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Evaluation of Safety and Environmental Metrics for Potential Application at Chemical Agent Disposal Facilities (2009)

Chapter: 4 Assessment of Other Metrics Potentially Applicable to Chemical Agent Disposal Facilities

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Suggested Citation:"4 Assessment of Other Metrics Potentially Applicable to Chemical Agent Disposal Facilities." National Research Council. 2009. Evaluation of Safety and Environmental Metrics for Potential Application at Chemical Agent Disposal Facilities. Washington, DC: The National Academies Press. doi: 10.17226/12580.
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Suggested Citation:"4 Assessment of Other Metrics Potentially Applicable to Chemical Agent Disposal Facilities." National Research Council. 2009. Evaluation of Safety and Environmental Metrics for Potential Application at Chemical Agent Disposal Facilities. Washington, DC: The National Academies Press. doi: 10.17226/12580.
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Page 20

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4 Assessment of Other Metrics Potentially Applicable to Chemical Agent Disposal Facilities To accomplish the last two items on its statement of and/or worker compensation costs. The data used were task, the committee assessed the development and use almost exclusively lagging indicators—that is, they of leading and lagging indicators by various government were collected after an incident, to determine strategies and private organizations, including any new initiatives based on recorded outcomes to prevent future incidents. that the committee learned about in the course of its While lagging indicators serve useful purposes, they fact finding. Although it conducted this assessment the need to be supplemented with leading indicators to committee developed no related recommendations for ensure continuous improvement of an ESH program. implementation by the chemical agent disposal facili- Also, lagging indicators are of minimal use for an ties (CDFs). Each such facility is in a unique situation organization such as the Chemical Materials Agency with respect to site-specific geography, agent and (CMA), whose mission is changing, moving from dis- munitions to be disposed of, demographics, culture, posal of chemical agents to plant closure and disposal management, and regulatory climate. As a result, each of hazardous and secondary waste. site needs to be able to determine the metrics that are Companies and organizations like the CMA that most appropriate for it. A top-down prescription for a want to be the best in the field have recognized the standard set of metrics to be used at all CDFs would limitations of lagging indicators and are seeking to be less than helpful in the committee’s view. Instead, use leading indicators to anticipate possible incidents the committee presents a general overview of the types within the ESH categories. While the literature is of metrics that might provide general guidance to the replete with information on leading indicators, their CDFs for the continuing development of their safety actual implementation to achieve continuous improve- and environmental programs and culture. ment is limited at best. Notwithstanding this, leading The committee assessed metrics that are currently indicator models appear to have certain elements in used by the Department of the Army and the Federal common: Aviation Administration. They also assessed those of the Center for Chemical Process Safety of the American • Identifying hazards through risk assessment, Institute of Chemical Engineers (AIChE), Corning, • Communication, Dow Chemical, Motorola, and Praxair. The discussion • Training, of applicable metrics that follows is based on informa- • Documentation, tion compiled in Appendix B. • Periodic review by top management, Data on environment, safety, and health (ESH) mat- • Follow-up on findings and corrective action, ters have historically been collected to provide manage- • Analysis of near misses, ment with quantifiable outcomes such as actual and • Sharing of lessons learned, hidden costs, lost time, and worker illness and injury. • Worker involvement, and These data were often tied to regulatory compliance • Audits and assessments. 19

20 Evaluation of Safety and Environmental Metrics While the definitions of lagging and leading indica- with the production line. The task processes are often tors varied from one organization to the next, when the evaluated by means of a job hazard analysis/process combined information from these organizations was analysis as required under the Occupational Safety and considered some common themes for developing a sys- Health Administration Voluntary Protection Programs tem for using leading indicators became apparent. The (VPPs). While preventive maintenance may not in itself definitions developed by this committee (see Appendix be an ESH direct indicator, the failure of a mechanical A) capture the intent of all of the organizations reviewed. system may lead to an event that can produce an injury, The entire committee agrees that measurement is the exposure, or environmental insult. To this end, keeping precursor to control, and that the usual lagging indica- to the preventive maintenance schedule and monitoring tors (e.g., those used by CMA and reviewed in Chapter the completion of the tasks in that schedule are leading 3) should not be neglected as they ultimately lead to indicators of ESH. improvement in safety performance outcomes. Analysis of measured data is vital to ensuring evi- Any measurements and derived indicators must be denced-based control of safety. Analyses could entail part of an overall system—an environmental policy or the more thorough investigation of incidents and/or near a commitment to continuous improvement—if they are misses to ensure that the causative factors have been to be effective in driving improvement. This system identified; application of standard methodologies such must possess a control philosophy (whether it is called as root-cause analysis; generation of indices in terms of risk management or safety management or is a business rates rather than absolute numbers; and application of strategy such as Six Sigma), the commitment of top quality control techniques for visualizing trends. Such management, and specific goals for each indicator. analyses provide a bridge between the raw data and Input measures are the precursors to good safety management action, so that management has a clearer performance. They include ensuring that safety is understanding of what needs to be changed and the designed into all equipment and procedures, timely and potential effects of its actions on safety performance. effective training for all personnel, setting and meeting Accountability at both the organizational and indi- individual safety goals, and completion of tasks set vidual levels is essential. Many organizations require (e.g., corrective actions, preventive actions, and permits the evaluation of support for and actual performance issued). These inputs do not in themselves guarantee a of ESH matters in employee and supervisor appraisals. safe organization, but they are a sign of how ready an In the organizations that excel in ESH, accountability organization is to achieve and improve safety. includes penalties for specifically defined substandard Process measures are indicators that the organiza- performance. tion and its workforce are performing their duties in Overall, much can be learned from the practices a safe manner. Again, they do not guarantee safety, of industrial and government organizations about the but without such indicators, reported levels of safety derivation and use of leading indicators that could be may reflect chance avoidance of rare events rather applied to chemical demilitarization operations. Again, than safety levels achieved as a result of design and because of the unique circumstances in which each control. Typical process measures of safety include chemical agent disposal facility finds itself, the com- the number of near misses or incidents, behavior-based mittee generalized its assessment to assist facilities in safety observations, rates of compliance with written furthering their safety and environmental programs and procedures, participation in pretask hazard assess- cultures. The International Civil Aviation Organization ments, and audits or assessments of task performance summarizes overall safety management as follows: and workplace factors. Note that assessments can be A safety management system . . . , as a minimum, identifies self-assessments, which provide useful training and safety hazards, ensures that remedial action necessary to involve the workforce, or independent assessments, maintain an acceptable level of safety is implemented . . . , which provide unbiased assurance of the state of pro- provides for continuous monitoring and regular assessment cesses. Ideally, all of these leading process measures of the safety level achieved . . . , and aims to make continuous improvement to the overall level of safety. should have been validated against outcome (lagging) indicators to ensure that they are indeed necessary conditions for safety performance, a step that is often Elwyn Jordan, Aviation Safety Inspector, Federal Aviation Ad- neglected. Process measures include the actual physical ministration, “Introduction to safety management systems (SMS),” processes of each task on a production line as well as presentation to the Federal Air Regulation 135 Seminar on April completion of all preventive maintenance associated 19, 2007.

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By the end of 2009, more than 60 percent of the global chemical weapons stockpile declared by signatories to the Chemical Weapons Convention will have been destroyed, and of the 184 signatories, only three countries will possess chemical weapons-the United States, Russia, and Libya.

In the United States, destruction of the chemical weapons stockpile began in 1990, when Congress mandated that the Army and its contractors destroy the stockpile while ensuring maximum safety for workers, the public, and the environment. The destruction program has proceeded without serious exposure of any worker or member of the public to chemical agents, and risk to the public from a storage incident involving the aging stockpile has been reduced by more than 90 percent from what it was at the time destruction began on Johnston Island and in the continental United States.

At this time, safety at chemical agent disposal facilities is far better than the national average for all industries. Even so, the Army and its contractors are desirous of further improvement. To this end, the Chemical Materials Agency (CMA) asked the NRC to assist by reviewing CMA's existing safety and environmental metrics and making recommendations on which additional metrics might be developed to further improve its safety and environmental programs.

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