The roles of aridification and sea level changes in the diversification and persistence of freshwater fish lineages
The process of publishing science is a lengthy one – there are many rounds of revisions, assessments, and review required before a paper can be published. With that, I’m very proud to announce that the first paper from my PhD has recently been published in the journal Molecular Ecology. This paper is a collection of a lot of complex analyses, and addressing some relatively complicated biogeographical questions, so I’ve decided to provide a simplified summary here.
Earlier in the year, I had made a comment that, as part of the natural evolution of this blog, I would try to change up the writing format every now and then to something a little more personal, emotional and potentially derivative from science. I must confess that this is one of those weeks, as it’s been an emotional rollercoaster for me. So, sorry in advance for the potentially self-oriented, reflective nature of this piece.
Just a few applications of genetic information in conservation management, such as in breeding programs and pedigrees (left), identifying new/cryptic species (centre) and identifying and maintaining populations and their structure (right).
The Invaders
Contrastingly, sometimes we might also use genetic information to do the exact opposite. While so many species on Earth are at risk (or have already passed over the precipice) of extinction, some have gone rogue with our intervention. These are, of course, invasive species; pests that have been introduced into new environments and, by their prolific nature, start to throw out the balance of the ecosystem. Australians will be familiar with no shortage of relevant invasive species; the most notable of which is the cane toad, Rhinella marina. However, there are a plethora of invasive species which range from notably prolific (such as the cane toad) to the seemingly mundane (such as the blackbird): so how can we possibly deal with the number and propensity of pests?
A table of some of the most prolific mammalian invasive species in Australia, including when they were first introduced and why, and their (relatively) recently estimated population sizes. Source: Wikipedia (and studies referenced therein). Some estimated numbers might not reflect current sizes as they were obtained from studies over the last 10 years.
Tools for invasive species management
There are a number of tools at our disposal for dealing with invasive species. These range from chemical controls (like pesticides), to biological controls and more recently to targeted genetic methods. Let’s take a quick foray into some of these different methods and their applications to pest control.
Some of the broad categories of invasive species control. For any given pest species, such as the cane toad (top), we might choose to use a particular set of methods to reduce their numbers. These can include biological controls (such as the ladybird, for aphid populations (left)); chemical controls such as pesticides; or even genetic engineering technologies.
The broad life cycle of the cactus moth and how it controls the invasive prickly pear in Australia. The ravenous caterpillar larvae of the moth is effective at decimating prickly pears, whilst the moth’s specificity to this host means there is limited impact on other plant species.
The potential secondary impact of biological controls, and the degree of unpredictability in how they will respond to a new environment (and how native species will also respond to their introduction) leads conservationists to develop new, more specific techniques. In similar ways, viral and bacterial-based controls have had limited success (although are still often proposed in conservation management, such as the planned carp herpesvirus release).
Genetic information, more broadly, can also be useful for pest species management without necessarily directly feeding into genetic engineering methods. The various population genetic methods that we’ve exploredovera numberof different posts can also be applied in informing management. For example, understanding how populations are structured, and the sizes and demographic histories of these populations, may help us to predict how they will respond in the future and best focus our efforts where they are most effective. By including analysis of their adaptive history and responses, we may start to unravel exactly what makes a species a good invader and how to best predict future susceptibility of an environment to invasion.
A comprehensive table of the different ways genetic information could be applied in broader invasive species management programs, from Rollins et al. (2006). This paper specifically relates to pest management within Western Australia but the concepts listed here apply broadly. Many of these concepts we have discussed previously in a conservation management context as well.
The better we understand invasive species and populations from a genetic perspective, the more informed our management efforts can be and the more likely we are to be able to adequately address the problem.
Managing invasive pest species
The impact of human settlement into new environments is exponentially beyond our direct influences. With our arrival, particularly in the last few hundred years, human migration has been an effective conduit for the spread of ecologically-disastrous species which undermine the health and stability of ecosystems around the globe. As such, it is our responsibility to Earth to attempt to address our problems: new genetic techniques is but one growing avenue by which we might be able to remove these invasive pests.
Note: For some clear, interesting presentations on the topic of de-extinction, and where some of the information for this post comes from, check out this list of TED talks.
The current conservation crisis
The stark reality of conservation in the modern era epitomises the crisis disciplinethat so often is used to describe it: species are disappearing at an unprecedented rate, and despite our best efforts it appears that they will continue to do so. The magnitude and complexity of our impacts on the environment effectively decimates entire ecosystems (and indeed, the entire biosphere). It is thus our responsibility as ‘custodians of the planet’ (although if I had a choice, I would have sacked us as CEOs of this whole business) to attempt to prevent further extinction of our planet’s biodiversity.
At least from a genetic perspective, this sometimes involves trying to understand the nature and potential of adaptation from genetic variation (as a predictor of future adaptability). Or using genetic information to inform captive breeding programs, to allow us to boost population numbers with minimal risk of inbreeding depression. Or perhaps allowing us to describe new, unidentified species which require their own set of targeted management recommendations and political legislation.
How my overactive imagination pictures ‘genetic rescue’.
There’s one catch (well, a few really) with genetic rescue: namely, that one must have other populations to ‘outbreed’ with in order add genetic variation to the captive population. But what happens if we’re too late? What if there are no other populations to supplement with, or those other populations are also too genetically depauperate to use for genetic rescue?
Believe it or not, sometimes it’s not too late to save species, even after they have gone extinct. Which brings us from this (lengthy) introduction to this week’s topic: de-extinction. Yes, we’re literally (okay, maybe not) going to raise the dead.
Your textbook guide to de-extinction. Now banned in 47 countries.
Backbreeding: resurrection by hybridisation
You might wonder how (or even if!) this is possible. And to be frank, it’s extraordinarily difficult. However, it has to a degree been done before, in very specific circumstances. One scenario is based on breeding out a species back into existence: sometimes we refer to this as ‘backbreeding’.
This practice really only applies in a few select scenarios. One requirement for backbreeding to be possible is that hybridisation across species has to have occurred in the past, and generally to a substantial scale. This is important as it allows the genetic variation which defines one of those species to live on within the genome of its sister species even when the original ‘host’ species goes extinct. That might make absolutely zero sense as it stands, so let’s dive into this with a case study.
A map of the Galápagos archipelago and tortoise species, with extinct species indicated by symbology. Lonesome George was the last known living member of the Pinta Island tortoise, C. abingdonii for reference. Source: Wikipedia.
One of these species, Chelonoidis elephantopus, also known as the Floreana tortoise after their home island, went extinct over 150years ago, likely due to hunting and trade. However, before they all died, some individuals were transported to another island (ironically, likely by mariners) and did the dirty with another species of tortoise: C. becki. Because of this, some of the genetic material of the extinct Floreana tortoiseintrogressed into the genome of the still-living C. becki. In an effort to restore an iconic species, scientists from a number of institutions attempted to do what sounds like science-fiction: breed the extinct tortoise back to life.
When you saw the title for this post, you were probably expecting some Jurassic Parklevel ‘dinosaurs walking on Earth again’ information. I know I did when I first heard the term de-extinction. Unfortunately, contemporary de-extinction practices are not that far advanced just yet, although there have been some solid attempts. Experiments conducted using the genomic DNA from the nucleus of a dead animal, and cloning it within the egg of another living member of that species has effectively cloned an animal back from the dead. This method, however, is currently limited to animals that have died recently, as the DNA degrades beyond use over time.
The same methods have been attempted for some extinct animals, which went extinct relatively recently. Experiments involving the Pyrenean ibex (bucardo) were successful in generating an embryo, but not sustaining a living organism. The bucardo died 10 minutes after birth due to a critical lung condition, as an example.
The challenges and ethics of de-extinction
One might expect that as genomic technologies improve, particularly methods facilitated by the genome-editing allowed from CRISPR/Cas-9 development, that we might one day be able to truly resurrect an extinct species. But this leads to very strongly debated topics of ethics and morality of de-extinction. If we can bring a species back from the dead, should we? What are the unexpected impacts of its revival? How will we prevent history from repeating itself, and the species simply going back extinct? In a rapidly changing world, how can we account for the differences in environment between when the species was alive and now?
The Chaotic Neutral (?) approach to de-extinction.
There is no clear, simple answer to many of these questions. We are only scratching the surface of the possibility of de-extinction, and I expect that this debate will only accelerate with the research. One thing remains eternally true, though: it is still the distinct responsibility of humanity to prevent more extinctions in the future. Handling the growing climate change problem and the collapse of ecosystems remains a top priority for conservation science, and without a solution there will be no stable planet on which to de-extinct species.
You bet we’re gonna make a meme months after it’s gone out of popularity.