Nipah virus (NiV) (genus Henipavirus) is a zoonotic virus that first emerged in Malaysia in 1998. It caused a large outbreak of respiratory disease in pigs, and severe encephalitis in humans with a high mortality rate (∼40%) [Reference Chua1]. Seasonal outbreaks of NiV have also been reported in Bangladesh with ∼75% mortality rates and some human-to-human transmission, highlighting the threat NiV poses to public health [Reference Hsu2–Reference Gurley4].
Worldwide there are about 65 recognized species of bats in the genus Pteropus. Flying-foxes (genus Pteropus) are considered the reservoir hosts for NiV [Reference Eaton5, Reference Chua6], with spillover into pigs and humans thought to occur through close contact with infected body fluids [Reference Chua1, Reference Hsu2, Reference Epstein7]. Widespread evidence exists for infection of NiV or related henipaviruses in flying-foxes which span tropical and subtropical regions of the Western Pacific to the east coast of Africa [Reference Calisher8]. Although NiV disease has not been reported in Australia, evidence of NiV infection has been found in flying-foxes in some of Australia's closest neighbours including Sumatra, Java and Timor-Leste [Reference Breed9, Reference Sendow10]. Additionally, of the four flying-fox species found on the Australian mainland, two (Pteropus alecto and P. conspicillatus) are also found in Papua New Guinea (PNG) and Indonesia [Reference Field11]. P. alecto has expanded its range southwards along the east coast of Australia, from the Mary River in the 1930s [Reference Ratcliffe12] to Sydney in 2007 [Reference Roberts, Law, Eby, Lunney and Lumsden13], a distance of more than 950 km. These facts, and the ability of individual flying-foxes to fly long distances, provide an opportunity for pathogens to enter Australia through flying-fox movements [Reference Breed14].
In this study we used the Office International des Epizooties (OIE) risk assessment framework  to assess the risk of NiV establishing in Australian flying-fox populations through flying-fox movements from neighbouring regions of the eastern archipelago of Indonesia (Lesser Sunda and Molucca Islands), Timor-Leste and PNG, referred to as ‘pre-border’ regions in this study. The qualitative approach was chosen primarily because quantitative data is sparse, and a qualitative approach provides a transparent and systematic means for identifying the basic model structure, key input parameters, and areas of data scarcity [Reference Clough, Clancy and French16, Reference Peeler17].
Events surrounding the emergence of new diseases such as NiV are typically highly uncertain. In this study there are a number of uncertainties identified in the risk pathway. Formal expert elicitation provides a structured and transparent method to address these uncertainties and data gaps [Reference Knol18]. Generally, a group of experts tend to provide better estimates than the average individual expert [Reference Mosleh, Bier and Apostolakis19, Reference Van der Fels-Klerx20]. The modified Delphi method is an elicitation technique designed to capture the judgement of multiple experts without the biases and heuristics that can result from group discussions [Reference Mosleh, Bier and Apostolakis19, Reference Larreche and Moinpour21–Reference O'Hagan24]. However, as consensus is not necessarily achieved with this technique, further mathematical combination is needed after the interactive process.
Conflicting opinion exists in the literature on which method performs best when combining expert judgements. A number of methods have been described, and Knol et al. [Reference Knol18], Clemen & Winkler [Reference Clemen and Winkler25], and O'Hagan et al. [Reference O'Hagan24] provide good reviews. Simple averaging techniques for combining expert opinion perform well in comparison to more complex techniques [Reference O'Hagan24, Reference Clemen and Winkler25]. The objectives of this study were to qualitatively assess the risk of NiV establishing in Australian flying-fox populations through the movements of pre-border flying-foxes using literature and expert opinion where data gaps exist; and to compare five methods of combining expert opinion and use these as inputs in the model to assess changes in overall risk.
Risk assessment model
The OIE framework for import risk analyses was used for this assessment . It is divided into ‘release’, ‘exposure’, and ‘consequence’ assessments, where ‘release’ refers to the probability of entry of NiV into Australia via flying-foxes, ‘exposure’ considers the probability Australian flying-foxes are exposed to NiV, and ‘consequence’ considers the probability NiV establishes itself in Australian flying-fox populations. These are subdivided into events in a pathway, where each event is conditional on the previous event occurring (Fig. 1).
The probability of an event occurring was defined in qualitative terms on a linear six-level scale, ranging from negligible to high probability (Table 1). This was derived from the scale used by the OIE and that used by experts in the expert opinion workshop. Since events described in this model are uncommon, more precision was required at the lower end of the scale, so six levels were used.
Due to the conditional nature of each event occurring in the pathway, probabilities for each event must be sequentially multiplied together for the final probability estimation. However, in steps 2 (2a and 2b) and 3 (3a and 3b), events are independent of each other, so must be ‘added’ together. A matrix was used to determine the result of multiplying two qualitative probabilities together following the methods of a previous assessment which uses the fact that probabilities lie between 0 and 1, so the result of multiplying two probabilities together cannot be higher than the lower probability [Reference Scholz and Hansmann26, Reference Gale27] (Table 2).
Input data were derived from the scientific literature and expert opinion. Expert opinion was elicited through a two-stage modified Delphi technique comprising a workshop and a questionnaire completed in pre-workshop (stage 1) and post-workshop (stage 2). This technique was used to preserve independence and anonymity of the experts through the questionnaire, and exploit the benefits of group interactions with the workshop [Reference Mosleh, Bier and Apostolakis19, Reference Gustafson22, Reference Riggs23, Reference Normand28]. The workshop was run during a 2-day Henipavirus Research Adoption Forum in Australia on 16–17 July 2007 with participants including leading scientists in the area from Australia, Bangladesh, Malaysia and the USA. The 2-h workshop was led by a professional facilitator and started with a short background to the topic followed by discussion on each of the steps in the risk pathway. Only post-workshop results were used in the analysis.
A multi-disciplinary group of nine experts were selected from the research adoption forum to provide expertise in flying-fox ecology, virology, disease ecology, epidemiology, and risk assessment. All experts that were asked to participate in the workshop completed the exercise. Experts gave probability and uncertainty scores for ten questions on NiV introduction into Australia through flying-fox movements (Tables 3 and 4). Only responses from questions directly relevant to the model were used in this study.
Expert opinion combination
No single ideal technique is described for combining experts' judgements. In this study we used five different averaging methods for combining experts' probability scores: median, mean, uncertainty-weighted median, expertise-weighted median and linear opinion pooling (LOP). The median was used as the reference combination method as it is simple and robust [Reference Larreche and Moinpour21, Reference Scholz and Hansmann26, Reference Ariely29]. The first two approaches are simple central tendency measures while the last three methods provide weighting of the responses. Weighting was used to assess the effects of ‘better’ expert opinion on risk outcomes. LOP [Reference Clemen and Winkler25] is a weighted linear average of each expert's probability distribution. Probabilities were provided by experts as scores rather than distributions. Higher weights were given to expert responses when experts were more certain of their answer. For example, in question 2 of the questionnaire the sum of the experts' uncertainty scores was 31. Expert 1 had an uncertainty score of ‘4’ and a probability score of ‘2’. Thus the weighting for expert 1 would be 4/31 and their probability estimate would be 4/31 × 2. Figures were rounded to the nearest whole number.
Similarly, for the uncertainty-weighted median and expertise-weighted median methods, experts' responses were weighted higher if they were more certain of their estimates or were regarded as having more expertise, respectively. Expertise was weighted according to their level of background knowledge and involvement in NiV and flying-fox research. Three categories were used, with the lowest weight allocated to someone who had expertise in a relevant discipline but no direct involvement with NiV or flying-fox research; the middle category was for experts who had worked on NiV or flying-foxes and contributed fewer than 20 peer-reviewed papers in the area; and the top category was for experts who had contributed over 20 peer-reviewed papers on NiV or flying-foxes and worked extensively in the area. The allocation of weights to each expert follows the same technique as described by Gale et al. [Reference Gale27].
The final probability scores were integrated into the model where expert opinion was required (P 2a, P 3a, P 4, P 5).
Uncertainty in the input parameters was categorized with the scale used in Table 5. When combining uncertainty of the risk estimates the highest uncertainty score was used, based on a precautionary approach .
Two approaches were used to assess uncertainty in the model. To assess the effect of changing the combination method on the model, outputs of five methods of combining expert opinion were compared in the model. The baseline model used the median combination method, and was compared with the other four combination methods to assess changes in overall risk.
To assess the effects of changes to highly uncertain events on the model outputs, baseline probability estimates for the highly uncertain events (P 2a, P 3a, P 4, P 5) were changed consecutively, so that the baseline probability estimates for a single event were increased and decreased by one qualitative category while keeping other parameters constant.
Probability a flying-fox is infected in a pre-border region (P 1 )
The prevalence of NiV in bats and flying-fox ecology will influence the probability a flying-fox is infected in pre-border areas. Evidence for NiV has been found in flying-foxes in Malaysia, Thailand, Cambodia and Indonesia (Java and Sumatra) [Reference Chua6, Reference Sendow10, Reference Wacharapluesadee30, Reference Reynes31]. In addition, evidence for NiV in flying-foxes has been found in the pre-border regions considered in this study: PNG, Indonesia (Sumba) and Timor-Leste [Reference Breed9]. Snary et al. [Reference Snary32] provide a list of seroprevalence estimates of henipaviruses in flying-foxes from nearby countries to Australia. However, the extent of NiV infection in flying-foxes in pre-border regions is largely unknown. Flying-foxes can fly considerable distances and have been observed, via telemetry studies, to travel between Malaysia and Sumatra [Reference Daszak, Collinge and Ray33] and PNG and Queensland [Reference Breed14]. There also appears to be a reasonable level of connectivity between bats in pre-border regions since genetic studies of P. vampyrus show high levels of gene flow between populations in Indonesia, Malaysia and Timor-Leste [Reference Olival34]. Given these long-distance movements and connectivity, it is possible that NiV could spread between flying-fox populations in pre-border regions. Indeed, in Australia Hendra virus (HeV) is found in all flying-fox species which have overlapping ranges along the east coast [Reference Field11]. Consequently P 1 was estimated to be ‘medium’.
Probability a flying-fox enters Australia (P 2 )
Flying-fox entry into Australia is considered from two routes.
Probability a flying-fox arrives in Australia via non-migratory routes (P 2a )
The ‘unintentional’ entry of flying-foxes moving beyond the recognized species distribution can occur through episodic climatic events such as storms and strong winds. Severe storms are not uncommon throughout the range of flying-foxes, and periodically affect island fauna in the Asia Pacific [Reference Robertson, Wilson and Graham35]. For example, P. scapulatus was found in New Zealand after storm activity, 1600 km from its residence in Australia [Reference Daniel36]. From these observations and expert opinion (question 1), P2a was estimated to be ‘low’.
Probability a flying-fox migrates to Australia (P 2b )
The only potential migratory route considered for flying-foxes into Australia is across the Torres Strait from PNG to Cape York, a distance of 150 km. The distances between Australia and the Lesser Sunda Islands (Timor-Leste and Indonesia) are several hundred kilometres further and there is currently no evidence of bats regularly travelling between these islands and Australia.
Flying-foxes can migrate long distances, and satellite telemetry studies of P. alecto have shown movement occurs across the Torres Strait [Reference Breed14]. Therefore P 2b was estimated to be ‘high’.
Probability a flying-fox contacts Australian flying-foxes (P 3 )
Flying-foxes must survive and contact local flying-foxes, so ecology, entry route into Australia, and food sources will influence the probability a flying-fox will contact resident Australian flying-foxes. Flying-foxes are gregarious by nature and are known to share camps with other flying-fox species where their distributions overlap [Reference Field11]. Flying-foxes also time large-scale movements with the seasonal availability of food [Reference Pierson, Rainey, Wilson and Graham37, Reference Palmer and Woinarski38], so when food is abundant, increased contact rates are expected between individuals.
Probability a ‘non-migratory’ flying-fox contacts Australian flying-foxes (P 3a )
In northern Australia, a relatively undisturbed ecosystem provides a reasonable food supply for flying-foxes, so large and relatively stable camps of P. alecto and P. scapulatus exist [Reference Vardon and Tidemann39, Reference Hall and Richards40]. Since the likelihood of survival and contact is difficult to determine expert opinion (question 3) was needed, and P 3a was estimated to be ‘low’.
Probability a ‘migratory’ flying-fox contacts Australian flying-foxes (P 3b )
Given the short distance and interceding islands en route to Australia, survival is likely. It is assumed migratory flying-foxes are somewhat familiar with local habitats and bat populations. Indeed, P. alecto have been observed roosting with P. conspicillatus in north Queensland and with P. neohibernicus in PNG [Reference Breed14]. Therefore, P 3b was estimated to be ‘medium’.
Probability flying-fox transmits NiV to Australian flying-foxes (P 4 )
Transmission requires excretion of virus from the infected flying-fox to a susceptible host. Although transmission of NiV among bats is poorly understood, transmission in other species is believed to be through close contact with infected body fluids or tissues [Reference Fogarty41]. NiV has been isolated from urine, uterine and kidney tissues in bats [Reference Middleton42]. Australian flying-foxes are susceptible to NiV as experimental infection shows episodic low-level viral excretion [Reference Middleton42]. This may be sufficient to maintain NiV infection through aerosol transmission of urine particles in high-density roosts, or directly through contact with urine used for grooming [Reference Hall and Richards40]. The high seroprevalence of HeV in Australian flying-foxes suggests highly efficient transmission, or that infection is maintained for long periods of time [Reference Breed43]. Different species of flying-fox share roosts together and HeV isolates from different Australian flying-fox species show almost identical nucleotide sequences [Reference Birt and Markus44, Reference Halpin45]. Whether the same transmission characteristics can be applied to NiV is unknown. Some studies suggest similarities exist, since there may be a higher risk of henipavirus transmission from flying-foxes to domestic animals or humans during the gestation period of flying-foxes [Reference Wacharapluesadee30, Reference Breed43, Reference Plowright46]. It is conceivable that prior infection and immunity to HeV may limit or prevent infection with NiV given the shared cross-reactive antigenic domains in both viruses [Reference Defang47, Reference Chan48]. Given these uncertainties expert opinion was used (question 7) and P 4 was estimated to be ‘low’.
Probability infection establishes in Australian flying-fox populations (P 5 )
Infection could spread easily and widely among Australian flying-foxes, given their overlapping distributions, close genetic relationship, and co-roosting behaviour [Reference Webb and Tidemann49]. However, endemic HeV infection in Australian flying-foxes places uncertainty on NiV establishment, so expert opinion was used (question 6) and P 5 was estimated to be ‘very low’.
Final risk estimate
The probability of NiV establishing in Australian flying-foxes through non-migratory or migratory routes were both estimated to be ‘very low’. The overall risk of establishment via either route was estimated to be ‘very low’ with high uncertainty (Table 6).
* There are two final risk estimates that describe the probability of flying-foxes establishing in Australia via migratory or non-migratory routes of entry.
Combining expert opinion
Results of comparing the methods for combining expert opinion showed minor differences (Fig. 2). When incorporated into the model and compared to the baseline final risk, both weighted-median methods produced the same final risk of ‘very low’, and the mean and LOP methods increased the risk to ‘low’ (Table 7).
Model output was insensitive to the changes made to the highly uncertain events except for P 5 (probability of NiV establishing in an Australian flying-fox population), where the final risk increased to ‘low’ when a higher category was used and decreased to ‘extremely low’ when a lower category was used (Table 8).
The risk of NiV establishing in Australian flying-foxes through pre-border flying-fox movements was estimated to be low, with an associated high level of uncertainty. This outcome is strongly influenced by the probability of NiV establishing in Australian flying-fox populations (P 5) following introduction. The sensitivity analysis also supports this finding. Hence the results highlight the importance of step P 5 in the model. Further, the likelihood of NiV entry and spread (release and exposure assessments) is non-negligible (low and medium for the release assessment for non-migratory and migratory routes, respectively), so how the virus behaves once it arrives in Australia is critical. Given the high uncertainty associated with P 5, further research in this area would be valuable. Recent studies show that African Green Monkeys vaccinated with a HeV subunit vaccine are protected against challenge with NiV [Reference Bossart50], suggesting that cross-protection may be afforded against NiV infection following previous exposure to HeV. The findings of a seroepidemiological study by Breed et al. [Reference Breed43] suggest the probability of an Australian flying-fox population or subpopulation having a very low level of herd immunity to HeV at any particular time is less than previously thought. Hence it seems plausible that the presence of continually moderate to high herd immunity to HeV in Australian flying-foxes may act as a barrier to NiV incursion. However the limited knowledge of various aspects of henipavirus disease ecology (e.g. differences in infection dynamics between host and virus species, potential for co-infection of henipaviruses, role of cross-neutralizing antibodies in preventing infection) curtail better understanding of the factors that may influence this scenario and preclude an accurate assessment of its probability. If, however, Australian flying-fox populations were entirely susceptible to NiV infection, the final risk may increase significantly. NiV establishment in Australian flying-foxes has obvious animal and public health concerns, particularly given the overlapping human, domestic and feral pig, and flying-fox populations in eastern Australia. Further research on the infection dynamics of HeV and NiV (including pathogenesis and immunity) could greatly reduce the uncertainty in several parts of this risk assessment and hence improve the accuracy of the risk estimates.
The movement of bats between Australia and the immediate countries to the north is known to occur, although the frequency is not. Satellite telemetry studies of P. alecto have shown movements occur across the Torres Strait [Reference Breed14]. Evidence of movement and exchange of viruses between flying-fox populations in Australia and pre-border countries could be derived from genetic analyses of the henipaviruses present in pre-border countries. The infection dynamics of henipaviruses and other bat-borne viruses in pre-border countries is largely unknown. More data on the distribution of henipaviruses in bat populations, including clear differentiation between the virus species, and increased knowledge of the movement patterns of flying-foxes would contribute to a greater understanding of this area.
The different methods for combining expert opinion showed similar results. This may be influenced by the limited variation between experts' scores before combination and the moderating effects of averaging [Reference Ariely29, Reference Holt51]. If opinions were more skewed or ‘extreme’ then more variation between combination methods may have resulted. The modified Delphi approach is designed to provide synthesis and analysis of knowledge through open discussions, while retaining the benefits of multiple judgements without the biases of group discussions [Reference Mosleh, Bier and Apostolakis19, Reference Larreche and Moinpour21–Reference Riggs23]. In the workshop used for this study, experts in one subject area provided insights and knowledge to those in other areas. For example, the two experts in flying-fox ecology discussed the distances flying-foxes are likely to travel, behaviour of different species and level of contact between and within species of flying-fox. This resulted in greater knowledge of the entire group. However, the success of group interactions is dependent on the ability of the facilitator to encourage the sharing of knowledge and recognition of expertise, and to avoid the biases that can result from group discussions such as dominant personalities and overconfidence [Reference O'Hagan24]. During the workshop conducted in this study, subject-matter experts as defined by Knol et al. [Reference Knol18], tended to contribute more to the discussion than the normative experts who provided more input on probabilities and pathways. This was one of the objectives of the workshop, allowing information on the subject to be shared between participants, and more harmonized estimates to result. It is not surprising then that the model output was relatively robust to the different combination methods used. However, some notable differences were apparent. When using the mean and LOP combination methods higher risk estimates resulted, where risk increased from very low to low. It is interesting to note that weighted methods did not influence the final risk estimates anymore than non-weighted methods. In light of the subjective nature of weighting experts, simpler methods for combining expert opinion may suffice. This may be particularly the case where little variation exists between experts' opinions, and simple averaging techniques are appropriate. Similar findings have been reported by Scholz & Hansmann [Reference Scholz and Hansmann26]. An alternative approach may be based on a precautionary approach, where the technique that yields the highest risk could be used. Ultimately the decision to use one method over another is a difficult one, and will depend on the elicitation method used, type of assessment undertaken, and data obtained for the study.
There are few published risk assessments on the introduction and spread of a pathogen into a country through the movement of wildlife and hence validation of the assessment is limited. Snary et al. [Reference Snary32] performed a qualitative release assessment of henipavirus entry into the UK via different routes of introduction. In that study, researchers found a medium probability of importing infected flying-foxes from regions where henipaviruses are found, due to the medium probability that a fruit bat is infected, survives and goes undetected through the importation process.
The present study assumes that flying-foxes are the reservoir host for NiV and non-pteropid bats do not play a significant role in the risk of introduction of NiV to Australia. While some data indicate henipavirus infection may occur in bats of several other genera, available evidence suggests flying-foxes are the predominant host [Reference Calisher8, Reference Chua52, Reference Hayman53]. The assessment also assumes that NiV transmission to other flying-foxes is dependent on direct or indirect contact with an infected flying-fox, i.e. via contaminated urine, saliva, or other bodily fluids. Significant uncertainty exists on the mode of transmission of NiV within and between bat species. HeV transmission between Australian flying-fox species almost certainly occurs, since HeV isolates from different species show almost identical nucleotide sequences [Reference Smith54]. However, transmission is expected to be higher within species than between species, since contact rates are higher within species. Although different species share roosts together, they tend to segregate within roosts so contact is reduced [Reference Birt and Markus44]. Additionally, the apparent lack of clinical illness in flying-foxes infected with NiV is based on very limited information [Reference Middleton42]. The publication of further information in these areas may warrant revision of this risk assessment.
Qualitative risk assessments provide a systematic way of assessing risk that can be communicated to decision makers readily. However, assigning probability estimates in qualitative categories is subjective without a standardized methodology. This can lead to inconsistent, unrepresentative or misleading outcomes in the risk pathway. Indeed, uncertainties arising from words with imprecise or different meanings, or differences between verbal and numerical probability estimates can lead to risk being interpreted differently by different individuals, such as risk assessors, decision makers and experts [Reference Gigerenzer55–Reference Franklin58]. Despite these limitations, subjectivity can be reduced through a transparent approach. For example, the OIE provides a scale to classify and standardize qualitative probability categories . National agencies in Australia (Biosecurity Australia), Canada (Canadian Food Inspection Agency) and the USA (United States Department of Agriculture) have used numerical ordinal scales that correspond to verbal expressions of risk for their qualitative risk assessments [Reference Holt, Black and Abdallah59]. For example, very low, low, …, high is equivalent to 1, 2, …, n, where n is the number of points on the scale. These scales offer a relative measure of risk and provide an option to differentiate risk when it is impossible to quantify using probability measures [Reference Holt51]. In this assessment, we used the OIE scale to qualify our probability estimates and aligned this scale to the one used by experts in the workshop.
Difficulties also arise in qualitative risk assessments when combining steps in the pathway that are independent of each other. While there is a large number of matrices used to combine qualitative probabilities that are dependent on each other (see [Reference Peeler17, Reference Gale27, Reference Moutou, Dufour and Ivanov60] for examples), there is no such rule for addition of qualitative probabilities. A case by case approach was taken in a risk assessment performed by Snary and co-workers [Reference Snary32]. In this assessment, independent pathways (P n and P m ) were provided with separate probability estimates. To obtain an overall probability estimate, probabilities were ‘combined’ using the same mathematical rules that would be used for a quantitative assessment.
Expert opinion is subjective by nature. In highly uncertain events such as those presented in this model, experts' probability estimates can be difficult to quantify [Reference Vose61]. Consequently, the high level of uncertainty placed on many events in this model implies caution when considering the risk outputs. However, it provides a useful tool for communicating these risks to decision makers, and provides a clear model structure, key information needs and areas of uncertainty. The assessment also highlights the influence that different methods for combining expert opinion has on final risk estimates and the need to be aware of these methods when interpreting the findings.
Despite the large gaps in knowledge as outlined above, sensible and ethical policy and management options are currently required given the probable presence of NiV within a bat's ‘flying-distance’ of Australia [Reference Breed9]. Suggestions for reducing the probability of transmission of henipaviruses to domestic animals in Australia are outlined in Breed et al. [Reference Breed62]. These include: the planting of trees that are not attractive to flying-foxes in preference to those that are currently often planted around areas where livestock are kept (i.e. figs, melaleucas, various eucalypts and introduced fruit trees should be avoided); ensuring that feed bins and water troughs are not placed under trees in which flying-foxes feed or roost; and the placing of feed bins and water troughs under cover. The risk to human health from contact with livestock can be managed by adoption of infection control protocols and risk-related biosecurity measures, including the use of appropriate personal protective equipment. While the culling of flying-foxes has been suggested by some as a management activity, there is strong evidence from other wildlife diseases, including rabies in bats, that culling may well exacerbate the problem rather than provide a solution [Reference Breed62, Reference Streiker63]. Human, livestock and environmental health authorities are increasingly adopting a One Health approach to infectious diseases, recognizing that these three sectors are inextricably linked and interdependent.
This work was supported by the Australian Biosecurity Cooperative for Research Centre Emerging Infectious Disease and the consulted experts. We thank Katarina Staerk, Emma Snary, Robin Simons and Kim Stevens for advice on incorporation of expert opinion to risk analysis, and Lisa Adams and Deb Cousins for facilitating and helping to organize the workshop.
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