Risk Assessment Oil and Gas


VALUE-ADDED OF NSS-DERIVED PRODUCTS



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OILGAS
ADNOC Toolbox Talk Awareness Material 2020, ADNOC Toolbox Talk Awareness Material 2020, TRA-Installation of Field Instruments, Road Maintenance Plan & Status-Map Format
2.3. VALUE-ADDED OF NSS-DERIVED PRODUCTS
In the beginning of this section, we enumerated generic benefits of NSS data for environmental analysis efforts such as this one, which involved using GIS as an analytical tool.
Elements of this system were derived from NSS data, so as to allow us to better predict adverse environmental consequences of oil exploration. There are four basic ways that NSS-derived products can add value to GIS databases used for environmental risk assessment: (1) National
Security Systems provide imagery collected since the early 1960s, a unique baseline data set to compare with current conditions; (2) risk assessment often requires GIS layers at high spatial resolution, e.g., oil field pumps and buildings, which are obtainable only with NSS data; (3) NSS
data can provide “ground truth” for broad-area risk analyses based on civilian sensor data; and (4)
NSS imagery may be the only data available for otherwise remote and inaccessible areas.
Nevertheless, NSS were designed for use in the national security arena and, despite the national security implications of environmental issues, their use for environmental matters is new and somewhat controversial. Accordingly, it was felt that it would be valuable to more specifically quantify the value added to environmental analysis by NSS. We begin by developing an analytical approach structure. Such a generic approach consists of the following four steps
1. Enumerate the NSS products used (archival material, high-resolution imagery, etc.).
2. For each NSS product used, indicate the best non-NSS source of the same type of information and provide the available resolution (space, time, or accuracy) of each.
3. Rerun the risk assessment using the non-NSS sources in place of the NSS data.
4. Document the difference that results from the different quality and quantity of information inputs, in terms of:
a. The resulting spatial detail of the locations where risk is higher than the decision-making tolerance.
b. The resulting temporal detail of the conditions when risk is higher than the decision-making tolerance.
c. The costs, in frequency of false positive and false negative decisions, resulting under the two data sources.
Examples of decision rules that might be driven by results of a risk assessment are:
The planned activity is precluded wherever (or whenever) the local risk measure exceeds a critical threshold.
Some mitigation investment is required wherever (or whenever) local risk measure exceeds a critical threshold.


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A false positive would be a case, for example, in which a decision is made that mitigation action is needed, when in fact it is not. A false negative would be a case where a mitigation action is not triggered, when in fact it should have been. It can be proven mathematically that, on the average, more and better data will result in lower false positive and false negative error rates when the decision rule optimizes the expected costs of the outcome. In other words, on the average the costs of the consequences of wise risk management will be lower if the input information is better.
The cost-benefit analysis of the value of the additional information hinges on whether the direct cost of obtaining that information is larger or smaller than the cost savings expected from its use in a decision process that relies on the results of a risk assessment based on that information.


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