Skip to main content
Log in

Groundwaters of Florence (Italy): Trace element distribution and vulnerability of the aquifers

  • Original Paper
  • Published:
Environmental Geology

Abstract

Geochemical and hydrogeological research has been carried out on 109 wells in the alluvial plain of Florence, in order to evaluate conductivity and main chemistry of ground waters, the pattern of some possible pollutant chemical species (Fe, Mn, Cr, Cu, Pb, Zn, NO2, NO3), and the vulnerability of the aquifers. The plain is made up of Plio-Quaternary alluvial and lacustrine sediments for a maximum thickness of 600 m. Silts and clays, sometimes with lenses of sandy gravels, are dominant, while considerable deposits of sands, pebbles, and gravels occur along the course of the Arno river and its tributary streams, and represent the most important aquifer of the plain. The groundwaters analyzed belong to this aquifer or to the smaller ones, hosted in the gravel lenses. Most waters show conductivity values around 1000–1200 μS, and almost all of them have an alkaline-earth-bicarbonate chemical character; these features are consistent with the mainly calcareous lithology of the aquifers. In the western areas a higher salt content of the groundwaters is evident, probably related to the presence of industrial activities which use water desalinators. Heavy metal and NO2, NO3 analyses point out that no important pollution phenomena affect the groundwaters; all the mean values of the chemical considered species are below the maximum admissible concentration (MAC) fixed by the European Community for drinkable waters. Nevertheless, some anomalies of NO2, NO3, Fe, Mn, and Zn are present in the plain. Apart from Mn, which seems to be released by certain calcareous gravels, the other anomalies have a local influence, since they disappear even in the nearest wells. The most plausible causes can be recognized in losses of the sewage system (NO2=3–4 mg/t); use of nitrate compounds in agriculture (NO3=60–70 mg/l); oxidation of well pipes (Fe ≈ 20 mg/l; Zn ≈ 6 mg/l). As regards Cr, Cu, and Pb, all the observations are below the MAC; therefore, the median values of < 3, 3.9, and 1.1 μg/l, respectively, could be considered reference concentrations for groundwaters circulating in calcareous lithotypes, under undisturbed natural conditions. Finally, a map of vulnerability related to the most superficial and important aquifer has been elaborated on the basis of thickness and permeability of the covers. The map shows that the areas near the Arno river are highly vulnerable, for the minimum thickness (or lacking) of sediments covering the aquifer. On the other hand, in the case of pollution, several factors not considered in the map could significantly increase the self-purification capacity of the aquifer, such as the dilution of groundwaters caused by the feeding of the rivers, the bacteria oxidation of nitrogenous species, and the sorption capacity of clay minerals and organic matter with respect to trace metals.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Similar content being viewed by others

References

  • APHA (American Public Health Association) (1985) Standard methods for the examination of water and waste water. 16th ed. Washington, DC, APHA

    Google Scholar 

  • Bencini A and Franci G (1984) Geochimica analitica della determinazione dei nitrati + nitriti nelle acque: uso del Nitra VerR. Rend Soc Ital Mineral Petrol 39:455–463

    Google Scholar 

  • Bortolotti V (1962) Contribute alla conoscenza della stratigrafia della serie Pieraforte-Alberese. Boll Soc Geol Ital 81:225–304

    Google Scholar 

  • Brondi M, Dall'Aglio M, Falchi G and Orlandi C (1983a) Trace element distribution in the major aquifers of the Latium Region, Italy. Proceedings, Heavy metals in the environment, International conference, Heidelberg, Germany, pp 680–683

  • Brondi M, Dall'Aglio M, Ghiara E and Gragnani R (1983b) Trace element analysis in natural waters. Proceedings, Heavy metals in the environment, International conference, Heidelberg, Germany, pp 204–207

  • Brooks RR (1978) Pollution through trace elements. In: Bockris JM (Ed), Environmental Chemistry. New York: Plenum Press, pp 429–473

    Google Scholar 

  • Capecchi F, Guazzone G and Pranzini G (1976) Ricerche geologiche ed idrogeologiche nel sottosuolo della pianura di Firenze. Boll Soc Geol Ital 94:661–692

    Google Scholar 

  • Castany G (1982) Principes et méthodes de l'hydrogéologie. Paris: Dunod

    Google Scholar 

  • Civita M, Giuliano G and Zavatti A (1987) Protezione degli acquiferi ed azioni di risanamento: Alcune esperienze italiane. Mem Soc Geol Ital 37:311–331

    Google Scholar 

  • Cook R (1984) Major bio-geochemical cycles and anthropogenic changes. Episodes 7:3–7

    Google Scholar 

  • Dall'Aglio M (1982) Distribution of trace elements in major Italian rivers. WHO-Environment Canada Water Quality Bull 7:163–168

    Google Scholar 

  • Ercolanelli R and Sbaragli A (1991)Indagine preliminare sulle acque di falda di Firenze. Proceedings, First national meeting of young researchers in applied geology. Gargnano, Italy, CUEM, Milano, pp 377–386

    Google Scholar 

  • EEC (European Economic Community) (1980) Quality of waters destined to human use. Dir. 7-15-1980.

  • Forstner U and Wittman GTW (1981) Metal pollution in the aquatic environment. Berlin: Springer-Verlag

    Google Scholar 

  • Fortescue JAC (1980) Environmental geochemistry. Berlin: Springer-Verlag

    Google Scholar 

  • Fuge R and Perkins W (1991) Aluminium and heavy metals in potable waters of the North Ceredigion area, Mid-Wales. Environ Geochem Health 13(2):56–65

    Google Scholar 

  • Gargini A (1990) Permeability of nonsaturated medium and pollution vulnerability of primary porosity aquifers: Proposal of a new valuation method. Unpublished PhD thesis. Department of Earth Science, University of Florence

  • Gnanadesikan R (1977) Methods for statistical data analysis of multivariate observations. New York: Wiley

    Google Scholar 

  • Golwer A (1983) Underground purification capacity. Proceedings, Ground water in water resources planning, International symposium, Koblenz, Germany

  • Harris J, Loftis JC and Montgomery RH (1987) Statistical methods for characterizing groundwater quality. Ground Water 25:185–193

    Google Scholar 

  • Hendry MJ, Gillham RW and Cherry JA (1983) An integrated approach to hydrogeologic investigations—a case history. J Hydrol 63:211–232

    Google Scholar 

  • Horowitz AJ, Elrick KA and Colberg MR (1992) The effect of membrane filtration artifacts on dissolved trace element concentrations. Water Res. 26(6): 753–763

    Google Scholar 

  • Jackson KS, Jonasson IR and Skippen JB (1978) The nature of metal-sediment-water interactions in freshwater bodies, with emphasis on the role of organic matter. Earth Sci Rev 14:97–146

    Google Scholar 

  • Maest AS, Crerar DA, Stallard RF and Ryan JN (1990) Metal and nutrient behaviour in the Raritian estuary, New Jersey, U.S.A.: The effect of multiple freshwaters and industrial waste inputs. Chem Geol 81:133–149

    Google Scholar 

  • Margat J and Monition L (1970) Qualité des eaux-pollutions. Bull BRGM4

  • Nicholson RV, Cherry JA and Reandon EJ (1983) Migration of contaminants in groundwater at a landfill: A case study. 6. Hydrogeochemistry. In: Cherry JA (Guest Ed), Contaminants in groundwater at a landfill: A case study. J Hydrol 63:131–176

    Google Scholar 

  • Pedersen JK, Bjerg PL and Christensen TH (1991) Correlation of nitrate profiles with groundwater and sediment characteristics in a shallow sandy aquifer. J Hydrol 124:263–277

    Google Scholar 

  • Reuter JH and Perdue EM (1977) Importance of heavy metal-organic matter interactions in natural waters. Geochim Cosmochim Acta 41:325–334

    Google Scholar 

  • Roberts G and March TI (1987) The effects of intensification of agriculture on nitrate concentrations in British groundwaters.Proceedings, MAB-UNESCO Workshop, Resources by Nitrate, November 1985, Budapest, pp 205–225

  • Shotyk W (1984) Metal-organic species in natural waters. Environ Geochem 10:45–66

    Google Scholar 

  • Spalding RF, Exner ME, Lindau CW and Eaton DW (1982) Investigation of sources of groundwater nitrate contamination in the Burbank-Wallula area of Washington, U.S.A. J Hydrol 58:307–324

    Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Rights and permissions

Reprints and permissions

About this article

Cite this article

Bencini, A., Ercolanelli, R., Sbaragli, A. et al. Groundwaters of Florence (Italy): Trace element distribution and vulnerability of the aquifers. Geo 22, 193–200 (1993). https://doi.org/10.1007/BF00767403

Download citation

  • Received:

  • Accepted:

  • Issue Date:

  • DOI: https://doi.org/10.1007/BF00767403

Key words

Navigation