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Project title: Knowledge integration and Management Strategy Evaluation modelling Modelling the future of the Kimberley region |
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Strategy Analysis (Ecospace) - Summary ResultsFollowing on the results of the cluster analysis applied to the 18 modelled scenarios, here we discuss the impact of the management strategies applied to the representatives of the ‘High’, ‘Medium’ and ‘Low Pressure’ scenario clusters (see Figure 1).
Following the structure used to analyse the scenario results, Figure 2 shows the violin plot of the state of all indicators (y axis) at the end of Ecospace simulation (2050), expressed as ratio of change over the value at the beginning of the simulation (2015). These end states now reflect the impact of the management strategies. To help the comparison, the violin plots obtained from the scenarios analysis (without management strategies) (coloured violins) are also included in Figure 2, to which the distributions from the scenario analysis (black and white violins) are superimposed.
From a simple visual inspection of Figure 3 we note:
The analysis of Figure 4 lleads to the following observations:
Finally, we have applied a cluster analysis the end states of the system under different management strategies, as we did for the scenario analysis. The results are shown in Figure 13, where different clusters are represented with different colours. The visual inspection of these clusters confirms the general results described so far in this section. Pressure due to different scenarios (‘High’, vs ‘Medium’ vs ‘Low’) still has a clear impact on the clustering (vertical differentiation). However, the effect of the management strategies is also noticeable (horizontal differentiation) especially in the ‘High’ and ‘Medium’ strategies on the one hand, vs the ‘Reversed’ and ‘Worst’ strategies on the other.
Figure 5 shows the Total Divergence between the end states for each of the system under different management strategies the state of the system at the beginning of the simulations. Figure 16 reminds us once again how the impact due to warming is the main stressor the region is likely to have to address and that the efficacy of any strategy will largely depend on this. To conclude this section, it is important to remind the reader that the reliability of these results needs to be verified with local biomass sampling inside and outside of the sanctuary zones. Assumptions about movements and migrations also need to be verified and biomass estimates improved. Overall, a better model parameterisation would allow better analysis of trends in target species such as Barramundi, Threadfin, Spanish mackerel, Snappers and Emperors. For example, the dispersal rates for most of these target species is difficult to estimate given sparse information on movement behaviour of species in the Kimberley region, although it is likely to have important effects on the overall outputs. An improved understanding on the biology of key species would also strengthen some of the assumptions in the model parameterisation employed in this study |