Page 212 - DCAP601_SIMULATION_AND_MODELING
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Simulation and Modelling



                      Notes
                                            Figure 12.3:  Two versions of Anderson’  model of  the eutrophication  of a  lake
                                           (Anderson 1973);  left: a  model  of  a  lake  subject to  simulation experiments,  right:
                                                     a  model of  the lake  and its  (agri-)  cultural  environment






























                                    The difference between the two approaches is twofold:
                                    1.   In the original approach Anderson took a formal model of the physical, chemical and
                                         biological processes running in a lake to simulate what could happen if these processes
                                         were  disturbed  by  external  influences  imposed  on  the  model  by  the  simulating
                                         experimenter — whereas the extended model embeds the model of a lake into its social,
                                         political and economic environment and models influences external to the lake as internal
                                         to the model, thus taking into account that the lake and its socioeconomic environment
                                         interact and are interdependent.
                                    2.   The original approach starts from physical, chemical and biological theory providing the
                                         equations between  the main  variables describing the lake  and generates  quantitative
                                         simulation results (predictions) which might be compared to further observation data and
                                         help improve (fine tune) the theory of the biochemical processes occurring in a lake —
                                         whereas the extended model  takes the behaviour of the lake  for granted and adds  a
                                         number of assumptions about the behaviour and actions of a number of human actors
                                         which are (or at least could have been) based on everyday observation and discussions
                                         with  stakeholders,  and these  assumptions  are  not  aimed  at generating  quantitative
                                         predictions about the effect of the tax rate imposed on artificial fertilisers on the oxygen
                                         concentration in the lake, but  only in  qualitative predictions  answering the question
                                         under which tax regime and under which additional measures taken by government and
                                         other neighbours of the lake its eutrophication could or could not be avoided.
                                    Both approaches would serve as explanatory models: the restricted model would explain how
                                    and why under certain external or internal circumstances a lake would be eutrophicated and
                                    suffocate and what was the physical and biochemical mechanism behind the processes leading
                                    to total consumption of oxygen  at the ground of the lake —and it would at  the same  time
                                    recommend countermeasures and allow for an estimation for their potential success; and the
                                    extended model would explain under which conditions such countermeasures would be taken
                                    by the population living around the lake and what incentives one part of the population would
                                    have to promise another part of the population to take the necessary countermeasures.



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