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Research & development

Results

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The implementation of the conceptual model allowed to
identify four potential sources of contamination, facing
the harbour basin: the gas station in front of the quay, the
Florio industries where tuna processing was performed,
the Camperia’s building (where boats storage and
maintenance was performed and, finally, a discharge
of untreated wastewater. A flow diagram of conceptual
model for contamination is reported in Figure 6.

6HGLPHQWVFKDUDFWHULVDWLRQ                                     FIGURE 7 Cumulative grain size determined for each
The characterisation of superficial sediments allowed                        of the all 4 samples
to determine both physical and chemical properties
of particles. The grain size revealed a percentage of silt    for Cadmium, Arsenic, Lead, Tin, IPA and TBT. The
and clay of about 1% and a D50 of approximately 0,215         exceedances have led to classify sediments with “yellow”
mm (Figure 7). The analytical tests detected a moderate       color, i.e. with values of analytical tests that fall within the
exceedance of limits, indicated in columns A and B of         90% limit imposed by the column 5 of Annex B to Part IV of
Annex 5 to Part IV of Legislative Decree no. 152/2006,        Legislative Decree no. 152/2006 (Table 1) [15].

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                                                              In the present work, the list of technologies considered
                                                              are biological, physical-chemical and electro-thermal.
                                                              The most common know-how is organised following the
                                                              approach proposed by Bortone and Palumbo (2007), in
                                                              order to identify the Best Available Technologies (BAT)
                                                              for each different treatment approach. A summary of
                                                              results is presented in Table 2, which shows the range of
                                                              costs in €/m3 and possible investment costs.

FIGURE 6 Conceptual model of contamination for sediments      &ODVVLƂFDWLRQRIVHGLPHQWV
              within Favignana’s Harbour                      DQGPDQDJHPHQWVFHQDULRV
                                                              A preliminary project was prepared in order to allow
                                                              the local authorities to allocate the necessary budget
                                                              for dredging operations within Favignana’s Harbor
                                                              according to the procedures indicated by the national
                                                              legislation (e.g. characterisation of sediment up to 1-2 m
                                                              of depth).The project considered all phases of sediment
                                                              removal and management, and particular attention was
                                                              given to the presence of protected marine species,
                                                              such as Posidonia oceanica meadow. Therefore, two
                                                              options were identified, considering different volume

42 EAI Energia, Ambiente e Innovazione 4/2015
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