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Life Cycle Analysis of Anaerobic Digestion of Wastewater Treatment Plants  287


                                       Inputs (materials, energy)



                                             Recovered electricity and heat


                          Sludge          Anaerobic  Biogas  Energy  Electricity and heat
             Waste sludge
                        conditioning      digestion       recovery
                                             Digestate

                                         Dewatering


                                           Land
                                         application
                                       (nutrient recovery)




                                           Outputs

           FIGURE  13.3  Scheme  process  of  waste  sewage  sludge  management  through  anaerobic
           digestion.
           recovery of energy and nutrients. Thus, as reported by Heimersson et al. (2017), the
           main function of the system would be the sludge treatment and the end-use, whereas
           the secondary function would be production of biogas and digestate, which in addi-
           tion can have further functions, such as energy and nutrient recovery. In these cases,
           the most common approach to solve multifunctionality is by expansion/reduction
           or by substitution. In the first case, some functions can be included (expansion) or
           excluded (reduction), as already explained. These approaches are usually applied to
           make different systems comparable, and consequently, they are most commonly used
           to compare ADWWS with other technologies (Pradel et al., 2016). In the substitu-
           tion approach, additional functions are considered (energy and/or nutrient recovery)
           and the avoidance of impacts related to the replacement of using energy or resources
           (Heimersson et al., 2017). This approach is the most recommended, according to ISO
           14044:2006, when secondary functions (use of biogas and/or digestate) are studied
           to quantify the avoided emissions related to the substitution of energy and nutrient
           resources. Finally, the allocation approach is hardly used in LCAs of ADWWS, since
           the functions of this system (waste treatment, biogas, and organic digestate) cannot
           be related by a common factor. Regarding economic allocation, great uncertainty
           exists in determining the profits and cost of the different functions (Heimersson
           et al., 2017).
              Quality of inventory data is essential to ensure the reliability of LCA results.
           There is a wide variety of ways in which inventory data are obtained for LCAs on
           ADWW. The most suitable option should take data from real systems (WWTPs) or
           use experimental data obtained in the laboratory. This is the most common option
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