La governance dei rifiuti in Europa. Territori, conflitti e partecipazione

I rifiuti come oggetti impegnano tutte le istituzioni umane in una lotta di definizione del posto che occupano e quindi del valore che assumono. In tale dinamica la gestione dei rifiuti diventa un fatto sociale totale che coinvolge tutte le istituzioni umane in una lotta di definizione territorializzata. La storia del movimento ambientalista ci mostra come partendo dal disagio nei confronti dell’oggetto si è passati ad un disagio nei confronti delle idee che lo generano. Modernizzazione ecologica e modernizzazione democratica sembrano andare per un certo periodo d’accordo. Nei casi di conflittualità recente, e nello studio di caso approfondito di un piano provinciale della gestione rifiuti, il carattere anticipatore dell’attivismo ambientalista, sta rendendo sempre più costosi e incerti, investimenti e risultati strategici . Anche i principi delle politiche sono messi in discussione. La sostenibilità è da ricercare in una relativizzazione dei principi di policy e degli strumenti tecnici di valutazione (e.g. LCA) verso una maggiore partecipazione di tutti gli attori. Si propone un modello di governance che parta da un coordinamento amministrativo territoriale sulle reti logistiche, quindi un adeguamento geografico degli ATO, e un loro maggior ruolo nella gestione del processo di coordinamento e pianificazione. Azioni queste che devono a loro volta aprirsi ai flussi (ecologici ed economici) e ai loro attori di riferimento: dalle aziende multiutility agli ambientalisti. Infine è necessario un momento di controllo democratico che può avere una funzione arbitrale nei conflitti tra gli attori o di verifica. La ricerca si muove tra la storia e la filosofia, la ricerca empirica e la riflessione teorica. Sono state utilizzate anche tecniche di indagine attiva, come il focus group e l’intervista.

Enzimi, acidi organici ed altri metaboliti coinvolti nella patogenesi di Penicillium spp

Blue mould caused by Penicillium expansum Link is one of the most destructive rot of pome fruit in all growing areas (Snowdon, 1990; Jones and Aldwinckle, 1991; Tonini,1996) In the past, Penicillium rot has been controlled by fungicide postharvest treatment mainly by thiabendazole (TBZ) and benomyl (Hardenburg and Spalding, 1972), but their intense use produced the appearance of resistant strains with a great reduction of their activity The aims of the present study were to characterize the isolates of Pencillium sp causing blue mold on pear in Italy by physiological and biochemical parameters. In particular differencing also the behavior of isolates to relationship with sensitivity or resistance to TBZ treatments. We have examined the early stage of infection in relation to enzyme activity, local modulation of pH, production of organic acids, and to secondary metabolism of pathogen. The results described here confirm that the majority of P. expansum isolates from pears packing houses are resistant to TBZ, Among the TBZ-resistant isolates scored in this work, different isolates (RR) showed higher percentage of conidial germination on TBZ-amended medium compared to non amended medium. This may indicate a stimulatory effect of TBZ on conidial germination. Therefore TBZ treatments are not only ineffective for controlling P. expansum, but they may also increase the severity of blue mould on fruits. In the absence of fungicide, isolates showed a significant difference for infection severity, R and RR isolates are characterized by higher pathogenic fitness on fruits, producing larger lesions than S isolates. These data are supported by the study with laboratory-induced resistant isolates, which shows the lack of correlation between TBZ resistance and osmotic sensitivity, and highlights the association between TBZ resistance and infection severity (Baraldi et al 2003). Enzymatic screening gave a positive reaction to esterase, urease, pectinase activity, in addition, the pathogen is able to synthesize a complex enzyme act to degrade the main components of the cell wall especially pectin and cellulose. Isolated sensitive and resistant are characterized by a good activity of pectinase, especially from poligactoronase, which, as already reported by several studies (D'hallewin et al, 2004; Prusky et al, 2004), are the basis of degradative process of cell wall. Also, although the measure was minor also highlighted some activities of cellulase, but even note in the production of this kind of cellulase and hemicellulase P. Expansum were not targeted, studies have found no other source of information in this regard. Twenty isolates of Penicillium expansum, were tested in vitro ad in vivo for acid production ability and pH drop. We have found that modulation of pH and the organic acids extrusion were influence to various parameter:  Initial pH: in general, the greatest reduction of pH was observed in isolates grown at pH 7, except for four isolates that maintained the pH of the medium close to 7, the others significantly decreased the pH, ranging from 5.5 to 4.1.. In extreme acid condition (pH 3,0) growth and modulation of pH is most lower respect optimal condition (pH 5,0). Also isolates R and RR have showed a greater adaptation to environmental condition more than isolates S.  Time: although the acidification continues for some days, PH modulation is strongest in early hours (48-72 hours)of inoculation process. Time also affects the quality of organic acids, for example in vitro results showed an initial abundant production of succinc acid, followed to important production of galacturoinc acid.  Substrates: there are many differences for the type of acids produced in vitro and in vivo. Results showed in vivo an abundant production of galacturonic, malic, and citric acids and some unknown organic acids in smaller concentrations. Secondary metabolite analysis revealed intra-specific differences, and patulin was found in all isolates, but most significant reduction was observed between in vitro and in vivo samples. There was no correlation between the concentration of patulin, and the percentage of infected fruits, but sample with a lower infection severity of rotten area than the others, showed a significantly lower mycotoxin concentration than samples with a higher lesion diameter of rotten area. Beyond of patulin was detected the presence of another secondary metabolite, penitrem A.

Life Cycle Assessment comparativo tra il processo di co-digestione della frazione organica dei rifiuti solidi urbani e dei fanghi di depurazione disidratati e il sistema di gestione attuale. Il caso di Bagnacavallo (RA)

Waste management is becoming, year after year, always more important both for the costs associated with it and for the ever increasing volumes of waste generated. The discussion on the fate of organic fraction of municipal solid waste (OFMSW) leads everyday to new solutions. Many alternatives are proposed, ranging from incineration to composting passing through anaerobic digestion. “For Biogas” is a collaborative effort, between C.I.R.S.A. and R.E.S. cooperative, whose main goal is to generate “green” energy from both biowaste and sludge anaerobic co-digestion. Specifically, the project include a pilot plant receiving dewatered sludge from both urban and agro-industrial sewage (DS) and the organic fraction of MSW (in 2/1 ratio) which is digested in absence of oxygen to produce biogas and digestate. Biogas is piped to a co-generation system producing power and heat reused in the digestion process itself, making it independent from the national grid. Digestate undergoes a process of mechanical separation giving a liquid fraction, introduced in the treatment plant, and a solid fraction disposed in landfill (in future it will be further processed to obtain compost). This work analyzed and estimated the impacts generated by the pilot plant in its operative phase. Once the model was been characterized, on the basis of the CML2001 methodology, a comparison is made with the present scenario assumed for OFMSW and DS. Actual scenario treats separately the two fractions: the organic one is sent to a composting plant, while sludge is sent to landfill. Results show that the most significant difference between the two scenarios is in the GWP category as the project "For Biogas" is able to generate “zero emission” power and heat. It also generates a smaller volume of waste for disposal. In conclusion, the analysis evaluated the performance of two alternative methods of management of OFMSW and DS, highlighting that "For Biogas" project is to be preferred to the actual scenario.

Studio della gestione integrata dei rifiuti urbani nell'ambito della provincia di Bologna

This work is an analysis of integrated urban waste management in the province of Bologna. It consists of five chapters and one enclosure. Primarily, it focuses on the legislative framework at european, national and local level. Then the study analyses the situation of urban waste system adopted in the reference territory from 2003 to 2007 to show its evolution process. Chapter 3 is based on considerations about the percentage of effective recover of materials derived from separate collection that has been reached in the province of Bologna in 2006. The following chapter describes the urban waste management at national level using dates of 2005 and 2006 by APAT (National Agency for environmental protection). Then, it has been made a comparison with Emilia-Romagna and district of Bologna. Chapter 5 focuses on the description of innovative strategies introduced in the district of Bologna to increase separate collection level and optimize waste management. In particular, it analyses two sperimental projects: one based on door to door collection and the other founded on an integrated collection system which provides the application of two collection models (door to door collection in industrial areas and collection by containers in urban ones). Finally, in the enclosure, it is also descrided best practices of waste management sector about collection models, treatment plants and innovative strategies available at that moment in Europe.

Valorizzazione energetica dei rifiuti urbani: produzione e utilizzi attuali del CDR

Descrive le caratteristiche chimico fisiche del combustibile derivato dai rifiuti, il suo processo produttivo e i suoi utilizzi. Nella parte finale analizza un impianto di produzione del CDR situato a Cavallino( LE) e una centrale termoelettrica a Massafra (TA) che lo utilizza.