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266  4 Life Cycle Impact Assessment

                    separately by experiment. If exclusively aerobic degradable organic substances are
                    present in the water the COD is equal to the BOD, otherwise the COD is always
                    larger. Therefore a consideration of the COD in the impact category, eutrophication,
                    under precautionary criteria always refers to the maximum possible value.
                      The following consideration correlates the COD with the EP:
                      Because the damaging impact of biodegradable carbon compounds is the result
                    of an ‘oxygen depletion’ 258)  the oxygen demand is taken for a definition of the EP-
                    value (kg of phosphate equivalents). To completely oxidise a molecule of the model
                    biomass it is presumed that 138 molecules of oxygen are additionally necessary
                    besides the 110 oxygen atoms already present in the molecule (Equation 4.24). The
                    chemical species considered for N and P following the oxidation are NO 3 −  and
                    HPO 4 2−  which prevail in aerobic water with usual pH levels:

                         C 106 H 263 O 110 N P + 138O → 106CO + 122H O
                                                              2
                                                      2
                                     16
                                              2
                                                 + 16NO 3  –  + 1HPO  4 2–  + 18H +259)
                      Sample Calculation

                      A molar ratio of n (P)/n (O ) = 1/138 results in
                                          2
                                                 3− )
                                     m(O )× M(PO
                                3− )=   2       4
                           m(PO
                               4
                                       M(O )× 138
                                           2
                                                         −1
                      (M (O ) = 32gmol −1  and M (PO 4 3− ) = 95gmol )
                          2
                      For 1 kg COD calculated as O thus 0.022 kg phosphate equivalent results.
                                            2
                      Thus, somewhat artificially, the correlation of the impact of eutrophication by
                    oxidisable organic compounds with oxygen depletion is quantitatively achieved.
                    The COD of persistent (‘refractory’) compounds should actually not be included in
                    the calculations, as these materials do not contribute to oxygen consumption. The
                    COD is therefore a worst case approximation of the BOD.
                      For the calculation of the terrestrial EP mainly emissions into the air are consid-
                    ered, for the aquatic EP direct and indirect entries into the waters. 260)  The majority
                    of continental emissions into the air reach the soil by dry and wet deposition. The
                    emissions into water and the settling on soil influence ecosystems which can be
                    over-fertilised. Soil and water are interconnected: Washing-off surplus fertilisers
                    from agricultural surfaces and penetration into the groundwater (nitrate pollution).
                    Over-fertilisation of agriculturally used grounds (technosphere, not ecosphere) is
                    not considered here because by definition the inadvertent eutrophication includ-
                    ing the unavoidable sequel impacts is discussed exclusively. This is because of
                    the restriction of LCA towards environmental pollution. Clearly, in the case of

                    258) Classical eutrophication due to P and N induces oxygen depletion as a frequent secondary effect.
                    259) Kummert and Stumm (1989).
                    260) Mauch and Sch¨ afer (1996).
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