Indirect human exposure assessment of airborne lead deposited on soil via a simplified fate and speciation modelling approach

Cadmium Bioavailability, Uptake, Toxicity and Detoxification in Soil-Plant System

This review summarizes the findings of the most recent studies, published from 2000 to 2016, which focus on the biogeochemical behavior of Cd in soil-plant systems and its impact on the ecosystem. For animals and people not subjected to a Cd-contaminated environment, consumption of Cd contaminated food (vegetables, cereals, pulses and legumes) is the main source of Cd exposure. As Cd does not have any known biological function, and can further cause serious deleterious effects both in plants and mammalian consumers, cycling of Cd within the soil-plant system is of high global relevance.The main source of Cd in soil is that which originates as emissions from various industrial processes. Within soil, Cd occurs in various chemical forms which differ greatly with respect to their lability and phytoavailability. Cadmium has a high phytoaccumulation index because of its low adsorption coefficient and high soil-plant mobility and thereby may enter the food chain. Plant uptake of Cd is believed to occur mainly via roots by specific and non-specific transporters of essential nutrients, as no Cd-specific transporter has yet been identified. Within plants, Cd causes phytotoxicity by decreasing nutrient uptake, inhibiting photosynthesis, plant growth and respiration, inducing lipid peroxidation and altering the antioxidant system and functioning of membranes. Plants tackle Cd toxicity via different defense strategies such as decreased Cd uptake or sequestration into vacuoles. In addition, various antioxidants combat Cd-induced overproduction of ROS. Other mechanisms involve the induction of phytochelatins, glutathione and salicylic acid.

A review of ion and metal pollutants in urban green water infrastructures

In urban environments, the breakdown of chemicals and pollutants, especially ions and metal compounds, can be favoured by green water infrastructures (GWIs). The overall aim of this review is to set the basis to model GWIs using deterministic approaches in contrast to empirical ones. If a better picture of chemicals and pollutant input and an improved understanding of hydrological and biogeochemical processes affecting these pollutants were known, GWIs could be designed to efficiently retain these pollutants for site-specific meteorological patterns and pollutant load. To this end, we surveyed the existing literature to retrieve a comprehensive dataset of anions and cations, and alkaline and transition metal pollutants incoming to urban environments. Based on this survey, we assessed the pollution load and ecological risk indexes for metals. The existing literature was then surveyed to review the metal retention efficiency of GWIs, and possible biogeochemical processes related to inorganic metal compounds were proposed that could be integrated in biogeochemical models of GWIs.

Framework for combining REACH and national regulations to obtain equal protection levels of human health and the environment in different countries - comparative study of Denmark and Korea

The aim of this paper is to present a conceptual framework for a systems approach to protect the environment and human health by taking into account differences in the cumulative risks of total human exposure in a territorial context. To this end the measures that are available and that can be included in REACH exposure scenarios in order to obtain territorially relevant chemical safety assessments (CSAs) were explored. The advantage of linking the REACH exposure scenarios with background environmental quality data reported under other national regulations is discussed. The main question is how REACH may be improved to protect the environment and human health inside and outside the EU. This question is exemplified in a comparative case study of two countries, Denmark and Korea, each with its own set of different environmental qualities and national regulations. As a member of the EU Denmark is obliged to adopt REACH, while Korea implemented REACH to improve the competitiveness of Korean industry within the EU market. It is presented how differences in national regulations and environmental qualities in these two countries affect background human exposure concentrations. Choosing lead as a model compound, the territorial differences in background exposure to endocrine and neurological interfering stressors were modelled. It is concluded that the different territorial soil and air lead pollution levels contribute differently to the total childhood lead exposure in the two countries. As such, the probability of the total exposure from air and soil exceeding 10% of the provisional Total Daily Intake (PTDI) is estimated to be 55.3% in Denmark and 8.2% in Korea. The relative contribution from air inhalation and soil ingestion to childhood lead exposure is estimated to be 1-99% in Denmark while it is 83-17% in Korea.

External costs of atmospheric lead emissions from a waste-to-energy plant: a follow-up assessment of indirect exposure via topsoil ingestion

In this study the Impact Pathway Approach (IPA) was used to calculate the external costs associated with indirect exposure, via topsoil ingestion, to atmospheric emissions of lead (Pb) from a waste-to-energy plant in Denmark. Three metal-specific models were combined to quantify the atmospheric dispersion of lead, its deposition and accumulation in topsoil, and the increase in blood lead concentration for children resulting from lead intake via topsoil ingestion. The neurotoxic impact of lead on children was estimated using a lead-specific concentration-response function that measures impaired cognitive development in terms of IQ points lost per each incremental μg/dl of lead in blood. Since IQ loss during childhood can be associated with a percent decrease in expected lifetime earnings, the monetary value of such an impact can be quantified and the external costs per kg of lead emitted from the plant were then calculated. The costs of indirect exposure calculated over a time horizon of 100 years, for the sub-population of children of 0-3 years, and discounted at 3%, were in the range of 15-30 €/kg. Despite the continued accumulation of lead in topsoil resulting in increasing future indirect exposure, the results indicate that costs associated with this exposure pathway are of the same order of magnitude as costs associated with direct exposure via inhalation, calculated at 45-91 €/kg. Moreover, when the monetary value of future impacts is discounted to the present, the differences between the two exposure pathways are diminished. Finally, setting a short time horizon reduces the uncertainties but excludes part of the costs of indirect exposure from the assessment.

Addressing geographic variability in the comparative toxicity potential of copper and nickel in soils

Comparative toxicity potentials (CTP), in life cycle impact assessment also known as characterization factors (CF), of copper (Cu) and nickel (Ni) were calculated for a global set of 760 soils. An accessibility factor (ACF) that takes into account the role of the reactive, solid-phase metal pool in the soil was introduced into the definition of CTP. Geographic differences in fate, accessibility, bioavailability, and terrestrial toxicity were assessed by combining the USEtox characterization model, empirical regression models, and terrestrial biotic ligand models. The median CTPs for Cu and Ni with 95% geographic variability intervals are 1.4 × 10(3) (1.7 × 10(2) to 2.0 × 10(4)) and 1.7 × 10(3) (2.1 × 10(2) to 1.1 × 10(4)) m(3)/kg · day, respectively. The geographic variability of 3.5 orders of magnitude in the CTP of Cu is mainly associated with the variability in soil organic carbon and pH. They largely influence the fate and bioavailability of Cu in soils. In contrast, the geographic variability of 3 orders of magnitude in the CTP of Ni can mainly be explained by differences in pore water concentration of magnesium (Mg(2+)). Mg(2+) competes with Ni(2+) for binding to biotic ligands, influencing the toxicity. Our findings stress the importance of dealing with geographic variability in the calculation of CTPs for terrestrial ecotoxicity of metals.