Risk-Based Decision-Making for Evacuation in Case of Imminent Threat of Flooding
Abstract
:1. Introduction
2. Decision-Making for Evacuation
3. Methodology “Evacuation Diagram”
- To minimize the risk of loss of life.
- To minimize the economic risk.
- To minimize the total risk considering the combination of economic risk and risk of loss of life.
- as the number of prevented loss of life by evacuation. is defined as the number (persons) of lives lost in the case of a flood event with evacuation, is defined as the number (persons) of lives lost in the case of a flood event without evacuation;
- as the value (Euro) of the goods that are saved by evacuation.
- as the number of lives lost because of evacuation (these also occur when the flood does not occur for example in car accidents of hospital evacuation);
- as the costs (Euro) of the evacuation because of the limitations of economic and social processes and economic costs of the use of equipment and resources (this is estimated by the reduction of the added value to the gross regional product).
4. Case Study: Evacuation Decision for Polders in The Netherlands
4.1. Introduction
- Everyone has to be given the same minimum level of protection: the basic level of protection, expressed as Local Individual Risk (LIR). LIR is defined as the probability of flooding × mortality × (1 − evacuation fraction). The LIR may not exceed 1/100,000 per year.
- Where the impact of flooding is very high, a lower probability of flooding (or a higher level of protection) is appropriate, the standards are based on societal risk and a Societal Cost–Benefit Analysis (SCBA).
4.2. Numerical Examples
- ; the value for the loss of life for the Netherlands is based on [54], based on econometric considerations.
- persons; the number of lives lost due to an evacuation (in reality, this is related to the number of people that evacuate, with special attention paid to people with special needs). Although no figures are known regarding the loss of life due to evacuation in the Netherlands, it is expected, based on international experience, that some loss of life will occur because of traffic accidents during evacuation and evacuation of hospitalized people (in dozens of threatened hospitals). It is expected that s2 depends on the number of hospitals and the condition of patients who have to be evacuated, and further (empirical) research is recommended here to determine its sensitivity to the overall outcomes.
- ; it is assumed that an evacuation including the return of the people will stop economic processes for a week and affect approximately 50% of the Netherlands. The total Gross Domestic Product of the Netherlands in 2010 was 590 Billion € [55]. The costs of evacuation are estimated at 1% (1/52 × ½) of the Gross Domestic Product.
- Because of the limited possibilities of evacuating all people, most effort will be given to reducing loss of life. In addition, movable goods can be evacuated to reduce damage. Because of uncertainty in the damage reduction, an optimistic and pessimistic assumption is taken into account:
- ○
- For the optimistic assumption is 10% of the total damage in the case of a flood. For a worst credible flood on the western coast, the damage is estimated at 120 Billion € [56]; is therefore 12,000 M€;
- ○
- For the pessimistic assumption, is 0.01% of total damage in the case of a flood; is 12 M€;
- Risk aversion is not taken into account, and are equal to 1.
4.3. Exercise Waterproef
- was estimated at 40–45% by the water authorities.
- − was estimated by the National Operational Team at 8000 people if the call for evacuation was made; only 2000 fatalities would occur in case of the flood. When no decisions were made by the authorities regarding evacuation, the loss of life was estimated at 10,000 people (minimum strategy) in the case of a flood. Also, a strategy of partial evacuation was presented, reducing the number of lives lost to 4000 people.
- and were not quantified in the exercise; neither information regarding the consequences was given to the decision-makers. During the crisis meetings, the issue of credibility related to the fear of a call for evacuation not followed by a flood was discussed by the decision-makers.
- was not quantified in the exercise. is not taken into account in this analysis because it is outnumbered by far by the number of lives lost in the case of a flood.
- 21,000 M€ when is 12 M€ which is a pessimistic approach;
- 26,000 M€ when is 12,000 M€ which is an optimistic approach.
- The priority of saving lives is only relevant for the planning document; in real events, this priority is less relevant. However, this seems to conflict with the expectations of the public and the messages sent out by decision-makers and the experiences of many other disasters.
- The assumed economic value of human life (6.7 M€) is too high. However, this seems to be in conflict with research that has been carried out on the value of human life and flood risk assessments in the Netherlands. When is 12,000 M€, the perceived economic value of human life is 0.4 M€, and when is 12 M€, the perceived economic value of human life is 1.9 M€. This economic value of 0.4 M€ of a life is outside the scope of the bandwidth as presented in the literature for flood risk management in the Netherlands [54]. This value for human life is also far less than, for example, the economic value for human life in traffic, which was 2.6 million euro in 2009 [62].
- The lack of information on the costs of evacuation, in combination with the awareness among decision-makers about the large consequences of evacuation and with the load of information about the benefits, created a circumstance in which the call for evacuation was delayed in order to wait for more accurate information. Also, the limited understanding (or different interpretation) of risk could have influenced the outcome of the decision-making process because different opinions could be given.
5. Concluding Remarks
Author Contributions
Funding
Conflicts of Interest
References
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Objective: Minimise Loss of Life | |||||
Prevented loss of life(−) | 100 | 500 | 1000 | 2000 | 6000 |
Minimal value forin % | 25% | 5% | 2.5% | 1.3% | 0.4% |
Objective: minimise economic risk; Minimal value forin%: | |||||
Minimal value forin % for optimistic prevented economic damage (is 12,000 M€) | 50% | ||||
Minimal value forin % for pessimistic prevented loss of economic damage (is 12 M€) in % | No evacuation | ||||
Objective: minimise economic risk including economic value for loss of life | |||||
Prevented loss of life (−) in persons | 100 | 500 | 1000 | 2000 | 6000 |
Minimal value forin % for optimistic loss of economic damage (is 12,000 M€) in % | 49% | 40% | 33% | 24% | 12% |
Minimal value forin % for pessimistic prevented loss of economic damage (is 12 M€) in % | No evac. | No evac. | 92% | 46% | 15% |
Prevented loss of life(−) in persons | 100 | 500 | 1000 | 2000 | 6000 |
Minimiseloss of life whenandare equal to 0.5 | |||||
Minimal value forin % for optimistic loss of economic damage (is 12,000 M€) | 97% | 80% | 66 | 49% | 24% |
Minimal value forin % for pessimistic prevented loss of economic damage (is 12 M€) | No | No | No | 92% | 31% |
Minimiseloss of life whenandare equal to 2 | |||||
Minimal value forin % for optimistic loss of economic damage (is 12,000 M€) | 24% | 20% | 16 | 12% | 6% |
Minimal value forin % for pessimistic prevented loss of economic damage (is 12 M€) | No | 92% | 46 | 23% | 8% |
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Kolen, B.; Van Gelder, P.H.A.J.M. Risk-Based Decision-Making for Evacuation in Case of Imminent Threat of Flooding. Water 2018, 10, 1429. https://doi.org/10.3390/w10101429
Kolen B, Van Gelder PHAJM. Risk-Based Decision-Making for Evacuation in Case of Imminent Threat of Flooding. Water. 2018; 10(10):1429. https://doi.org/10.3390/w10101429
Chicago/Turabian StyleKolen, Bas, and P.H.A.J.M. Van Gelder. 2018. "Risk-Based Decision-Making for Evacuation in Case of Imminent Threat of Flooding" Water 10, no. 10: 1429. https://doi.org/10.3390/w10101429
APA StyleKolen, B., & Van Gelder, P. H. A. J. M. (2018). Risk-Based Decision-Making for Evacuation in Case of Imminent Threat of Flooding. Water, 10(10), 1429. https://doi.org/10.3390/w10101429