Lost taxa: the danger of seemingly harmless concepts
By Branden Holmes. Published on 19 October 2025.
Introduction: the danger of rogue concepts
Evolution and extinction are often treated as entirely distinct phenomena in the popular press. And they are increasingly being deliberately contrasted in order to emphasise the present greatly heightened extinction rate due to the current biodiversity crisis, when compared with the theoretical background extinction rate that more or less occurs during relatively "ordinary" periods in the history of a life-bearing planet. The current anthropogenically-driven biodiversity crisis is so bad that it is actually hindering evolution, through the loss of genetic diversity, demographic changes including skewing of sex ratios and mortality rates, fragmenting of populations (which has a raft of negative effects!), reduction in suitable habitat that reduces carrying capacities, and even the loss of entire functional traits. And that is just from the perspective of the survivors (for now). After all, there are relatively few phylogenetically unique taxa which lack relatives at the ordinal level (i.e. taxonomic rank: order). Most species belong to higher-level taxonomic groups that will survive the loss of individual species, and thus survive the loss of functional traits among their brethren.
Yet evolution itself, when unabated by environmentally-caused extinctions, and when sufficiently cumulative in the absence of geographically-mediated modes of speciation (i.e. the process of production of novel species), will result in the population's genetic and functional traits paradoxically diverging from itself over time. The population remains a single interbreeding conglomerate throughout its history, without fissioning off any evolutionary branches, and slowly changes over time (called anagenesis). The foundational stock will give way to a new species simply through the accumulation of net change after net change, so long as these net changes do actually accumulate, and do not cancel each other out (thus resetting the trait profile over and over again more or less to that of the foundational stock). This kind of in situ extinction, as a species goes extinct in virtue of evolving into a novel species, is known as phyletic extinction or pseudoextinction. In light of the current biodiversity crisis, it is important to understand the concept of extinction in its fullest expression, which can arise out of evolution itself. Indeed, it is important to appreciate all of the relevant concepts at a high level.
In contrast, the IUCN RedList considers the conservation category 'Extinct' to only be applicable to a taxon when no individuals are left:
"A taxon is Extinct when there is no reasonable doubt that the last individual has died. A taxon is presumed Extinct when exhaustive surveys in known and/or expected habitat, at appropriate times (diurnal, seasonal, annual), throughout its historic range have failed to record an individual. Surveys should be over a time frame appropriate to the taxon’s life cycle and life form." (IUCN, 2012:14)
The fundamental problem with this rogue conception of extinction is that it occurs far too late in the extinction process to be meaningful, and worse it is not benign as it raises further problems. Taxa do not technically qualify as Extinct according to the IUCN simply because they have an extant individual or two, even if the population isn't viable. In the midst of a biodiversity crisis, the fact that such ignorance is being perpetuated by a supposed conservation authority does not serve us well. Extinction is a complicated process with many possible causes and timeframes, but it is objectively achieved long before the last individual takes their last breath. A population is viable if it has the potential to survive indefinitely into the future, with no specific expiry date imposed upon the population. But if the population loses enough individuals, or sex ratios become too skewed, or it becomes highly fragmented, or is being hybridised out of existence, or has its habitat utterly destroyed, it can no longer continue into the future with hope, for it has none. It has been earmarked for geologically imminent extinction, and there is nothing left but for the deaths of the last remaining individuals to be actualised. It is therefore a false hope to automatically equate every population of >0 individuals with being meaningfully extant. Especially if we take a holistic approach, taking into account planned habitat destruction (especially damming), geological activity (e.g. volcanic activity), and the effects of global warming, even if we cannot yet precisely predict these events. As long as there is an objective upper temporal bound sufficiently close in time so as to prevent dispersal if they are not already ecologically abandoned to their fate.
There is thus no biological law which says that non-viable populations cannot reproduce. In fact, non-viable populations can persist multi-generationally before succumbing, especially if the cause of impending extinction is geological activity. We therefore need to be extremely careful when making assumptions about the conservation status of taxa simply because we encounter extant individuals, witness reproduction, and observe recruitment of young into the mature population. All three of these individually, and certainly all three in conjunction, clearly take place among viable populations. But they also take place among non-viable populations too. And therefore, diagnosing which populations are viable and which are not is clearly a complex problem, and must include markers beyond the three already mentioned. This is not helped by simplistic approaches such as that taken by the IUCN. On the other hand, we must also understand that not all absences from the scientific record are equally concerning. There are many traits that taxa can possess which predispose them to only being rarely recorded by humans. This includes fossorial and other subterranean ecologies, and the many plant taxa that survive solely in a soil seed bank for extended periods (sometimes many years) before inducive conditions prevail that triggers the germination of this latent genetic material.
Lost taxa: another rogue concept
The fact that we can observe the three markers already mentioned (i.e. extancy, reproduction, recruitment), and that these are not diagnostic either way with respect to viability, helps to emphasise the fact that extinction is knowledge-independent (and is certainly belief-independent). Our mental lives have not the slightest causal potency in and of themselves to prevent (or cause) extinctions, and there is no metaphysical obligation for taxa to inform us of their extinction. But none of this diminishes the importance of conservation monitoring, in fact it amplifies the need. We need to monitor populations globally so that we can put conservation plans into place if necessary, long before the point at which we can hardly tell whether a population is viable or not: prevention is clearly superior to cure here. But many populations are not merely not being monitored but have not been sighted for decades or even centuries. Given the ease with which taxa can go extinct, especially during the present extinction crisis, it is encumbent upon us to do more to actively monitor the world's biodiversity. In this vein, a small but growing literature has emerged around the idea of 'lost' taxa (Butchart et al., 2005; Tobias et al., 2006; Butchart, 2007; Ladle et al., 2011; Villarroel et al., 2014; Watson & Davis, 2017; Long & Rodríguez, 2022; Martin et al., 2023; Lindken et al., 2024).
Long & Rodríguez (2022) in particular have attempted to standardise the concept:
"A lost species is one not confirmed alive by photographic, audio or genetic information for over 10 years in the wild and has no ex situ population under human care. We consider under human care the maintenance of whole, living specimens, not cryopreserved samples in a biobank. A species’ lost status is independent of its category on the IUCN Red List of Threatened Species but has not met the conditions to be classified as Extinct or Extinct in the Wild. Although a simple definition, it is applicable to all taxa irrespective of life traits or the biome in which they live.
Some have called for a shorter time period to consider a species lost, as much can change in 10 years. We recommend using missing species for those not seen in the wild and not held under human care for > 5 years but < 10. The term long-lost has also been applied (Villarroel et al., 2014; David [sic] Watson & Davis, 2017), and we propose a time span of 50 years for these species. By consistently using these terms we identify a pathway from missing to lost to long-lost that facilitates the catalysis of stage-specific actions to prevent species identified as missing from becoming lost and subsequently becoming long-lost." (Long & Rodríguez, 2022)
This initially seems like a wholly laudable effort, particularly from those papers that publish aggregated lists of such 'lost' taxa (e.g. Martin et al., 2023), making it easier to know which taxa to target. The project of looking for 'missing' (> 5 years but < 10), 'lost' (>10 years) and 'long-lost' (>50 years) taxa is absolutely needed as we know that taxa can quickly go extinct at the best of times, but especially in the midst of the current biodiversity crisis. Threatening processes can quickly and quietly arise and devastate entire populations. So we should prioritise searching for long-lost taxa first and clearing that list, allowing us to move on to the other two categories in succession. Though taxa in the missing and lost categories can be sympatric (i.e. occurring in the same area) with long-lost taxa, so that knowledge of the other two categories is equally important so that we can oportunistically search for them too if we are already in the general area looking for a long-lost taxon. However, there are three major underlying problems with the model being proposed, which all stem from the fact that when lost taxa are finally recorded alive they are automatically considered as rediscovered (Long & Rodríguez, 2022). 1) Having temporal thresholds decreasing in duration allows for massive biases in search efforts and funding allocations. 2) Our conception and understanding of rediscovery is negatively affected by the proposed model. And 3) rediscovery is only valuable when there is conservation potential.
Time for a chat
1) Having temporal thresholds decreasing in duration allows for massive biases in search efforts and funding allocations
Once we have cleared the list of long-lost taxa (>50 years), we will then be down to lost taxa (>10 years) and can then clear that list too. We can then move on to those that are simply missing (> 5 years but < 10). But these temporal categories are far too granular. The shorter the time interval that we get down to, the greater the potential for bias among search efforts. When the turnover time from rediscovery to need to rediscover again is as short as a decade, it allows individuals to ignore plants, fungi and invertebrates in favour of getting their name(s) published alongside those of the giants in the field as having each rediscovered a particular vertebrate taxon. We as individuals, often unjustifiably obsessed with vertebrates, can simply argue that we do not have time to look for those plants, fungi and invertebrates that are also lost when there are so many lost vertebrates constantly in need of rediscovery and which have much larger ecological footprints, especially the so-called 'megafauna'. After all, there is no higher term than rediscovery. To rediscover a taxon means to discover an extant population where there was none known (or in rare cases, was thought to be functionally extinct). So we cannot nominally escalate taxa that receive less conservation attention that way. Instead, under the current model, we simply have to wait until the lapse in time escalates them from lost to long-lost.
Obviously, we can close the gap from lost (>10 years) to long-lost (>50 years) by lowering the long-lost threshold to say 25 years (i.e. by halving it), but then the arbitrariness of these demarcations becomes even more obvious. The closer the gap between lost and long-lost, the easier it is for us to completely ignore these purely temporal thresholds, and thus ignore taxa that we are not personally interested in. Even though there are far more non-vertebrates that are lost than vertebrates. Not to mention the fact that it would make the aggregation of such temporally-demarcated lists far more complicated. We also have to take into consideration the amount of money and resources that we can amass in order to conduct the necessary surveys. The more often taxa are in need of rediscovery, the shorter the onto-epistemic cycle, the more money and resources we need to allocate to them. This then allows for even more bias to enter the fray in terms of the allocation of funds. Given the arbitrariness of these temporal criteria, taxa that have simply gone unrecorded for an extended period should only be considered minimally rediscovered, in contrast to those taxa that were actively searched for many times and on the brink of extinction. I have elsewhere proposed a taxonomy of rediscovery (see my article entitled 'Exscovery' for the technical details) with nominal categories1. The first category of rediscovery is 'relocation', which has only a temporal qualifier. In contrast with the other two categories (viz. rediscovery s.s. and exscovery) for which survey efforts and extinction risk are the qualifying criteria to determine which category applies. Allocation of funding should thus be geared towards extinction risk, which will hopefully help to correct current biases towards vertebrates.
Given the current biodiversity crisis and its Pandora's box of threats, some obvious and static but many difficult to detect and spreading, even in the most absolutely pristine habitats (as far as we are aware) we are obligated to confirm persistence every so often so as to refute that theoretical scenario of extinction no matter how improbable we consider it. However, this temporal threshold should not come with the automatic designation of rediscovered if successful contact is made. One could easily argue that this singular temporal threshold (in contrast to the tri-fold one in the current model) should be 50 years (or even less), but the list of taxa that have gone unrecorded for a century (<1926) is already massive (many 1,000's), and bringing it down to 50 years would expand the list many times over. Thus if we are truly hoping to accomplish something with this kind of temporally-orientated project then we need to carefully engineer the number and values of the temporal thresholds so as to produce a manageable list of qualifying taxa that we can earnestly work through, one that is not marred by bias, including effective publicity for each taxon so as to raise awareness in case they are encountered by chance. The singular concept of a centurion taxon, one not recorded in at least 100 years, is an excellent starting point for such a temporally-orientated project. Though clearly we want to whittle it down absolutely as far as we can in the future. Thus the concept of a centurion taxon is merely an initial stepping stone towards a theoretically ever-shortening temporal threshold. Thus we must excise rediscovery from the picture otherwise the threat of the massive biaes detailed above will roar back into the fray via a slippery slope.
Rediscovering rediscovery
2) Our conception and understanding of rediscovery is negatively affected by the proposed model
If we allow taxa to qualify as rediscovered simply for having gone unrecorded for five years ('missing') followed by a record, then the same taxon can clearly be rediscovered again and again and again. Especially if we retrospectively backdate the policy to include every single scientific record and the negative reality of the gaps present therein. We become accustomed to rediscovery, and even risk normalising it. Making it even harder to stir the public into action to combat the current biodiversity crisis, when the rate of rediscovery is being artificially inflated to many times that of declarations of extinction. Sadly fueled in part by the hitherto failure of conservationists to nominally distinguish between clearly different categories of rediscovery, even though they have long been recognised by conservationists. With the vastly different reasons that taxa may disappear from the scientific record, from mere lack of surveys to total extinction (Ladle et al., 2011), often being lost on those not familiar with the details of the individual cases of rediscovery. Moreover, a taxon may habitually disappear from the scientific record for the same reason (e.g. ecology, cryptic behaviour, difficulty of field identification), leading us to be less concerned about its future disappearances. But if it disappears next time for a different, much more serious reason we may be reluctant to search for it yet again, potentially letting it slip into extinction. Assuming that the reason/s for its disappearance are made known. Because one study found that roughly half (c.50%) of plant and animal taxa assessed as Extinct or Extinct in the Wild by the IUCN RedList used 'long time missing' as evidence, but only 12-28% of accounts mentioned survey/search efforts and 15-27% did not indicate why the assessors evaluated the taxa in those conservation categories (Fisher & Humphreys, 2024). While taxa in these two conservation categories are by definition excluded from being lost taxa (Long & Rodríguez, 2022), this bolsters my claim that there is a broader trend among conservations of treating time missing in and of itself as central to conservation assessments, and also evidences a major shortfall in conservationists publicly conveying the justification for taxon assessments. The latter clearly negatively affects public concern for lost taxa.
Often we do not know precisely why a taxon has disappeared from the scientific record, with so many knowledge shortfalls at play (Hortal et al., 2015). Many taxa are widespread and common, but many others are highly localised and often inherently difficult to study. But when we do have a reasonable idea they should not just be triaged in accordance with best practice and cutting-edge knowledge, but that this should be adequately conveyed to the public. Or at least made accessible to them should they wish to consult the relevant online resources. After all, it is increasingly being recognised that citizen scientists can (and do) play an important role in biodiversity monitoring and recording. Notably, this includes population trends, migratory behaviour, range extensions, range expansions, and even the discovery of novel taxa and the rediscovery of others. Through surveys, oral and written reports, and photographic records via online platforms like iNaturalist and BugGuide.net. But the potential of citizen scientists to meaningfully contribute to conservation biology will not be fully realised until we build frameworks for them to actively participate in conservation work beyond mere opportunism. This includes educational resources that intellectually lift them up sufficiently for them to be able to autonomously read the peer-reviewed literature. Unlike many other subjects, the sheer importance of the natural world means that conservation biology should be the earnest remit of every single person on Earth. It is thus essential for us to get across the fact that rediscovery is a spectrum with three distinct zones.
The first zone, relocation, relates strictly to temporality. It is met when a taxon is recorded on the first search attempt, or prior to this serendipitously. Perhaps as part of a broader biological survey of the area. While the other two zones pertain more objectively to previous failed survey efforts and extinction risk. The second zone is occupied by rediscovery s.s., which minimally requires at least one failed taxon-specific survey to have taken place for the taxon. Though it could have been rather informal in nature, and therefore it is variable as to how much we can infer about the actual conservation status of taxa from such failed surveys. Thus in our search for lost taxa that have been missing for more than a decade, it may take us multiple rounds of surveys to actually record them alive, in which case relocation clearly does not apply. Although taxa that we know are extant in a particular area can also be missed by methodologically appropriate surveys. It is only when surveys are exhaustive that we can have a clear picture of the conservation status of a taxon, assuming that all potentially suitable habitat has been surveyed. But rediscovery, when it occurs, is hopefully the start of a conservation process as many rediscovered taxa remain highly threatened long thereafter (Fisher, 2011; Scheffers et al., 2011). But there are many lost taxa that have never been searched for and likely are not threatened, especially those from pristine habitats (Ladle et al., 2011). If we do not start to meaningfully distinguish between the different categories of rediscovery then cases of mere relocation, including potentially many instances involving the same taxon, will flood the internet and other information sources, making it seem like cases of rediscovery in which a well documented historical decline to near extinction has taken place are much rarer than they are. This will give the completely false impression that the biosphere is much healthier than it is. The true significance of rediscovery lies in the conservation potential that it uncovers, and can show that a taxon thought lost forever (or nearly lost) can in fact bounce back to healthy population levels given the right conservation plan, funding and conservation actions. Whereas many relocated taxa were never really thought to be extinct (or even non-viable), and thus their rediscovery is far less important (though still significant) as nobody seriously doubted the taxon's viability and thus the conservation potential of the population/s.
Conservation potential
3) Rediscovery is only valuable when there is conservation potential
One of the issues we face when organising a search for a lost taxon is the accuracy of locality and ecological (including phenological) data. Knowing where to look, and when, is vital to the success of such searches, assuming that the targeted taxon is still extant. Taxonomic data can also be very important, allowing us to know exactly what we are searching for (e.g. Balchin, 2007:7). All of this relates to locating those population(s) of lost taxa that have previously been recorded, but it is also perfectly relevant to locating additional populations which may exist but have not yet been discovered by science (though many are surely ethnoknown). The 2019-2020 bushfire season here in Australia was one of the worst on record, so bad in fact that there was widespread discussion of possible global extinctions as part of the devastating effects. According to Marsh et al. (2023), 382 invertebrate species had their entire known range destroyed in the fires, but because these taxa were only known from one or two records the true overlap of the fires with their actual ranges is not currently known. It is likely that many of the 382 species are extinct, since their true range even if much broader than that known may still have been encompassed by the enourmous fires. But many may still be extant in the form of hithero undocumented populations, each of which is of conservation importance if they are viable. Thus we do not simply want to rediscover lost taxa, we want to rediscover each and every known/suspected population of every taxon, and to also search for any undiscovered ones too. Yet the overly thin concept of lost taxa does not adequately take into account the individual populations that collectively comprise a taxon. Rediscovering a lost taxon by showing that one or two individuals from a single population technically survive, does not show that the taxon is viable.
The study of these "first" individuals may help our understanding of the biology, physiology, ecology, behaviour, habitat preferences, etc., of the taxon, depending upon our prior level of knowledge, and thus help inform search methodologies for other possible surviving individuals. But until there is sufficient evidence of viability, including the three markers already mentioned, any rediscovery (whether reported or not) is arguably nominal and premature (see 'Introduction' above). Because it is epistemically dangerous to assume that other individuals must exist, given that we are in a global biodiversity crisis. It is true that taxa exist in a non-viable state for a geological instant when compared with their long evolutionary history, rendering it statistically near certain that it would be viable if we were to visit it on a random day along its evolutionary path. However, it does not follow that almost all of the taxa extant at a given time are viable, because of the potential for clustering of non-viability across many taxa simultaneously, either stochastically or during a biodiversity crisis. The only real concern can be as to how likely it is that we would ever find any individuals from these non-viable taxa2, given that their population levels would be inherently tiny. But methodologically appropriate taxon-specific surveys are highly efficacious by their very nature, as they explicitly target a single taxon by taking into account it's biology, ecology, phenology, etc., and creating an ideal method of detection. Thus the failure of a given search effort for these stipulated last individuals is not down to any theoretical deficiency with the concept in general, but rather with practical factors such as its application to a particular taxon for which we lack key knowledge, funding, thoroughness, etc. In reality, we do not know which lost taxa are viable and which are non-viable (and which are totally extinct), so that if we do succeed in finding a few individuals we need to continue searching to see whether these are the last of their kind, or an arbitrary few from a much larger population. We need to find out whether there is conservation potential present, and if it turns out that there is, then and only then should we declare a rediscovery. Lest we give false hope, do public damage to conservation biology, and continue to be misguided and thus potentially make other mistakes.
Lost taxa are by definition not considered Extinct, but Long & Rodríguez (2022) nevertheless uphold the IUCN RedList's 'Extinct' conservation category, and thus by implication the rediscovery of lost taxa rules out the applicability of that conservation category. But until the taxon is shown to be viable, there has been no meaningful rejection of functional extinction, which is clearly the pertinent sense of extinction. The discovery of a couple of extant individuals from a functionally extinct population may allow for genetic samples to be taken, which can have both epistemic and ontic benefits, but these are of extremely limited utility in service of the conservation of the taxon. To argue otherwise is to double down on the thinnest possible notion of 'Extinct' beyond all possible ecological soundness. To maintain that functionally extinct populations are not meaningfully extinct is to claim that there is still conservation potential within these very last individuals. The only logically possible potentials being, (a) deliberate hybridisation to salvage some modicum of their genetic legacy (e.g. Garnett et al., 2011), (b) cloning to increase the population (e.g. Folch et al., 2009), or (c) de-extinction. But none of these is a major answer to the unfolding crisis. The widespread loss is happening at many biological levels: alleles, genes, populations, taxa, functional traits, ecosystem services, etc., confounded by changes in abundance and composition, and subject to extinction debt. So bringing back a few dozen vertebrate taxa that make ideal candidates for de-extinction is not going to meaningfully contribute to its avertion when the plants and invertebrates they interacted with are forced to stay extinct. Assuming that de-extinction is even metaphysically possible in the first place, thus it is not clear that there is any real conservation potential involved. While hybridisation deliberately drives pure individuals extinct in order to ensure that some of their genetic makeup survives, and thus at best constitutes quasi-conservation potential. That leaves cloning, which by its very nature produces genetically identical individuals that are especially susceptible to diseases, and inhibits adaptation which is needed in the face of climate change. Thus none of the three re-viability processes reliably injects conservation potential back into non-viable taxa and their doomed populations.
Lost taxa and ex situ care
Not all Extinct in the Wild taxa have equal potential to be reintroduced to the wild (ex situ) or to have heavy management removed (in situ), nor is either a guarantee that a viable population will remain so. Thus the conservation status of a taxon in the wild (and not being heavily managed) is vital, irrespective of whether or not it exists in captivity or is being heavily managed. Yet Long & Rodríguez (2022) explicitly preclude Extinct in the Wild taxa from being lost taxa, even if there is no real chance of reintroduction or removal of management. This fails to appreciate the importance of unmanaged wild populations, and helps to prevent non-researchers from learning a valuable conservation lesson. This is one last way in which the concept of lost taxa is ecologically unsound, in addition to the three major problems arising from its deep association with rediscovery.
Conclusion
The broader concept of looking for taxa that have not been recorded by science for years, and often for many years, is itself highly laudable. However, this does not mean that any approach whatsoever will achieve the desired goal. There is more to consider here than just the target taxa. Public perceptions of the current biodiversity crisis can be impacted by many factors, but especially science communication in its various forms and via different mediums. Unfortunately, the concept of lost taxa does not bode well for public understanding of the current biodiversity crisis because it suffers from three major flaws. Firstly, it treats arbitrary temporal threshholds as preeminent, which allows for biases in search efforts and public, private and research funding. It also takes focus away from the real metrics: threats and extinction risk. Secondly, it artificially lowers the bar for rediscovery to take place by introducing a new minimum criterion, merely five years without a record, with no further justification needed. This unjustifiably broadens the concept of rediscovery, which negatively affects our understanding of rediscovery by skewing the relative rates of mundane versus serious cases in favour of the former. And thirdly, it glosses over the importance of viability/conservation potential by allowing for rediscovery to take place even if only a single individual is found with no evidence of any others. It therefore openly welcomes impostor cases of rediscovery masquerading as legitimate rediscoveries, which provides us with false hope and does damage to the public reception of conservation biology.
It does not bode well for some scientists either, who have not only proposed such a flawed model but actively promoted it as well. This flawed thinking and action is part of the reason why the current biodiversity crisis is so grim. Our response as a species has been completely inadequate, from theory right through to practice and beyond. We are continually making innumerable localised attempts to solve a global problem, with so much division within conservation biology and beyond that is slowly sawing off the very branch we are sitting on of the Tree of Life. And it all starts with the philosophy of conservation biology. Making sure that we have a sound understanding of the basic concepts at play, and upholding these through experimental design, practical research, technical publication and science communication. Central to all of this is ecology, the study of how species make their living from the wider environment. Any factor that can negatively affect ecology (or our understanding of it) needs to be carefully delineated, described and studied. Central to this is rediscovery, which shows that a particular taxon is either more ecologically robust than we thought, or we prematurely gave up on it. And everytime we write off a taxon only for it to re-enter the biosphere, we should be reminded of how careful we need to be when proclaiming the conservation status of taxa. But instead of distinguishing between different categories of rediscovery, which are vastly different in nature and implications, the idea is being promoted of consistently rediscovering taxa decade after decade. Scientists are potentially crying wolf about many taxa, so that when they really do disappear nobody believes them. And there is no evidence that we can really de-extinct any species, or scientific careers for that matter.
Notes
1 To date, prior to my own attempt to create a taxonomy of rediscovery and nominally distinguish them, I am only aware of the attempt of Ladle et al. (2011) to do so. But their typology was simply from (1)-(4), "based on decreasing level of certainty that the rediscovered species was extinct" (Ladle et al., 2011). Unfortunately, there has been no real uptake of their system of more than a decade ago, possibly because it was numeric rather than nominal, although that is pure speculation on my part. Given the fact that taxa can be prematurely declared extinct, there is no real distinction between their category (1) and category (2), leaving three categories like my own. They do suggest a possible fifth category, namely those unrecorded/lost taxa that are elevated from sub-species to full species. But regarding the latter, I think we should rename subspecies as proto-species, firstly because this is more accurate from an evolutionary point of view. And secondly, this will help to bridge the taxonomic and conservation attention gap between species and subspecies.
2 This concern is logically equivalent to the assumption that whenever we find a tiny number of individuals of a taxon, others exist. Because from this it follows that there are no cases where we find an individual but there are no other individuals extant. Thus the two are logically equivalent. But putting it the way I have makes the discussion and answer much clearer.
References
Balchin, Chris. (2007). Back from the dead! A potpourri of recent rediscoveries in the Neotropics. Neotropical Birding 2: 4-11.
Butchart, Stuart H. M. (2007). Birds to find: a review of 'lost', obscure and poorly known African bird species. Bulletin of the African Bird Club 14(2): 139-157.
Butchart, Stuart H. M., Collar, Nigel J., Crosby, M. J. and Tobias, J. A. (2005). Asian enigmas: Lost and poorly known birds: targets for birders in Asia. Birding Asia 3: 41-49.
Fisher, Diana O. (2011). Cost, effort and outcome of mammal rediscovery: neglect of small species. Biological Conservation 144(5): 1712-1718. https://doi.org/10.1016/j.biocon.2011.03.005
Fisher, Diana O. and Humphreys, Aelys M. (2024). Evidence for modern extinction in plants and animals. Biological Conservation 298: 110772. https://doi.org/10.1016/j.biocon.2024.110772
Folch, J., Cocero, M. J., Chesné, P., Alabart, J. L., Domínguez, V., Cognié, Y., Roche, A., Fernández-Árias, A., Martí, J. I., Sánchez, P., Echegoyen, E., Beckers, J. F., Sánchez Bonastre, A. and Vignon, X. (2009). First birth of an animal from an extinct subspecies (Capra pyrenaica pyrenaica) by cloning. Theriogenology 71(6): 1026-1034. https://doi.org/10.1016/j.theriogenology.2008.11.005
Garnett, Stephen T., Olsen, Penny T., Butchart, Stuart H. M. and Hoffmann, Ary A. (2011). Did hybridization save the Norfolk Island boobook owl Ninox novaeseelandiae undulata? Oryx 45(4): 500-504. https://doi.org/10.1017/S0030605311000871
Hortal, J., De Bello, F., Diniz-Filho, J. A. F., Lewinsohn, T. M., Lobo, J. M. and Ladle, R. J. (2015). Seven shortfalls that beset large-scale knowledge of biodiversity. Annual Review of Ecology, Evolution, and Systematics 46(1): 523-549. https://doi.org/10.1146/annurev-ecolsys-112414-054400
IUCN. (2012). IUCN Red List Categories and Criteria: Version 3.1. Second edition. Gland, Switzerland & Cambridge, UK: IUCN. iv + 32 pp.
Ladle, Richard J., Jepson, P., Malhado, A. C. M., Jennings, S. and Barua, M. (2011). The causes and biogeographical significance of species rediscovery. Frontiers of Biogeography 3: 104-111. https://doi.org/10.21425/F5FBG12432
Lindken, Tim, Anderson, Christopher V., Ariano-Sánchez, Daniel, Barki, Goni, Biggs, Christina, Bowles, Philip, Chaitanya, Ramamoorthi, Cronin, Drew T., Jähnig, Sonja C., Jeschke, Jonathan M., Kennerley, Rosalind J., Lacher, Thomas E. Jr., Luedtke, Jennifer A., Liu, Chunlong, Long, Barney, Mallon, David, Martin, Gabriel M., Meiri, Shai, Pasachnik, Stesha A., Reynoso, Victor Hugo, Stanford, Craig B., Stephenson, P. J., Tolley, Krystal A., Torres-Carvajal, Omar, Waldien, David L., Woinarski, John C. Z. and Evans, Thomas. (2024). What factors influence the rediscovery of lost tetrapod species? Global Change Biology 30(1): e17107. https://doi.org/10.1111/gcb.17107 [Supporting Information (Appendices A-D)]
Long, Barney and Rodríguez, Jon Paul. (2022). Lost but not forgotten: a new nomenclature to support a call to rediscover and conserve lost species. Oryx 56(4): 481-482. https://doi.org/10.1017/S0030605322000618
Martin, Thomas E., Bennett, Gareth C., Fairbairn, Andrew J. and Mooers, A. Ø. (2023). ‘Lost’ taxa and their conservation implications. Animal Conservation 26(1): 14-24. https://doi.org/10.1111/acv.12788 [Appendix S2 (1617 taxa not seen >10 years); Appendix S3 (562 taxa not seen >50 years)]
Scheffers, B. R., Yong, D. L., Harris, J. B. C., Giam, X. and Sodhi, N. S. (2011). The world’s rediscovered species: back from the brink? PLoS ONE 6: e22531. https://doi.org/10.1371/journal.pone.0022531
Tobias, Joseph A., Butchart, Stuart H. M. and Collar, Nigel J. (2006). Lost and found: a gap analysis for the Neotropical avifauna. Neotropical Birding 2006: 4-22.
Villarroel, D., Quintino de Faria, J. E. and Barnes Proença, C. E. (2014). One new and one long-lost species of Eugenia (Myrtaceae) from the Bolivian Cerrado. Novon 23(2): 244-249. https://doi.org/10.3417/2011094
Remembering Lost Species: Anthropogenic Extinction in 10 Stories
By Matthew Stanfield. Published on 12 August 2025.
The following ten stories were originally published as individual blog posts on the Rememberance Day for Lost Species website (www.lostspeciesday.org), and are here collated and reproduced with the kind permission of Matt. I have not included the accompanying illustrations/photos so that you will hopefully peruse the original blog posts.
The species and their stories:
- Sloane’s urania (Urania sloanus)
- Liverpool pigeon (Caloenas maculata)
- Baiji (Lipotes vexillifer)
- Day geckoes (Phelsuma edwardnewtoni and P. gigas)
- Hawaiian passerines
- Rougette (Pteropus subniger)
- Giant tortoises (Cylindraspis sp.)
- Rabbs’ fringed-limbed tree frog (Economiohyla rabborum)
- Ground Sloth (Acratocnus ye)
- Thylacine (Thylacinus cynocephalus)
Remember Sloane’s urania (Urania sloanus)
Originally published here on May 3, 2017
‘If we and the rest of the back-boned animals were to disappear overnight, the rest of the world would get on pretty well. But if the invertebrates were to disappear, the world’s ecosystems would collapse.’ – Sir David Attenborough
From a human perspective, there is much about invertebrates which can be hard to relate to, or even to conceive of at all. As mammals, our instincts likely count against them. It is no great stretch for many of us to empathise with an orang utan or a wildcat – but an octopus, or a lobster? Even the word “invertebrate” implies a lesser form of life, defined by what it lacks – a backbone.
Historically, perhaps the most high-profile invertebrate grouping has been the gigantic order known as Lepidoptera (butterflies and moths). These creatures are arguably quite well-known from a human perspective, by virtue of their appeal to our well-developed sense of sight. Their frequently bold and distinctive colouration has drawn our interest for millennia. One striking result of this interest has been the identification of approximately one hundred and eighty thousand individual species of butterfly and moth. For context, the total number of all vertebrate species known is below seventy thousand.
Sadly, amidst the ranks of described species of all kinds there exists a growing body of organisms which will never be seen alive again. One such is Sloane’s urania, a large moth formerly native to Jamaica. Though moths are often thought of as less brightly coloured than butterflies, this species was a glorious exception.
The large size and dazzling colour of these animals seems to have bought them to the attention of science quite quickly. The species was first described in 1776, being named in honour of the recently deceased Sir Hans Sloane, whose collection formed the basis of the British Museum. Whilst most moths are active at night, Sloane’s urania was a day flier whose beautiful wings served notice to would-be diurnal predators that it was, in fact, toxic.
Unfortunately, this moth’s natural defences would prove useless in the face of human activity. Surviving relatives of Sloane’s urania migrate periodically, after population explosions amongst their caterpillars defoliate certain areas. Consequently, their populations are not only subject to significant natural fluctuations, but they require multiple large bodies of suitable plants on which to feed. Interestingly, most adult moths do not eat at all, doing all their feeding at the larval stage and living only to mate once they emerge from their cocoons.
It is suspected that, during the late nineteenth century, when Jamaica’s lowland rainforests were being cleared for agriculture, one of this species’ key larval foodplants was lost. Urania larvae in general are picky eaters, feeding solely on a single genus of rainforest vine. Without a food supply for the next generation, extinction beckoned. Sloane’s urania was last reported in 1895 and is believed to have vanished entirely by the early years of the twentieth century.
Although six members of the Urania genus, similar in appearance and habits to Sloane’s urania, are still known to exist, this does not lessen the significance of the species’ loss. Indeed, the mere fact that Sloane’s urania is known to have gone extinct at all renders it hugely significant. Whereas it can be reasonably assumed that most of Earth’s mammal species are known to science, the same is much less true for other classes of animals, perhaps none more so than insects. Estimates of the total number of insect species stand at between six and ten million, of which around one million have been described.
The upshot of our continuing profound ignorance of so much invertebrate life is that no-one has much idea of how many species humans have driven to extinction. A 2005 study estimated that around 44,000 insect species had been driven extinct by human activity since the fifteenth century. More worrying still, in 2014 entomologists concluded that the total number of insects on Earth has dropped by about forty-five per cent since the 1970s. However, the number of documented insect extinctions in that time period stands at around seventy. Sloane’s urania is a rare insect indeed in that its passing managed to draw the attention of its nemesis.
Recent dramatic declines in bee numbers appear to have begun to alert humanity to the stupefying risk inherent in gambling with the future of invertebrate life on our planet. We would do well to remember that even the asteroid strike which ended the Dinosaur Age did not manage to cause a mass extinction amongst insects.
The strange tale of the Liverpool pigeon (Caloenas maculata)
Originally published here on May 27, 2017
Where does a species belong? This question has a variety of interlinked answers. For instance, there is the geographic answer: the species’ natural habitat. Then there is the ecological answer: the role which a species plays in its ecosystem. There is also the issue of taxonomy: where the species fits into the evolutionary tree of life.
This is the tale of a species for which all these questions were long unanswered: the Liverpool pigeon. Despite its common name, this creature was never native to the north-western port city, nor indeed to any part of the British Isles.
The first known record of this pigeon dates from 1783, when English ornithologist John Latham described it, having seen two taxidermied birds in private collections. Latham gave these birds their original common name, the “spotted green pigeon”. In 1789, this apparently new species got its first binomial: Columba maculata. Decades later, Latham illustrated his descriptions.
One of the specimens Latham saw belonged to a London-based military officer and sometime naturalist named Thomas Davies. After Davies’ death in 1812, his pigeon was purchased by the 13th Earl of Derby, journeying with him to Merseyside. The fate of the other taxidermied pigeon which Latham saw is unknown. This lost specimen may have been more mature than the Earl’s pigeon, since Latham also drew a more brightly-coloured version of the bird. In 1851, the Earl’s collection was incorporated into the Derby Museum, later renamed the World Museum, Liverpool.
By the late nineteenth century, with no new specimens forthcoming, let alone any observations in the wild, the species faded into obscurity. In 1901, famed zoologist Walter Rothschild had this to say on the spotted green pigeon, lumping it together with the Nicobar pigeon in Part II of his Notes on Papuan Birds:
‘It is extraordinary that the home of this bird is not yet discovered, and we suggest the possibility – although there were two specimens – that it is an abnormity.’
For a century after Rothschild’s dismissal of the bird as an abnormal Nicobar pigeon, virtually no attention was paid it. The IUCN deemed it ‘Not Recognised’ and so it might have stayed if not for the attentions of natural history author and illustrator Errol Fuller. In 2001 Fuller suggested the reason for the bird’s fall into obscurity rested largely with Rothschild’s unwillingness to consider it a distinct species. Fuller also coined a new common name for the animal: “the Liverpool pigeon”, in recognition of the only known bird’s final resting place.
Soon after, the IUCN also recognised the contentious skin as representative of a species. The Liverpool pigeon thus made an ignominious move from “Not Recognised” to “Extinct” on the Red List. The basis for the decision to list the species as extinct lies in the lack of hard evidence for the pigeon’s continued existence beyond the early 1780s.
Whilst now acknowledged once again as a distinct species, many questions about where the Liverpool pigeon truly belonged remained unanswered.
By extracting and analysing DNA from two of the bird’s feathers, the species’ story became a little less opaque. The results indicated that the Liverpool pigeon is indeed a true species, sharing a genus with the Nicobar pigeon of the Indian Ocean and South Pacific. Consequently, it was given a new binomial: Caloenas maculata. Fittingly, the test results would also make it a fairly close relative of the likewise lost and enigmatic dodo.
So, with the Liverpool pigeon’s (former) place in the tree of life now apparently resolved at last, can any light be shed on where this bird once made its home? Besides the dodo, the species has two other close extinct relatives: the peculiar solitaire of Rodrigues and the Kanaka pigeon of the South Pacific. The latter species is known only from subfossils, most likely being hunted to extinction by the ancestors of the Polynesians around 500BCE. Given all the Liverpool pigeon’s closest known relatives are island dwellers, it is reasonable to think it too favoured this way of life. Tahiti has been suggested as the bird’s possible home, with stories of a similar-looking bird being recorded there in 1928, but this is far from a definitive answer.
For millions of years, the Indian Ocean and South Pacific proved an excellent home for pigeons, thought to have island-hopped from Oceania or South-East Asia, often developing terrestrial habits or even flightlessness in the process. The Liverpool pigeon appears to have taken a different evolutionary path.
Based on analysis of the World Museum’s pigeon, some hypotheses have been advanced about its ecology. It has been suggested the bird was a canopy-dweller, foraging in trees for soft fruits to eat, and thus functioning as a seed disperser within its ecosystem. It has also been proposed that this species avoided flying across open water, staying put on its island home, which may well have been small and remote.
The precise cause of the pigeon’s extinction is also mysterious. The IUCN considers it a reasonable assumption that human hunting in addition to possible predation by introduced species is likely to have ended its existence. This fate has been shared by many island birds since humans began expanding across Earth’s oceans. It is also thought likely that by the time Europeans first encountered the creature, it was already on the brink of extinction.
The species’ story now comes to its sad end. In 1851, the Earl’s taxidermied pigeon was crudely refashioned into a study skin and now forms part of the World Museum’s cabinet collection. Once a living part of an island ecosystem and a member of a strikingly diverse grouping of birds, for the last 166 years the Liverpool pigeon has belonged only in a drawer.
Deicide on the Long River: The Story of the Baiji (Lipotes vexillifer)
Originally published here on July 1, 2017
Chinese history stretches back thousands of years, with much of the modern nation’s heartland falling under the control of a single dynasty before the Romans even finished conquering Italy. In the ensuing millennia the Yangtze, Earth’s third-longest river, would become a major focal point of East Asia’s grandest civilisation.
In the days of Imperial China, the waters of what would come to be known as the “Long River” held a multitude of marvels. Amidst the ranks of the Yangtze’s endemic fish species were the high-fin loach, nicknamed an “ugly duckling in reverse” and the mighty Yangtze paddlefish, reaching lengths of over twelve feet. Besides the fish were other giants and oddities, including soft-shelled turtles weighing as much as a lion and diminutive finless porpoises.
Arguably the most celebrated of all the river’s residents was Lipotes vexillifer, the “Goddess of the Yangtze”. Commonly known as the baiji, this species of river dolphin occupies a special place in ancient Chinese mythology. The fable once told of the baiji is infused with human suffering and death, as indeed was these animals’ ultimate fate.
The story goes that a beautiful young girl lived on the banks of the Yangtze with her cruel stepfather. One day, he took the girl onto the river by boat, meaning to sell her at market. En route, he became intoxicated by her beauty, deciding to take advantage of her. The girl freed herself by plunging into the river, whereupon a storm sank her stepfather’s boat. Once the storm passed, a beautiful dolphin was seen swimming and taken to be the incarnation of the girl. The animal was dubbed the Goddess of the Yangtze: a symbol of peace, prosperity and protection.
For millennia, thousands of these blue-and-cream cetaceans swam in the Yangtze beneath the sailboats of traders and fishermen. But nothing lasts forever, and two centuries of bloody upheaval would end Imperial China and the baiji alike. In 1793, a British diplomatic mission to the Chinese Emperor was haughtily dismissed as a rabble of barbarians. However the “barbarians” would return, with a strength born of their Industrial Revolution, sailing thousands of troops up the Yangtze into the heart of China. By the mid-nineteenth century, steam-powered Western gunboats patrolled the Emperor’s greatest waterway.
China’s national humiliation and brutal treatment by the West, and later the Japanese, triggered the overthrow both of the imperial regime and its republican successor. This second Chinese revolution, concluding in 1949, would have grave consequences indeed. Following decades of brutal war, the Communist leader Mao Zedong proclaimed the People’s Republic of China. Mao sought to restore his ravaged homeland’s once paramount standing amongst nations. China would be forever changed.
In 1950, the lower Yangtze held around six thousand baiji, much the same number as when China’s first imperial dynasty was founded. In 1958 Mao initiated China’s “Great Leap Forward”. This attempt to create industrialised socialism in the People’s Republic was a cataclysmic disaster. Perhaps as many as fifty-five million Chinese died in the resulting famine. The Great Leap Forward also proved an ecological catastrophe. A massive nationwide furnace-building drive led to rampant deforestation to provide fuel, which in turn exacerbated desertification. Certain traditions were also denounced, including the venerated status of the baiji.
No longer protected by custom, the dolphins were made horribly vulnerable at a stroke. Against a backdrop of famine, they were hunted for their meat. A grisly cottage industry also emerged, with baiji skin being cut and stitched into handbags and gloves. Whilst the Great Leap Forward only lasted four appalling years, severe damage had been done. The Goddess of the Yangtze was in deep trouble.
China’s rapid population growth after the famine meant ever more mouths to feed. Fishing activity in the baiji’s home waters intensified, with motorised boats dragging thousands of hooks each behind them through the cloudy river. Baiji became entangled in this new fishing apparatus and drowned, with others scythed to death by propellers.
In 1979 China’s government officially declared the dolphins endangered. By now, maybe a tenth of their mid-century population remained. In the following decades, attempts were made to save the baiji, but time was already short and the odds were ever-mounting against the species’ survival.
In 2006, a six-week survey of the Yangtze by thirty researchers found no sign of the baiji. They were declared functionally extinct in December that year, since fewer were thought to survive than the continuation of the species required.
Research indicates that the loss of the baiji is of particular significance: it was the sole representative of the Lipotidae, an entire cetacean family. More than twenty million years of unique evolutionary history gave Earth the baiji. We took about one-millionth of that time to drive them to the brink of extinction.
Scientists’ despondency about the baiji is sadly well-placed. Almost a half-billion people inhabit the Yangtze drainage basin. The river itself is astoundingly polluted, fringed by over four hundred-thousand “chemical enterprises”, turning former baiji habitat into what PRC state media call a “pollution belt”. Unsurprisingly, many of the river’s other species are at risk of following the dolphins into oblivion.
The suffering of China’s people in the centuries since a newly-industrialised West first turned its sights on the vast Qing Empire has been mirrored by the suffering of its wildlife and ecosystems. Unfortunately, another sinister innovation of Mao’s now has environmental repercussions far beyond the People’s Republic: namely his promotion of “Traditional Chinese Medicine”. This highly-lucrative field is a now a major driver of species endangerment worldwide.
One poignant example of this endangerment is the vaquita, native to the Gulf of California. This child-sized porpoise may soon vanish due to insatiable Chinese demand for the swim bladders of the totoaba fish who share its habitat. Nearly all Earth’s vaquita have already drowned in the nets of Mexico’s totoaba fishery. It would be a grim irony indeed if two disparate cetacean species were lost in such quick succession, paying the ultimate price for China’s bitter struggle to reclaim its former glory.
Lucy Campbell’s works explore the worlds of lost, disappearing and mythical creatures. Her baiji painting was made as part of a shared project with storyteller Andreas Kornevall – read Andreas’ version of the ancient baiji myth, illustrated by Lucy, on his website.
The Lost Pollinator Lizards of Rodrigues (Phelsuma edwardnewtoni and P. gigas)
Originally published here on August 2, 2017
The notion of a lizard being a pollinator is rather strange. Unlike hummingbirds or bees, these creatures are hardly synonymous with dynamism or industry. An unfair characterisation of reptiles as sluggish, dull and abhorrent may have contributed to the role of certain lizards in pollination going largely overlooked.
Pollinator decline is rightly making headlines, but for some species the decline has already proven terminal. Two such creatures lived on the Indian Ocean island of Rodrigues. This isolated speck of land, along with the other Mascarenes, is often seen as a hotspot for recent island extinctions. However it might better be considered an unusually well-documented example, due to only having been settled during the seventeenth century.
The lost pollinators in question are the Rodrigues day gecko (Phelsuma edwardnewtoni) and the Rodrigues giant day gecko (Phelsuma gigas). Both common names are a little misleading. The Rodrigues day gecko was one of the largest members of its genus and the Rodrigues giant day gecko is thought to have been nocturnal!
Insects and nectar are believed to have comprised the bulk of these species’ diets. In the process of their nectar sipping, it is thought the geckos accumulated pollen on their faces and inadvertently spread it between flowers during their meals. This behaviour has recently been observed in other members of Phelsuma. Interestingly, one genus of Mascarene flowering plants produces coloured nectar, an extremely rare trait amongst plants. This nectar attracts Phelsuma geckos better than standard colourless nectar, suggesting coevolution between these plants and their reptilian pollinators.
The Rodrigues giant day gecko (P. gigas) was the first of the two to become extinct. It was described in 1708 by François Legaut as being: “of greyish colour, and very ugly: they are as big and long as one’s arm.” In the opinion of this lizard enthusiast, Legaut was wrong to call this impressive-looking animal ugly, but was right to emphasise its size. The Rodrigues giant day gecko was the largest known gecko ever, potentially reaching over half a metre in length.
Like Mauritius and Réunion, Rodrigues was ravaged by European colonial activity. Its forests were burnt down to flush out its giant tortoises and clear land for livestock rearing. Along with habitat loss, Earth’s biggest gecko was dealt a sucker punch with the introduction of rats and cats, who feasted on the lizards and their eggs.
By 1840, Phelsuma gigas was confined to a few offshore islets. On the basis of five living geckos taken from one of these refugia, the species was formally described in 1842 by a French librarian named Liénard. One survived several months in captivity, refusing all food except sweetened water from a spoon. Liénard’s spoon-fed lizard was the last of its kind recorded alive. Nothing but a handful of assorted bones still remains.
The Rodrigues day gecko (Phelsuma edwardnewtoni) appears to have hung on a little longer than its larger relative. Legaut again provides the earliest record of these animals, who made quite a favourable impression on him and his companions:
“The palm trees and Latan palms are always laden with lizards about a foot long, the beauty of which is very extraordinary…the colour of each the most lively and bright of any of its kind…They are not mischievous, and so tame, that they often come and eat the melons on our tables, and in our presence, and even in our hands; they serve for prey to some birds. When we beat ‘em down from the trees with a pole, these birds would come and eat them from our hands, tho’ we did our utmost to hinder them; and when we offered to oppose them, they came on still after their prey”
Within two centuries of the publication of this curiously touching tale of island naivety, the Rodrigues day gecko had been eradicated from the main island. Habitat destruction and introduced predators were responsible. By the latter half of the nineteenth century rats were spreading across Rodrigues’ surrounding islets. Two last Phelsuma edwardnewtoni were collected in 1917 and sent to Paris, where they are preserved in alcohol for posterity. The species is thought to have succumbed to rats shortly thereafter. Today Rodrigues has no surviving endemic reptiles.
Elsewhere in the Mascarenes, geckos do continue to pollinate certain plants, particularly Trochetia flowers with their colourful nectar. The blue-tailed day gecko, a diminutive relative of Rodrigues’ lost lizards, still serves as a crucial pollinator of Mauritian Trochetia.
Recently it has been suggested that Gunther’s gecko, another large Mascarene day gecko species, could be introduced onto some of Rodrigues’ now rat-free islets. This rewilding project could serve two useful purposes. First, Gunther’s gecko is endangered, presently confined to a single area of less than two square kilometres. Establishing a second population of this animal could help ensure its survival. Second, Gunther’s gecko is considered an ecologically-comparable species to Rodrigues’ lost geckos. Potentially it could revive vanished interplays between plant and lizard. As with other rewilding proposals, only time will tell whether it will come to fruition.
Hawaii’s emptying skies (Passeriformes)
Originally published here on September 9, 2017
Not long ago, the Hawaiian archipelago supported a plethora of pollinating birds. Today, many are extinct, with others feared lost or experiencing worrisome declines. Since the early nineteenth-century, twelve of Hawaii’s specialist avian nectar-eaters have become extinct, leaving at most eight known species behind. Seeing images of all twelve of these birds gathered together in one place is an effective and affecting way of getting a true sense of Hawaii’s losses.
The Hawaiian Islands are thought to have first been settled fewer than eight hundred years ago, at the tail end of Polynesian expansion across the Pacific. The arrival of humans in these isolated ecosystems bought with it our species’ calling card: an extinction pulse. The Polynesians, along with the pigs, dogs, chickens and rats who accompanied them, are thought to have been responsible for the loss of many lifeforms.
European arrival from the late eighteenth-century onwards contributed its own wave of death and destruction. Smallpox and other diseases killed many native Hawaiians, and the fauna of the islands experienced further depletion.
Hawaiian nectarivorous birds are divided into two groups: honeycreepers and honeyeaters (though the latter are no relation of the other bird species which are referred to as honeyeaters) Akialoa were honeycreepers, in a genus containing four living members when Europeans arrived in Hawaii. Today all are gone.
The Lanai akialoa disappeared first. Its decline seems to have predated European arrival, as fossils suggest it once inhabited other islands besides Lanai. Habitat loss and the ongoing damage wrought on Hawaii’s ecosystem by the Polynesians’ pigs likely doomed it.
Oahu’s akialoa fared a little better, with the last report dating from 1940. Forest clearance for American sugarcane ventures deeply damaged these birds. They also suffered a more sinister scourge: avian influenza. Spread by mosquitoes, who may have arrived in the bilge water of whaling ships, this disease continues to ravage Hawaiian avifauna to this day.
The Big Island’s Hawaii mamo was imperilled before James Cook’s 1778 landfall on the archipelago. The birds’ six to eight yellow feathers were used to manufacture garments for Hawaiian nobles and royalty. One particular cloak may have cost an obscene sixty thousand mamo their lives. Still, the Hawaii mamo might yet live today without the bitter blows dealt by European-led deforestation for cattle ranching, and avian flu.
Often seen with a pollen-dusted forehead after feeding on lobelia flowers, the black mamo, whose range had already been reduced by the Polynesians, was scientifically described in 1893. The last recorded bird was shot fourteen years later. The introduction of cattle, deer and mongooses is blamed for the loss of this species.
Eating both nectar and insects, the greater amakihi does not appear to have been known to the natives of Hawaii’s Big Island. Western collectors discovered this bird perhaps only a decade before Western investors destroyed it. Scientifically described in 1892, the species was last recorded in 1901, just before its tiny home range was cleared to make way for a sugarcane plantation.
The Laysan honeycreeper, which favoured the nectar of its island’s native flowers, was last recorded in 1923. Europeans, not Polynesians, seem to have been the first people to settle Laysan. Just one of them served to seal the birds’ fate: Max Schlemmer, who released rabbits there in the 1890s, hoping to use them for meat. The rabbits bred explosively, eradicating most of the vegetation on which the Laysan honeycreepers fed.
So far as can be gleaned, none of the akialoa species were common by the time Europeans reached the Hawaiian Islands. Both of these pollinators were ultimately undone by the sugarcane industry’s ruination of forests working in tandem with the invisible spread of mosquito-borne avian diseases. The lesser akialoa has not been reported since 1940. In 1969, when the ultimate agent of its demise first walked on the moon, the Kauai akialoa was last reported. With its passing, the entire akialoa genus ended.
Whilst gravely damaged by human activity, several nectarivorous Hawaiian honeycreepers yet persist. The Hawaiian honeyeater family (Mohoidae) was less fortunate. They are generally thought to be the only avian family extinct in modern times. Even within an order as large as that of the perching birds, losing a whole family is significant. For instance chameleons, in all their distinctiveness, represent a single family amongst Earth’s snakes and reptiles. The kioea, last recorded in 1859, is thought to have been a victim of logging, introduced species and hunting.
Black, yellow and beautiful, these two species have been extinct for some time. The Oahu Oo vanished nearly two hundred years ago, last being recorded in 1837. Hunting by native Hawaiians for its yellow feathers may have contributed, though the prime causes of extinction are thought to have been introduced disease and habitat destruction in the wake of European contact. The Hawaii Oo was last recorded in 1934, suffering a similar fate to its relative on Oahu.
Bishop’s Oo was last definitively recorded in 1904, although reports persisted for decades afterwards on its former island home of Molokai. As with other species in this piece, fossil remains indicate it may have been more widespread before the arrival of Polynesian settlers. In recent times, the range of these birds was much more restricted. The most recent notable sighting was in 1981. Given this species has not been unequivocally seen alive in over a century, it is surely lost now. Cattle ranching and pineapple cultivation have much altered Molokai, and introduced avian diseases are as problematic there as elsewhere.
Kauai’s Oo was the last survivor of the Mohoidae. Once common, it entered a steep decline during the early twentieth century. Again, habitat destruction and disease-bearing mosquitoes were the key culprits. In 1987, the mating song of a male Kauai Oo was recorded. Over untold millennia, his species had evolved a delicate call-and-response duet. But for Earth’s last Kauai Oo, there would be no answer. He died later that year.
Rougette (Pteropus subniger)
Originally published here on October 27, 2017
A triple thread of discrimination, exploitation and subjugation runs through many historical extinctions. These injustices have long constrained the agency of entire strata of human societies. Above the disadvantaged many, a revolving cast of small elites have sat and called the shots. How many wage-slaves in the so-called rich world possess one iota of the power of the super-rich? And what of the agency of those trapped in the sweatshops and subsistence farms of the world?
Of course, injustice is not just an economic issue. Racism, misogyny, religiously-inspired bigotry and much more besides all fuel the malign inequities of the modern age. Moreover, cruelty and callousness amongst humans has a long, sad history of bleeding far beyond the boundaries of our own species.
This is one such tale. It is a story of slavery, in this case carried out for the benefit of French and British plantation owners, at the expense of the life and liberty of many living around the Indian Ocean. This tale of despoliation on Mauritius and Réunion also accounts for the extinction of a small and singular bat species: the rougette.
The Dutch abandoned Mauritius in 1710 and five years later France laid claim to it. French settlers had already established themselves on nearby Île Bourbon (later Réunion) decades prior. One hundred-and-twelve years of Dutch activity on Mauritius had profoundly harmed its ecosystem. Six bird species and one lizard are thought to have vanished, with likely much more besides. Yet Mauritius retained a great many wondrous species.
Amongst these was the small Mauritian flying fox (Pteropus subniger), also found on Réunion. Alluding to the band of reddish fur around their necks, the French often called them rougettes. The Pteropus genus contains some of Earth’s largest bats, such as Pteropus vampyrus, whose wings might span five feet. As suggested by their English common name, rougettes were far smaller, about two feet from wingtip to wingtip. When the French began settling Mauritius in earnest during the 1720s, the creatures were common.
This would not last. Mauritius’ new masters had a plan for it. Thousands of enslaved African, Malagasy and Asian people were shipped there to work in the lucrative sugar industry. For over a century Île de France, as the island was renamed, would be a brutal slave colony. Though the percentage of Île de France covered in sugar plantations grew quite slowly, about one-sixth of the already disturbed forests were felled under French rule. The enslaved were tasked with carrying out the backbreaking clearances.
Rougettes were especially vulnerable to deforestation due to their unusual roosting habits. Early observers wrote that up to four hundred might roost inside a single old hollow tree. Most of the rougette’s congeners roost on tree branches, not crammed together in crevices. As old-growth forest was destroyed, suitable roosts for this bat grew scarcer. P. subniger suffered a further consequence of human cruelty: enslaved people were fed appallingly, with those working the sugar fields given far fewer calories than required, and negligible quantities of protein. Survival depended on supplementing what were basically starvation rations.
Eating the native fauna was the best hope for long-term survival available to enslaved people on Île de France and Île Bourbon alike. The eighteenth-century French observer De la Nux claimed rougette hunting on Île Bourbon originated with enslaved Madagascans, though this is unverifiable. Anyhow, by the eighteenth century rougettes were, in De la Nux’s unsympathetic opinion, part of the diets of ‘numerous poorly off and unfastidious people’. P. subniger were fatty creatures, an adaptation to the cooler temperatures of their favoured high-altitude forests. This made them an invaluable source of calories for many denizens of the French Mascarenes.
In 1815, after the French Revolution broke the power of the Bourbon kings and Napoleon lost his wars, Britain became the colonial master of Île de France, restoring the name of Mauritius to the island. Île Bourbon stayed under French rule.
Deforestation cost Mauritius around a quarter of its remaining virgin forest over just twenty years of British rule. Simultaneously sugar cane cultivation expanded vastly, though cane fields did not replace much of the forest. Instead the felled wood fuelled the sugar-mills. Despite all this, at least one record suggests Mauritian rougettes may have remained reasonably common into the early 1830s.
Everything changed for Mauritius on 1 April 1835, with the formal abolition of slavery. Three in every four of Mauritius’ inhabitants were told that they were now free. Tragically “emancipation” was a poisoned chalice. Whilst Britain’s government compensated former slave owners for their “inconvenience”, nearly eighty thousand former slaves on Mauritius faced two unpromising options. Either they could serve an “apprenticeship” to their former masters, or try to eke out a life away from the settled parts of the island. Unsurprisingly the majority chose to abandon the savagery of the plantations, heading for isolated parts of the island to practice slash-and-burn peasant agriculture. Though this internal diaspora of the desperate likely harmed rougette populations, especially in those parts of the highlands which were settled, none of those involved had chosen to be on the island in the first place.
Much the greater act of ecological harm in the wake of 1835 was the work of the “plantocracy”. It proved profitable for plantation owners to import indentured Indian labourers to replace their slaves. The sugar industry boomed. The cost was the suffering of tens of thousands of Indians and the halving of Mauritius’ forested area in just a decade.
On Île Bourbon things were no better. Slavery remained legal there until 1848, when political upheaval in France led to formal abolition and a new name for the island: Réunion. In an inversion of the situation on Mauritius, it was impoverished white settlers who occupied the highlands of Réunion which harboured the island’s remaining rougettes.
In the end, nearly two centuries of plantation agriculture-driven hunting and habitat destruction would drive P. subniger extinct. The final record on Réunion came in 1862, with the animal last reported on Mauritius two years later. Live rougettes were not heard of again.
The sting in the tail of the bats’ demise is that, being primarily nectarivorous, plants which they pollinated might have passed into oblivion with them. We’ll never know.
Bibliography
Cheke, Anthony & Hume, Julian P., Lost Land of the Dodo (London, 2009)
Flannery, Tim & Schouten, Peter, A Gap in Nature (London, 2001)
Macmillan, Allister, Mauritius Illustrated (London, 1914)
Various authors, IUCN Red List, online (2017)
Various authors, Volume 1: Truth and Reconciliation Committee Report (Mauritius, 2012)
Lost Tortoises of the Indian Ocean (Cylindraspis sp.)
Originally published here on March 31, 2017
Strewn across the Indian Ocean to the east of Madagascar, the Mascarene Islands (Mauritius, Réunion and Rodrigues) are well known as the former home of the dodo and other strange extinct birds. However, dodos and their kin were only part of the unique ecosystem encountered by early visitors to these islands. As with Madagascar, the Mascarenes had been geographically cut off from the rest of the world for millions of years prior to human discovery. This isolation combined with their tropical location to produce an abundance of singular forms.
Today it is hard to imagine an environment virtually unaltered by human activity, so thorough has our species’ effect on every part of the biosphere been. Even in 1598, the year in which present-day Mauritius was named by the Dutch, such a task would have been difficult. In fact the Mascarenes were the very last sizeable tropical islands to be settled by humans. Though the Renaissance-era Dutch sailors who stumbled ashore on a warm September day had no way of knowing it, they would be amongst the last humans in history to behold the full splendour of what evolution can conjure on a good-sized tropical canvas.
The Dutch landed in a mountain-ringed bay draped in thick forests, home to well over one hundred times as many endemic flowering plant species as mainland France in an area less than one two-hundredth of the size. Within the forests roamed an array of island oddities. Besides the famed dodo, bulky broad-billed parrots lumbered through the undergrowth, whilst navy-blue pigeons perched above, puffing out crests of slim white feathers. The largest animal inhabitants of this paradise were the giant tortoises (genus Cylindraspis), of which five species were scattered across Mauritius, Réunion and Rodrigues. Giant and unafraid of humans, these creatures made quite an impression on the Dutch, as shown in this fanciful 1601 engraving of mariners riding (a ridiculously oversized) one.
French and Dutch settlers arriving on Réunion and Rodrigues in the seventeenth century found great herds of native tortoises. One early arrival on Rodrigues described whole fields covered in the creatures! Unfortunately for all five Mascarene giant tortoise species, their large size combined with apparent tameness and slow movement to render them ridiculously easy prey. Before refrigeration, islands served as gigantic larders for malnourished and hungry sailors. Faced with abundance, humans responded as they so often have: with rampant plunder.
The slow metabolic rate of the Mascarenes’ biggest natives counted horribly against them. Able to survive without food or water for months on end, they were viewed as an ideal food source, to be loaded alive en masse into ships’ holds. Thousands of captive tortoises died before they could even be eaten, since their shells had diminished in thickness due to an absence of native predators, causing many to be crushed to death within the stockpiles.
Our species’ fixation with oil also played a part in the demise of these animals. Long before the petroleum era, humans already lusted for the substance, searching for it inside living creatures. One seventeenth-century Mauritian governor reports a grisly tableau of dead and dying tortoises with holes smashed into their shells in search of fat to be boiled down. Apparently, up to fifty might be slain before a single fat individual was found, with each barrel of “tortoise oil” requiring the deaths of at least 400 fat testudines.
Unsurprisingly, such wanton slaughter soon turned beguiling plenty into vanishing rarity. Even by the standards of a Europe that burned, beheaded and hanged tens of thousands of its own as witches during this period, the treatment of Mascarene tortoises was seen as reckless by officialdom. As early as 1639, legislation was put in place on Mauritius to protect its tortoises. Sadly this proved ineffective and it would not be until 1771 that the remaining tortoises would receive meaningful protection.
It is unclear exactly how many of the original five species remained extant by 1771. Certainly the number of survivors would have been very low. The bountiful lands of Mauritius, Réunion and Rodrigues had largely been laid waste by slash-and-burn deforestation, with feral cats and pigs wandering freely amidst remaining tortoise nesting sites.
During this twilight of the tortoises, a handful of scientific observations were made, including at least one image of a live animal. That 1792 sketch, reproduced below, shows a Réunion giant tortoise. It was the largest species, capable of growing over a metre in length.
Tantalising scraps of evidence, including an alleged photograph of a living tortoise, survive from the late nineteenth century. However, the last generally-accepted record of Mascarene giant tortoises was in 1844. A British expedition to Round Island, off the coast of Mauritius, found several living tortoises. A female was captured and laid eggs, with the hatchlings distributed amongst various friends of one of the explorers. There is no information available as to which of the two Mauritian species was found on Round Island, nor is there anything known about what became of the hatchlings. Given that goats and rabbits were introduced to Round Island shortly thereafter, it is probable that one of the hatchlings became the endling of the genus Cylindraspis.
Disappearing when they did, at a time when modern science was still emerging, the Mascarene giant tortoises occupy a strange halfway house between poorly-understood human-induced casualties of the early modern era and better-known lost species of more recent times. Unlike some of their vanished compatriots, such as the Mascarene grey parakeet, their life appearance is fairly well-known, but there is still a deep air of mystery about them. The world’s only taxidermied specimen is kept in Paris, in the sombre setting of the Room of Endangered & Extinct Species. Below is a (slightly blurred) picture which seems a poignant reminder of these peculiar giants, now forever receding into the mists of time.
Tribute to Toughie (Economiohyla rabborum)
Originally published here on October 3, 2016
When considering the ever-growing list of species driven to extinction by human activity, certain creatures inevitably tend to stand out in the mind. Dodos are the most obvious example, having come to symbolise the Sixth Mass Extinction; the Passenger pigeon is another, plummeting from millions to none over a single human lifespan; the Thylacine would be a third, living on as a spectral icon of Tasmania’s threatened wildernesses.
Rabbs’ fringe-limbed tree frog seems an unlikely candidate for the pantheon of iconic human-induced extinctions. It was neither large, averaging no more than four inches long, nor particularly colourful, being primarily mottled-brown. To human eyes, it might seem small, slimy and strange.
Despite this, it would be entirely wrong to adopt a dismissive attitude towards this now vanished species. It bears repeating that few treated Dodos, Passenger pigeons or Thylacines with any respect whilst they still lived. Even more importantly, an anthropocentric approach to assessing the worth of species is at the root of today’s extinction crisis.
Here then will be written a tribute to Economiohyla rabborum, the Rabbs’ fringed-limbed tree frog.
A mere eleven years separate the species’ discovery and its extinction. This bleak fact was not lost on Joseph R. Mendelson III of the Department of Herpetology at Zoo Atlanta. Mendelson was part of the expedition to central Panama which first bought Rabbs’ tree frog to the attention of science. He has described himself as a “Forensic Taxonomist”, since the amphibians which he works on describing are dying off almost as fast as he can name them. Reading his reflections upon the morbid aspect which his scientific career has taken on, Mendelson’s sense of loss can be acutely felt.
The Panama expedition was launched as a direct response to extinction, specifically to the ongoing spread of chytridiomycosis amongst amphibian populations. This fungal infection can inflict a one-hundred per cent mortality rate amongst infected amphibians, letting it destroy entire species. Its origins, at least in its most virulent form, remain unclear. The introduction of fungus-infected African clawed frogs to the Americas, in combination with climate change, is currently the prime suspect.
In 2004, the chytrid pathogen was confirmed present in central Panama. The following year, Mendelson and other scientists headed to the region to find amphibians and take them into captive safe-keeping before chytridiomycosis could eradicate them.
There within the cloud forests of the mountains above El Valle de Antón, Rabbs’ tree frog was discovered. Unlike so many of the species which human activity has condemned to death, Rabbs’ tree frog was observed in the wild. As with other members of its genus, Rabb’s tree frog could use the webbing on its hands and limbs to glide through the air from the canopy down to the forest floor. Uniquely amongst known amphibians, it was the males who took the responsibility for feeding the young. Wild males were seen staying with the developing eggs and occasionally inserting themselves into the mass of growing tadpoles, letting their offspring feed off scraps of their skin.
Several dozen Rabbs’ tree frogs, adults and tadpoles alike, were loaded into crates and sent from Panama to US facilities in the hope of saving the species via captive breeding. Among the adult frogs was a young male, later known as ‘Toughie’. He was destined to become the very last of his kind.
Toughie spent most of his life at the Atlanta Botanical Garden, ensconced inside a converted shipping container known as the FrogPOD. This biosecure structure is strictly off-limits to visitors and was designed to serve as an ark for critically endangered amphibians, including Rabbs’ tree frogs.
At first he had company. The captured tadpoles were the first to die, failing to metamorphose in their new surroundings. They were followed by Toughie’s own offspring, born in captivity and dying as tadpoles. In 2008, Rabb’s tree frog was scientifically described. By the end of the following year, the species was functionally extinct. The last known female, one of Toughie’s FrogPOD companions, died taking any hope of the frogs’ survival with her. For the next seven years, Toughie would live alone. After three years, his loneliness became absolute, when the only other Rabbs’ tree frog known to exist was euthanized at another US zoo.
Around this time, Toughie came by his name. It was given him by the young son of the Garden’s Amphibian Conservation Co-ordinator. The boy’s explanation for the frog’s moniker was simple: ‘Because he’s the only one that made it!’
Unfortunately for Toughie and his carers, “making it” can seldom have been a more hollow triumph. Despite the best efforts of concerned scientists, all attempts to eke out a future for the Rabbs’ tree frog had ended with nothing more than an old male, sitting alone in a hollow log with nothing ahead of his species but oblivion.
Whilst comfortable, Toughie’s final home was not large enough for him to glide as he might have done in the Panamanian cloud forests. Judging by the accounts of those who knew him best, he was a wilful frog who disliked being handled, frequently pinching the hands of those who tried to hold him. Thus, apart from his weekly weighings, he was left largely undisturbed.
For most of his life, Toughie was very much the strong and silent type, living on grouchily as his species faded from existence around him. In the wild, male Rabbs’ tree frogs were heard calling, even after chytridiomycosis crept into their forest refuge. In captivity, Toughie fell mute. None of his kind would hear his voice again.
On December 15th 2014, something remarkable happened. The last Rabbs’ tree frog on Earth began to call out from his tank in the FrogPOD. His deep barking was recorded by the Amphibian Conservation Co-ordinator at the Botanical Garden. Once, such sounds might have been considered a mating call. From Toughie, they are the death rattle of a species.
Conservative current estimates suggest any given species of terrestrial vertebrate might expect to exist for one million years. How long Rabbs’ tree frog had lasted prior to September 2016 is as yet unknown. Had they managed merely one per cent of the aforementioned million years though, the frogs would still comfortably pre-date the entire written history of the species whose activities eradicated them.
More than seven thousand amphibian species share our planet. At least two thousand are in imminent danger of extinction. To get a sense of the scale of this crisis, consider that the last common ancestor of all of modern amphibians lived two-hundred-and-fifty million years ago. Staggeringly this means that the cumulative individual years of evolution which went into producing today’s IUCN Red List of amphibians runs well into the billions. This may seem unbelievable yet the great apes alone, with just seven living species, have well over thirty million years of individual evolution between us.
Should we lose all those amphibians which until so recently kept company with Toughie on the endangered list, we stand to lose a living record of evolutionary time greater than the age of the Earth itself. That is what mass extinction means.
Monolithic as the above figures are, they are arguably too big to effectively convey what species loss represents. For that, Toughie’s first and last recorded calls may serve far more eloquently.
(The call of the last Rabbs’ fringe-limbed tree frog, recorded by Keith Hughes in 2015 at Atlanta Botanical Garden)
Dedicated to the memory of Toughie and all his kind before him.
Getting to Know the Last Ground Sloths (Acratocnus ye)
Originally published here on March 2, 2018
The Americas lost most of their giant beasts when a wave of extinction swept them between the twelfth and the eighth millennia BC. Precisely what caused this cataclysm remains a source of controversy. That said, humans appear to have expanded their range of settlement in the Western Hemisphere around this time, so it is likely we had at least a hand in the matter.
At any rate, amongst the victims of the prehistoric American extinction pulse were the giant ground sloths, a highly successful group once found from Patagonia to the Great Lakes. Yet the ground sloths’ final curtain did not come down in the eighth millennium BC. Colossi such as Megatherium americanum might have vanished, but on a series of refugia, remnants persisted. The last ground sloths still wandered Caribbean forests around the time that Ancient Egypt’s first pyramids were raised. These animals were much smaller than their lost relatives. The biggest, such as Megalocnus rodens of Cuba, were comparable in size to a large sheep.
The Caribbean islands are thought to have lost at least seven sloth species in the last nine thousand years, with at least one within the last five thousand. It is believed the end of the ground sloths was precipitated by human settlement in the Caribbean, six thousand years or more ago. Certainly, few ground sloth remains have been carbon-dated to times much beyond the earliest evidence of humans on their islands.
The relative proximity of these creatures’ last days to our own time fascinates me. Compared to their continental kin, the Antillean sloths are obscure, with restorations of their life appearance hard to come by. Wanting to develop my understanding of these peculiar leftovers, I decided to try a life reconstruction of one such sloth. I selected Acratocnus ye, whose scientific name translates into English as “yesterday’s powerless sloth”. Taxonomists can be very cruel…
A. ye, though tiny compared to titans like Megatherium, was not as hapless as its name suggests. Standing on its hind legs, the solidly-built sloth reached a respectable metre or so in height. This is far in excess of the roughly guinea pig-sized Hispaniolan hutia, the biggest native mammal species remaining in A. ye’s former range.
The obscurity of Acratocnus ye meant I could only find a few pictures of subfossil bones and a medium-resolution image of a complete skeleton for reference. This limited supply of visual references suited me well. I prefer reconstructing obscure animals because not only does uncertainty give me more room for imagination, but, on a more prosaic note, the fewer total drawings of a species that exist, the fewer better drawings than mine there are likely to be! Below is a sketch of the skeletal photo which I used as the main reference for my piece (I think the original image is copyrighted, hence the reproduction).
Reconstructions of recently-extinct species are not only a learning experience for me, but an emotive one. Working on these pieces forces close consideration of those anatomical details that define an animal’s appearance. This process, I find, infuses a personal notion of the organism’s essence into my memory. It actually has a vaguely devotional feel to it, since I usually feel more attached, in some way, to creatures which I have drawn, as opposed to those I have not.
In the case of ground sloths, the matter of the animals’ “essence” is a challenging one to address. If you wanted to reconstruct the life appearance of say, a sabre cat or mastodon, there are living creatures which provide a viable reference point. Less so for ground sloths. Contemporary tree sloths are highly adapted to an idiosyncratic lifestyle, meaning that even the smaller ground sloths had a markedly different external appearance to their arboreal relatives. Thus, I aimed to give my Acratocnus a “look” distinct from extant animals.
Ground sloths being tricky to pin down visually, I found that the Acratocnus ye on my page passed through various “looks”. Initially, the stocky legs and long tail gave the lost mammal taking shape on the page a kangaroo-like aspect. The addition of a barrel-shaped torso conjured up thoughts of a bear standing on its hind legs. When it came time to cap off the Acratocnus, it took some work to stop the head from (unexpectedly) resembling an otter’s.
After dozens of hours, the piece was complete. Sadly, due to the technique which I used, it doesn’t photograph brilliantly. Be assured though that thousands of individually-drawn hairs went into the pelt, not to mention the time taken on claws, eyes, muzzle and ears. Whilst I’m finally satisfied enough with my tribute to A. ye to make it public, there are various snags I was unable to fully rectify. Firstly, the limited reference material caused me some confusion regarding the sloth’s feet (which is why they aren’t shown). Second, not having a scale for the species, for most of the drawing process I envisaged A. ye as about double its actual size. Resultantly, my ground sloth has a bit more heft than it perhaps should. Lastly, I somewhat lazily portrayed Acratocnus ye in a very over-used pose for ground sloths: rearing up and leaning on a tree. There’s no excuse for my repeating of this tired trope. Nevertheless, I hope that you enjoy my visual salute to a virtually unknown animal that vanished on the very cusp of the historical era.
Bibliography
With reference to Cooke, Dávalos, Mychajliw, Turvey & Upham, ‘Anthropogenic Extinction Dominates Holocene Decline of West Indian Mammals’, in Annual Review of Ecology, Evolution and Systematics. August 23, 2017. 48:301-27. Consulted at https://www.annualreviews.org/doi/abs/10.1146/annurev-ecolsys-110316-022754
Acknowledgements
With thanks to Mo Hassan of https://www.mocoillustration.com for help with translation of A. ye’s binomial
On Thylacine Day 2017 (Thylacinus cynocephalus)
Originally published here on September 6, 2017
The last captive thylacine died on September 7th, 1936
There’s nothing else like the thylacine. Nearly twenty years on, the memory of first discovering these bewitching animals remains vivid. As a child, my mum gave me her old collection of nature magazines from the mid-seventies. One particular article stood out.
‘Is the Thylacine Really Gone?’ the title asked. The piece was about five pages long, lavishly illustrated with grisly images of grim-faced men in Victorian agricultural dress posing with the corpses of one of the most captivating animals I had ever seen. Arguably the thylacine is a strange species for me to be so drawn to. Due to some negative experiences in the past, I’m not especially keen on dogs, to which thylacines are often likened. To my mind though, they’re at most akin to a highly experimental take on the dog.
Besides the tale of these animals’ persecution at the hands of a miserably myopic sheep lobby, the article also focused heavily on continued reports of sightings from Tasmania. Even for a piece written forty years ago, the notion of surviving thylacines was extremely optimistic. Whilst I am fairly certain that “Benjamin” was not truly the last thylacine, the notion of the species holding out until even the late nineteen-fifties seems highly improbable. Like most people with an interest in the thylacine, I would dearly love for a miraculous rediscovery to occur, but the odds on that are so tiny as to be insignificant.
However, believing that the thylacine is forever lost to the world does little to diminish what has proven an enduring obsession. Reading the story of these scandalously vilified marsupials not only awoke an interest which occasionally induces an adrenaline rush on glimpsing a mangy urban fox in southern England, but was the beginning of a sense of profound anger at human stupidity and greed.
This anger, aimed at the craven irresponsibility of so many in positions of influence, who play to the basest of human emotions and are so quick to find a convenient scapegoat to let themselves off the hook, drives my involvement in environmental concerns. This frustration at the deep and malignant injustices which are perpetrated every day, to the detriment of life itself, began with the thylacine’s tale.
After reading that first article, I started seeking out anything and everything thylacine-related. Books, TV shows, newspaper articles, I devoured them all. Sometimes I would draw thylacines, which is an excellent way to get a sense of how singular these animals truly were. The highlight was always natural history museums. No longer was it just about the dinosaurs – the unfashionable corners of the mammal exhibits held a new allure. Perhaps I hadn’t fully grasped the concept of taxidermy, or maybe I was caught up in the magical thinking of childhood, but on staring at the faded skins I half-felt if I wished hard enough, the scraps of creature behind the glass might reanimate.
A little later, I pinned my hopes on cloning. Sadly, even the wonders of genetic science are not yet equal to the task of returning this iconic ghost to the mortal realm. They may well never be: thylacines were behaviourally complex enough that even if one were to shamble stiffly out of a laboratory, it would not and could not know how to actually be what it supposedly was. The thylacine’s closest living relative is the numbat, an insectivore whose adult size is barely bigger than that of a thylacine joey.
Thylacines today might be no more than memories and relics, but I believe that these matter immensely, and not only for their scientific value. The importance of seeing extinct animals’ remains first-hand was never clearer to me than at the French national museum of natural history. Within a darkened hall dedicated to extinct and threatened species, skin and bone testify to human vandalism.
Each skeleton, skin and pickled corpse of a species lost because of us is a vital reminder of our place as increasingly unchecked global superpredators. If extinction is a spectrum, the terminal phase may be for an organism to be altogether forgotten. As long as pictures, photographs, footage and the physical remains of our victims endure, it is that much harder to downplay the cost of humanity’s ways. Seeing so many vanished creatures in a single room in central Paris sparked a sense of coming reckoning for all that we have done, and do.
Thylacines walk Tasmania’s woodland no more, for the small and stupid reason of panic over the safety of sheep. By the time the slaughter of these animals was recognised for the abomination it was, the hour was too late.
There are other “thylacines” though. They are those similarly unique species who are approaching extinction right now. Lots can be found at http://www.edgeofexistence.org/
Should the thylacine’s demise move you, spare a thought for the elusive saola, the mighty Philippine eagle, or the gorgeous Malagasy rainbow frog. Without effective action, all these and innumerable others could be following the thylacine into oblivion soon enough.
Women in Australia: Books on the subject
Gentle, Tayla, Herd, Margaret, Moran, Patrick, Sullivan, Leanne and Wilson, Lana (ed.). (2014). Who's Who of Australian Women: Time Capsule: 100 Years From Now. South Melbourne, VIC: Crown Content Pty Ltd. 1223 pp.
Gillard, Leanne, Herd, Margaret and Moran, Patrick (eds.). (2015). Who's Who of Australian Women (10th edition). East Melbourne, VIC: AAP Directories.
Harfull, Liz. (2012). Women of the Land: Eight Rural Women and Their Remarkable Everyday Lives. Crows Nest, NSW: Allen & Unwin. xii + 324 p., [16] p. of plates.
Lofthouse, Andrea (ed.). (1982). Who’s Who of Australian Women. North Ryde, NSW: Methuen Australia. 504 pp. [compiled by Andrea Lofthouse; based on research by Vivienne Smith]
Ohlsson, Ingrid and Duffy, Helen. (1999). Women of Australia: Their Lives & Times: A Photographic Gallery. Sydney, NSW: Pan Macmillian Australia. 272 pp.
Pearce, Suzannah. (2006). Who's Who of Australian Women: A Biographical Dictionary of Notable Australian Women. North Melbourne, VIC: Crown Content Pty Ltd. 1192 pp.
Saunders, Kay. (2014). The Big Book of Scandalous Australian Women. ABC Books AU. 688 pp.
Ghosts in Australia
Books
Anonymous. (n.d.). Frederick Fisher and the legend of Fisher’s Ghost: Your guide to Campbelltown’s most infamous resident. Campbelltown City Council.
Brownrigg, Jeff. (2021). Heaven, earth and Canberra: Shakespeare and the ghosts of Australia's National Film and Sound Archive. Port Adelaide, SA: Ginninderra Press. 328 pp.
Cusack, Frank (ed.). (1967). Australian ghost stories. Melbourne & London: Heinemann. xiv + 177 pp.
Cusack, Frank (ed.). (1968). True Australian ghost stories. Sydney: Angus & Robertson. xii + 177 pp.
Cusack, Frank (ed.). (1969). True Australian ghost stories. Sydney: Angus & Robertson. [paperback]
Cusack, Frank (ed.). (1975). Australian Ghosts: Authentic Tales of Australia's Supernatural (Arkon ed.). London: Angus & Robertson. 177 pp.
Daniel, Renata. (2016). Newcastle ghost stories: book 2. Newcastle, NSW: Renata Daniel. 201 pp.
Davis, Richard. (1998). The ghost guide to Australia. Sydney, NSW: Bantam Books. xvi + 432 pp.
Davis, Richard (ed.). (2012). Great Australian Ghost Stories. Sydney South, NSW: ABC Books, HarperCollins Publishers. 282 pp. [EPUB is 320 pp.]
Davis, Richard (ed.). (2014). Great Australian Ghost Stories. Sydney South, NSW: HarperCollins Publishers. 314 pp.
Dengler-McKerchar, Rosemarie. (2007). Frederick Fisher's ghost. Armadale, WA: Rosemarie Dengler-McKerchar. 42 pp. [contains at least some poetry]
Emberg, Joan Dehle and Emberg, Buck Thor. (c.1991). Ghostly tales of Tasmania. Launceston, TAS: Regal. x + 126 pp.
Fouler, Verlie. (1991). Colonial days in Campbelltown : the legend of Fisher's ghost (rev. ed.). Campbelltown, NSW: Campbelltown & Airds Historical Society. 20 pp.
Gane, Leonie. (c.2005). The hungry ghosts of Boggo Road: background, beliefs, and fate in the afterlife of Chinese prisoners executed in Queensland. Fairfield Gardens, QLD: Boggo Road Goal Historical Society. iii + 61 pp.
Giordano, Margaret. (c.1994). Tasmanian tales of the supernatural. Launceston, TAS: Regal Publications. vi + 151 pp.
Gomm, Kevin. (2023). Haunted and mysterious Albany: true-life local accounts of the strange, eerie and the unexplained. Albany, WA: Digger Press. 112 pp.
Griffith, Tracie (ed.). (2017). Port Fairy ghost stories. Maryborough, Victoria: McPhersons Printing Group. 213 pp.
Griffith, Tracie (ed.). (2024). Port Fairy ghost stories (2nd ed.). Port Fairy, Victoria: Port Fairy Ghost Stories Inc. viii + 245 pp.
Hack, Helen. (2000). The mystery of the Mayanup poltergeist. Boyup Brook, WA: Helen Hack / Carlisle, WA: Hesperian Press. xi + 92 pp.
Healy, Tony and Cropper, Paul. (2014). Australian Poltergeist: The Stone-Throwing Spook of Humpty Doo and Many Other Cases. Sydney, NSW: Strange Nation. ix + 300 pp.
Healy, Tony and Cropper, Paul. (2015). Australian Poltergeist: The Stone-Throwing Spook of Humpty Doo and Many Other Cases. Brio Books. 256 pp.
Heffernan, John. (2005). Haunted Australia. Scholastic Press. 163 pp.
Hogg, David and Bacchus, Darren. (2020). Ghost Crime Tales. Bloomington, IN : Author Solutions, LLC. x + 90 pp. [eBook]
Hogg, David and Bacchus, Darren. (2022). Ghost crime tales. Volume 2, Ghosts of the North Kapunda Hotel. Adelaide, SA: Peacock Publications. ix + 67 pp.
Howard-Wright, Miriam. (1980). Eyewitness: Australian ghosts. East Perth, WA: Artlook. 221 pp.
Howard-Wright, Miriam. (1991). Eyewitness: Australian ghosts. West Leederville, WA: Concept Media. 221 pp.
Kamper, Jeanette (author) and Genderen, Jen (ed.). (2015). Ghost hunting made simple! : basics & techniques. Glenfield, NSW: Spirit Connection Publishers. viii + 136 pp.
Kamper, Jeanette (author), Genderen, Jen (ed.) and Fardon, Michael (illustrator). (2016). Australia's haunted history. Volume III. Glenfield, NSW: Spirit Connection Publishers. x + 245 pp.
Kamper, Jeanette (author), Genderen, Jen (ed.) and Fardon, Michael (illustrator). (2017). Australia's haunted history. Volume II. Glenfield, NSW: Spirit Connection Publishers. x + 317 pp.
Kamper, Jeanette (author), Genderen, Jen (ed.) and Fardon, Michael (illustrator). (2018). Australia's haunted history. Volume III. Glenfield, NSW: Spirit Connection Publishers. x + 279 pp.
Kamper, Jeanette (author), Genderen, Jen (ed.) and Fardon, Michael (illustrator). (2019). Australia's haunted history. Volume IV. Glenfield, NSW: Spirit Connection Publishers. xviii + 327 pp.
Krakouer, Ray. (c.1999). Yarns from the Alkimos & other yarns. Perth, W.A.: Ray Krakouer. 36 pp.
Laughton, Valerie Joy and Falkenberg, Darren, (photographer). (1991). Valerie J. Laughton’s true Barossa ghosts (gathered together with good spirits). Nurioopta, SA: Laughton. 83 p., [1] p. of plates. [also titled 'True Barossa ghosts']
Ligato, Caterina. (2012). The Australian ghost whisperer. Sydney, NSW: Hachette Australia. 268 pp.
Machado, Karina. (2009). Spirit sisters: Australian women reveal true-life stories of the paranormal. Sydney, NSW: Hachette Australia. xviii + 282 pp.
Machado, Karina. (2011). Spirit sisters: Australian women reveal true-life stories of the paranormal (2nd ed.). Sydney, NSW: Hachette Australia. xviii + 282 pp.
Machado, Karina. (2014). Love never dies: true Australian stories of after-death contact. Sydney, NSW: Pan Macmillan Australia. 274 pp.
Machado, Karina. (2020). Spirit sisters: Australian women reveal true-life stories of the paranormal (First edition. Updated tenth anniversary edition). Sydney, NSW: Hachette Australia. xxii + 281 pp.
Marshall, Gordon de L. (with assistance from Richard Shar). (2012). Ghosts and hauntings of South Australia. Jannali, NSW: Gordon de L. Marshall. xi + 353 pp.
McDonald, Brian (comp.). (1999). Now I believe - in ghosts!: ghost stories from the Quarantine Station, North Head. Bondi, NSW: Brian McDonald. 40 pp.
McKenzie, Valerie and McKenzie, Timothy (illustrated by Robyn and Martin Simpson). (1984). A Glimpse Of Ghosts: Mysterious Places And Haunted Houses Of Early Australia. Chatswood, NSW: Centennial Publications. 160 pp. [hardcover]
Miller, Julie and Osborn, Grant. (2010). Something is out there: unlocking Australia's paranormal secrets. Crows Nest, NSW: Arena / Allen & Unwin. xvii + 363 pp.
Montgomery, J. G. (2017). Haunted Australia: Ghosts of the Great Southern Land. Schiffer Publishing. 256 pp.
Nairn, John, with the cooperation of Jack Sue. (1975). The ghost of Alkimos. Perth, W.A.: Skindivers. 52 pp.
Oborn, Alison. (2010). Ghosts of the past: one paranormal team's experiences in the Adelaide Gaol. One Tree Hill, SA: A. Oborn and Paranormal Field Investigators. xii + 139 pp.
Phelps, James. (2024). Australian ghost stories: shocking true crime stories of the haunted, the supernatural and paranormal happenings. Sydney, NSW: HarperCollins Publishers. 288 pp.
Pinkney, John. (2000). A paranormal file: an Australian investigator's casebook. Noble Park, VIC: Five Mile Press. 222 pp.
Pinkney, John. (2005). Haunted: the book of Australia's ghosts. Rowville, VIC: Five Mile Press. [16] p. of plates, 333 pp.
Pinkney, John. (2011). Haunted: The Ghosts That Share Our World. Kindle Edition. 359 pp.
Pinkney, John. (2013). Murders mysteries & hauntings: true Australian stories of the unsolved, unexplained, unknown. Scoresby, VIC: The Five Mile Press. 503 pp., 16 unnumbered pages of plates. [combined edition: Haunted first published 2005; Great Australia mysteries first published 2003]
Pobjie, Ben. (2022). 100 tales from Australia's most haunted places. South Melbourne, VIC: Affirm Press. 288 pp.
Porter, Trevor J. (c.2000). Gaol ghosts: the residents: gaol sightings, events, happenings and the unexplained in Adelaide Gaol, South Australia. Parafield Gardens, SA: Wednesday Press. 28 pp.
Salter, John. (c.1998). Chronicles of a genuine Australian ghost remover. Ripley, QLD: The Author.
Salter, John. (2002). Chronicles of a genuine Australian ghost remover. Ripley, QLD: The Author. 155 pp.
Sim, Jack. (2008). The ghosts of Boggo Road gaol: ghosts and gallows. Sunnybank Hills, QLD: Jack Sim Publications. ii + 41 pp.
Simmons, Andrew and McCulloch, Julie. (1990). Ghosts of Port Arthur. Port Arthur, TAS: A.D. Simmons. 40 pp.
Smith, Keith. (1991). Supernatural! : Australian encounters. Sydney: Pan. 230 p., [8] p. of plates.
Smith, Keith. (1993). Supernatural no. 2: more Australian encounters. Sydney: Pan Macmillan. 178 pp.
Stubbs, Rex. (1982). Ghosts and myths of the Hawkesbury. Windsor, NSW: Ladan Pty. Ltd. 25 leaves.
Stubbs, Rex. (1984). Ghosts and myths of the Hawkesbury (2nd ed.). Windsor, NSW: Ladan. 30 leaves
Sue, Jack Wong and Sue, Barry. (2001). Ghost of the Alkimos. Midland, Western Australia: L Smith (WA) Pty Ltd T/A Jack Sue WA Skindivers Publication. 158 pp.
Talbot, Don. (2004). Ghostly Tales of Toowoomba. Toowoomba, QLD: Don Talbot.
Tiller, Allen. (2014). The haunts of Adelaide: ... history, mystery and the paranormal. South Australia: Custom Book Publications. 99 pp.
Tiller, Allen. (2016). Ghosts of the Port: walking tour. Gawler, SA: The City of Port Adelaide Enfield Council. 31 pp. [eBook]
Tiller, Allen. (2020). The haunts of Adelaide: history, mystery and & paranormal (rev. ed.). Gawler, South Australia?: Allen Tiller. 166 pp., 17 unnumbered pages.
Tiller, Allen. (2021). Haunted Adelaide. Gawler, SA: Allen Tiller. xxi + 295 pp.
Tiller, Allen. (2021). The haunting history of Salisbury: walking tour. Salisbury, SA: City of Salisbury. 32 pp. [eBook]
Tiller, Allen. (2023). Haunted Salisbury: South Australia. Gawler, SA: Allen Tiller. 141 pp.
Tiller, Allen. (2024). Haunted Adelaide Plains. Adelaide, SA: Allen Tiller. 129 pp.
Tiller, Allen. (2025). Haunted Kapunda. Gawler, SA: Allen Tiller. 296 pp.
Toohill, Trudy (comp. and ed.). (2016). Australia's Haunted History. Salisbury, Qld: Boolarong Press. xiv + 193 pp. [paperback]
Williams, Stephan (comp.). (1990). Fisher's ghost & other Australian tales of ghosts and murder. Woden, ACT: Popinjay. 51 leaves. [Limited ed. of 50 copies]
Williams, Stephan. (c.1990). Four accounts of Fisher's ghost. Woden, ACT: Popinjay. 26 leaves.
Possible additions
Hilton, Sienna. (2019). Haunted history. Toowoomba, QLD: Boogie Books. [unpaginated]
Ivanoff, George. (2021). The supernatural survival guide: there is so much weird stuff out there - but the truth is in here! Docklands, Victoria: Puffin Books. 176 pp.
McRobbie, David. (1995). Haunted too: stories. Dingley, VIC: Mammoth Australia. 236 pp.
Magazine Articles
Fisher's ghost. (1853). Household Words 7: 6-9. [cited by Nickell, 2001]
Nickell, Joe. (2001). In Search of Fisher's Ghost. Skeptical Inquirer May/June 2001: 20-21, 66.
Newspaper articles
Anonymous. (1955). Ghost that trapped a murderer? The Sun-Herald, Sydney, NSW, July 3.
Anonymous. (1957). Fisher's Ghost appears but crowd disappoints. Campbelltown-Ingleburn News [Campbelltown, NSW], June 18.
Cranfield, Louis. (1963). Was Australia's greatest ghost story a hoax? Chronicle [Adelaide, SA], October 24.
Lee, C. N. (1963). Another ghost version. Campbelltown-Ingleburn News [Campbelltown, NSW], February 12.
Oral Interviews
Gratte, Stan (interviewee) and Lowenstein, Wendy (interviewer). (1971). Stan Gratte interviewed by Wendy Lowenstein for the Wendy Lowenstein Australian folklore and social history collection. Interview conducted in August 1971 in Geraldton, Western Australia. 1 sound tape reel (approximately 17 min.) : analog ; 5 in. [NLA record; Wendy Lowenstein's website; includes Stan's sighting of the Ambania ghost]
Papers and Journal Articles
Patrick, David. (1998). The Harrow: the Fisher's Ghost Pub. Grist Mills 11(3). [November 1998 edition]
Television Series
Haunting: Australia. (2014). Premiered on 3 February 2014 on Syfy. 1 season with 8 episodes in total. Release: 3 February–24 March 2014.
Videos/Documentaries
Moss, Warwick (host & Presenter). (2001). Kapunda: most haunted town in the Western World. Release date: September 24, 2001. 1hr 15mins.
Waddington, David (dir.). (2003). Ghosts of Port Arthur. Narrated by Peter Richman. Produced by Winning Post Productions, Hobart, Tasmania. 46 mins duration.
No viability? No rediscovery!
By Branden Holmes. Published on 27 April 2025.
Introduction
Given the rapidly declining state of the world’s biodiversity, any global rediscovery s.l. of a taxon is very important, not just for its conservation but for other reasons too (Diesmos et al. 2005; Ladle et al. 2011; Vilela et al. 2022). Yet reporting that one or two individuals of a taxon that is considered (possibly) extinct are in fact extant should not immediately overturn its assigned conservation status. Every genuine disappearance from the human record is caused by a population decline whose precise severity is unknown, while rediscovery itself does not abate threats, so until the population is shown to be viable it is not clear that the taxon has actually avoided a singular path to extinction. Such premature pronouncements of global rediscovery aren’t meaningful, may provide false hope, and artificially decrease the gap between the current extinction rate and rediscovery rate. The assumption that other individuals exist is epistemically dangerous.
The critical importance of biological viability
Intrinsic viability here refers to any inter-individual biological unit (species, subspecies, population, clade, etc.) that theoretically has the intrinsic potential to survive indefinitely into the future (in generational terms), not factoring in the extrinsic conditions it faces in the real world. A single, non-gravid, individual of a sexually reproducing taxon clearly lacks such potential (unless parthenogenetic or a self-fertile hermaphrodite), and thus is no better chance to survive >0 number of generations into the future than a wholly extinct one because it is impossible for both to do so (despite one of them having an extant individual). There is clearly therefore not just a non-zero lower bound for the size of a population of a sexually reproducing taxon in order for it to be able to persist indefinitely, generation after generation, into the future. Other criteria must be met too, that collectively reach the necessary conditions for intrinsic viability (e.g. minimum population size, reproductive connectivity, genetic diversity). This necessary (but not sufficient) condition for the long-term persistence and indeed recovery of a taxon has not been lost on scientists, with rediscovery sometimes being explicitly or implicitly couched in terms of the population rather than individuals (e.g. Keith & Burgman 2004; Humphreys et al. 2019; Toledo et al. 2023). Yet at least 12 papers (representing 11 taxa) published in 2022 reported only a single individual (e.g. Sumanapala et al. 2022; Turner & Bradley 2022; Wood & Walsh 2022), and a further 12 papers (representing 13 taxa) reported collecting every individual they found for preservation/study (e.g. Huang et al. 2022; Jałoszyński 2022; Vilela et al. 2022). Meaning that for 24 taxa there was no more than a single known extant individual at the time of publication (see Appendix). There is therefore no evidence presented that these taxa have been meaningfully rediscovered as they have not been shown to be intrinsically viable.
On the other hand, vegetative reproduction and self-compatibility in plants, and self-fertile hermaphrodism and parthenogenesis in animals, means that such taxa remain intrinsically viable even when down to a single individual. Yet despite this intrinsic viability, the practical risk that they or their offspring will die for any number of reasons before successfully reproducing is unacceptably high. Having genuinely declined because of one or more threatening processes (or stochastic events), these remain as extrinsic factors (when not abated, such as via ex situ conservation or by heavily managing the population) that will almost certainly prevent the theoretically minimum number of individuals required for intrinsic viability (this is the theoretical lower bound) from actually being viable over time in the real world. To this end, the concept of a Minimum Viable Population (MVP) has been very important (Nunney & Campbell 1993), which seeks to quantify the "needed" number of individuals such that the population will have an acceptably high chance of surviving a certain number of years in the future, and is therefore probabilistic in nature (this is the probabilistic lower bound). Unfortunately, precisely quantifying the MVP for a taxon is extremely difficult because it differs from taxon to taxon (Reed et al. 2003), and through time as each taxon’s genetic/demographic/connectivity/threat profile changes. While various models and assumptions have been/are/can be used to arrive at "the" MVP for a population, and it is important to acknowledge this diversity. But the general point here is that there is both a theoretical lower bound (i.e. intrinsic viability) and a probabilistic lower bound (i.e. the MVP), no matter how disputed the latter may be, and so we can simply bracket off the specific/disputed details.
Proto-viability
The probabilistic lower bound by its very nature cannot be lower than the theoretical lower bound, and given the nature of the myriad factors that negatively affect population size through time the probabilistic lower bound is invariably significantly higher than the theoretical lower bound. Conservationists in practice seek to conserve significantly more individuals than the theoretical lower bound as a buffer against extinction, and optimally will create further insurance populations if feasible. But the difficulties inherent with quantifying either lower bound presents an epistemic problem that affects the publication process and thus presents a practical problem. The demand to arrive at a full blown MVP value for a population (since the probabilistic lower bound is more important in practice), and then show that the population size actually meets that mark, would be extremely onerous on those seeking to publish peer-reviewed papers that report global rediscoveries. Regular publication of papers helps to disseminate knowledge and aid communication between researchers, which has benefits over fewer papers of a larger size, and helps to catalyse conservation actions/study into individual populations. Withholding these papers altogether would do active damage to the field of conservation biology. Therefore, the reporting of a global rediscovery should be reserved for cases where it has at least been shown that the taxon is comprised of a sizeable (sexually diverse, if applicable) population with active breeding and recruitment of young into the adult population, which we might term proto-viability. There are potentially many ways of defining what constitutes a "sizeable" population, but as long as it is sensible it will work well enough for the purpose. This then places less burden on those involved in the highly laudable exercise of trying to rediscovery viable populations of taxa thought to be (functionally) extinct, while still rightly holding them accountable to a satisfactory level by demanding that they meet a standard of evidence that a particular taxon has been meaningfully rediscovered.
By assuming that a taxon must be proto-viable even if we only find one or two individuals, we risk trivialising the concept of global rediscovery and inflating the perceived rate of global rediscovery relative to the rate of global extinction. Which would then make it appear as if the current biodiversity crisis isn’t as bad as it is. As well as potentially offering false hope, which if actualised can hurt the reputation of conservation biology, de-incentivising public donations, resources and co-operation. To remedy this situation, I propose a unique interim conservation category, quasi-extant, to label taxa that have been discovered to technically be extant after being considered (probably) extinct but have not yet been shown to be proto-viable. It is also applicable to taxa that have been continuously sighted/reported, but whose numbers are now suspected to be so low as to call into question whether they are viable any more. Once a taxon has been shown to remain proto-viable after initially disappearing it can then be meaningfully reported as rediscovered and assigned to the appropriate conservation category, such as ‘Critically Endangered’ or ‘Endangered’. Or if the taxon proves not to be proto-viable, it should then be listed as functionally extinct, at which point human intervention and technology may or may not be able to assist in the recovery of its proto-viability status (Folch et al. 2009; Albani Rocchetti et al. 2022).
The error of assuming other individuals must exist
The implicit reasoning behind such a high rate of reporting of global rediscovery in the absence of known proto-viability (or greater) is plausibly explained by the belief that it is extremely unlikely that the individuals discovered actually represent the entire global population, given (1) the existence of suitable habitat, (2) the fallibility of targeted searches, (3) the very short window during which populations survive in a non-viable state, and (4) when young are recorded it implies relatively recent reproduction by other individuals that likely still exist. Each point can be addressed to show that it does not have any serious force.
Suitable habitat (1) is a necessary, not a sufficient, condition for the existence of a proto-viable population. Habitat destruction/degradation is a leading cause of extinctions, but many other threats (e.g., introduced species, hunting/poaching, illegal collecting) leave the broader habitat largely intact while driving individual taxa extinct. Which can be exacerbated by concomitant emerging threats such as inbreeding depression due to loss of reproductive connectivity. Therefore, suitable habitat only potentially indicates the existence of a viable population and cannot be used to infer the actual existence of such a population.
The fallibility of targeted searches (2) is perhaps best illustrated by the phenomenon of rediscovery. Successive failure to find a taxon that we later record, and hence can retrospectively know that we missed it previously. But the generic potential to miss one or more individuals, which might not even make the population proto-viable anyway, is evenly matched on the other side by the clear potential efficacy of taxon specific targeted surveys to find individuals from extremely small populations or even lone individuals (e.g., Chelonoidis abingdonii, C. phantasticus, Nesiota elliptica, Stenostomum tomentosum). Such considerations need to be applied on a case-by-case basis for one to potentially eclipse the other.
The window will be very short (3) in terms of relative duration compared with the long existence of the taxon, but the actual duration can be centuries for extremely long-lived organisms like giant tortoises and trees, and years for many if not most other species. During which they can still consist of a small number of fertile individuals, and therefore reproduction may still take place, so the mere observation of recent reproduction in a population (4) cannot be used to infer that it is still proto-viable. While the potential to find these last individuals is increased by the chance of luck, in addition to targeted surveys that may involve many people. Moreover, since we are in the midst of a biodiversity crisis, there will be many thousands of taxa that dip below a proto-viable level, so that even if any single population goes extinct rapidly in a non-viable state, there are so many such populations that the chance of finding individuals from non-viable populations in general is a virtual certainty.
Conclusion
Global rediscovery is not as simple as showing that a single individual remains extant. The ecology of a population is an important but often overlooked factor when reporting rediscoveries, which places inherent limits on how few individuals can manage to constitute a viable population. While the threats that have historically affected the taxon, and contributed to its decline and disappearance, often remain. While others can emerge as compound effects of other threats, such as inbreeding depression and population fragmentation. For putatively extinct taxa, and those considered functionally extinct, the discovery of one or more extant individuals should not move the needle much in terms of the conservation status of the population, and should instead be treated as quasi-extant until such time as they are shown to be proto-viable. At which point, they can be meaningfully reported as globally rediscovered, although this is very much the beginning of research and conservation, and certainly not the end. As many rediscovered taxa remain highly endangered decades after their recall from biological oblivion.
Appendix: Reported global rediscoveries published in 2022.
Taxon | Total number of individuals reported | Number of individuals remained alive | Reference |
Agalope aurelia | 8 | 0 | Huang, Si-Yao, Zhu, Li-Juan, Chen, En-Yong, Xu, Yong-Qiang, Wang, Min, Fan, Xiao-Ling, Pan, Zhao-Hui and Espeland, Marianne. (2022). Contribution to the knowledge of the genus Agalope Walker from mainland China with descriptions of four new species (Lepidoptera, Zygaenidae, Chalcosiinae). Zootaxa 5165(4): 557–574. https://doi.org/10.11646/zootaxa.5165.4.7 |
Agalope lucia | 7 | 0 | Huang, Si-Yao, Zhu, Li-Juan, Chen, En-Yong, Xu, Yong-Qiang, Wang, Min, Fan, Xiao-Ling, Pan, Zhao-Hui and Espeland, Marianne. (2022). Contribution to the knowledge of the genus Agalope Walker from mainland China with descriptions of four new species (Lepidoptera, Zygaenidae, Chalcosiinae). Zootaxa 5165(4): 557–574. https://doi.org/10.11646/zootaxa.5165.4.7 |
Aniptumnus quadridentatus | 7 | 0 | Widyastuti, Ernawati and Rahayu, Dwi Listyo. (2022). The new record of Heteropilumnus sasekumari (Serène, 1971) and Aniptumnus quadridentatus (De Man, 1895) (Crustacea, Decapoda, Brachyura, Pilumnidae) from mangrove habitat in Papua, Indonesia. Oseanologi dan Limnologi di Indonesia 7(1): 15–22. |
Anisogomphus ceylonicus | 1 | 1 | Sumanapala, A. P., Ranasinghe, T. and Sumanapala, D. (2022). Rediscovery of Anisogomphus ceylonicus (Odonata: Gomphidae) based on its larva. TAPROBANICA: The Journal of Asian Biodiversity 11(1): 35–37. https://doi.org/10.47605/tapro.v11i1.276 |
Anolis lamari | 10 | 10 | Barnett, Joseph et al. (2022). Rediscovery of Anolis lamari Williams, 1992: morphological variation and nocturnal ecology (Squamata: Dactyloidae). Herpetology Notes 15: 329–334. |
Anthroscopus caroli colomanni | 1 | 1 | Turner, Donald A. and Bradley, James E. (2022). The rediscovery of the colomanni von Madarász subspecies of the Grey Penduline-tit Anthroscopus caroli. Scopus 42(1): 41–44. |
Apantesis eureka | ≥1 | ? | Fisher, Makani L. and Schmidt, B. Christian. (2022). Rediscovery of Apantesis eureka (Erebidae: Arctiinae: Arctiini): Contributions to the Distribution and Biology of a Great Basin Endemic. The Journal of the Lepidopterists' Society 76(3): 210–213. |
Astrohydra japonica | Many | Many | Peterson, Miles I. et al. (2022). A description of a novel swimming behavior in a dioecious population of Craspedacusta sowerbii, the rediscovery of the elusive Astrohydra japonica and the first genetic analysis of freshwater jellyfish in Japan. Plankton and Benthos Research 17(2): 231–248. |
Atelopus guanujo | >1 | >1 | Jaynes, Kyle E. et al. (2022). Harlequin frog rediscoveries provide insights into species persistence in the face of drastic amphibian declines. Biological Conservation 276: 109784. https://doi.org/10.1016/j.biocon.2022.109784 |
Atelopus petersi | >1 | >1 | Jaynes, Kyle E. et al. (2022). Harlequin frog rediscoveries provide insights into species persistence in the face of drastic amphibian declines. Biological Conservation 276: 109784. https://doi.org/10.1016/j.biocon.2022.109784 |
Atelopus sp. nov. 'Chimborazo' | ≥1 | ? | Jaynes, Kyle E. et al. (2022). Harlequin frog rediscoveries provide insights into species persistence in the face of drastic amphibian declines. Biological Conservation 276: 109784. https://doi.org/10.1016/j.biocon.2022.109784 |
Balthasaria mannii | >1 | >1 | Stévart, T. et al. (2022). Diversity of the Vascular Plants of the Gulf of Guinea Oceanic Islands, pp. 249-271. In: Ceríaco, L.M.P., de Lima, R.F., Melo, M., Bell, R.C. (eds.). Biodiversity of the Gulf of Guinea Oceanic Islands. Cham, Switzerland: Springer. |
Begonia elatostematoides | Many | Many | Mazo, Kean Roe F., Salatan, Noel L., Santos, Ian Earl A. and Rubite, Rosario R. (2022). Two new species of Begonia (section Petermannia, Begoniaceae) from Zamboanga Peninsula, Philippines with notes on an amended description of B. elatostematoides. Taiwania 67(3): 441–449. |
Begonia jocelinoi | 65 | 65 | Paglia, Isis et al. (2022). A narrowly endemic species of Begoniaceae: rediscovery, distribution and conservation of Begonia jocelinoi. Oryx 56(6): 935–938. |
Begonia parvilimba | <50 mature individuals | <50 mature individuals | Mazo, Kean Roe F. and Rubite, Rosario R. (2022). Two new species of Begonia (section Petermannia, Begoniaceae) from the Zamboanga Peninsula, Philippines, and a redescription of Begonia parvilimba. Phytotaxa 538(2): 163–171. |
Bufoides kempi | 24 | 16 | Naveen, R. S., Chandramouli, S. R., Kadam, G., Babu, S., Karunakaran, P. V., Kumara, H. N. and Parthasarathy, N. (2022). Systematics of the enigmatic and narrowly endemic toad genus Bufoides Pillai & Yazdani, 1973: rediscovery of Bufoides kempi (Boulenger, 1919) and expanded description of Bufoides meghalayanus (Yazdani & Chanda, 1971) (Amphibia: Anura: Bufonidae) with notes on natural history and distribution. Journal of Threatened Taxa 14(12): 22277–22292. |
Bulbophyllum barbatum | Many | Many | Menezes, Euler L. F., Giordani, Samuel C. O., Rosim, Mauro S. and Gonella, Paulo M. (2022). Over a century later and 400 kilometers apart: rediscovery of Bulbophyllum barbatum (Orchidaceae) in Diamantina, Minas Gerais, Brazil. Phytotaxa 536(2): 175–182. |
Callicarpa chazaliei | Many | Many | Moura, Andreza Campos De, Campos, Felipe Ferreira and Pérez, Carlos Daniel. (2022). Rediscovery and redescription of Callicarpa chazaliei Versluys, 1899 (Cnidaria: Hydrozoa) in the southwestern Atlantic Ocean. Zootaxa 5120(2): 251–262. |
Cambarus sheltae | 2 | 2 | Dooley, Katherine E., Niemiller, K. Denise Kendall, Sturm, Nathaniel and Niemiller, Matthew L. (2022). Rediscovery and phylogenetic analysis of the Shelta Cave Crayfish (Orconectes sheltae Cooper & Cooper, 1997), a decapod (Decapoda, Cambaridae) endemic to Shelta Cave in northern Alabama, USA. Subterranean Biology 43: 11–31. |
Carya poilanei | c.50 mature individuals | c.50 mature individuals | Zhang, W-P., Bai, W-N. and Zhang, D-Y. (2022). The rediscovery of Carya poilanei (Juglandaceae) after 63 years reveals a new record from China. PhytoKeys 188: 73–82. |
Chelonoidis phantasticus | 1 | 1 [now ex situ] | Jensen, Evelyn L. et al. (2022). The Galapagos giant tortoise Chelonoidis phantasticus is not extinct. Communications Biology 5: 546. https://doi.org/10.1038/s42003-022-03483-w |
Connarus beyrichii | Many | Many | Toledo, Cássio A. P., Lucas, Eve J. and Souza, Vinicius Castro. (2022). Hiding behind the rocks: rediscovery of Connarus beyrichii (Connaraceae), an endangered species endemic to montane outcrops of southeast Brazil. Kew Bulletin 77: 505-511. |
Crataegus pisifera | Many | Many | Gilman, Arthur V. and Haines, Arthur. (2022). Rediscovery of Crataegus pisifera (Rosaceae: Maleae). J. Bot. Res. Inst. Texas 16(2): 357–372. |
Dendrobium petrophilum | Many | Many | Pignal, Marc, Laudereau, Christian, Gâteblé, Gildas and Laudereau, Pierre-Louis. (2022). Dendrobium petrophilum (Kraenzl.) Garay ex N.Hallé, a well-named species describing its unusual chasmophytic ecology. Adansonia, sér. 3, 44(1): 1–9. |
Diaforobiotus hyperonyx | >1 | 0 | Stec, Daniel and Morek, Witold. (2022). Reaching the Monophyly: Re-Evaluation of the Enigmatic Species Tenuibiotus hyperonyx (Maucci, 1983) and the Genus Tenuibiotus (Eutardigrada). Animals 12(3): 404. https://doi.org/10.3390/ani12030404 |
Dicerapanorpa triclada | ≥1 | ? | Wang, Ji-Shen. (2022). New and little-known species of the genus Dicerapanorpa from northwestern Yunnan, China (Mecoptera: Panorpidae). Acta Entomologica Musei Nationalis Pragae 62(1): 1–13. |
Diospyros bambuseti | >500 | >500 | Duangjai, Sutee et al. (2022). Rediscovery of Diospyros bambuseti (Ebenaceae) in Thailand: Emended taxonomic description, lectotypification, and phylogenetic placement. Phytotaxa 542(3): 271–282. |
Dipodomys gravipes | >1 | ? | Andrade, Jorge, Arteaga, María Clara and Mellink, Eric. (2022). Was the San Quintín Kangaroo Rat really rediscovered? Canadian Journal of Zoology 101(2): 114–121. https://doi.org/10.1139/cjz-2022-0082 |
Euphorbia remyi hanaleiensis | c.100 | c.100 | Wood, Kenneth R. and Walsh, Seana K. (2022). Notes on the Hawaiian Flora: Kaua‘i Rediscoveries and Range Extensions. Records of the Hawaii Biological Survey for 2021. Edited by Neal L. Evenhuis, N.L. Bishop Museum Occasional Papers 142: 27–34. |
Fibulia myxillioides | 10 | 0 | Schejter, Laura, Cristobo, Javier and Ríos, Pilar. (2022). Rediscovering Fibulia myxillioides (Burton, 1932) (Porifera, Poecilosclerida) in the SW Atlantic Ocean. Pan-American Journal of Aquatic Sciences 17: 16. doi.org/10.54451/PanamJAS.17.1.16 |
Gasteranthus extinctus | Many | Many | Pitman, N. C. A., White, D. M., Guevara Andino, J. E., Couvreur, T. L. P., Fortier, R. P., Zapata, J. N., Cornejo, X., Clark, J. L., Feeley, K. J., Johnston, M. K., Lozinguez, A. and Rivas-Torres, G. (2022). Rediscovery of Gasteranthus extinctus L.E.Skog & L.P.Kvist (Gesneriaceae) at multiple sites in western Ecuador. PhytoKeys 194: 33–46. |
Haemaphysalis danieli | 127 | 0 | Ahmad, Iftikhar, Ullah, Shafi, Alouffi, Abdulaziz et al. (2022). Description of Male, Redescription of Female, Host Record, and Phylogenetic Position of Haemaphysalis danieli. Pathogens 11(12): 1495. https://doi.org/10.3390/pathogens11121495 |
Justicia tanalensis | ≥1 | ? | Onjalalaina, Guy E., Jiang, Hui, Rakotonasolo, Andrimalala R., Wanga, Vincent Okelo and Hu, Guang-Wan. (2022). Reappraisal and lectotypification of Justicia tanalensis S. Moore (Acanthaceae), rediscovered from central Madagascar more than 100 years since the last collection. Phytotaxa 573(2): 293–300. |
Lasia pulla | 1 | 0 | Barahona-Segovia, Rodrigo M., Valdés-Guzmân, Vicente, Pañinao-Monsálvez, Laura and Araya, Juan Francisco. (2022). Rediscovery and redescription of the rare hummingbird fly Lasia pulla (Diptera: Acroceridae) from the Valdivian evergreen forest, Chile. Caldasia 44(1): 194–199. |
Lecocarpus leptolobus | ≥1 | ? | Tye, Alan and Díaz, Patricia Jaramillo. (2022). Rediscovery of the Galapagos endemic Lecocarpus leptolobus (Asteraceae), its morphology, distribution and taxonomy relative to its congeners. Botanical Journal of the Linnean Society 200(2): 270–284. |
Leiostracus carnavalescus | 3 | 3 | Rosa, Rafael Masson, Cavallari, Daniel Caracanhas and Salvador, Rodrigo Brincalepe. (2022). iNaturalist as a tool in the study of tropical molluscs. PLoS ONE 17(5): e0268048. https://doi.org/10.1371/journal.pone.0268048 |
Leptochilus quintus | 14 | 2 |
Polašek, Ozren. (2022). The description of Leptochilus quintus Gusenleitner, 1991, female, with further notes on its distribution and life cycle (Hymenoptera, Vespidae). Linzer biol. Beitr. 54(1): 251–256. Polašek, Ozren. (2022). Re-discovery of Leptochilus quintus Gusenleitner from Mosor Mountain, Croatia (Hymenoptera; Vespidae), after 136 years of presumed extinction. Natura Croatica 31(2): 217–224. |
Lepus altamirae | 2 | 2 | Silva-Caballero, Adrián and Rosas-Rosas, Octavio Cesar. (2022). Rediscovery of the Tamaulipas white-sided jackrabbit (Lepus altamirae) after a century from its description. Therya Notes 3: 1–5. |
Leratia scaberrima | ≥1 | ? | He, Si et al. (2022). Rediscovery of the Chinese endemic Florschuetziella scaberrima (Bryophyta: Orthotrichaceae) a century after its description leads to its transfer to Leratia. Bryophyte Diversity & Evolution 45(1): 188–198. |
Leutea translucens | Many? | >1 | Ghorbanalizadeh, Atefeh and Akhani, Hossein. (2022). Plant diversity of Hyrcanian relict forests: An annotated checklist, chorology and threat categories of endemic and near endemic vascular plant species. Plant Diversity 44(1): 39–69. |
Luperosaurus sorok | ≥1 | ? | Fukuyama, Ibuki, Hossman, Mohamad Yazid and Nishikawa, Kanto. (2022). Rediscovery of Luperosaurus sorok Das, Lakim, and Kandaung, 2008 (Squamata, Gekkonidae) With Notes on Its Taxonomy and Natural History. Journal of Herpetology 56(2): 241–248. |
Machadagrion garbei | 10 | 0 | Vilela, Diogo Silva, Lencioni, Frederico Augusto De Atayde, Furieri, Karina Schmidt and Santos, Jean Carlos. (2022). The rediscovery of Machadagrion garbei (Santos, 1961) (Odonata: Coenagrionidae) with notes on the hitherto unknown female. Zootaxa 5124(3): 391–396. |
Macromia flinti | 12 | 12 | Sumanapala, A. P., Ranasinghe, T. and Pushpalal, M. G. S. (2022). Rediscovery of Macromia flinti with observations on the female and novel faunistic records (Odonata: Macromiidae). Notulae Odonatologicae 9(9): 419–428. |
Masirana glabra | ≥5 | ≥2 | Ballarin, Francesco and Eguchi, Katsuyuki. (2022). Rediscovery of the troglobitic midget-cave spiders Masirana glabra (Komatsu 1957) with redescription of the male and first description of the unknown female (Araneae: Leptonetidae). Acta Arachnologica 71(1): 53–58. |
Melanoplus macclungi | Many | Many | Harman, Alexander J. and Hoback, W. W. (2022). New state records for Melanoplus macclungi (Orthoptera: Acrididae) and notes on its biology. Journal of the Kansas Entomological Society 94(1): 1–12. |
Melicope nealae | 1 | 1 | Wood, Kenneth R. and Walsh, Seana K. (2022). Notes on the Hawaiian Flora: Kaua‘i Rediscoveries and Range Extensions. Records of the Hawaii Biological Survey for 2021. Edited by Neal L. Evenhuis, N.L. Bishop Museum Occasional Papers 142: 27–34. |
Mischocyttarus tapuya | Many | 0 | Silveira, Orlando T. et al. (2022). Rediscovery of the social wasp Mischocyttarus (Kappa) tapuya Schulz, with description of the female, larva and nest (Vespidae, Polistinae). Zootaxa 5120(2): 289–294. |
Molophilus flavocingulatus | 5 | 0 | Billingham, Zacariah D. and Theischinger, Gunther. (2022). New and poorly known species of crane flies (Diptera: Limoniidae) from New South Wales, Australia. Records of the Australian Museum 74(1): 19–40. |
Mycelephas robustus | ≥1 | ? | Miglio, Beatriz Valente and Monteiro, Josiane Santana. (2022). Mycelephas robustus (Ascomycota incertae sedis) rediscovered in the Amazon after 37 years. Phytotaxa 544(3): 295–300. |
Myopordon aucheri | <50 | <50 | Dinarvand, M. and Mozaffarian, V. (2022). Rediscovery of Myopordon aucheri Boiss. (Asteraceae) from southwest Iran. Iranian Journal of Botany 28(2): 161–164. |
Nesokia bunnii | 1 | 0 | Mahmoudi, Ahmad, Jalali, Ali Sajad, Burgani, Keramat Hafezi, Saki, Mohammad and Kryštufek, Boris. (2022). First record of the elusive and endangered long-tailed nesokia, Nesokia bunnii, in Iran. Mammalia 86(4): 338–341. |
Nesokia bunnii | 1 | 1 | Dinets, Vladimir and Maikov, Michael. (2022). Long-tailed Bandicoot Rat (Nesokia bunnii) is not extinct. Zoology in the Middle East 68(2): 180–182. |
Octomeria romerorum | <50 | <50 | Krahl, Dayse Raiane Passos, Krahl, Amauri Herbert, Chiron, Guy and Terra-Araújo, Mário Henrique. (2022). Rediscovery and first record of Octomeria romerorum (Orchidaceae, Pleurothallidinae) for Brazil. Brittonia 74: 202–206. |
Oligodon melaneus | 1 | 0 [roadkill specimen] | Das, Abhijit et al. (2022). Rediscovery and systematics of the rarely encountered Blue-bellied kukri snake (Oligodon melaneus Wall, 1909) from Assam, India. Zootaxa 5138(4): 417–430. |
Papaipema dribi | ? | ? | Metzler, Eric H. (2022). Rediscovery of Papaipema dribi Barnes & Benjamin, 1926 (Noctuidae: Noctuinae: Apameini) After 95 Years. The Journal of the Lepidopterists' Society 76(2): 149–151. |
Paragalactinia hypoleuca | Many | Many | van Vooren, N. (2022). Rediscovery of Galactinia hypoleuca in Portugal and Corsica, and its combination in Paragalactinia (Pezizaceae). Fungi Iberici 2: 89–96. |
Perlodinella microlobata | 5 | 0 | Huo, Qing-Bo et al. (2022). Rediscovery of Perlodinella microlobata Wu, 1938, with notes on Tibetisoperla sclerotica Yan, Chen, Bozdogan & Li, 2022 (Plecoptera: Perlodidae). Zootaxa 5205(2): 26–34. |
Phrynomedusa appendiculata | "breeding population" | only 1 specimen collected | Pavan, Dante, Martensen, Alexandre Camargo, Amaro, R. C., Bata, Dlio and Moraes, Leandro J. C. L. (2022). Rediscovery of the rare Phrynomedusa appendiculata (Lutz, 1925) (Anura: Phyllomedusidae) from the Atlantic Forest of southeastern Brazil. Zootaxa 5087(4): 522–540. |
Phyllanthus allemii | Many | Many | Mendes, Jone Clebson Ribeiro et al. (2022). Novelties in Phyllanthus (Phyllanthaceae) from the Brazilian Cerrado: new records of the rare species P. allemii. Phytotaxa 538(2): 149–156. |
Platerus pilcheri | 1 | 1 | Sankararaman, H., Agarwal, A., Lemaître, V. A. and Ghate, H. V. (2022). Rediscovery of Platerus pilcheri Distant (Hemiptera: Reduviidae), a forgoten assassin bug from India, with comments on its range extension. Journal of Threatened Taxa 14(2): 20631–20636. |
Primula esquirolii | 44 mature individuals | 44 mature individuals | Wu, Zhikun, Wu, Yuan and Zhang, Na. (2022). Rediscovery of the Critically Endangered Primula esquirolii, a karst cave species with an extremely small population endemic to China. Oryx 57(4): 540–542. https://doi.org/10.1017/S0030605322001223 |
Primula xanthopa | 1 | 1 | Shacha, N., Sangay, K. , Dendup, T. and Ghalley, T. B. (2022). Endemic Primula xanthopa Balf.f. & R.E. Cooper: rediscovery after 88 years from Bumdeling Wildlife Sanctuary, Bhutan. Journal of Threatened Taxa 14(4): 20946–20950. |
Pristimantis alalocophus | 1 | 1 | González-Acosta, Cristian and Duarte-Marín, Sebastián. (2022). Rediscovery of the Quindío robber frog Pristimantis alalocophus in a new locality in the Department of Quindío, Colombia. The Herpetological Bulletin 159: 38–40. |
Pristimantis nebulosus | 3 | 0 | Köhler, Jörn et al. (2022). Rediscovery, redescription and identity of Pristimantis nebulosus (Henle, 1992), and description of a new terrestrial-breeding frog from montane rainforests of central Peru (Anura, Strabomantidae). Zoosystematics and Evolution 98(2): 213–232. |
Promenaea microptera | >1 | >1 | Barberena, Felipe Fajardo V. A., Gastin, Jorge Rodrigues and Smidt, Eric De Camargo. (2022). Taxonomical remarks on Promenaea microptera (Orchidaceae: Epidendroideae): the rediscovery of a poorly known micro-endemic orchid from the Brazilian Atlantic Forest. Phytotaxa 545(2): 229–233. |
Psychotria catanduaniensis | 1 | 1 | Biag, Rachel D. and Alejandro, Grecebio Jonathan D. (2022). Range extension and emended description of the threatened Psychotria catanduaniensis (Rubiaceae) in the coastal area in Palanan, Isabela, Luzon, Philippines. Nordic Journal of Botany 2022(4). https://doi.org/10.1111/njb.03422 |
Psychotria exellii | >1 | >1 | Stévart, T. et al. (2022). Diversity of the Vascular Plants of the Gulf of Guinea Oceanic Islands, pp. 249-271. In: Ceríaco, L. M. P., de Lima, R. F., Melo, M. and Bell, R. C. (eds.). Biodiversity of the Gulf of Guinea Oceanic Islands. Cham, Switzerland: Springer. |
Punctulum reticulatum | >1 | 0 | Hasegawa, Kazunori. (2022). Bathyal Rissoidae (Gastropoda: Rissooidea) off the Russian Far East coast of the Sea of Japan, with redescription of Punctulum reticulatum Golikov, 1986. Ruthenica 32(2): 85–92. |
Retiperidiolia reticulata | >1 | >1 | Kraisitudomsook, Nattapol, Choeyklin, Rattaket, Boonpratuang, Thitiya, Pobkwamsuk, Maneerat, Anaphon, Sakaokan and Smith, Matthew E. (2022). Hidden in the tropics: Retiperidiolia gen. nov., a new genus of bird’s nest fungi (Nidulariaceae), and a systematic study of the genus Mycocalia. Mycological Progress 21: 56. https://doi.org/10.1007/s11557-022-01807-y |
Rheumaptera mochica | 14 | 0 | Vargas, Héctor A., Solis, M. Alma and Vargas-Ortiz, Marcelo. (2022). The South American moth Rheumaptera mochica (Dognin, 1904) (Lepidoptera, Geometridae, Larentiinae) rediscovered after more than a century of anonymity. ZooKeys 1085: 129–143. |
Rhinolophus hilli | 46 | 46 | Flanders, Jon et al. (2022). Rediscovery of the critically endangered Hill's horseshoe bat (Rhinolophus hilli) and other new records of bat species in Rwanda. Biodiversity Data Journal 10: e83546. https://doi.org/10.3897/BDJ.10.e83546 |
Scydmaenus kasuganus | 5 | 0 | Jałoszyński, Paweł. (2022). Rediscovery and re (re) description of Scydmaenus kasuganus Franz, the only Japanese species of the subgenus Mascarensia Franz (Coleoptera, Staphylinidae, Scydmaeninae). Zootaxa 5093(1): 38–48. |
Themeda saxicola | Many | Many | Chorghe, Alok R. and Kulloli, R. N. (2022). Rediscovery and IUCN threat assessment of Themeda saxicola (Poaceae: Andropogoneae), an endemic grass from the Eastern Ghats, India, Phytotaxa 532(2): 161–168. |
Varronia neowediana | ≥1 | ? | de Sousa Silva, Thaynara, Athiê-Souza, Sarah Maria and de Melo, José Iranildo Miranda. (2022). Taxonomic novelties in Varronia (Cordiaceae): Rediscovery of V. neowediana and lectotypification of V. macrocephala. Brittonia 74: 280–289. |
References
Albani Rocchetti, G., Carta, A., Mondoni, A., Godefroid, S., Davis, C. C., Caneva, G., Albrecht, M. A., Alvarado, K., Bijmoer, R., Borosova, R., Bräeuchler, C., Breman, E., Briggs, M., Buord, S., Cave, L. H., Da Silva, N. G., Davey, A. H., Davies, R. M., & Dickie, J. B., …Abeli, T. (2022). Selecting the best candidates for resurrecting extinct-in-the-wild plants from herbaria. Nature Plants 8: 1385–1393.
Diesmos, A. C., Parham, J. F., Stuart, B. L., & Brown, R. M. (2005). The phylogenetic position of the recently rediscovered Philippine forest turtle (Bataguridae: Heosemys leytensis). Proceedings of the California Academy of Sciences 56(3): 31–41.
Folch, J., Cocero, M. J., Chesné, P., Alabart, J. L., Domínguez, V., Cognié, Y., Roche, A., Fernández-Árias, A., Martí, J. I., Sánchez, P., Echegoyen, E., Beckers, J. F., Sánchez Bonastre, A., & Vignon, X. (2009). First birth of an animal from an extinct subspecies (Capra pyrenaica pyrenaica) by cloning. Theriogenology 71(6): 1026–1034.
Hilbers, J. P., Santini, L., Visconti, P., Schipper, A. M., Pinto, C., Rondinini, C., & Huijbregts, M. A. J. (2017). Setting population targets for mammals using body mass as a predictor of population persistence. Conservation Biology 31(2): 385–393.
Huang, S.-Y., Zhu, L.-J., Chen, E.-Y., Xu, Y.-Q., Wang, M., Fan, X.-L., Pan, Z.-H., & Espeland, M. (2022). Contribution to the knowledge of the genus Agalope Walker from mainland China with descriptions of four new species (Lepidoptera, Zygaenidae, Chalcosiinae). Zootaxa 5165(4): 557–574.
Humphreys, A. M., Govaerts, R., Ficinski, S. Z., Lughadha, E. N., & Vorontsova, M. S. (2019). Global dataset shows geography and life form predict modern plant extinction and rediscovery. Nature Ecology & Evolution 3: 1043–1047.
Jałoszyński, P. (2022). Rediscovery and re (re) description of Scydmaenus kasuganus Franz, the only Japanese species of the subgenus Mascarensia Franz (Coleoptera, Staphylinidae, Scydmaeninae). Zootaxa 5093(1): 38–48.
Keith, D. A., & Burgman, M. A. (2004). The Lazarus effect: can the dynamics of extinct species lists tell us anything about the status of biodiversity? Biological Conservation 117(1): 41–48.
Ladle, R. J., Jepson, P., Malhado, A. C. M., Jennings, S., & Barua, M. (2011). The causes and biogeographical significance of species’ rediscovery. Frontiers of Biogeography 3(3): 111–118.
Nunney, L., & Campbell, K. A. (1993). Assessing minimum viable population size: demography meets population genetics. Trends in Ecology & Evolution 8(7): 234–239.
Reed, D. H., O'Grady, J. J., Brook, B. W., Ballou, J. D., & Frankham, R. (2003). Estimates of minimum viable population sizes for vertebrates and factors influencing those estimates. Biological Conservation 113(1): 23–34.
Sumanapala, A. P., Ranasinghe, T., & Sumanapala, D. (2022). Rediscovery of Anisogomphus ceylonicus (Odonata: Gomphidae) based on its larva. Taprobanica: The Journal of Asian Biodiversity 11(1): 35–37. https://www.doi.org/10.47605/tapro.v11i1.276
Toledo, L. F., de Carvalho-e-Silva, S. P., de Carvalho-e-Silva, A. M. P. T., Gasparini, J. L., Baêta, D., Rebouças, R., Haddad, C. F. B., Becker, C. G., & Carvalho, T. (2023). A retrospective overview of amphibian declines in Brazil's Atlantic Forest. Biological Conservation 277: 109845. https://doi.org/10.1016/j.biocon.2022.109845
Turner, D. A., & Bradley, J. E. (2022). The rediscovery of the colomanni von Madarász subspecies of the Grey Penduline-tit Anthroscopus caroli. Scopus 42(1): 41–44.
Vilela, D. S., Lencioni, F. A. D. A., Furieri, K. S., & Santos, J. C. (2022). The rediscovery of Machadagrion garbei (Santos, 1961) (Odonata: Coenagrionidae) with notes on the hitherto unknown female. Zootaxa 5124(3): 391–396.
Wood, K. R., & Walsh, S. K. (2022). Notes on the Hawaiian Flora: Kaua‘i Rediscoveries and Range Extensions. Records of the Hawaii Biological Survey for 2021. Edited by Neal L. Evenhuis, N.L. Bishop Museum Occasional Papers 142: 27–34.