqueur d'exposition spécifique au BaP et par conséquent, il fournit un point de départ pour explorer la quantification du lien entre l'exposition au BaP et ses effets néfastes sur la santé de l'être humain. L’utilisation de la spectrométrie de masse est nécessaire à confirmer l’identité des diolBaP avant d'aller de l'avant.Benzo[a]pyrene (BaP) is one of the more commonly studied polycyclic aromatic hydrocarbons (PAHs), a group of omnipresent pollutants in the environment formed through incomplete combustion processes. It is listed as a confirmed carcinogen to human beings by the International Agency for Research on Cancer (IARC) and is highly present in many workplaces. Although presenting a significant health risk to workers, there are currently no convenient compound-specific biomarkers that enable the tracking and monitoring of occupational exposure to BaP. 3-Hydroxybenzo[a]pyrene (3-OHBaP) is the most developed, as a biomarker, amongst the metabolites of BaP. It’s mostly excreted with the faeces, presenting in trace amounts in urine, which makes it difficult to measure; it is also demonstrates renal retention, which adds a layer of complexity in its use as a biomarker because there are many factors to take into consideration when looking at its kinetic time course. 1-Hydroxypyrene (1-OHP), in the other hand, is a urinary metabolite of pyrene that serves as a good representative of PAH presence. It is, however, the metabolite of a non-carcinogenic PAH, and is not fully capable of representing the cancer risk posed in a given scenario. This thesis sought to detect and assess BaP exposure through tracking its urinary metabolites: 4,5-dihydrodiol-benzo[a]pyrene and 7,8-dihydrodiol-benzo[a]pyrene (4,5-diolBaP and 7,8-diolBaP; diolBaPs). 4,5-DiolBaP and 7,8-diolBaP were evaluated through two studies: The first study, the “shampoo experiment”, featured a volunteer who self-exposed to PAHs in a controlled setting by using a coal-tar-based shampoo. The study consisted of two experiments. The first focused on a single exposure and the second on multiple exposures. This study was set to evaluate the time course of 7,8-diolBaP in humans and verifying its potential as a biomarker of exposure through a comparison with 1-OHP in the same experimental framework. The second study consisted of a comparative analysis of 4,5-diolBaP, 7,8-diolBaP, 1-OHP and 3-OHBaP in an occupational setting, evaluating the competency of the diolBaPs in a real-world setting alongside established biomarkers of BaP and PAH exposure. Five workers at a carbon anode production plant volunteered to participate in this study. For both of these studies, the urine samples were analysed by ultra-high-pressure liquid chromatography (UHPLC) coupled with fluorescence. “Shampoo Experiment”: The single and multiple exposures revealed a monoexponential elimination on the part of 7,8-diolBaP, identical to 1-OHP, with similar magnitudes of concentration. 1-OHP was also confirmed to undergo a more rapid elimination from the system, where after each exposure for 7,8-diolBaP, the ensuing peak value is higher. This finding demonstrated evidence of accumulation of 7,8-diolBaP throughout the week, whereas with 1-OHP, the second peak is larger, then the third one is smaller, thus showing less accumulation over the same time frame. “Worker Study”: The results showed that the analytical method used was unable to properly discern 4,5-diolBaP from other urinary contaminants eluting during the same retention time. 7,8-DiolBaP, on the other hand, eluted at urinary concentrations that were a similar order of magnitude to 1-OHP, as can be seen in all of the workers evaluated. For some workers, the urinary concentration of 7,8-diolBaP was consistently at its peak prior to the start of a shift and elimination took place during the shift, to provide a lower concentration value at the end of the shift. With 1-OHP, the rise was immediate with exposure, peaking at the end of every shift. For other workers, both 7,8-diolBaP and 1-OHP are consistently higher at the end of the shift. These variations are likely to indicate different routes of exposure. This thesis showed the potential use of 7,8-diolBaP as a compound-specific biomarker of exposure for BaP and thus provides a starting point in exploring the quantification of BaP exposure and negative health effects in humans. Confirmation of the compound’s identity is needed through the use of mass spectrometry

Zombie Apocalypse: Engaging Students In Environmental Health And Increasing Scientific Literacy Through The Use Of Cultural Hooks And Authentic Challenge Based Learning Strategies

Environmental Health (EH) is an essential profession for protecting human health and yet as a discipline it is under-recognised, overlooked and misunderstood. Too few students undertake EH studies, culminating in a dearth of qualified Environmental Health Officers (EHOs) in Australia. A major deterrent to students enrolling in EH courses is a lack of appreciation of the relevance to their own lives. This is symptomatic of a wider problem of scientific literacy: the relevance gap and how to bridge it. Employing a cultural hook offers a means to connect students to science and the fundamental elements of EH. Zombies feature prominently in the contemporary cultural landscape – movies, TV, gaming, music, cosplay, ‘Zombie Marches’. A Zombie Apocalypse provides an engaging platform to convey key EH concepts such as microbes and toxins, whilst improving the scientific literacy skills of both science and non-science students. Engaging students through this cultural hook bridged the relevance gap, connected students to science, and inspired an increased interest in EH

Towards a framework for environmental risk assessment of CCS: subsea engineering systems

Nowadays, we are observing a continuous rise in trends of greenhouse gasses’ concentration in the atmosphere, especially of carbon dioxide, and this is, in great part, attributable to human activities. The first detrimental effects on climate have already been observed and ever more long-term changes in weather patterns should be expected if no concrete action to contrast these trends is put in practice. The scientific community is thus suggesting innovative and practical solutions for both mitigating climate change and adapting to its impacts: carbon capture and storage (CCS) is one such option. CCS involves capturing carbon dioxide (CO2) from power plants, industrial activities and any other sources of CO2 and storing it in a geological formation. The appeal of this technique resides in the fact that CCS is able to combine the use of fossil fuels, on which our society still relies a lot, with the environmental exigency to cut carbon dioxide’s emissions. However, despite the interesting mitigation option offered by CCS, there is the impelling need, as for any other human activity, to assess and manage risk; this work is intended to do so. The focus is, more precisely, on marine environmental risk posed by CO2 leakages, as how this risk should be addressed still represents a largely debated topic. Specific risks can be associated to each of the stages of a CCS system (capture, transport and storage). The focus of this work is on the subsea engineering system, thus, offshore pipelines (transport) and injection / plugged and abandoned wells (part of the storage). The aim of this work is to start approaching the development of a complete and standardized practical procedure to perform a quantified environmental risk assessment for CCS, with reference to the specific activities mentioned above. Such an effort would be of extreme relevance not only for companies willing to implement CCS, as a methodological guidance, but also, by uniformizing the ERA procedure, to begin changing people’s perception about CCS, that happens to be often discredited due to the evident lack of systematized methods to assess the impacts on the marine environment. The backbone structure of the framework developed sees the integration of ERA’s main steps, which are the problem formulation, exposure assessment, effect assessment and risk characterization, and those belonging to the well-known quantified risk assessment (QRA). This, in practice, meant giving relevance to the identification of possible hazards, before the fate of CO2 in seawater could be described (exposure assessment), and estimating the frequencies of the leakage scenarios, in order to finally describe risk as a combination of magnitude of the consequences and their frequency. The framework developed by this work is, however, at a preliminary stage, as not every single aspect has been dealt with in the required detail, thus, several alternative options are presented to be used depending on the situation. Further specific studies should address their accuracy and efficiency and solve the knowledge gaps emerged, in order to establish and validate a final and complete procedure. Regardless of the knowledge gaps and uncertainties, that surely need to be addressed, this preliminary framework can already find some relevance in on field applications, as a non-stringent guidance to perform CCS ERA, and, anyways, it constitutes the foundation of the final framework

Diatom teratologies as biomarkers of contamination: Are all deformities ecologically meaningful?

Contaminant-related stress on aquatic biota is difficult to assess when lethal impacts are not observed. Diatoms, by displaying deformities (teratologies) in their valves, have the potential to reflect sub-lethal responses to environmental stressors such as metals and organic compounds. For this reason, there is great interest in using diatom morphological aberrations in biomonitoring. However, the detection and mostly the quantification of teratologies is still a challenge; not all studies have succeeded in showing a relationship between the proportion of abnormal valves and contamination level along a gradient of exposure. This limitation in part reflects the loss of ecological information from diatom teratologies during analyses when all deformities are considered. The type of deformity, the severity of aberration, species proneness to deformity formation, and propagation of deformities throughout the population are key components and constraints in quantifying teratologies. Before a metric based on diatom deformities can be used as an indicator of contamination, it is important to better understand the “ecological signal” provided by this biomarker. Using the overall abundance of teratologies has proved to be an excellent tool for identifying contaminated and non-contaminated environments (presence/absence), but refining this biomonitoring approach may bring additional insights allowing for a better assessment of contamination level along a gradient. The dilemma: are all teratologies significant, equal and/or meaningful in assessing changing levels of contamination? This viewpoint article examines numerous interrogatives relative to the use of diatom teratologies in water quality monitoring, provides selected examples of differential responses to contamination, and proposes solutions that may refine our understanding and quantification of the stress. This paper highlights the logistical problems associated with accurately evaluating and interpreting teratologies and stimulates more discussion and research on the subject to enhance the sensitivity of this metric in bioassessments

Societal and ethical issues in human biomonitoring – a view from science studies

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