Abstract

Groundwater in urban areas around the globe happens to be contaminated by toxic substances. Among the various sources of contamination, industries determine the heaviest impacts when toxic compounds are released in the underground, mainly through leaking tanks or pipelines. Some contaminants (typically chlorinated hydrocarbons) tend to persist within the underground and are hard to biodegrade. As a result, substances that leaked decades ago are still impacting groundwater. Milano and its hinterland (Functional Urban Area) are a good example of an area that has been hosting for over a century, industries of all dimensions, many of them contributing chlorinated hydrocarbons in the underground. While the position of the biggest industrial facilities is well known, many smaller sources are hard to identify in many cases where direct surveys haven’t been undertaken. Furthermore, the overlapping effects of big, small, known and unknown sources on groundwater contamination makes it hard to identify the contribution of each. In order to identify the contribution of several Point Sources responsible of Tetrachloroethylene contamination in Public Water Supply Wells, a numerical model (MODFLOW-2005) has been implemented and calibrated (PEST) in the Northwestern portion of Milano Functional Urban Area. In contaminant transport modeling, the deterministic approach is still favored over the stochastic because of the simplicity of its application. Nevertheless, the latter is considered by the authors as the suitable dealing with problems characterized by high uncertainty, such as hydrogeological parameters distribution. Adopting a Null-Space Monte Carlo analysis, 400 different sets of hydraulic conductivity fields have been randomly generated, of which only 336 have been selected using an objective function threshold. Subsequently, a particle back-tracking has been performed for each of the accepted hydraulic conductivity fields, by placing particles in a contaminated well. The number of particle passages is considered as being proportional to the contribution of each unknown Point Source to the Tetrachloroethylene contamination identified in the target well. The study provides a methodology to help Public Authorities to locate the most probable than not area responsible to the Tetrachloroethylene contamination detected in groundwater and to focus environmental investigations in specific sectors of Milano city.

Highlights

  • In urban areas impacted by historical industrialization, the main problem of groundwater contamination is related to chlorinated hydrocarbons (CHCs) (Menichetti and Doni, 2017; La Vigna et al, 2019)

  • The area is historically affected by many chlorinated hydrocarbon plumes originating from the northern outer border of the Milano municipality (Giovanardi, 1979; Segre, 1987; Provincia di Milano, 1992); over the last 40 years, the contamination has migrated into Milano city because of the intake area induced by the water supply wells, which provoked a coalescence of several plumes and causing a deterioration of water quality

  • The northwestern area in the Milano Functional Urban Area is affected by a strong presence of chlorinated hydrocarbons, originating from several contaminated sites historically present in the territory

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Summary

Introduction

In urban areas impacted by historical industrialization, the main problem of groundwater contamination is related to chlorinated hydrocarbons (CHCs) (Menichetti and Doni, 2017; La Vigna et al, 2019) Such contamination is typically associated with point sources (PS) or discrete zones, formerly linked to petrochemical plants, refineries, automotive, dry-cleaning, or metal degreasing operations. In the Lombardy Region (Italy), one of the most urbanized and industrialized areas in Europe, nearly 3,000 potential brownfields are present in the contaminated site regional database (AGISCO, ARPA Lombardia, 2019) In such a context, there are many obstacles for remediation as suggested by Alderuccio et al (2019) and Barilari et al (2020). The link, always “causal,” requires strong supporting “evidence”; in this sense, the criterion of “more probable than not” can be applied This is a fundamental step for regional authorities that, without identifying those responsible for contamination, have to take charge of the remediation processes. It enables the public authorities to focus their investigations and to effectively apply the “Polluter Pay Principle”

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