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Dead or Alive? Factors Affecting the Survival of Victims during Attacks by Saltwater Crocodiles (Crocodylus porosus) in Australia

  • Yusuke Fukuda ,

    Affiliation Northern Territory Department of Land Resource Management, Palmerston, Northern Territory, Australia

  • Charlie Manolis ,

    Contributed equally to this work with: Charlie Manolis, Keith Saalfeld, Alain Zuur

    Affiliation Wildlife Management International Pty. Limited, Karama, Northern Territory, Australia

  • Keith Saalfeld ,

    Contributed equally to this work with: Charlie Manolis, Keith Saalfeld, Alain Zuur

    Affiliation Northern Territory Department of Land Resource Management, Palmerston, Northern Territory, Australia

  • Alain Zuur

    Contributed equally to this work with: Charlie Manolis, Keith Saalfeld, Alain Zuur

    Affiliation Highland Statistics Limited, Newburgh, United Kingdom

Dead or Alive? Factors Affecting the Survival of Victims during Attacks by Saltwater Crocodiles (Crocodylus porosus) in Australia

  • Yusuke Fukuda, 
  • Charlie Manolis, 
  • Keith Saalfeld, 
  • Alain Zuur


Conflicts between humans and crocodilians are a widespread conservation challenge and the number of crocodile attacks is increasing worldwide. We identified the factors that most effectively decide whether a victim is injured or killed in a crocodile attack by fitting generalized linear models to a 42-year dataset of 87 attacks (27 fatal and 60 non-fatal) by saltwater crocodiles (Crocodylus porosus) in Australia. The models showed that the most influential factors were the difference in body mass between crocodile and victim, and the position of victim in relation to the water at the time of an attack. In-water position (for diving, swimming, and wading) had a higher risk than on-water (boating) or on-land (fishing, and hunting near the water's edge) positions. In the in-water position a 75 kg person would have a relatively high probability of survival (0.81) if attacked by a 300 cm crocodile, but the probability becomes much lower (0.17) with a 400 cm crocodile. If attacked by a crocodile larger than 450 cm, the survival probability would be extremely low (<0.05) regardless of the victim’s size. These results indicate that the main cause of death during a crocodile attack is drowning and larger crocodiles can drag a victim more easily into deeper water. A higher risk associated with a larger crocodile in relation to victim’s size is highlighted by children’s vulnerability to fatal attacks. Since the first recently recorded fatal attack involving a child in 2006, six out of nine fatal attacks (66.7%) involved children, and the average body size of crocodiles responsible for these fatal attacks was considerably smaller (384 cm, 223 kg) than that of crocodiles that killed adults (450 cm, 324 kg) during the same period (2006–2014). These results suggest that culling programs targeting larger crocodiles may not be an effective management option to improve safety for children.


Conflicts between humans and wildlife, especially large carnivores such as crocodilians, are becoming a complex conservation challenge worldwide [13]. In the case of crocodilians, they pose a threat to people, livestock or pets in local urban and rural communities [4, 5]. Crocodile attacks result in serious injury or death of a victim in most cases [68], and even crocodilian species that are considered harmless to humans are often viewed with fear. During the 1950s to 1980s, many crocodilian species were threatened due to overexploitation and habitat loss [9], but protection and implementation of effective conservation programs have seen some populations achieve extensive recovery [1012] while others remain endangered [1315]. Conservation actions typically aim to increase depleted crocodilian populations, and the success of such conservation programs invariably leads to an increase in negative interactions between people and crocodilians (human-crocodile conflict; HCC) [16]. Increased HCC may also be related to increasing human populations [17], urbanisation and encroachment by humans into crocodile habitats for tourism, recreation, agriculture or other purposes [18].

While HCC may be an increasing issue, numerous attacks by crocodilians go unreported or are poorly documented in many countries where crocodilians are distributed [16]. Attacks by American alligators (Alligator mississippiensis) are well documented, although many attacks are provoked (e.g. while handling animals) [1921]. Fatal attacks by A. mississippiensis are uncommon, reflecting their smaller size and more docile nature relative to other crocodilian species [22]. More aggressive species such as saltwater crocodiles (Crocodylus porosus) and Nile crocodiles (C. niloticus) [23] are responsible for a much higher mortality of humans in unprovoked attacks. Between January 2008 and October 2013, 528 attacks by C. porosus and 466 by C. niloticus were reported worldwide [24]. A lack of details for increasingly common but poorly documented attacks prevents systematic examination of the incidents, although such evidence-based information is essential for management programs to improve human safety and reduce HCC. While some statistics of crocodilian attacks are reported elsewhere [17, 21, 25, 26], there have been no studies that specifically examined factors affecting the fate of a victim, whether they would be injured or killed during an attack.

Here we examine a 42-year dataset of attacks by C. porosus, the largest [27], most aggressive [23] extant crocodilian species in northern Australia where one of the largest C. porosus populations in the world exists [28]. We hypothesize that the outcome of an attack is affected by certain factors associated with a crocodile, victim, and environment, and identify which of these factors most significantly affects the probability of a victim’s survival. We use the results to inform the key messages for public safety programs, especially for children, the sector considered most vulnerable to fatal attacks in recent years.

Materials and Methods

We conducted this retrospective study under approval by the Northern Territory Department of Land Resource Management and the Parks and Wildlife Commission of the Northern Territory.

Study area

The study area was the tropical coastal regions of northern Australia, consisting of the Northern Territory, Queensland, and Western Australia. The study area covers the natural distribution of C. porosus in Australia (Fig 1) where it inhabits a range of brackish, freshwater and saline water bodies, including beaches, billabongs, floodplains, lagoons, lakes, mangroves, rivers, swamps, and waterholes [29, 30]. The climate is monsoonal with distinct wet (November-April) and dry (May-October) seasons. The annual minimum and maximum temperature typically ranges from 16 to 37°C, and the annual rainfall is 1000–1700 mm [31]. The area covers several towns and townships, including many remote indigenous communities.

Fig 1. Distribution of Crocodylus porosus in the world and Australia.

N is the number of crocodile attacks used in the analysis.

Historical data

We compiled historical records of C. porosus attacks across northern Australia since the species was protected in Western Australia (1970), the Northern Territory (1971), and Queensland (1974), by 1) collating the internal reports and databases kept within government and police agencies, 2) searching media sources, such as archived newspapers and websites, and 3) consulting with independent databases (Y. Fukuda, C. Manolis, unpublished data). We excluded: provoked attacks resulting from voluntary contact with crocodiles such as when catching crocodiles or collecting their eggs; attacks by crocodiles in captivity or escapees from crocodile farms, even if unprovoked; attacks that did not cause any injury (including death), because these attacks were often not reported; and, suspected incidents such as victims going missing without witness or evidence as a crocodile attack. In two cases two victims were involved in an attack by the same crocodile. We treated such a case as two separate attacks because our focus was whether a victim was injured or killed (result) rather than whether a victim was attacked or not (causation). We collected details of each incident, including 1) the date, time, location, and severity of an attack, 2) the total length of the crocodile either measured or estimated, and 3) the age, origin (local or visitor), and activity of the victim at the time of the incident. All of our compiled data, except for confidential information, are accessible in a publicly available database [24] and general trends are summarized by [17]. Personal information on the victims was anonymized and de-identified prior to the analyses.


To examine the consequence of crocodile attacks and their attributes, we modelled the relationships as a binary logistic regression, using Generalized Linear Models (GLM). We coded the crocodile attacks into fatal and non-fatal as a binary response variable (0 = fatal, 1 = non-fatal). From the information we collected for each incident, we prepared explanatory variables that we considered biologically and statistically meaningful for the management of HCC. For example, review of a few fatal cases, for which detailed information was available in coroner’s reports [32], revealed that victims were dragged under the water by a crocodile and the primary cause of their death was drowning. This indicates that the size of a crocodile was an important factor affecting the fate of a victim, but it may also be affected by the size of the victim. To account for this relationship we derived an explanatory variable, the difference in size between a crocodile and victim. We considered the size of both crocodile and human best expressed as body mass (kg) rather than length or height. Although the weight of individual crocodiles involved in incidents is unknown, we estimated it from their length, using a length-weight equation. As a previous conversion equation [30] erroneously overestimates the body mass of a crocodile, we derived a new equation by fitting an exponential function (Y = aXb where Y and X are the body mass and length of a crocodile, respectively) to morphological data of saltwater crocodiles in different sizes reported in previous studies [27, 33]. We estimated the weight of victims from their sex and age, using equations obtained by fitting a quadratic function (Y = aX2 + bX + c where Y and X are the body mass and height of a person, respectively) to the average height and weight of people in Australia (males and females, separately) at the age of 20–80 years [34]. Because the data for the weight of people under 20 years of age were not available for Australia, we used the World Health Organization (WHO) growth reference data for 5–19 years [average height and Body Mass Index (BMI)] [35] to estimate the weight of 5–19 years old (males and females, separately). Although the WHO dataset included countries other than Australia, we assumed that these international estimates would approximate those of Australians. As a result, we derived a continuous explanatory variable, the difference in body mass between a crocodile and the victim (Δ weight).

Other explanatory variables we selected were position of a victim at the time of an incident, alcohol status of a victim (Alcohol), time of an incident (Day/night and Month), presence of a companion directly rescuing a victim from a crocodile (Assistance), age (Age), and origin (Origin) of a victim. Some of these variables were dichotomous variables such as Alcohol (intoxicated or not), Assistance (assisted or not), Day/night (day or night), Origin (local or visitor). Months were grouped into seasons (Season) that consisted of early dry (May-July), late dry (August to October), and wet (November to April) according to [36]. Age was continuous integers. Position of a victim at the time of an incident was a three-level categorical variable (on land, on water, or in water). On-land position represented fishing from the bank, hunting, and other activities such as camping near the water or collecting the water with a bucket. On-water position was boating, and in-water position included diving, swimming and wading.

We followed standard procedures for data exploration [37] and ensured that there were no outlying observations in the variables and also no collinearity between the explanatory variables. We fitted a binary logistic regression to the historical data of crocodile attacks, using the logit link function in the binomial family of GLM [38] using R version 3.1.1. We used the information-theoretic approach [39] to identify a minimum adequate model from a set of a priori models in which each model labelled M1-M10 was associated with a specific hypothesis (Table 1). Our sample size was relatively small (N = 87) and thus we used Akaike Information Criteria corrected for small samples (AICc). We compared the models using AICc and Akaike weight. We assessed the importance of each explanatory variable within the minimum adequate model, using likelihood ratio test. We then predicted the probability that a victim would survive a crocodile attack using the explanatory variables identified as most significant within the model.

Table 1. A priori candidate models of binary logistic regression to explain the fate of a saltwater crocodile attack.

Based on the findings from the analysis, we provided recommendations and management implications to improve public safety and reduce the incidence of HCC, particularly in relation to a risk to children. We highlighted differences between children and adults as a victim of fatal crocodile attacks by comparing the proportion of each group since the first fatal attack on a child (2006), and the average size of crocodiles responsible for these attacks. In this study we defined children as less than 18 years of age.


Between 1970 and 2014, there were 109 unprovoked attacks on humans by C. porosus in the wild across northern Australia. However, 22 records did not have the full detail of the crocodile, incident or victim, and were excluded from the analysis, leaving a full sample size of 87 attacks (27 fatal and 60 non-fatal). The number of attacks generally increased over years (Fig 2).

Fig 2. Number of fatal and non-fatal attacks by Crocodylus porosus divided into 5-year periods between 1970 and 2014 in Australia.

The exponential function fitted to estimate crocodile weight showed a significant fit (a = 2.552 with SE = 0.011, b = 3.321 with SE = 0.002), as did the quadratic functions fitted to estimate human weight (amale = -0.012 with SE = 0.001, bmale = 1.201 with SE = 0.104, and cmale = 60.346 with SE = 2.346, and afemale = -0.008 with SE = 0.001, bfemale = 0.813 with SE 0.113, and cfemale = 52.378 with SE = 2.570). These fitted equations enabled the continuous estimation of Δ weight to be included in the candidate GLM as one of the explanatory variables.

In the set of a priori models, the smallest AICc (51.04) was achieved by M3 (Table 2). Assistance showed a large standard error in relation to the estimated coefficient (Table 3). Further investigation indicated that we had quasi-complete separation due to the Assistance variable. Quasi-complete separation is a relatively unknown feature of Bernoulli GLMs, and it occurs when a predictor (Assistance) separates the binary response variable (Survival) up to a certain high degree [40]. In this case we had the ‘Yes’ level of Assistance (N = 12) exclusively linked to ‘Non-fatal’. With quasi-complete separation, the maximum likelihood estimation of the corresponding parameter does not exist. However, the likelihood ratio test is still valid in quasi-complete separation, and results indicated that Assistance was significant (L = 3.59, df = 1, P = 0.02, Table 4).

Table 2. Model selection values of the candidate models of binary logistic regression.

Table 3. Estimate and standard error (SE) of the explanation variables in the minimum adequate model (M3) of the binary logistic regression.

Table 4. Likelihood ratio test (LRT) of the minimum adequate model (M3) of the binary logistic regression.

As a result we selected the model with Assistance, Δ weight, and Position (M3) as the minimum adequate model. In the selected model, Δ weight showed a much more significant effect on the response than Position while the effect of Assistance was marginal because of the quasi-complete separation (Table 4). Probability of victim’s survival decreased over the consistent range of Δ weight more rapidly in water than on water or on land (Fig 3).

Fig 3. Estimated probability (solid line) that a victim survives a saltwater crocodile attack over the difference in weight between a crocodile and victim in on-land, on-water, and in-water positions.

Grey shade is 95% confidence band and open symbols are the raw binary data of crocodile attacks (N = 87).

The first fatal attack involving a child in Australia occurred in 2006 in the Northern Territory. Since 2006, six out of nine fatal attacks (66.7%) across Australia have involved children. The average size of crocodile involved in fatal attacks on children and adults was 384 cm (223 kg) and 450 cm (324 kg), respectively.


The probability of survival in a crocodile attack may not be decided by a single factor but rather a complex synergy of multiple variables in a unique situation. However, our results indicated that certain variables affected the probability of a victim’s survival more strongly than others. The difference in body mass between crocodile and victim was the most significant factor deciding the fate of a victim. In the in-water position (for diving, swimming or wading) an average-sized person weighing 75 kg would have a relatively high probability of survival (0.81) if attacked by a 300 cm crocodile. The probability of survival becomes lower (0.17) with a 400 cm crocodile, and is greatly reduced (0.02) with a 450 cm crocodile. Even a person with very large body mass (120 kg) would have a very low survival probability (0.05) with a 450 cm crocodile. This is consistent with most attacks involving >450 cm C. porosus resulting in fatalities in east India [41] and the Northern Territory of Australia [17].

The minimum size of C. porosus reported responsible for a fatal attack in Australia is 235 cm, but the victim was a 13-year-old boy whose body mass was small enough for the crocodile to drag him under the water. The probability of survival of children is lower than adults, even with a smaller crocodile. The average size of crocodiles killing children was noticeably smaller (384 cm, 223 kg) than that of crocodiles killing adults (430 cm, 324 kg). This stark contrast highlights the particular vulnerability of children to a crocodile attack. Nevertheless, it should be noted that the size of a crocodile has a much greater influence than that of a victim because crocodile body mass increases exponentially with size (e.g. a 617 cm saltwater crocodile weighed 1075 kg, [27]).

The position of a victim at the time of an incident highlights risks associated with different depth of water and its influence on the survival of the victim is significant. For a 75 kg person being attacked by a 400 cm crocodile, on-water (boating) and on-land (fishing, hunting or other) positions improves the probability of their survival from 0.17 to 0.73 and 0.97, respectively. There were only two fatal cases associated with boating, although boating is a common leisure activity in the study area. It should be noted that the victims of both fatal cases were in small (<350 cm long) boats, including a canoe. The use of boats smaller than 450 cm in habitats containing C. porosus carries a higher risk. If attacked by a 450 cm crocodile, the probability of survival of a victim on water lowers to 0.21, but that of a victim on land remains relatively high (0.73).

Taking together the effect of the body mass and position, our results suggest that the primary cause of death during a crocodile attack is drowning. This is further supported by observations in the Northern Territory that the bodies of some of the victims retrieved within 24 hours after a fatal attack were relatively intact with no major trauma [32] (Dani Best unpublished data). Drowning is also reported as a major cause of death in attacks by A. mississippiensis [20] and C. porosus elsewhere [41]. This contrasts with shark attacks where most victims die of excessive loss of blood [42]. In none of the fatal post-1970 crocodile attacks was there evidence that the victim escaped the attack and died as a result of wounds later. However, in four attacks by C. porosus in Australia before 1873, the victim reportedly escaped from the crocodile, but died later as a result of the wounds received (Charlie Manolis unpublished data). These historical cases are considered to reflect the lack of medical facilities and transport at that time. Improved communication, access to remote locations and medical care has most likely prevented some non-fatal attacks resulting in fatality due to trauma.

Another variable potentially important as shown by the likelihood ratio test was the presence of a second person proving assistance to a victim. All attacks in Australia by crocodiles larger than 400 cm on un-aided victims in the water were fatal [22], but the presence of company increased the survival probability of a victim in most cases by preventing them from being dragged into the water and moving them out of range.

These factors identified as significant provide important implications for the mitigation of HCC. Safety awareness programs need to be designed to target the risk to children from crocodile attack. In five of the six fatal cases involving children, the victim was swimming in deep water, which is the highest risk activity that a person may undertake in crocodile habitat. Given that any waterway within the range of C. porosus in northern Australia should be considered occupied habitat due to the recovery of crocodile populations to near pre-unrestricted hunting levels [12, 30], any swimming activity other than in locations identified “safe” by the authority poses an unacceptable risk. More crocodile attacks tend to happen at the beginning and end of the wet season although fatal cases occur all year around [17]. However, the survival of a victim does not depend on seasons or time of a day (daylight or night). This suggests that extreme caution should be exercised whenever entering crocodile habitats.

Inevitably, following any attack there are calls for culling of the crocodile population to reduce the risk of crocodile attack [43]. If culling were considered a management option, it would most likely target larger animals as these are commonly seen by the public as posing the greatest risk. Intensive culling could reduce the encounter rate with larger individuals. However, the effect of removing dominant individuals on the dynamics of a population is unknown [44]. Removal of large crocodiles may lead to a higher number of subordinate individuals. It should be noted that children would remain vulnerable to smaller crocodiles even if larger crocodiles are removed. To assure safety, any culling program would have to remove all crocodiles from a location, which is not a practical option for management given the high mobility and dispersal of the species across a range of habitats [4547]. Culling programs would not ensure the absence of crocodiles in a targeted area [43, 48] and water-related activities in crocodile habitats would remain unsafe to the public. Within a decade after protection four fatal attacks occurred even though crocodile abundance was very low across northern Australia. Continuous public education campaigns to raise the safety awareness may be a more effective management option to reduce HCC. In many cases, crocodiles attacks can be prevented through such education programs [17].

Crocodile attacks are not a major cause of mortality in Australia. In the study area between 2004 and 2013, 0.02 deaths per 100,000 people (12 in total) were associated with crocodile attacks, in contrast to 8.12 deaths per 100,000 (5432) by road accidents [49]. However, the frequency of crocodile attacks has been increasing [17, 22] and management programs should incorporate evidence-based options to mitigate HCC. Our findings and recommendations may apply to other countries where C. porosus is distributed, as well as to other species known to commonly attack people [16] such as American crocodile (C. acutus), Mugger crocodile (C. palustris) and C. niloticus.


This study was conducted under approval by the Northern Territory Department of Land Resource Management and the Parks and Wildlife Commission of the Northern Territory as part of the Northern Territory Government’s crocodile management program [50]. It did not involve any treatment of live animals. The crocodile management program complies with the Animal Welfare Act [51] and the Code of Practice on the Humane Treatment of Wild and Farmed Australian Crocodiles [52]. We thank K. Appel, T. Nichols, D. Best and J. Papple at the Parks and Wildlife Commission of the Northern Territory, G. Lindner at Parks Australia, K. Boddington, S. Bradley and M. Casey at the Northern Territory Police, and many others from various organisations for their assistance in compiling historical crocodile attack data. G. Edwards and A. Fisher provided comments on the manuscript.

Author Contributions

Conceived and designed the experiments: YF AZ. Performed the experiments: YF. Analyzed the data: YF CM KS AZ. Contributed reagents/materials/analysis tools: YF CM AZ. Wrote the paper: YF CM KS AZ.


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