Broadly speaking, a risk assessment is the combination effort of 1. identifying and analyzing potential (future) events that may negatively impact individuals, assets, and/or the environment (i.e., risk analysis); and 2. making judgements "on the tolerability of the risk on the basis of a risk analysis" while considering influencing factors (i.e., risk evaluation). Put in simpler terms, a risk assessment analyzes what can go wrong, how likely it is to happen, what the potential consequences are, and how tolerable the identified risk is. As part of this process, the resulting determination of risk may be expressed in a quantitative or qualitative fashion. The risk assessment plays an inherent part of an overall risk management strategy, which attempts to, after a risk assessment, "introduce control measures to eliminate or reduce" any potential risk-related consequences.
Individual risk assessmentEdit
Risk assessment is necessary in individual cases, including patient and physician interactions. Individual judgements or assessments of risk may be affected by psychological, ideological, religious or otherwise subjective factors, which impact rationality of the process.
There is a tendency for individuals to be less rational when risks and exposures concern themselves as opposed to others. There is also a tendency to underestimate risks that are voluntary or where the individual sees themselves as being in control, such as smoking. A 2017 systematic review from the Cochrane collaboration suggests “well-documented decision aids” are helpful in reducing effects of such tendencies or biases. The ways statistics are expressed and communicated, both through words and numerically also impact the interpretation of benefit and harm. For example, a fatality rate may be interpreted as less benign than the corresponding survival rate.
Systems risk assessmentEdit
Risk assessment can also be made on a much larger "systems" scale, for example assessing the risks of a nuclear power plant (an interactively complex mechanical, electronic, nuclear, and human system) or a hurricane (a complex meteorological and geographical system). Systems may be defined as linear and nonlinear (or complex), where linear systems are predictable and relatively easy to understand given a change in input, and non-linear systems unpredictable when inputs are changed. As such, risk assessments of non-linear/complex systems tend to be more challenging.
In the engineering of complex systems, sophisticated risk assessments are often made within safety engineering and reliability engineering when it concerns threats to life, environment, or machine functioning. The agriculture, nuclear, aerospace, oil, railroad, and military industries have a long history of dealing with risk assessment. Also, medical, hospital, social service, and food industries control risks and perform risk assessments on a continual basis. Methods for assessment of risk may differ between industries and whether it pertains to general financial decisions or environmental, ecological, or public health risk assessment.
Rapid technological change, increasing scale of industrial complexes, increased system integration, market competition, and other factors have been shown to increase societal risk in the past few decades. As such, risk assessments become increasingly critical in mitigating accidents, improving safety, and improving outcomes. Risk assessment consists of an objective evaluation of risk in which assumptions and uncertainties are clearly considered and presented. This involves identification of risk (what can happen and why), the potential consequences, the probability of occurrence, the tolerability or acceptability of the risk, and ways to mitigate or reduce probability of the risk. Optimally, it also involves documentation of the risk assessment and its findings, implementation of mitigation methods, and review of the assessment (or risk management plan), coupled with updates when necessary. Sometimes risks can be deemed acceptable, meaning the risk "is understood and tolerated ... usually because the cost or difficulty of implementing an effective countermeasure for the associated vulnerability exceeds the expectation of loss."
Part of the difficulty in managing risk is that both the quantities by which risk assessment is concerned—potential loss and probability of occurrence—can be very difficult to measure. The chance of error in measuring these two concepts is high. Risk with a large potential loss and a low probability of occurrence is often treated differently from one with a low potential loss and a high likelihood of occurrence. In theory, both are of near equal priority, but in practice it can be very difficult to manage when faced with the scarcity of resources—especially time—in which to conduct the risk management process.
To see the risk management process expressed mathematically, one can define total risk as the sum over individual risks, , which can be computed as the product of potential losses, , and their probabilities, :
Even though for some risks , we might have , if the probability is small compared to , its estimation might be based only on a smaller number of prior events, and hence, more uncertain. On the other hand, since , must be larger than , so decisions based on this uncertainty would be more consequential, and hence, warrant a different approach.
Financial decisions, such as insurance, express loss in terms of dollar amounts. When risk assessment is used for public health or environmental decisions, loss can be quantified in a common metric such as a country's currency or some numerical measure of a location's quality of life. For public health and environmental decisions, loss is simply a verbal description of the outcome, such as increased cancer incidence or incidence of birth defects. In that case, the "risk" is expressed as
If the risk estimate takes into account information on the number of individuals exposed, it is termed a "population risk" and is in units of expected increased cases per a time period. If the risk estimate does not take into account the number of individuals exposed, it is termed an "individual risk" and is in units of incidence rate per a time period. Population risks are of more use for cost/benefit analysis; individual risks are of more use for evaluating whether risks to individuals are "acceptable".
Quantitative risk assessmentEdit
In quantitative risk assessment an annualized loss expectancy (ALE) may be used to justify the cost of implementing countermeasures to protect an asset. This may be calculated by multiplying the single loss expectancy (SLE), which is the loss of value based on a single security incident, with the annualized rate of occurrence (ARO), which is an estimate of how often a threat would be successful in exploiting a vulnerability.
The usefulness of quantitative risk assessment has been questioned, however. Barry Commoner, Brian Wynne and other critics have expressed concerns that risk assessment tends to be overly quantitative and reductive. For example, they argue that risk assessments ignore qualitative differences among risks. Some charge that assessments may drop out important non-quantifiable or inaccessible information, such as variations among the classes of people exposed to hazards, or social amplification. Furthermore, Commoner and O'Brien claim that quantitative approaches divert attention from precautionary or preventative measures. Others, like Nassim Nicholas Taleb consider risk managers little more than "blind users" of statistical tools and methods.
Assessment of riskEdit
The process of risk assessment may be somewhat informal at the individual social level, managing economic and household risks, or a sophisticate process at the strategic corporal level. However, in both cases, ability to anticipate future events and create effective strategies for mitigating them when deemed unacceptable is vital.
At the individual level, a simple process of identifying objectives and risks, weighing their importance and creating plans, may be all that's necessary. At the strategic organisational level, more elaborate policies are necessary, specifying acceptable levels of risk, procedures to be followed within the organisation, priorities, and allocation of resources.:10 At the systematic level, management involved with the project produce project level risk assessments with the assistance of the available expertise as part of the planning process, and set up systems to ensure that required actions to manage the assessed risk are in place. At the dynamic level, the personnel directly involved may be required to deal with unforeseen problems in real time. The tactical decisions made at this level should be reviewed after the operation to provide feedback on the effectiveness of both the planned procedures and decisions made in response to the contingency.
The first step in risk assessment is to establish the context. This restricts the range of hazards to be considered.
This is followed by identification of visible and implied hazards that may threaten the project, and determining the qualitative nature of the potential adverse consequences of each hazard. Without a potential adverse consequence, there is no hazard.
It is also necessary to identify the potential parties or assets which may be affected by the threat, and the potential consequences to them if the hazard is activated.
If the consequences are dependent on dose, i.e. the amount of exposure, the relationship between dose and severity of consequence must be established, and the risk depends on the probable dose, which may depend on concentration or amplitude and duration or frequency of exposure. This is the general case for many health hazards where the mechanism of injury is toxicity or repetitive injury, particularly where the effect is cumulative.
For other hazards, the consequences may either occur or not, and the severity may be extremely variable even when the triggering conditions are the same. This is typical of many biological hazards as well as a large range of safety hazards. Exposure to a pathogen may or may not result in actual infection, and the consequences of infection may also be variable. Similarly a fall from the same place may result in minor injury or death, depending on unpredictable details. In these cases estimates must be made of reasonably likely consequences and associated probability of occurrence.
In cases where statistical records are available they may be used to evaluate risk, but in many cases there are no data or insufficient data available to be useful. Mathematical or experimental models may provide useful input.
Dose dependent riskEdit
- Dose-Response Analysis, is determining the relationship between dose and the type of adverse response and/or probability or the incidence of effect (dose-response assessment). The complexity of this step in many contexts derives mainly from the need to extrapolate results from experimental animals (e.g. mouse, rat) to humans, and/or from high to lower doses, including from high acute occupational levels to low chronic environmental levels. In addition, the differences between individuals due to genetics or other factors mean that the hazard may be higher for particular groups, called susceptible populations. An alternative to dose-response estimation is to determine a concentration unlikely to yield observable effects, that is, a no effect concentration. In developing such a dose, to account for the largely unknown effects of animal to human extrapolations, increased variability in humans, or missing data, a prudent approach is often adopted by including safety or uncertainty factors in the estimate of the "safe" dose, typically a factor of 10 for each unknown step.
- Exposure Quantification, aims to determine the amount of a contaminant (dose) that individuals and populations will receive, either as a contact level (e.g., concentration in ambient air) or as intake (e.g., daily dose ingested from drinking water). This is done by examining the results of the discipline of exposure assessment. As different location, lifestyles and other factors likely influence the amount of contaminant that is received, a range or distribution of possible values is generated in this step. Particular care is taken to determine the exposure of the susceptible population(s).
The results of these steps are combined to produce an estimate of risk. Because of the different susceptibilities and exposures, this risk will vary within a population. An uncertainty analysis is usually included in a health risk assessment.
Dynamic risk assessmentEdit
During an emergency response, the situation and hazards are often inherently less predictable than for planned activities (non-linear). In general, if the situation and hazards are predictable (linear), standard operating procedures should deal with them adequately. In some emergencies this may also hold true, with the prepared and trained responses being adequate to manage the situation. In these situations, the operator can manage risk without outside assistance, or with the assistance of a backup team who are prepared and available to step in at short notice.
Other emergencies occur where there is no previously planned protocol, or when an outsider group is brought in to handle the situation, and they are not specifically prepared for the scenario that exists but must deal with it without undue delay. Examples include police, fire department, disaster response and other public service rescue teams. In these cases ongoing risk assessment by the involved personnel can advise appropriate action to reduce risk. HM Fire Services Inspectorate has defined dynamic risk assessment (DRA) as:
The continuous assessment of risk in the rapidly changing circumstances of an operational incident, in order to implement the control measures necessary to ensure an acceptable level of safety.
Dynamic risk assessment is the final stage of an integrated safety management system which can provide appropriate response during changing circumstances. It relies on experience, training and continuing education, including effective debriefing to analyse not only what went wrong, but also what went right, and why, and to share this with other members of the team and the personnel responsible for the planning level risk assessment.
Fields of applicationEdit
Application of risk assessment procedures is common in a wide range of fields, and these may have specific legal obligations, codes of practice and standardised procedures. Some of these are listed here.
There are many resources that provide health risk information.
- TOXNET (databases on hazardous chemicals, environmental health, and toxic releases),
- the Household Products Database (potential health effects of chemicals in over 10,000 common household products),
- TOXMAP (maps of the U.S. Environmental Protection Agency Superfund and Toxics Release Inventory data).
The Environmental Protection Agency began actively using risk assessment methods to protect drinking water in the United States after passage of the Safe Drinking Water Act of 1974. The law required the National Academy of Sciences to conduct a study on drinking water issues, and in its report the NAS described some methodologies for doing risk assessments for chemicals that were suspected carcinogens, recommendations that top EPA officials have described as perhaps the study’s most important part.
Considering the increase in junk food and its toxicity, FDA required in 1973 that cancer-causing compounds must not be present in meat at concentrations that would cause a cancer risk greater than 1 in a million over a lifetime. The US Environmental Protection Agency provides extensive information about ecological and environmental risk assessments for the public via its risk assessment portal. The Stockholm Convention on persistent organic pollutants (POPs) supports a qualitative risk framework for public health protection from chemicals that display environmental and biological persistence, bioaccumulation, toxicity (PBT) and long range transport; most global chemicals that meet this criteria have been previously assessed quantitatively by national and international health agencies.
When risks apply mainly to small sub-populations, there is uncertainty at which point intervention is necessary. For example, there may be a risk that is very low for everyone, other than 0.1% of the population. It is necessary to determine whether this 0.1% is represented by:
- all infants younger than X days or
- recreational users of a particular product.
If the risk is higher for a particular sub-population because of abnormal exposure rather than susceptibility, strategies to further reduce the exposure of that subgroup are considered. If an identifiable sub-population is more susceptible due to inherent genetic or other factors, public policy choices must be made. The choices are:
- to set policies for protecting the general population that are protective of such groups, e.g. for children when data exists, the Clean Air Act for populations such as asthmatics or
- not to set policies, because the group is too small, or the costs too high.
Acceptable risk criteriaEdit
The idea of not increasing lifetime risk by more than one in a million has become commonplace in public health discourse and policy. It is a heuristic measure. It provides a numerical basis for establishing a negligible increase in risk.
Environmental decision making allows some discretion for deeming individual risks potentially "acceptable" if less than one in ten thousand chance of increased lifetime risk. Low risk criteria such as these provide some protection for a case where individuals may be exposed to multiple chemicals e.g. pollutants, food additives or other chemicals.
In practice, a true zero-risk is possible only with the suppression of the risk-causing activity.
Stringent requirements of 1 in a million may not be technologically feasible or may be so prohibitively expensive as to render the risk-causing activity unsustainable, resulting in the optimal degree of intervention being a balance between risks vs. benefit. For example, emissions from hospital incinerators result in a certain number of deaths per year. However, this risk must be balanced against the alternatives. There are public health risks, as well as economic costs, associated with all options. The risk associated with no incineration is potential spread of infectious diseases, or even no hospitals. Further investigation identifies options such as separating noninfectious from infectious wastes, or air pollution controls on a medical incinerator.
Intelligent thought about a reasonably full set of options is essential. Thus, it is not unusual for there to be an iterative process between analysis, consideration of options, and follow up analysis.
For audits performed by an outside audit firm, risk assessment is a crucial stage before accepting an audit engagement. According to ISA315 Understanding the Entity and its Environment and Assessing the Risks of Material Misstatement, "the auditor should perform risk assessment procedures to obtain an understanding of the entity and its environment, including its internal control". Evidence relating to the auditor’s risk assessment of a material misstatement in the client’s financial statements. Then, the auditor obtains initial evidence regarding the classes of transactions at the client and the operating effectiveness of the client’s internal controls. Audit risk is defined as the risk that the auditor will issue a clean unmodified opinion regarding the financial statements, when in fact the financial statements are materially misstated, and therefore do not qualify for a clean unmodified opinion. As a formula, audit risk is the product of two other risks: Risk of Material Misstatement and Detection risk. This formula can be further broken down as follows: inherent risk × control risk × detection risk.
In the context of public health, risk assessment is the process of characterizing the nature and likelihood of a harmful effect to individuals or populations from certain human activities. Health risk assessment can be mostly qualitative or can include statistical estimates of probabilities for specific populations. In most countries the use of specific chemicals or the operations of specific facilities (e.g. power plants, manufacturing plants) is not allowed unless it can be shown that they do not increase the risk of death or illness above a specific threshold. For example, the American Food and Drug Administration (FDA) regulates food safety through risk assessment.
In project management, risk assessment is an integral part of the risk management plan, studying the probability, the impact, and the effect of every known risk on the project, as well as the corrective action to take should an incident implied by a risk occur. Of special consideration in this area are the relevant codes of practice that are enforced in the specific jurisdiction. Understanding the regime of regulations that risk management must abide by is integral to formulating safe and compliant risk assessment practices.
Information technology risk assessment can be performed by a qualitative or quantitative approach, following different methodologies. One important difference[clarification needed] in risk assessments in information security is modifying the threat model to account for the fact that any adversarial system connected to the Internet has access to threaten any other connected system. Risk assessments may therefore need to be modified to account for the threats from all adversaries, instead of just those with reasonable access as is done in other fields.
Another notable difference is the strategic nature of IT risk assessments. Unlike tactical vulnerability assessments and penetration testing which aim to identify and close specific gaps in security, IT risk assessments are functional at the executive level to examine the broader picture of IT risk management.[clarification needed]
Megaprojects (sometimes also called "major programs") are extremely large-scale investment projects, typically costing more than US$1 billion per project. They include bridges, tunnels, highways, railways, airports, seaports, power plants, dams, wastewater projects, coastal flood protection, oil and natural gas extraction projects, public buildings, information technology systems, aerospace projects, and defence systems. Megaprojects have been shown to be particularly risky in terms of finance, safety, and social and environmental impacts.
Studies have shown that early parts of the system development cycle such as requirements and design specifications are especially prone to error. This effect is particularly notorious in projects involving multiple stakeholders with different points of view. Evolutionary software processes offer an iterative approach to requirement engineering to alleviate the problems of uncertainty, ambiguity and inconsistency inherent in software developments.[clarification needed]
Formal risk assessment is a required component of most professional dive planning, but the format and methodology may vary. Consequences of an incident due to an identified hazard are generally chosen from a small number of standardised categories, and probability is estimated based on statistical data on the rare occasions when it is available, and on a best guess estimate based on personal experience and company policy in most cases. A simple matrix is often used to transform these inputs into a level of risk, generally expressed as unacceptable, marginal or acceptable. If unacceptable, measures must be taken to reduce the risk to an acceptable level, and the final outcome of the risk assessment must be accepted by the affected parties before a dive commences. Higher levels of risk may be acceptable in special circumstances, such as military or search and rescue operations when there is a chance of recovering a survivor. Diving supervisors are trained in the procedures of hazard identification and risk assessment, and it is part of their planning and operational responsibility. Both health and safety hazards must be considered. Several stages may be identified. There is risk assessment done as part of the diving project planning, on site risk assessment which takes into account the specific conditions of the day, and dynamic risk assessment which is ongoing during the operation by the members of the dive team, particularly the supervisor and the working diver.
In recreational scuba diving, the extent of risk assessment expected of the diver is relatively basic, and is included in the pre-dive checks. Several mnemonics have been developed by diver certification agencies to remind the diver to pay some attention to risk, but the training is rudimentary. Diving service providers are expected to provide a higher level of care for their customers, and diving instructors and divemasters are expected to assess risk on behalf of their customers and warn them of site-specific hazards and the competence considered appropriate for the planned dive. Technical divers are expected to make a more thorough assessment of risk, but as they will be making an informed choice for a recreational activity, the level of acceptable risk may be considerably higher than that permitted for occupational divers under the direction of an employer.
Environmental Risk Assessment (ERA) aims at assessing the effects of stressors, often chemicals, on the local environment. A risk is an integrated assessment of likelihood and severity of an undesired event. In ERA, the undesired event often depends on the chemical of interest and on the risk assessment scenario. This undesired event is usually a detrimental effect on organisms, populations or ecosystems. Current ERAs usually compare an exposure to a no-effect level, such as the Predicted Environmental Concentration/Predicted No-Effect Concentration (PEC/PNEC) ratio in Europe. Although this type of ratio is useful and often used in regulation purposes, it is only an indication of an exceeded apparent threshold. New approaches start to be developed in ERA in order to quantifiy this risk and to communicate effectively on it with both the managers and the general public.
Biodiversity Risk Assessments evaluate risks to biological diversity, specially the risk of species extinction or the risk of ecosystem collapse. The units of assessments are the biological (species, subspecies or populations) or ecological entities (habitats, ecosystems, etc), and the risk are often related to human actions and interventions (threats and pressures). Regional and national protocols have been proposed by multiple academic or governmental institutions and working groups, but global standards such as the Red List of Threatened Species and the IUCN Red List of Ecosystems have been widely adopted, and are recognized or proposed as official indicators of progress toward international policy targets and goals, such as the Aichi targets and the Sustainable Development Goals.
- Acceptable loss
- Benefit risk
- Control self-assessment
- Cost risk
- Digital Continuity
- Duty of Care
- Edwards v. National Coal Board
- Extreme risk
- Flood risk assessment
- Form 696
- Global catastrophic risk
- HACCP: hazard analysis and critical control points, risk assessment in food
- Hazard (risk)
- Hazard Identification
- Health Impact Assessment
- Information assurance
- List of auditing topics
- ISO 28000
- ISO 31000
- Megaprojects and Risk
- Network Theory in Risk Assessment
- Optimism bias
- PIMEX a video exposure monitoring method
- Probabilistic risk assessment
- Probit model
- Project risk management
- Reference class forecasting
- Reliability Engineering
- Safety Engineering
- Risk aversion
- Risk based auditing
- Risk management
- Risk management tools
- Risk matrix
- Risk (statistics)
- Security risk
- Strategic misrepresentation
- Rausand, M. (2013). "Chapter 1: Introduction". Risk Assessment: Theory, Methods, and Applications. John Wiley & Sons. pp. 1–28. ISBN 9780470637647.
- Manuele, F.A. (2016). "Chapter 1: Risk Assessments: Their Significance and the Role of the Safety Professional". In Popov, G.; Lyon, B.K.; Hollcraft, B. Risk Assessment: A Practical Guide to Assessing Operational Risks. John Wiley & Sons. pp. 1–22. ISBN 9781118911044.
- Levi, Ragnar (June 1, 2018). "Getting Real About Both Benefits and Risks" (PDF). Swedish Agency of Health Technology Assessment and Assessment of Social Services. pp. 8–9. ISSN 1104-1250. Retrieved 2018-06-14 – via Science & Practice, English Special 2018.
- Hoffmann, Tammy C.; Del Mar, Chris (2015). "Patients' expectations of the benefits and harms of treatments, screening, and tests: a systematic review". JAMA Internal Medicine. 175 (2): 274–286. doi:10.1001/jamainternmed.2014.6016. ISSN 2168-6114. PMID 25531451.
- Stacey, Dawn; Légaré, France; Lewis, Krystina; Barry, Michael J.; Bennett, Carol L.; Eden, Karen B.; Holmes-Rovner, Margaret; Llewellyn-Thomas, Hilary; Lyddiatt, Anne (12 April 2017). "Decision aids for people facing health treatment or screening decisions". The Cochrane Database of Systematic Reviews. 4: CD001431. doi:10.1002/14651858.CD001431.pub5. ISSN 1469-493X. PMID 28402085.
- Rausand, M. (2013). "Chapter 6: Accident Models". Risk Assessment: Theory, Methods, and Applications. John Wiley & Sons. pp. 137–76. ISBN 9780470637647.
- Vamanu, B.I.; Gheorghe, A.V.; Kaina, P.F. (2016). Critical Infrastructures: Risk and Vulnerability Assessment in Transportation of Dangerous Goods: Transportation by Road and Rail. Springer. p. 11. ISBN 9783319309316.
- Lacey, Peter (2011). "An Application of Fault Tree Analysis to the Identification and Management of Risks in Government Funded Human Service Delivery". Proceedings of the 2nd International Conference on Public Policy and Social Sciences. SSRN 2171117.
- Shirey, R. (August 2007). "Internet Security Glossary, Version 2". Network Working Group. The IETF Trust. p. 9. Retrieved 19 July 2018.
- Kasperson, R.E., Renn, O., Slovic, P., Brown, H.S., Emel, J., Goble, R., Kasperson, J.X., Ratick, S. (1988). "The social amplification of risk: A conceptual framework". Risk Analysis. 8 (2): 177–187. doi:10.1111/j.1539-6924.1988.tb01168.x.
- Commoner, Barry. O'Brien, Mary. Shrader-Frechette and Westra 1997.
- The fourth quadrant: a map of the limits of statistics [9.15.08] Nassim Nicholas Taleb An Edge Original Essay
- Holzmann, R.; Jørgensen, S. (2001). "Social Risk Management: A New Conceptual Framework for Social Protection, and Beyond". International Tax and Public Finance. 8 (4): 529–56. doi:10.1023/A:1011247814590.
- Nakaš, N. (21 November 2017). "Three Lessons About Risk Management from Everyday Life". Knowledge Hub. Center of Excellence in Finance. Retrieved 19 July 2018.
- Lock, Gareth (June 2017). Phillips, Mark, ed. "Public Safety Diving-Dynamic Risk Assessment" (PDF). PS Diver Magazine. PSDiver.com (116): 9. Retrieved 20 June 2017.
- "Risk Assessment and Regulation Information from the NLM". NLM. Retrieved 9 June 2013.
- "Databases on toxicology, hazardous chemicals, environmental health, and toxic releases". TOXNET. NLM. May 2012. Retrieved 9 June 2013.
- "Household Products Database". U.S. Dept. of Health & Human Services. January 2013. Retrieved 9 June 2013.
- "Risk Assessment Portal". EPA. 13 May 2013. Retrieved 9 June 2013.
- EPA Alumni Association: Senior EPA officials discuss early implementation of the Safe Drinking Water Act of 1974, Video, Transcript (see pages 11,14).
- EPA, ORD, NCEA, US. "Risk Assessment". www.epa.gov. Retrieved 2016-04-07.
- Szabo DT, Loccisano AE (March 30, 2012). "POPs and Human Health Risk Assessment". Dioxins and Persistent Organic Pollutants. 3rd (Edition): John Wiley & Sons. doi:10.1002/9781118184141.ch19.
- Hunter, Paul R.; Fewtrell, Lorna (2001). "Acceptable Risk" (PDF). World Health Organization.
- Merrill, Richard A. "Food Safety Regulation: Reforming the Delaney Clause" in Annual Review of Public Health, 1997, 18:313-40. This source includes a useful historical survey of prior food safety regulation.
- Managing Project Risks - Retrieved May 20th, 2010
- Spring, J.; Kern, S.; Summers, A. (2015-05-01). "Global adversarial capability modeling". 2015 APWG Symposium on Electronic Crime Research (eCrime): 1–21. doi:10.1109/ECRIME.2015.7120797.
- Arnold, Rob. "3 Types of Security Assessments". Threat Sketch. Threat Sketch. Retrieved 17 November 2016.
- "ISM CODE – Amendments from 1st July 2010 Risk Assessment".
- "Diving Regulations 2009". Occupational Health and Safety Act 85 of 1993 – Regulations and Notices – Government Notice R41. Pretoria: Government Printer. Archived from the original on 4 November 2016. Retrieved 3 November 2016 – via Southern African Legal Information Institute.
- Staff (August 2016). "15 - General safety requirements". Guidance for diving supervisors IMCA D 022 (Revision 1 ed.). London, UK: International Marine Contractors Association. pp. 15-, 5.
- Staff (1977). "The Diving at Work Regulations 1997". Statutory Instruments 1997 No. 2776 Health and Safety. Kew, Richmond, Surrey: Her Majesty's Stationery Office (HMSO). Retrieved 6 November 2016.
- Gurr, Kevin (August 2008). "13: Operational Safety". In Mount, Tom; Dituri, Joseph. Exploration and Mixed Gas Diving Encyclopedia (1st ed.). Miami Shores, Florida: International Association of Nitrox Divers. pp. 165–180. ISBN 978-0-915539-10-9.
- Goussen, Benoit; Price, Oliver R.; Rendal, Cecilie; Ashauer, Roman (2016-10-26). "Integrated presentation of ecological risk from multiple stressors". Scientific Reports. 6. doi:10.1038/srep36004. ISSN 2045-2322. PMC 5080554. PMID 27782171.
- Jager, Tjalling; Heugens, Evelyn H. W.; Kooijman, Sebastiaan A. L. M. (2006-04-20). "Making Sense of Ecotoxicological Test Results: Towards Application of Process-based Models". Ecotoxicology. 15 (3): 305–314. doi:10.1007/s10646-006-0060-x. ISSN 0963-9292.
- Nicholson, Emily; Regan, Tracey J.; Auld, Tony D.; Burns, Emma L.; Chisholm, Laurie A.; English, Valerie; Harris, Stephen; Harrison, Peter; Kingsford, Richard T.; Leishman, Michelle R.; Metcalfe, Daniel J.; Pisanu, Phil; Watson, Christopher J.; White, Matthew; White, Matt D.; Williams, Richard J.; Wilson, Bruce; Keith, David A. (2015). "Towards consistency, rigour and compatibility of risk assessments for ecosystems and ecological communities". Austral Ecology. 40 (4): 347–363. doi:10.1111/aec.12148. ISSN 1442-9985.
- Keith, David A.; Rodríguez, Jon Paul; Brooks, Thomas M.; Burgman, Mark A.; Barrow, Edmund G.; Bland, Lucie; Comer, Patrick J.; Franklin, Janet; Link, Jason; McCarthy, Michael A.; Miller, Rebecca M.; Murray, Nicholas J.; Nel, Jeanne; Nicholson, Emily; Oliveira-Miranda, María A.; Regan, Tracey J.; Rodríguez-Clark, Kathryn M.; Rouget, Mathieu; Spalding, Mark D. (2015). "The IUCN Red List of Ecosystems: Motivations, Challenges, and Applications". Conservation Letters. 8 (3): 214–226. doi:10.1111/conl.12167. ISSN 1755-263X.
- Brooks, Thomas M.; Butchart, Stuart H.M.; Cox, Neil A.; Heath, Melanie; Hilton-Taylor, Craig; Hoffmann, Michael; Kingston, Naomi; Rodríguez, Jon Paul; Stuart, Simon N.; Smart, Jane (2015). "Harnessing biodiversity and conservation knowledge products to track the Aichi Targets and Sustainable Development Goals". Biodiversity. 16 (2–3): 157–174. doi:10.1080/14888386.2015.1075903. ISSN 1488-8386.
- Dorne, Jean-Lou C. M.; Kass, George E. N.; Bordajandi, Luisa R.; Amzal, Billy; Bertelsen, Ulla; Castoldi, Anna F.; Heppner, Claudia; Eskola, Mari; Fabiansson, Stefan; Ferrari, Pietro; Scaravelli, Elena; Dogliotti, Eugenia; Fuerst, Peter; Boobis, Alan R.; Verger, Philippe (2011). "Chapter 2. Human Risk Assessment of Heavy Metals: Principles and Applications". In Astrid Sigel; Helmut Sigel; Roland K O Sigel. Metal Ions in Toxicology. RSC Publishing. pp. 27–60. doi:10.1039/9781849732116-00027.
- Mumtaz, Moiz M.; Hansen, Hugh; Pohl, Hana R. (2011). "Chapter 3. Mixtures and Their Risk Assessment in Toxicology". In Astrid Sigel; Helmut Sigel; Roland K O Sigel. Metal Ions in Toxicology. RSC Publishing. pp. 61–80. doi:10.1039/9781849732116-00061.
- Committee on Risk Assessment of Hazardous Air Pollutants, Board on Environmental Studies and Toxicology, Commission on Life Sciences, National Research Council (1994), Science and judgment in risk assessment, Washington, D.C: National Academy Press, ISBN 0-309-04894-X, retrieved 27 September 2010
- Barry Commoner. “Comparing apples to oranges: Risk of cost/benefit analysis” from Contemporary moral controversies in technology, A. P. Iannone, ed., pp. 64–65.
- Hallenbeck, William H. Quantitative risk assessment for environmental and occupational health. Chelsea, Mich.: Lewis Publishers, 1986
- Harremoës, Poul, ed. Late lessons from early warnings: the precautionary principle 1896–2000.
- John M. Lachin. Biostatistical methods: the assessment of relative risks.
- Lerche, Ian; Glaesser, Walter (2006), Environmental risk assessment : quantitative measures, anthropogenic influences, human impact., Berlin: Springer, ISBN 3-540-26249-0, retrieved 27 September 2010
- Kluger, Jeffrey (November 26, 2006), "How Americans Are Living Dangerously", Time, retrieved 27 September 2010 Also published as December 4 cover title: "Why We Worry About the Wrong Things: The Psychology of Risk"
- Library of Congress. Congressional Research Service. & United States. Congress. House. Committee on Science and Technology. Subcommittee on Science, Research, and Technology (1983), A Review of risk assessment methodologies, Washington: U.S: report / prepared by the Congressional Research Service, Library of Congress for the Subcommittee on Science, Research, and Technology; transmitted to the Committee on Science and Technology, U.S. House of Representatives, Ninety-eighth Congress, first session
- Deborah G. Mayo. “Sociological versus metascientific views of technological risk assessment” in Shrader-Frechette and Westra.
- Nyholm, J, 2009 "Persistency, bioaccumulation and toxicity assessment of selected brominated flame retardants"
- O’Brien, Mary (2002), Making better environmental decisions: an alternative to risk assessment, Cambridge, Massachusetts: MIT Press, ISBN 0-262-15051-4, retrieved 27 September 2010 Paperback ISBN 0-262-65053-3 templatestyles stripmarker in
|postscript=at position 23 (help)
- Shrader-Frechette, Kristin; Westra, Laura, eds. (1997), Technology and values, Lanham, Maryland: Rowman & Littlefield, ISBN 0-8476-8631-0, retrieved 27 September 2010
- Risk Assessment Worksheet and Management Plan A comprehensive guide to risk assessment in project management, includes template - By John Filicetti
- Guideline from the Dutch Directorate-General for Public Works and Water Management on Performance based Risk Assessment