The United Nations (UN) produces glossaries to standardize vocabulary for policy and practice. Researchers and others frequently adopt these glossaries to ensure that science is useful and useable in practice. For disaster risk science, two UN secretariats have been the foci. First, from 1990 to 2000, the secretariat of the UN International Decade for Natural Disaster Reduction (IDNDR) was the main one and it produced a glossary of agreed terms (UNDHA 1992). Then, at the end of IDNDR, the secretariat for the UN International Strategy for Disaster Reduction (ISDR) was founded and was later renamed the UN Office for Disaster Risk Reduction, but retained the ISDR acronym.
For ISDR (see UNISDR 2015a), the agency’s first main glossary was published in 2002 but was superseded following feedback that led to a revised version (UNISDR 2004). Major revisions were published after five years (UNISDR 2009) and 13 years (UNISDR 2017). These four glossaries form the core material for examining the progression of key definitions (see also UNISDR 2015a). Many publications from IDNDR and ISDR included their own glossary, either repeating IDNDR’s or ISDR’s main terms or including specialized vocabulary related to the topic under discussion, from hydrology to warning systems. Other UN-related glossaries such as Comité National Japonais (1994) provide only translations of terms without providing definitions.
Hazard
The definition of “hazard” from UNDHA (1992, p. 44) is “A threatening event, or the probability of occurrence of a potentially damaging phenomenon within a given time period and area.” The focus on “event” or “phenomenon” would seem to exclude many hazardous processes, such as creeping environmental changes or creeping environmental processes/phenomena, defined as slow-moving changes to the environment cumulating in large-scale problems that are often not noticed or acknowledged until a threshold has been passed, leading to a disaster or crisis (Glantz 1994, 1999).
The same issue arises for the UNISDR (2004, vol. II, p. 4) definition of “hazard” as “A potentially damaging physical event, phenomenon or human activity that may cause the loss of life or injury, property damage, social and economic disruption or environmental degradation.” Nevertheless, the inclusion of “activity” moved from a delineated notion such as “event” or “phenomenon” to accepting that not all hazards clearly manifest “within a given time period and area” as in UNDHA (1992). Removing concepts of space and time from the definition generalizes it, acknowledging that hazards are diverse and might not always be easy to parameterize.
UNISDR (2009, p. 17) retained the same basic concepts and almost the same text, with “hazard” defined as “A dangerous phenomenon, substance, human activity or condition that may cause loss of life, injury or other health impacts, property damage, loss of livelihoods and services, social and economic disruption, or environmental damage.” The addition of “condition” further strengthens the definition by emphasizing that not all hazards are easily delineated events or phenomena.
This point became even more explicit in UNISDR (2017, online) defining “hazard” as “A process, phenomenon or human activity that may cause loss of life, injury or other health impacts, property damage, social and economic disruption or environmental degradation.” Here, the word “process” is included to support hazards being dynamic through time and over space, such as creeping changes. The word “dangerous” is excluded, perhaps recognizing that “danger” and “hazard” have differences in English.
One component retained throughout the definitions is that the hazard’s origin can be anthropogenic. This aspect is implicit with UNDHA (1992), but explicit in the three definitions from UNISDR (2004, 2009, 2017). This point is important in understanding from where disasters arise because some environmental processes and phenomena have hazardousness augmented due to human interventions. For river floods, dredging and building levees can increase parameters such as depth and speed, making any flood more hazardous, as witnessed in parts of the Mississippi River basin (Criss and Shock 2001). Many earthquakes are caused by human action including fracking, reservoirs, groundwater extraction, fossil fuel extraction, and nuclear tests (Ellsworth 2013). Urbanization affects wind speed and air temperature, exacerbating heat wave hazards in particular (Clarke 1972). The definitions of “hazard” accept that hazards might be entirely from nature (for example, a meteorite (unless it becomes a weapon in future wars)), entirely from human activity (for example, pollution), or a combination (for example, flood depth and speed augmented by channeling rivers).
The definitions also speak to the social construction of hazard viewpoint, in that some hazards might not be hazardous unless they interact with society, while hazardousness can be a function of this interaction. Rain is an essential environmental phenomenon for human and other life. Rain coming into a house through an open window has hazardous properties when falling on carpets and computers. If rain enters an open window and causes computer and carpet damage, is the hazard the rain, the open window, or the decision to leave damageable property beside an open window when it might rain? The carpet and computer themselves represent vulnerability (or exposure), discussed in the next section.
By analogy, if a housing development without earthquake resistance measures is approved in a known seismic zone, is the hazard the earthquake fault, the earthquake, the lack of seismic resistance measures in the buildings, or the decisions for planning, development, and construction? Again, the actual buildings represent vulnerability (or exposure). By analogy, a person falling off the roof of a tall building without any mitigating measures reveals gravity followed by the consequences of hitting the ground at a high speed. Is the hazard gravity, a hard landing, falling off the roof, a tall building, the lack of mitigating measures, or a combination? As with rain being useful, so is gravity and perhaps even earthquake faults in terms of bringing water to the surface in arid regions (Jackson 2001). For the latter, is the earthquake fault a hazard in itself or does hazardousness require an earthquake? Could tectonic uplift from an earthquake creating land from underwater be considered usefulness or a resource, keeping in mind that earthquakes also subside land below water? The answers to these questions more or less come down to definitions and philosophical renderings, meaning in effect that hazards and hazardousness are largely social constructions.
Yet the environmental phenomena or processes—such as rain, gravity, earthquake faults, and earthquakes—have materialities, energies, and forces irrespective of potentially being hazards to and resources for society simultaneously. They are resources for society only because people use them, such as for drinking and irrigation. They might sometimes be hazards because human activity makes them hazardous to society, just as Hewitt (1997, p. 68) states for biological hazards associated mainly with human activity that “it seems misleading to call them ‘natural’ hazards.” Even where some phenomena and processes originate in the environment, human activity can make them “unnatural hazards.” That is, they are neither natural hazards nor environmental hazards, instead being phenomena with properties that society can make hazardous.
Vulnerability
UNDHA (1992, p. 77) defines “vulnerability” as “Degree of loss (from 0% to 100%) resulting from a potentially damaging phenomenon.” This definition assumes that vulnerability is calculable and quantifiable, despite much earlier work describing vulnerability as having qualitative aspects and intangible elements (Lewis 1979; Hewitt 1983; see also the discussion of “(Disaster) Risk” in Sect. 2.3).
UNISDR (2004, vol. II, p. 7) adopts many of these scientific lessons, diverging from UNDHA (1992), by defining “vulnerability” as “The conditions determined by physical, social, economic, and environmental factors or processes, which increase the susceptibility of a community to the impact of hazards.” UNISDR (2009, p. 30) then defines “vulnerability” as “The characteristics and circumstances of a community, system or asset that make it susceptible to the damaging effects of a hazard.” UNISDR (2017, online) is similar, but much wordier, by defining “vulnerability” as “The conditions determined by physical, social, economic and environmental factors or processes which increase the susceptibility of an individual, a community, assets or systems to the impacts of hazards.” All three effectively define “vulnerability” with respect to susceptibility but do not define “susceptibility” or variations.
The most prominent difference amongst the UNISDR definitions is that UNISDR (2009) identifies “characteristics and circumstances” while UNISDR (2004) and UNISDR (2017) identify “conditions.” The connotation of “condition” tends to be with respect to mode or state; that is, a snapshot approach to characterize the entity under scrutiny. Aspects of circumstances and reasons for displaying observed conditions might form a secondary layer to the word’s meaning, although this part is more implicit than explicit. This fixed picture view of vulnerability through “conditions” contrasts with “characteristics and circumstances” that directly encompass a snapshot (characteristics) and reasons for those characteristics appearing (circumstances).
The importance of looking beyond a snapshot is demonstrated through understanding vulnerability as a process (Lewis 1979, 1999). The vulnerability process reveals two important points from understandings of vulnerability that are accepted by UNISDR (2009) and then removed from UNISDR (2017) in retrogressing back to UNISDR (2004). First, examining only the current state cannot provide a comprehensive view of vulnerabilities. Part of vulnerability is contextual in relation to aspects around and influencing what is vulnerable, but not necessarily within any specific element. The word “circumstances” indicates that any element must be examined beyond the element itself to understand vulnerability fully.
Second, vulnerability embraces a temporal dimension. Vulnerability is not simply what is observed at the current moment. Vulnerability must also establish how and why the current state was reached: What processes led to the characteristics and circumstances, why was the situation created, what could have happened instead, and what are potential future pathways? UNISDR (2009, p. 30) comments after the definition that “Vulnerability varies significantly within a community and over time,” accepting part of the spatial and temporal contexts of vulnerability as articulated by the vulnerability process (Lewis 1979, 1999; Hewitt 1983, 1997; Wisner et al. 2004). These points are missing from UNISDR (2004, 2017).
Both the 2004 and 2017 definitions, however, accept that processes are important as inputs into the condition of vulnerability. This process idea could have been integrated fully into defining vulnerability, given the long-standing science on this topic—especially when the 2009 definition did include the process idea to some degree.
Another ambiguity emerges with respect to the term “exposure.” Neither UNDHA (1992) nor UNISDR (2004) include the term “exposure.” UNDHA (1992) lists “exposure time” in reference to seismic risk, a different concept. In defining “risk,” UNISDR (2004, vol. II, p. 6) notes “Conventionally risk is expressed by the notation Risk = Hazards × Vulnerability. Some disciplines also include the concept of exposure to refer particularly to the physical aspects of vulnerability.”
UNISDR (2009, p. 15) welcomes “exposure” as a new term now relevant for disaster risk science with the definition “People, property, systems, or other elements present in hazard zones that are thereby subject to potential losses.” For “vulnerability,” UNISDR (2009, p. 30) explains in a post-definition comment, “This definition identifies vulnerability as a characteristic of the element of interest (community, system or asset) which is independent of its exposure. However, in common use the word is often used more broadly to include the element’s exposure,” thereby highlighting the ambiguity of separating vulnerability and exposure.
This nuancing disappears from UNISDR (2017), which presumably assumes that vulnerability and exposure are accepted as being separate and ostensibly independent. For UNISDR (2017, online), “exposure” is “The situation of people, infrastructure, housing, production capacities and other tangible human assets located in hazard-prone areas” with an annotation supposing that exposure, vulnerability, and capacity are quantitative and to be used for calculating quantitative risks.
The idea of exposure could potentially be complementary to vulnerability in that exposure describes what could be harmed by hazards while vulnerability explains why it is in harm’s way. The changes in defining “vulnerability” to diminish thoughts on the “process” might obviate the need for two different terms. From UNISDR’s (2017) definitions, it is not clear that the actual elements existing are separable from those elements’ conditions. The elements and their conditions could easily be combined into a single concept, exactly as UNISDR’s (2004, 2009) definitions do, with exposure being part of vulnerability, thus acknowledging interaction between elements and their conditions.
Buildings can shield each other from hazards. Landslide, flood, and wind parameters frequently diminish after encountering, damaging, or destroying a structure, reducing the hazard’s impact on the structures behind. Whether this situation means that fewer elements are subject to certain hazard parameters (exposure) or that conditions or potential damage differ (vulnerability) is semantics. Conversely, buildings might augment hazard-related damage. Many high-rises in Tokyo are designed to sway during an earthquake in order to avoid toppling. If the earthquake parameters experienced by adjacent high-rises are sufficient, then possibilities might exist for building collisions. Similarly, a collapsing building can damage structures nearby, weakening their ability to withstand subsequent hazards. Whether these situations mean that more elements are subject to certain hazard parameters (exposure) or that conditions or potential damage differ (vulnerability)—or that exposure and vulnerability augment hazard parameters—is again semantics.
Definitions much more rigorous than those supplied by UNISDR (2009, 2017) might be able to separate completely exposure and vulnerability. This separation would be artificial and is not really necessary considering that the point of developing these terms is to understand why disasters occur and to deal with them. A tenet within disaster research has long been that disasters occur due to long-term processes that prevent people from improving their situations, so they end up being adversely affected by events and processes that become hazardous (Lewis 1979, 1999; Hewitt 1983, 1999; Wisner et al. 2004). Interactions amongst conditions, characteristics, and circumstances are as important to disaster-related outcomes as the conditions, characteristics, and circumstances themselves, blending and deepening the ideas behind the definitions of “vulnerability” and “exposure.”
(Disaster) Risk
In UNDHA (1992, p. 64), risk is defined as “Expected losses (of lives, persons injured, property damaged, and economic activity disrupted) due to a particular hazard for a given area and reference period. Based on mathematical calculations, risk is the product of hazard and vulnerability.” UNDHA (1992) does not define “disaster risk,” but uses the phrase once (p. 18) in defining “acceptable risk” as the “Degree of human and material loss that is perceived by the community or relevant authorities as tolerable in actions to minimize disaster risk.”
UNISDR (2004) also does not define “disaster risk.” “Risk” is “The probability of harmful consequences, or expected losses (deaths, injuries, property, livelihoods, economic activity disrupted or environment damaged) resulting from interactions between natural or human-induced hazards and vulnerable conditions” (UNISDR 2004, vol. II, p. 7). A significant shift is evident from UNDHA (1992). “The probability of harmful consequences” is put on equivalent terms with “expected losses” for which examples are provided. Rather than assuming that risk is calculated as a product, as in UNDHA (1992), risk combines hazard and vulnerability for UNISDR (2004), but how this combination occurs is left open.
UNISDR (2009, p. 25) defines risk as “The combination of the probability of an event and its negative consequences.” “Disaster risk” is defined separately as “The potential disaster losses, in lives, health status, livelihoods, assets and services, which could occur to a particular community or a society over some specified future time period” (pp. 9–10). In effect, “disaster risk” is taken to mean “potential disaster losses,” which could be quantified or not.
UNISDR (2017) no longer presents a separate entry for “risk.” “Disaster risk” becomes much more complicated: “The potential loss of life, injury, or destroyed or damaged assets which could occur to a system, society or a community in a specific period of time, determined probabilistically as a function of hazard, exposure, vulnerability and capacity” (UNISDR 2017, online). “Disaster risk” is still, effectively, potential disaster losses, with a two-part specification. First, risk is defined probabilistically only, eliminating any qualitative approaches. Second, the concepts of “hazard, exposure, vulnerability and capacity” are re-introduced/introduced explicitly into the definition. The apparent separation of exposure, vulnerability, and capacity is not especially in line with earlier discussions (Sect. 2.2). Furthermore, it is unclear whether or not these four variables must be independent or, as other literature indicates, interact.
The change from UNDHA (1992) to UNISDR (2004) removed the assumption of calculation and quantification. This approach is retained implicitly by UNISDR (2009), but the assumption of quantification is reintroduced by UNISDR (2017). UNISDR’s (2009, 2017) definitions of “disaster risk” are generally in line with wider literature, but UNISDR (2009) was far more encompassing than UNISDR (2017) by not forcing quantification and by keeping the vocabulary more clear-cut than UNISDR (2017). The wider literature regarding the definition of “disaster risk” from previous decades of disaster risk science has also not always assumed calculation or quantification and has generally fallen into two principal categories.
First, as with UNDHA (1992), disaster risk is a combination or function of hazard and vulnerability, most notably variations of the mathematical product of hazard times vulnerability. Wisner et al. (2004, p. 45) refer to disaster risk = hazard × vulnerability as a “pseudo-equation” suggesting it as a mnemonic rather than as a meaningful calculation, which matches UNISDR (2004). Wisner et al. (2004) also introduce “capacity” and “mitigation” as reducing disaster risk in the pseudo-equation. Other terms added to the basic hazard-vulnerability product, as an equation and as a mnemonic, are from De La Cruz-Reyna (1996) who places “value (of the threatened area)” in the product, which is then divided by “preparedness,” while Granger et al. (1999) add only “elements at risk” into the product. Peduzzi et al. (2009) apply the latter formulation by specifying “elements at risk” as the number of people experiencing a hazard. In these formulations, “elements at risk” seem to match “exposure,” distinct from vulnerability, as discussed in Sect. 2.2.
The second category, as with UNISDR (2009), explains disaster risk as the combination (sometimes as a product) of the probability of an event and the consequences of the event. For example, it is applied to fire by Hurley (2015), but critiqued by Kaplan and Garrick (1981) who prefer “probability and consequence” rather than “probability times consequence.” “Probability-consequences” parallels “hazard-vulnerability” with “probability” typically interpreted as “probability of a hazard” and “consequences” matching the damage or losses that result or could result due to the hazard. Smith (2013, p. 11) thus concatenates the two definitional groupings by suggesting “disaster risk” as “the likely consequence…the combination of the probability of a hazardous event and its negative consequences.”
The core concept within the definition of “disaster risk” does not really change over time or across different references, referring to overlapping notions of either: (1) possible losses from a hazard; or (2) potential adverse consequences in a disaster. The power of this definition is that various calculative forms are possible along with qualitative interpretations that are precluded by UNISDR’s (2017) definition. Intangible, non-quantitative, non-calculative losses and consequences have long been known to arise from disasters (Butler and Doessel 1980). Damage to natural and cultural heritage exemplify these losses with examples being irreplaceable photos or documents, cemeteries, and species extinctions. Similarly, while casualties are easily quantifiable by counting, the numbers cannot capture the true experience of losing a loved one or dealing with life-changing injuries, so these consequences are sometimes considered to be intangible (Butler and Doessel 1980).
Disaster Risk Reduction (DRR) and Disaster Risk Management (DRM)
UNDHA (1992) does not include the phrase “disaster risk reduction,” although it was entrenched in the literature at the time (Davis and Lohman 1987; Johnson 1987; Vermeiren 1993). Similarly, “disaster risk management” is absent from UNDHA (1992) despite it being used in the field at least a decade before (Reams and Surrency 1982).
UNISDR (2004, vol. II, p. 3) defines “disaster risk management” as “The systematic process of using administrative decisions, organization, operational skills and capacities to implement policies, strategies and coping capacities of the society and communities to lessen the impacts of natural hazards and related environmental and technological disasters. This comprises all forms of activities, including structural and non-structural measures to avoid (prevention) or to limit (mitigation and preparedness) adverse effects of hazards.” This definition is heavily filled with jargon, yet it is forthright that DRM is a process involving human actions to deal with hazards and disasters.
“Disaster risk reduction (disaster reduction)” is defined by UNISDR (2004, vol. II, p. 3) as “The conceptual framework of elements considered with the possibilities to minimize vulnerabilities and disaster risks throughout a society, to avoid (prevention) or to limit (mitigation and preparedness) the adverse impacts of hazards, within the broad context of sustainable development.” This definition is quite clear and sensible, especially in terms of highlighting the need to minimize vulnerabilities while placing DRR within the broader construct of sustainable development. Mentioning “adverse impacts of hazards” recognizes that hazards do not inevitably have only negative consequences—which sits directly within the ethos of UNISDR’s (2004) “living with risk” title. DRR and DRM are delineated by the former being a framework and the latter being actions, although the goal is subtly dissimilar: “minimise vulnerabilities and disaster risks” compared to “lessen the impacts” of hazards and disasters.
Having dropped “disaster reduction,” UNISDR (2009, pp. 10–11) defines “disaster risk reduction” as “The concept and practice of reducing disaster risks through systematic efforts to analyse and manage the causal factors of disasters, including through reduced exposure to hazards, lessened vulnerability of people and property, wise management of land and the environment, and improved preparedness for adverse events.” This definition has a tautology in “disaster risk reduction” meaning “reducing disaster risks.” Otherwise, it is impressive in its elegance and directness, focusing on understanding and addressing “causal factors” while covering all hazards and all vulnerabilities. The examples given of actions strike at the long-established root causes of vulnerabilities and hence disasters. This definition captures the baseline of where disasters arise from, how they should be framed, and how they could be tackled (O’Keefe et al. 1976; Torry 1979; Hewitt 1983, 1997; Lewis 1999; Wisner et al. 2004).
Meanwhile, “disaster risk management” (UNISDR 2009, p. 10) is “The systematic process of using administrative directives, organizations, and operational skills and capacities to implement strategies, policies and improved coping capacities in order to lessen the adverse impacts of hazards and the possibility of disaster.” It seems as if DRM emerges as the operationalization of DRR, especially given that the goal is “to lessen” rather than “to manage.”
UNISDR (2017, online) defines “disaster risk reduction” as “Disaster risk reduction is aimed at preventing new and reducing existing disaster risk and managing residual risk, all of which contribute to strengthening resilience and therefore to the achievement of sustainable development.” An annotation reads “Disaster risk reduction is the policy objective of disaster risk management, and its goals and objectives are defined in disaster risk reduction strategies and plans.” Consequently, in contrast to UNISDR (2009), DRR seemingly emerges from DRM. “Disaster risk management” from UNISDR (2017, online) is “the application of disaster risk reduction policies and strategies to prevent new disaster risk, reduce existing disaster risk and manage residual risk, contributing to the strengthening of resilience and reduction of disaster losses.” Its annotation is “Disaster risk management actions can be distinguished between prospective disaster risk management, corrective disaster risk management and compensatory disaster risk management, also called residual risk management.”
The immediate concern with both these definitions is the amount of other nomenclature, such as “residual risk” and “resilience.” The annotation for DRM includes further terms, namely “prospective,” “corrective,” and “compensatory” DRM, without similar differentiations amongst different forms of DRR. It is laudable that DRR continues to be directly connected to the long-standing sustainable development agenda and, seemingly, is placed directly within it. It loses clarity given that the relationship between resilience and sustainable development has long been explored without resolution or consensus (Gardner 1989; Tarhan et al. 2016).
In the literature, an evolution has occurred in the use of DRR, DRM, and related terms. Initially, these terms were not formally defined in the glossaries. Later, they achieved formal recognition and relatively straightforward definitions. With formal acceptance came increasingly complicated and jargon-filled definitions. It also seems that relationships amongst DRR/DRM terms are set by definitions, rather than any innate or natural relationship existing. Permitting definitions to dictate connections amongst the vocabulary is advantageous in delineating solid, verifiable starting points for each term. When substantive definitional changes occur altering the connections and relationships, as in the change from UNISDR (2009) to UNISDR (2017), confusion can result when earlier documents are rendered obsolete merely due to a choice of words rather than from any inherent meanings.