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Systematic identification of plausible pathways to potential harm via problem formulation for investigational releases of a population suppression gene drive to control the human malaria vector Anopheles gambiae in West Africa
Malaria Journal volume 20, Article number: 170 (2021)
Population suppression gene drive has been proposed as a strategy for malaria vector control. A CRISPR-Cas9-based transgene homing at the doublesex locus (dsxFCRISPRh) has recently been shown to increase rapidly in frequency in, and suppress, caged laboratory populations of the malaria mosquito vector Anopheles gambiae. Here, problem formulation, an initial step in environmental risk assessment (ERA), was performed for simulated field releases of the dsxFCRISPRh transgene in West Africa.
Building on consultative workshops in Africa that previously identified relevant environmental and health protection goals for ERA of gene drive in malaria vector control, 8 potentially harmful effects from these simulated releases were identified. These were stratified into 46 plausible pathways describing the causal chain of events that would be required for potential harms to occur. Risk hypotheses to interrogate critical steps in each pathway, and an analysis plan involving experiments, modelling and literature review to test each of those risk hypotheses, were developed.
Most potential harms involved increased human (n = 13) or animal (n = 13) disease transmission, emphasizing the importance to subsequent stages of ERA of data on vectorial capacity comparing transgenics to non-transgenics. Although some of the pathways (n = 14) were based on known anatomical alterations in dsxFCRISPRh homozygotes, many could also be applicable to field releases of a range of other transgenic strains of mosquito (n = 18). In addition to population suppression of target organisms being an accepted outcome for existing vector control programmes, these investigations also revealed that the efficacy of population suppression caused by the dsxFCRISPRh transgene should itself directly affect most pathways (n = 35).
Modelling will play an essential role in subsequent stages of ERA by clarifying the dynamics of this relationship between population suppression and reduction in exposure to specific potential harms. This analysis represents a comprehensive identification of plausible pathways to potential harm using problem formulation for a specific gene drive transgene and organism, and a transparent communication tool that could inform future regulatory studies, guide subsequent stages of ERA, and stimulate further, broader engagement on the use of population suppression gene drive to control malaria vectors in West Africa.
The World Health Organization (WHO) estimated in 2019 there were 229 million cases of malaria globally, accounting for 409,000 deaths . Persistent threats from insecticide resistance have created the need for additional, complementary strategies to control the mosquito vectors that are responsible for transmission of disease [2,3,4,5]. Based on mathematical modelling studies, the use of gene drive in vectors such as Anopheles gambiae has been proposed as one such complementary approach to vector control [6,7,8,9,10,11,12].
Recent advances in the development of synthetic gene drives involve the use of a transgene encoding CRISPR-Cas9 endonuclease that is expressed from a germline promoter, coupled with expression of a guide RNA targeting a specific DNA sequence [13,14,15,16,17,18,19]. In heterozygous transgenics, the transgene is inserted at the target site of the guide RNA on one chromosome, while the target site on the homologous chromosome is wild type. In the germline of such heterozygotes, Cas9 uses the guide RNA to recognize and cleave the target sequence of the wild-type chromosome. This causes a double-stranded break in the germline at the target sequence, which is repaired using the homologous chromosome containing the transgene as a template, so that the transgene is copied onto the homologous chromosome that had previously been wild type, in a process known as ‘homing’.
Thus, homing converts a proportion of the germline in transgenics to homozygosity so that a greater proportion of gametes contain the transgene, and therefore a greater proportion of offspring will inherit the transgene than would otherwise be the case. Homing, therefore, allows the transgene to spread through a population with super-Mendelian inheritance. This means that, unlike some other genetically modified insect vector control approaches, gene drive transgenes are intended to increase in frequency and persist in the target organism (TO) to achieve lasting impact on disease transmission .
‘Population suppression gene drive’ is a potential way to exploit such a homing transgene in order to decrease the density of mosquito vector populations and thus reduce malaria transmission [5, 12, 21]. One method involves exploitation of a haplo-sufficient female fertility gene, mutations of which can cause female sterility when homozygous, but not when heterozygous [6, 12, 16, 17, 21]. The CRISPR-Cas9 system is encoded by a transgene that uses a guide RNA to target such a female fertility gene allowing the transgene to spread at super-Mendelian levels through the population via homing, disrupting the female fertility gene as it does so. As the heterozygous transgenics are fertile, their frequency steadily increases in the population after introduction of the transgene. As heterozygous transgenic females and males begin increasingly to encounter and mate with each another, the proportion of the female population that is homozygous for the transgene increases. However, as they are sterile, the number of viable eggs produced decreases until eventually the population is suppressed .
The Target Malaria not-for-profit research consortium has been engaged in the co-development of gene drive as a malaria vector control tool in Africa . Before a population suppression gene drive system undergoes regulatory review for field release, plausible risks to human health and the environment must first be identified and assessed [3, 4, 23,24,25,26,27,28,29,30,31,32,33,34,35]. Indeed, James et al.  proposed that “the safety standard for moving an investigational gene drive product from physical confinement to field testing should be a well-reasoned justification that it will do no more harm to human health than wild-type mosquitoes of the same genetic background and no more harm to the ecosystem than other conventional vector control interventions.”
Problem formulation is a rigorous scientific analysis that defines the overall parameters for an environmental risk assessment (ERA) and facilitates the systematic identification of potential harms or hazards, as well as their routes of exposure, whilst being transparent about the assumptions that have been made during the process (see Table 1 for Glossary of Terms) [33,34,35,36,37,38,39]. The WHO has developed a guidance framework for testing genetically modified mosquitoes to ensure that organisms are effective and competitive and that risks are reduced to acceptable levels , so that gene drive organisms intended for release should have already been tested for deleterious phenotypes or unacceptable, unintended effects during product development. Thus, ERAs can focus on the introduced genetic construct and the intended outcome. ERAs should specifically address protection goals that are identified from policy, legislative, regulatory and community requirements from the region where the intervention is being considered. Referring to such protection goals, a wide range of potential harms is initially considered in a highly iterative, systematic approach involving a diverse range of expert input. An ERA of the release of a genetically modified organism needs to consider both direct effects on individual organisms that the transgenic itself generates, such as via predation, competition, habitat alteration, hybridization and introduction of new parasites and diseases, and indirect effects such as those on individual organisms in the wider environment without immediate contact with the transgenic (Table 1) . Based on the biological information available on both the transgenic and its parental species, as well as the wider environment into which the transgene will be released, the plausibility of each pathway to potential harm to the identified protection goals is examined by establishing the causal chain of events, sometimes condensed to “pathway to harm” . To determine the cogency of each pathway, risk hypotheses are constructed that can be used to interrogate individual steps in the pathway. Next, an analysis plan is developed that includes both defined measurement endpoints to test risk hypotheses and other potential sources of evidence aimed at reducing identified areas of uncertainty surrounding pathways to each potential harm. Such evidence may be sought from pre-existing literature, modelling, new experimental investigations, previous experiences , or any combination thereof. The analysis plan will make important contributions to subsequent steps of hazard, exposure and risk characterization in the ERA. This also allows the identification of hypotheses that can be tested most reliably and efficiently. The potential for harms to occur can be considered negligible where a risk hypothesis can be accepted on the basis of unequivocal evidence and minimal remaining uncertainties surrounding the pathway. Where this is not possible, a number of risk hypotheses must be tested using a ‘weight of evidence’ approach that draws upon several sources of evidence for assessment of the pathway [35, 42].
Problem formulation has previously been used to identify potential harms or hazards and routes of exposure for the control of insect pests  and potential releases of generic gene drive systems for malaria vector control in Africa [44,45,46]. Romeis et al.  reported on pathways to harm for population suppression gene drive in the agricultural pest Drosophila suzukii, identifying (i) indirect food-web effects; (ii) toxicity from the transgene; and, (iii) gene transfer to other species as potential harms. David et al.  identified ecological harms as a first step towards an ERA, distinguishing between transient and steady state harms but without specific reference to protection goals or pathways. Roberts et al.  derived protection goals on human health, animal health, biodiversity and water quality for broad classes of gene drive, identifying numerous high-level potential harms belonging to each of these categories, although they were not mapped onto individual pathways to harm, so that risk hypotheses and analysis plans were not developed or reported. Based on a series of four workshops in different African countries, Teem et al.  reported a problem formulation exercise based on four different types of gene drive to control malaria, identifying many protection goals similar to those previously reported , along with six high-level, consensus pathways to harm. However, the authors recognized that the approach was not designed to constitute a comprehensive first step in a specific ERA exercise and developed only limited analysis plans for each pathway .
Here, problem formulation was used to systematically and comprehensively map 46 plausible pathways to potential harm from the simulated investigational release in West Africa of a population suppression gene drive that would employ the CRISPR-Cas9 system to target the doublesex female fertility gene (dsxFCRISPRh) [17, 19]. For each of these pathways, risk hypotheses and an analysis plan were developed , which will be used to inform subsequent steps of hazard and exposure characterization in an ERA for population suppression gene drive in West Africa.
Defining Anopheles gambiae
The Anopheles gambiae species complex, or Anopheles gambiae senso lato (s.l.), is currently considered to be made up of nine cryptic species, namely Anopheles amharicus, also referred to in earlier publications as “species B of Anopheles quadriannulatus” ; Anopheles arabiensis, referred to in earlier publications as “species B of An. gambiae” ; Anopheles bwambae, referred to in earlier publications as “species D of An. gambiae” ; Anopheles coluzzii, referred to as “the M form of An. gambiae sensu stricto (s.s.)” in earlier publications ; Anopheles fontenillei; An. gambiae s.s., referred to as “the S form of An. gambiae s.s.” in earlier publications ; Anopheles melas; Anopheles merus; and An. quadriannulatus, referred to in earlier publications as “species C of An. gambiae” or “species A of An. quadriannulatus” [48,49,50,51,52].
Throughout this paper, the term An. gambiae is used when referring to the An. gambiae species complex and An. gambiae s.s. when referring to that particular species within the An. gambiae complex. Anopheles gambiae s.s. and An. coluzzii were previously considered to be a single species, known as “species A of An. gambiae” in earlier publications, but appear to have been undergoing a process of speciation . Of species from the An. gambiae complex, An. coluzzii, An. gambiae s.s. and An. arabiensis have been identified as dominant malaria vectors , while others are considered to be minor vectors of malaria, often because of their preference for blood meals from animal hosts [54,55,56].
Defining the transgenic strain and release conditions
This problem formulation was based on a theoretical release of a strain of An. coluzzii, which contains a transgene encoding the fluorescent marker gene, DsRed, and the CRISPR-Cas9 system to target conserved sequences of a female-specific isoform of the haplo-sufficient doublesex gene (dsxF) . This transgene (dsxFCRISPRh) disrupts the female-specific exon of the doublesex gene so that homozygous transgenic females (dsxFCRISPRh/dsxFCRISPRh) are completely infertile, have altered morphology and do not bite, and therefore neither feed on blood nor transmit malaria. By contrast, heterozygotes (dsxFCRISPRh/+) are typically fertile and can bite, although somatic mosaicism has been reported in some heterozygous females that had received the dsxFCRISPRh allele paternally leading to anatomical alterations of varying penetrance . The hypothetical field protocol follows a scenario modelled in the simulated annual releases of 5000 transgenic heterozygous males over a six-year period in 1% of human settlements in a 1 million sq. km grid in West Africa, as described in North et al. .
Over this area, the predominant malaria vectors are the species An. gambiae s.s. and An. coluzzii [57,58,59]. Anopheles gambiae s.s. favours laying eggs in aquatic habitats that are small, clean, sunlit, lacking vegetation and ephemeral, so that they quickly dry out and thus development of aquatic stages of this species is relatively fast. By contrast, An. coluzzii favours larger, more permanent bodies of water, often with overhanging vegetation, such as the banks of rivers with slow-moving water or irrigation channels of rice paddies, where larval developmental times typically are longer [57,58,59].
The region of release consists of both savannah and semi-arid regions in the Sahel with areas experiencing a range of seasonality: some areas contain year-round larval aquatic habitats, whilst others have two main seasons, a rainy or wet season which lasts roughly from April to October and a dry season, which thus affects the availability of most aquatic habitats of An. gambiae. In addition, human settlements in the area also vary significantly in their degree of connectedness with other settlements, thus affecting the ease with which vectors can migrate from one human population to another.
A broad outline of intended efficacy outcomes from release of this strain is illustrated in Fig. 1. Spatial modelling has indicated that releases in this region of relatively small numbers of dsxFCRISPRh transgenics are likely to lead to a range of entomological outcomes from near-complete population suppression to intermediate states where transgenic and wild-type alleles reach equilibrium levels within the population depending on the seasonality and connectivity of the release location to other human settlements [19, 60].
Defining the population dynamics of gene drive genotypic risk profiles
The dynamics of the increase in frequency of the transgene in mosquito populations will vary across the landscapes where releases might take place, due to spatial and temporal heterogeneity in environmental conditions. In particular, differing levels of seasonality from one location to another may lead to spatial variation in risk exposure . Using the model developed by North et al. , a specific analysis was carried out to differentiate between the frequency of transgenic heterozygotes (dsxFCRISPRh/+) and homozygotes (dsxFCRISPRh/dsxFCRISPRh) under different conditions of seasonality and connectedness between human settlements (Fig. 2). Simulations found that the transgene typically establishes in local (village) populations via heterozygous mosquitoes, which then increase in abundance to precipitate the production of homozygotes. In aseasonal populations, the number of homozygotes will eventually surpass that of heterozygotes and this dynamic results in sustained population suppression. In populations that have strong seasonal fluctuations in size, however, both the transgenic genotypes may establish concurrently before being maintained at roughly equivalent levels in yearly cycles, resulting in more limited population suppression (Fig. 2). Seasonality may therefore influence risk exposure both through its effect on population suppression per se, and by how it mediates the relative frequencies of biting heterozygotes and non-biting homozygotes.
Defining target organisms
Species of the An. gambiae complex show only partial reproductive isolation and, for at least some of the species that live in sympatry, hybrids have been observed in nature at low frequencies [51, 61,62,63,64,65,66], and gene flow has been inferred from genomic analyses [65,66,67,68,69,70]. Moreover, because the guide RNA target sequence of the dsxFCRISPRh transgene is conserved in all of the above species examined , the transfer of this transgene between any of these species via hybridization may lead to functional gene drive and population suppression in those species. It is, however, possible that some species of the complex would undergo less efficacious population suppression than others, should they be inefficiently targeted by gene drive via assortative mating, or where there might be species-specific resistance (Fig. 1).
The most closely related species to those within the An. gambiae complex is Anopheles christyi, which is also in the pyretophorus series of sub-genus Cellia , but differs morphologically and is genetically distinct from species of An. gambiae, being separated by circa 9 million years of evolution . The absence of observed gene flow between species of An. gambiae and An. christyi supports the lack of any significant hybridization between these species so that, for even less closely related species of Anopheles, hybridization is considered implausible. Moreover, in species of Anopheles more distantly related to An. gambiae than An. christyi, the guide RNA target DNA sequence of the dsxFCRISPRh transgene diverges from that found in An. gambiae .
Therefore, for the purposes of this problem formulation, the nine species of An. gambiae listed above were considered to be ‘inside the complex’ and, therefore, TOs of the population suppression gene drive. All other species that are ‘outside the complex’ were therefore regarded as non-target organisms (NTOs), including the remaining 316 mosquito species (Family: Culicidae) that have been reported in countries of West Africa lying within the 1 million sq. km grid of simulated field releases from this study, namely Burkina Faso, Mali, Côte D’Ivoire, Ghana, Togo, Bénin, Nigeria, and Niger [19, 60, 73, 74].
Defining intended efficacy outcomes and their relationships to potential harms
The high-level pathway to intended efficacy outcomes was established and potential factors that could inhibit steps in this ‘efficacy pathway’ and the point at which they could occur were defined (Fig. 1), and from this an analysis plan was developed. Certain factors that could lead to a loss of efficacy are the subject of active screening during standard strain development processes before field release: for example, unexpected copy number or re-arrangements of the transgene would be detected by sequencing, or significant fitness costs from the transgene should be observed in insectary studies. Moreover, further assessments and field monitoring would accompany field releases, the specifications for which would be determined in subsequent risk management stages of an ERA.
While loss of efficacy following an investigational release of a population suppression gene drive would not be a harm per se, it would likely alter exposure levels to potential harms arising from both wild-type and dsxFCRISPRh transgenic vectors. For each pathway, the first steps involving intended efficacy outcomes, as illustrated in Fig. 1, are shown in dark blue, with branch points to subsequent steps in the pathway specific to the occurrence of that potential harm shown in lighter blue.
Defining protection goals and plausible pathways to potential harm
The protection goals used in this problem formulation were informed by the outputs of four, 4-day workshops organized by New Partnership for Africa’s Development of the African Union Development Agency (AUDA-NEPAD) at Accra, Ghana; Nairobi, Kenya; Gaborone, Botswana; and, Libreville, Gabon between 2016 and 2018  and a 2-day workshop organized by the Foundation for the National Institutes of Health (FNIH) at Accra, Ghana in February 2019. A 3-day workshop organized by the FNIH at Reston, USA in 2016 , extensive literature assessment, and ongoing dialogue with numerous scientific, risk and regulatory experts also contributed to this exercise. Four broad protection goals (biodiversity, water quality, human health, animal health) were identified from these previously published problem formulation exercises [45, 46]. In contrast to Teem et al. , but in keeping with Roberts et al. , soil quality was discounted as a broad protection goal that could plausibly be affected by population suppression gene drive, given that An. gambiae reflects a relatively insignificant proportion of the terrestrial biomass .
Importantly, ERA does not formally include socio-economic or legal issues, such as the potential for transboundary movement of transgenics, despite these warranting further exploration in the context of gene drive organisms that are anticipated to cross national borders. Additionally, some pathways which could extend to further potential economic and social harms beyond the direct biosafety considerations here, such as those involving potential harms to livestock, were considered out of scope for this problem formulation. Instead, such issues could be separately addressed under assessment frameworks explicitly suited to those endpoints, such as social, economic and health impact assessment [76, 77], as well as via any regional harmonization of regulatory processes [78, 79].
Potential harms to protection goals, their pathways and their analysis plans were refined in an iterative fashion involving multiple working group meetings amongst the authors, as well as subsequent review of conceptual models by 14 experts in medical entomology, vector biology, ecology, population genetics, molecular biology, protein engineering, and modelling from Africa, Europe and North America (see Acknowledgements). The plausibility of each pathway was considered, based on known biological and environmental evidence, and literature and the causal chain of events, or plausible pathway, which would be required for each potential harm to occur, were mapped out in a logical, linear order.
As part of the systematic process to validate pathways in the ERA, risk hypotheses for critical steps in each pathway were developed  and measurement endpoints were next defined to corroborate or invalidate a given risk hypothesis. By convention, each step of every pathway should ideally be accompanied by a corresponding risk hypothesis and measurement endpoints that could unambiguously test the veracity of each of those hypotheses . However, only key risk hypotheses and measurement endpoints were developed for each of the pathways here, principally to avoid duplication and to provide a transparent focus on what was considered to be the most salient elements contributing to potential harms. Additionally, other potential sources of evidence were identified that could act to reduce areas of uncertainty in certain plausible pathways. Together, measurement endpoints and potential evidence to reduce uncertainty constituted the analysis plan for each pathway. Analysis plans will therefore form a crucial aspect of the evidence base supporting subsequent stages of an ERA for the release of this population suppression gene drive in West Africa. Where relevant, an iterative and flexible tiered approach will be applied to analysis plans in both the testing of measurement endpoints and sourcing of other potential evidence in order to carry out a process that is relevant to further decisions, demonstrates confidence in safe development and is efficient in providing evidence for design and assessment [47, 80].
The term ‘fitness’ is used in many of the pathways to potential harm (Table 2). This is a deliberately broad, generic term that encompasses viability, such as larval and pupal survival, fecundity, such as number of eggs laid, or egg hatching rate, fertility, such as mating competitiveness, and vigour, such as adult longevity and survival under a range of environmental conditions, such as in the presence of insecticide, or over a range of temperatures, decreased humidity, or increased salinity. When appropriate and relevant, specific components of fitness were highlighted in individual pathways.
Defining ‘valued species’ and ‘ecosystem services’
Many biodiversity protection goals are based on ‘valued species’ and ‘ecosystem services’. Valued species is a generic term that refers to any species that is i) keystone; ii) charismatic; iii) threatened; or, iv) endangered. Individual valued species will be identified and characterized in subsequent steps of an ERA using evidence from National Biodiversity Strategies and Action Plans as set out by the Convention on Biological Diversity , or the International Union for Conservation of Nature Red List of Threatened Species , augmented where appropriate by local knowledge and expertise of research colleagues from African partners in Target Malaria , as well as any socio-economic scoping or impact assessment studies which may be undertaken. More broadly, operational protection goals will be defined in subsequent stages of an ERA using a framework building on the concept of ecosystem services that can include (i) provisioning services such as food, water or energy; (ii) regulating services such as pollination, pest control or water purification; and, iii) supporting services such as oxygen generation or decomposition of organic matter and nutrient recycling [84,85,86]. This will be used to further refine assessment endpoints and their associated measurement endpoints, as well as limits of concern , in subsequent stages of an ERA for this population suppression gene drive .
Defining ‘vectorial capacity’
‘Vectorial capacity’ is defined as the total number of potentially infectious bites that would eventually arise from all the mosquitoes biting a single completely infectious (i.e., all mosquito bites result in infection) host, be it human or animal, on a single day (Table 1) [88,89,90]. This value is relevant to a range of potential harms from the release of transgenic mosquitoes. The individual parameters contributing to vectorial capacity are shown in the equation at the bottom of Table 1 and include (i) host biting rate; (ii) vector competence; (iii) probability that a newly infected mosquito survives to become infectious; (iv) number of adult female mosquitoes per host; and, (v) daily probability that an infected adult female mosquito dies. Thus, changes to any one of these parameters in the dsxFCRISPRh transgenic could alter the vectorial capacity for transmission of a given disease. Although the numerical value of this equation would be of limited use to vector control programmes, the equation does represent a useful tool to identify specific elements that contribute to disease transmission by vectors and can facilitate evaluation of the contribution that each of those elements make to transmission in modelling studies. In any pathway involving vector-borne human or animal disease, relevant measurement endpoints contributing to vectorial capacity are highlighted using the equation in Table 1.
Defining off‐targeting and retargeting effects from the CRISPR/Cas9 system
Off-target mutations could theoretically occur in dsxFCRISPRh transgenics by promiscuous cleavage by Cas9 at non-target genomic sequences followed by their misrepair . Retargeting could also theoretically occur should the transgene mutate to modify the specificity of target sequence recognition and cleavage by Cas9, with misrepair leading to retargeted, off-locus mutations . Off-target, or retargeted, mutations could then accumulate in target populations if they were to occur at sufficient frequency or be positively selected. They would not, in themselves, represent a harm unless they produce phenotypes that augment vectorial capacity or negatively impact on environmental protection goals.
The propensity for off-target effects is dependent on the uniqueness of the guide RNA target site; the efficiency, intracellular concentration and duration of the nuclease activity; and, the chromatin state of the tissues and cells in which the nuclease is expressed . In vitro and in vivo molecular analyses have been developed to screen CRISPR-Cas9 transgenic lines for off-target mutations . Bioinformatic software for the cogent design of guide RNAs  and promoters with optimal the intracellular concentration, duration and germline cell-specificity of Cas9 expression for on-target efficacy can be exploited to minimize the potential for off-target effects .
In total, for investigational field releases of the dsxFCRISPRh transgene in West Africa, eight broad, potentially harmful effects were identified. These were stratified into 46 plausible pathways leading to potential harms to the four protection goals (Table 2). All 46 pathways are illustrated as Figs. 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25, 26, 27, 28, 29, 30, 31, 32, 33, 34, 35, 36, 37, 38, 39, 40, 41, 42, 43, 44, 45, 46, 47, and 48, but 10 specific examples of conceptual models are described in the following four sections on protection goals, which in each case describe (i) plausible pathways to potential harm; (ii) risk hypotheses to interrogate individual steps in those pathways; and, (iii) analysis plans to corroborate or invalidate those hypotheses.
Plausible pathways to potential harms to biodiversity protection goals
For biodiversity protection goals, eight plausible pathways to potential harm were identified, shown in Figs. 3, 4, 5, 6, 7, 8, 9 and 10. Conceptual models of three examples of these pathways are described. Potential harms involving wildlife were considered under biodiversity protection goals, whereas the health of livestock, domestic or companion animals were considered under animal health protection goals.
Pathway 1. Biodiversity: Potential toxicological effects of dsxFCRISPRh transgenics on NTOs could reduce ecosystem services
Pathway 1 involves toxicological effects from consuming dsxFCRISPRh transgenic material leading to a reduction in the density of predator, decomposer/scavenger or pollinator NTOs (Fig. 3). The plausible pathway to the potential harm illustrated how, following release and spread of the dsxFCRISPRh transgene, predators could eat living transgenics, decomposers or scavengers could eat dead transgenic material, or pollinators could consume water from aquatic habitats containing dead transgenics and their breakdown products. Transgenic material could then cause direct acute or chronic toxicological effects on these NTOs, reducing their population densities in the ecosystem. This pathway could also be relevant to water quality, human health and animal health protection goals in an indirect way, for example, by increases in the densities of other pest or vector species, if the predator were to feed on both An. gambiae and those other species.
Two risk hypotheses were developed to interrogate steps of this pathway. One hypothesized that NTO consumption of dsxFCRISPRh transgenic products would have no greater toxicological effects than from consumption of non-transgenic mosquito material. This could be tested in two ways. Firstly, bioinformatic and literature databases could be searched for any evidence of toxicity of Cas9 or DsRed. Such evidence would likely be more targeted towards toxicological outcomes in humans, but nonetheless could contribute to the weight of evidence corroborating or invalidating this risk hypothesis. Secondly, in toxicology studies recombinant transgenic proteins, such as Cas9, could be fed to representative sensitive indicator species. Defining the precise experimental conditions and choices of indicator species for these studies would most likely involve discussion with national regulators, with reference to international or other regulatory guidance and best practice, such as European Food Safety Authority’s guidance for the risk assessment of genetically modified animals and food and feed derived from them [26, 95].
A second risk hypothesis stated that levels of the transgene would be too low to produce toxic effects in NTOs. This could be tested by assessing the level of expression of transgenic products in the dsxFCRISPRh gene drive strain and then extrapolating anticipated levels of transgenic biomass in aquatic or terrestrial habitats. Assuming the intended efficacy at most locations in the release area, as the population suppression from the gene drive takes effect, there should be decreasing densities of An. gambiae and, therefore, decreasing likelihood that NTOs would be exposed to any potential toxicological effects.
Pathway 3. Biodiversity: Potentially cumulative Cas9/gRNA off-target or retargeted nuclease activity in dsxFCRISPRh transgenics could cause broader tolerances for humidity, temperature, salinity, or egg desiccation to reduce densities of valued species or ecosystem services
Pathway 3 involves the potential for off-target Cas9 nuclease activity , or retargeted off-locus nuclease activity , to generate mutations that could produce broader tolerances in dsxFCRISPRh transgenics for a range of environmental conditions that would then allow them to spread beyond the geographic range of non-transgenic comparators (Fig. 5). The plausible pathway to this potential harm illustrates how, following release and spread of the dsxFCRISPRh transgene, off-target or retargeted Cas9 nuclease activity could lead to misrepair and heritable mutations at genetic loci conferring broader phenotypic tolerances for environmental conditions such as temperature, humidity or salinity. This could then result in either increased competition from these variants with existing species within the current range of An. gambiae via extended survival into dry season compared to non-variants, or new competition with new species, or new populations of the same species, in new ranges.
As off-target mutations have been detected for a variety of guide RNAs in human cell lines ranging in frequencies from 0.03 to 60.1% , two manifestations of this pathway, in terms of ‘phenotypic changes due to mutation generation followed by natural selection’ versus ‘phenotypic changes due to mutation pressure’, were considered.
The former could be rare and difficult to observe reliably in the laboratory setting. Indeed, off-target single nucleotide variants have been detected in CRISPR-Cas9 edited mouse embryos at a frequency close to the spontaneous mutation rate , while no off-target mutations were detectable in some strains of transgenic mosquitoes . Therefore, the impact from such off-target mutations would be on the same scale as spontaneous mutations that would in any event be occurring naturally in large field populations of wild-type mosquitoes .
However, the latter case, phenotypic changes due to mutation pressure, would represent a plausible pathway to potential harm from the intervention, as it would arise from higher mutation rates than spontaneous levels. Moreover, these should be observable under laboratory conditions. Therefore, four risk hypotheses were developed to test the validity of steps in this pathway supported by a tiered analysis plan [47, 80]. In the first tier, the hypothesis that Cas9 causes no off-target cutting in the dsxFCRISPRh transgenic could be tested using bioinformatic assessments combined with in vitro experiments to determine if Cas9 would be predicted to cut non-target sequences, followed by genome sequencing in transgenics of any identified off-target sites to determine whether any of those sites would be the subject of off-targeting and mutation by misrepair in vivo and, if so, at what level.
A second tier of the analysis plan would test the hypothesis that the variants would have no broader tolerances for abiotic conditions outside the range of non-transgenic comparators. Here, measurement endpoints would involve assessment of the fitness of transgenics at lower and higher temperatures, humidity and salinity ranges than those found currently in West African for An. gambiae.
A third risk hypothesis posited that population suppression from gene drive would have a greater effect on population densities than any broadening of tolerance for humidity, temperature, salinity, or egg desiccation in variants and could be evaluated by calculating the net effect of identified changes in tolerances for environmental conditions and expected levels of population suppression. Assuming the intended efficacy at most locations in the release area (Fig. 2), the net effect of a population suppression gene drive could ultimately reduce this potential harm by reducing the density of mosquitoes, including variants.
A fourth risk hypothesis stated that An. gambiae did not have competitors that were either valued species or that provide essential ecosystem services which could be assessed via literature review.
Pathway 5. Biodiversity: Potential horizontal gene flow of the dsxFCRISPRh transgene to a NTO eukaryote could lead to its unintended population suppression, thus reducing densities of valued species or ecosystem services
Pathway 5 identifies how the horizontal transfer of the dsxFCRISPRh transgene could lead to the population suppression of an NTO eukaryote that is a valued species, thus affecting biodiversity (Fig. 7) . The plausible pathway to this potential harm illustrates how, following release and spread of the dsxFCRISPRh transgene, bacteria or viruses that are pathogenic to the valued species could acquire the transgene either directly, or via bacteriophage, or transposon. The virus or bacteria transformed with the dsxFCRISPRh transgene could then infect the valued species leading to transfer of the transgene to its germline cells. A functional version of the transgene would then have to integrate into the guide RNA target site, with its regulated expression causing heritable transmission of the transgene and population suppression in the valued species.
Four risk hypotheses were developed to investigate this pathway. Firstly, it was hypothesized that dsxFCRISPRh transgene would not get transferred from the transgenic to the germ cells of valued species on the expected timescale of a gene drive intervention, circa 10 years . To test this hypothesis, the literature could be assessed to determine the likelihood and expected timescale required for a stretch of DNA of circa 7 kb, the size of the functional gene drive transgene, to be transferred from transgenics to valued species by non-sexual means, such as via transposon intermediaries. Hybridization was not considered a plausible mechanism for transfer of the gene drive transgene from An. gambiae to NTOs, including valued species. Anopheles gambiae is made up of An. amharicus, An. arabiensis, An. bwambae, An. coluzzii, An. fontenillei, An. gambiae s.s., An. melas, An. merus, and An. quadriannulatus [48,49,50,51] and the guide RNA target sequence of the dsxFCRISPRh transgene is conserved in all of the above species examined . Transfer of this transgene between any of these species via hybridization would thus likely lead to functional gene drive and population suppression in those species. Thus, all of the above species are considered target organisms. By contrast, the most closely related species to An. gambiae outside of the complex is An. christyi, which differs morphologically, and is genetically distinct, from An. gambiae, with both species being separated by circa 9 million years of evolution . The absence of observed gene flow between both species supports the lack of any significant hybridization between these species, so that for even less closely related species of Anopheles, hybridization with An. gambiae is considered implausible.
The next two risk hypotheses were designed to interrogate the step in the pathway whereby the transgene would integrate into the guide RNA target of the genome of germline cells in the valued species, a prerequisite for the transgene to result in gene drive. There could be two possibilities: the first was represented by the risk hypothesis that the transgene would not insert randomly into the genome at the target site and could be tested by calculating the probability that the transgene (circa 7 kb) would insert at the guide RNA target site (23 bp) of the genome of a valued species’ germline cells. For reference, the An. gambiae s.s. genome is some 278 Mb . The second possibility was represented by the risk hypothesis that the Cas9 and guide RNA of the transgene would not be expressed, including transiently, so that the transgene could integrate faithfully into the target site. This would be assessed via literature review of the functionality of regulatory and coding sequences of the transgene in the germline of valued species of insects.
A fourth risk hypothesis postulated that the guide RNA target site would not be conserved in the genomes of valued species. Bioinformatics could be used to assess the degree of conservation of the RNA target site in valued species of insects associated with An. gambiae.
Plausible pathways to potential harms to water quality protection goals
Pathway 9. Water quality: Potential adverse impact on quality of water, and its flora and fauna, from reduced nutrient composition of aquatic habitats could be caused by potential toxicity of dsxFCRISPRh transgenic products
For Pathway 9, the accumulation of transgenic product could lead to toxicity in detritivores, leading to negative effects on water quality for aquatic NTO flora and fauna (Fig. 11). Four risk hypotheses were developed to interrogate this pathway. The first posited that the population suppression gene drive would inhibit the accumulation of transgenic products by decreasing the density of aquatic stages of the TO. This could be tested by calculating the net effects of accumulation of transgenic products from mortality rates in aquatic stages of transgenics and reduced density of aquatic transgenics via population suppression. The second risk hypothesis stated that the transgenic products, or indeed their amino acid breakdown products, would not accumulate in water. This could be tested in the analysis plan by assessing the literature for evidence on the environmental fate of transgenic and breakdown products, informed by quantitative analysis of their levels of expression in transgenics. A third risk hypothesis posited that transgenic products would not accumulate in sediment, which could be tested by both literature and assessing the environmental fate of transgenic products in sediments. The fourth risk hypothesis stated that transgenic products were not toxic. This could be tested in the analysis plan by bioinformatic and literature assessments for any evidence of toxicity of transgenic products in animals, as well as assessing the data from NTO toxicology studies described for Pathway 1 above.
Plausible pathways to potential harms to human health protection goals
For human health protection goals, 20 plausible pathways to potential harm were identified (Figs. 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25, 26, 27, 28, 29, 30, 31, 32). Conceptual models for four examples of such pathways are described below. In many but not all cases, plausible pathways to potential harm for human health were mirrored in pathways for animal health.
Pathway 11. Human health: Transgenic proteins could cause specific allergic or toxicological responses in humans from dsxFCRISPRh transgenic bites beyond responses to non-transgenic bites
Pathway 11 describes how expression of transgenic proteins DsRed or Cas9 in the saliva of dsxFCRISPRh transgenic mosquitoes could lead to allergic responses in humans from transgenic biting beyond those that occur from non-transgenic biting (Fig. 13). This pathway was based on the potential harm that could be caused to an individual human from exposure to transgenic proteins. It could, therefore, occur in the first generation after release of the transgenics, or at subsequent stages, for example, when the transgene increases in frequency in the mosquito population (Fig. 2).
The first risk hypothesis to investigate this pathway stated that Cas9 or DsRed were not detectable in the saliva of transgenic mosquitoes. The measurement endpoint to test this hypothesis relies on tiered assessment. Firstly, it would be determined whether Cas9 or DsRed were expressed in salivary glands in heterozygous dsxFCRISPRh transgenic mosquitoes that, unlike homozygotes, can bite. If those transgenic proteins were present in salivary glands, it would next be determined whether Cas9 or DsRed were present in the saliva of the transgenic mosquitoes. A second risk hypothesis proposed that the Cas9 and DsRed transgenic proteins did not cause increased allergenicity or toxicity in humans. This could be assessed by searches of bioinformatic and literature databases to determine if there was evidence of allergenicity of Cas9 or DsRed and by assessing toxicology data from selected NTO studies as outlined in the Analysis Plan of Pathway 1.
Pathway 21. Human health: Potentially altered anatomy, or host-seeking behaviour, in dsxFCRISPRh transgenics could increase the transmission of human diseases, including lymphatic filariasis
Pathway 21 relates to how altered anatomy in transgenics could lead to increases in the transmission of lymphatic filariasis (LF) (Fig. 23). After malaria, LF is the most burdensome disease transmitted by species of An. gambiae in western sub-Saharan Africa. For example, in Burkina Faso, malaria accounts for 17.96% of total disability-adjusted life years (DALYs), compared to 0.29, 0.05 and 0.0094% of total DALYs for LF, yellow fever and dengue, respectively . Despite this, direct laboratory assessment of the vector competence of An. gambiae for the most common LF parasite, Wuchereria bancrofti, has not yet reliably been established .
Homozygous dsxFCRISPRh transgenic mosquitoes have reported anatomical alterations, including specifically to mouthparts, with most heterozygotes appearing to be normal in this respect . This pathway is about the efficiency of transmission, so any relevant change in anatomical characteristics in dsxFCRISPRh transgenics may increase the probing rate of homozygous transgenics, or in heterozygotes increase the biting rate or the transmission rate from a given biting rate. Moreover, the cibarial armature is implicated in transmission of filariae to mosquitoes [103,104,105].
Four risk hypotheses were developed to investigate this pathway. In the first, it was hypothesized that transgenics did not differ anatomically to non-transgenics in anatomy related to the success of pathogen transmission. This could be assessed in transgenics and non-transgenics in insectary anatomical studies. The second risk hypothesis posited that transgenics did not bite humans more than non-transgenics to increase disease transmission. This could be tested in the laboratory by comparing the biting and probing rate of transgenics with non-transgenics using a panel of artificial attractants, and the increase in the number of infectious bites required to increase background disease transmission could be calculated. A third risk hypothesis proposed that transgenics showed no increase in vector competence, or decrease in extrinsic incubation period, compared with non-transgenics. Both of these parameters could be assessed in the laboratory for a representative panel of pathogens vectored by An. gambiae. A fourth risk hypothesis proposed that population suppression from gene drive would have a greater effect on vectorial capacity than any increase in vector competence caused by altered dsxFCRISPRh transgenic anatomy. This hypothesis could be tested by calculating the net effect on vectorial capacity of any such increase in vector competence in the presence of population suppression from gene drive.
Pathway 25. Human health: Potentially cumulative Cas9/gRNA off-target or retargeted nuclease activity in dsxFCRISPRh transgenics could cause heritable increase in insecticide resistance, fitness or vector competence to increase human disease
Pathway 25 describes how the accumulation in transgenics of Cas9/guide RNA off-target or retargeted mutations in genomic loci involved in insecticide resistance, fitness or vector competence could lead to an increase in vectorial capacity and human disease transmission (Fig. 27). Three risk hypotheses were constructed for this pathway, supported by a tiered analysis plan [47, 80]. In the first, Cas9/guide RNA was hypothesized to cause no off-target or retargeted mutations in transgenics, which could be tested firstly by bioinformatic assessment on the potential for off-target or retargeted effects using Anopheles 1,000 genomes reference genome sequence [106, 107], and secondly by genomic sequence analysis (e.g. using in vitro CIRCLE-Seq ) of mosquito DNA to identify potential non-target sites. These non-target sites could then be sequenced in transgenics to search for in vivo evidence of their mutation .
Where off-target or retargeted mutations would be detected in transgenics by molecular and bioinformatic analyses, as discussed for Pathway 3 above, they could occur via two scenarios: ‘phenotypic changes due to mutation generation followed by natural selection’ or ‘phenotypic changes due to mutation pressure’. The former may not be observable in the laboratory but would, in any event, be occurring naturally in large field populations in the absence of the transgene [34, 93, 97]. The latter does however represent a plausible pathway to potential harm caused by this transgene but would require high mutation rates that should be observable under laboratory conditions . Therefore, to address this latter scenario, a second tier of the analysis plan would be to test a second risk hypothesis that the off-target or retargeted variants show no difference in vectorial capacity, which could be tested experimentally by comparing the insecticide resistance, fitness and vector competence for a representative panel of diseases in transgenics with non-transgenics following multiple generations of nuclease expression in the germline.
A third hypothesis proffered that population suppression from the gene drive would have a greater effect on vectorial capacity than from any increase in insecticide resistance, fitness or vector competence, the net effects of which could be calculated empirically.
Pathway 29. Human health: Potentially reduced density of a predator species caused by population suppression of Anopheles gambiae could lead to increases in density of another human disease vector species
Pathway 29 describes how population suppression of An. gambiae could cause reductions in the density of a predator that leads to and expansion in the density of another human disease vector (Fig. 31). This would occur because, under normal circumstances, the predator species P would have stronger density-dependent response from feeding on An. gambiae (G) than from feeding on another species (D) which is a human disease vector, so that under such normal circumstances G and D would be in asymmetric apparent competition with each other . However, with population suppression gene drive in An. gambiae, the population density of P could also reduce. This could, in effect, release D from asymmetric apparent competition with G, leading to increases in the population density and vectorial capacity of D, resulting in increased disease transmission in human by D.
Five risk hypotheses were developed to interrogate this pathway. In the first, it was posited that no predator predominantly feeds on An. gambiae. This could be tested in the first tier of an analysis plan by assessing the literature and field observations for evidence of predators that predominately feed on An. gambiae, such as from studies DNA barcoding the gut contents of predators . A second risk hypothesis, which stated that no predator that predominately feeds on An. gambiae also feeds on another human disease vector species, would only need to be investigated where the first risk hypothesis was falsified. This could be tested in the second tier of the analysis plan by further literature investigation and field observations for evidence of shared predators between An. gambiae and other vector species.
A third risk hypothesis posited that there are no other human disease vectors in asymmetric apparent competition with An. gambiae, which could be investigated via ecological modelling. A fourth risk hypothesis proffered that D is a less efficient vector of diseases that are also transmitted by An. gambiae and/or the diseases transmitted by An. gambiae are more harmful than those transmitted by D. This could be tested by modelling the net effect of disease transmission of An. gambiae and D both before and after population suppression of An. gambiae, as well as assessing the literature on the burden of human disease in West Africa from mosquito species that share predators with An. gambiae.
The fifth, and last, risk hypothesis for this pathway stated that the disease burden in West Africa will not increase following population suppression of An. gambiae, which would be tested by assessing the literature on the entomological and epidemiological impacts of conventional vector control measures against An. gambiae, such as indoor residual spraying or insecticide-treated bed nets .
Plausible pathways to potential harm for animal health protection goals
For animal health protection goals, 16 plausible pathways to potential harm were identified (Figs. 33, 34, 35, 36, 37, 38, 39, 40, 41, 42, 43, 44, 45, 46, 47, 48). Conceptual models for two of these pathways are described below. In most cases, the animals considered were livestock, but these pathways could equally be applicable to domestic or companion animals. Potential harms to wildlife were considered under biodiversity protection goals. In all cases, pathways to potential harm for animal health were mirrored in pathways for human health, so that the examples presented below are also relevant to plausible pathways to potential harm for human health protection goals.
Pathway 32: Animal health: Potentially decreased mosquito defence response to pathogen in dsxFCRISPRh transgenics from altered levels of endogenous RNA, protein or microbiome could lead to increased disease in livestock
Pathway 32 defines how decreases in transgenic mosquito defence responses via alterations to endogenous RNA, protein or microbiomic species could lead to increased livestock disease (Fig. 34). Mosquito RNA or protein in saliva, midgut or haemolymph, or contents of the microbiome, can alter defence responses to human pathogens such as Plasmodium or O’nyong’nyong virus (ONNV) [112,113,114,115,116]. It was, therefore, considered to be plausible to envisage that the same process could be modulating mosquito responses to animal pathogens. Any such alterations in transgenics compared to non-transgenics could alter the vector competence of transgenics and thus vectorial capacity.
Two risk hypotheses were developed to interrogate this pathway. In the first, it was proposed that transgenics would not transmit higher levels of animal pathogens than non-transgenics, which could be tested in the analysis plan using measurement endpoints in vector competence assays involving a representative panel of pathogens. The second hypothesis stated that population suppression from gene drive would have a greater overall negative effect on livestock disease incidence than any increased levels of vector competence, the net effect of which could be calculated from empirical data.
Pathway 43. Animal health: Increased or novel disease transmission in livestock could be caused by replacement of Anopheles gambiae niche with another disease vector
Pathway 43 describes how population suppression of An. gambiae could release another animal disease vector species from competition, thereby increasing the incidence of livestock disease (Fig. 45). The pathway was considered to be most likely to manifest itself in aquatic habitats of larval development, which have the most impact on vectorial capacity of An. gambiae [117, 118]. Diminishing density of larvae or pupae of An. gambiae could cause decreased competition with other mosquito vector species. This would then cause increases in the vectorial capacity of those competitor vectors, increasing the spread of animal pathogens in livestock.
Four risk hypotheses were developed to investigate steps in this pathway. In the first, it was hypothesized that species of An. gambiae do not have competitor species that are major vectors of animal disease. This could be tested by identifying vector species that share aquatic habitats with species of An. gambiae, assessing animal diseases spread by those species, examining published evidence for competition between these species and An. gambiae and DNA barcoding analysis of gut contents of An. gambiae and any co-located non-target species to assess if they consume the same food resources . A second hypothesis was developed which stated that competitor species which are major vectors for disease would not occupy the An. gambiae niche to the degree needed to increase animal disease, which could be assessed in the analysis plan by ecological modelling. A third risk hypothesis stated that the vectorial capacity of competitor species would not increase following reduction in the density of An. gambiae and could be tested by assessing literature on the competitive relationship between An. gambiae and associated competing vector species to identify potential for increased alternative vector density. The fourth risk hypothesis posited that the animal disease burden in West Africa would not increase following occupation of the former niche of An. gambiae by another target or non-target vector species. As with the analysis plan in Pathway 27, this could be tested by assessment of the literature on the burden of animal disease in West Africa from mosquito species that are competitors of An. gambiae and on the impacts on animal disease from conventional malaria vector control measures, such as the use of insecticides, against An. gambiae.
Drawing on protection goals identified from previous, published consultative exercises on gene drive involving a broad base of expertise from across Africa and under the direction of AUDA-NEPAD [45, 46], problem formulation was used here as the initial step in an ERA of the hypothetical release of the dsxFCRISPRh transgene-based population suppression gene drive for malaria vector control in West Africa. Eight potential adverse effects to protection goals were identified, such as reduced density of valued species or ecosystem services, or increased disease transmission in humans. In total, 46 plausible pathways to potential harms to protection goals to health and the environment were developed (Table 2). Each pathway was categorized by protection goal, cause, effect, correlation of exposure levels with transgene efficacy, and relevance to ERAs of other transgenic mosquito strains (Table 2). Although some of the pathways identified here were based on considerations arising from specific anatomical alterations observed in homozygous dsxFCRISPRh transgenics (n = 14), many of these could still be applicable to field releases of other strains of transgenic mosquito (n = 18). Other pathways could be selectively applicable to population suppression gene drive strains (n = 8), CRISPR-Cas9-based strains (n = 3) or other gene drive transgenic strains (n = 2) (Table 2).
Causes of potential harms
The intended outcome of population suppression gene drive in An. gambiae, decreased density of the target species, was not itself considered to be a potential harm, given that there is no evidence to support the complex playing a key role in ecosystems or provision of ecosystem services . Indeed, population suppression of these TOs is by definition an accepted outcome for any existing malaria vector control programme.
Most causes of harm related to changes in the biology of transgenics compared to non-transgenics at the level of the individual mosquito. For example, homozygous dsxFCRISPRh transgenic females are sterile, whereas heterozygotes are fertile . Homozygous dsxFCRISPRh transgenic females also have anatomical defects in the proboscis so that they cannot bite. Homozygous dsxFCRISPRh transgenic females also show additional anatomical alterations in the antennae, male accessory glands, spermatheca, claspers, cercus and pupal genital lobe . Given the presence of distinct visible anatomical defects in homozygous dsxFCRISPRh transgenics, as yet unobserved changes to physiology or behaviour in homozygous transgenic females were also considered plausible during the development of these pathways. Indeed, altered anatomy, physiology or behaviour in individual dsxFCRISPRh transgenics represented the most common category of cause of potential harm (n = 24), with sub-sets of this causes of potential harm category including changes in transgenic vector competence (n = 14) or in host biting rates (n = 5).
The second-most common category of causes of potential harm was fitness effects in transgenics (n = 11), with either increases in transgenic fitness (n = 8) or fitness costs in individuals possessing the dsxFCRISPRh transgene (n = 3). Increases in fitness could, for example, allow transgenics to extend their geographic range or contribute directly to increases in vectorial capacity unless the efficacy of population suppression were to outweigh the effect. Fitness costs in the transgenic were also causes of potential harms to water quality from increased larval and pupal mortality (n = 2). After fitness effects, the next most common category of cause of harm was from the transgenic containing a toxin or allergen (n = 9).
As well as potential harms caused by changes to the biology of transgenic mosquitoes at the individual level, some potential harms were identified that would occur at population level as a result of a population suppression gene drive (n = 7). Unlike those potential harms reported in Roberts et al.  and Teem et al. , plausible pathways to potential harm were developed which would be caused by horizontal gene transfer of the population suppression gene drive transgene cassette (n = 2), potentially leading to population suppression of a valued species of NTO (n = 1). As described in Methods, vertical gene transfer of the transgene via hybridization amongst species of the An. gambiae complex was considered to be an intended effect and not a harm itself, because spread of the gene drive transgene to all species of the An. gambiae complex is an expected outcome.
In other plausible pathways to potential harm, effective population suppression of An. gambiae would, of itself, be the primary cause of potential harm by leading to the release of other species from competition (n = 3; Pathways 7, 27, 43 in Figs. 9, 29, 45, respectively) or apparent competition (n = 2; Pathways 29 and 45 in Figs. 31 and 47, respectively) or the eventual loss of acquired or herd immunity to diseases transmitted by An. gambiae (n = 2; Pathways 30 and 46 in Figs. 32 and 48, respectively). It is worth noting, however, that any successful vector control programme has the potential to cause such consequent harms. For example, between 1955 and 1959, house residual spraying vector control programmes using dieldrin in East Africa resulted in almost complete elimination of malaria transmission, which correlated with decreases in the population densities of Anopheles funestus and concomitant sharp increases in densities of either Anopheles rivulorum or Anopheles parensis, which were attributed to release of the latter species from competition with An. funestus in aquatic habitats [119,120,121]. In an example supporting the loss of acquired immunity following a conventional malaria control programme, a longitudinal study in Senegal between 2007 and 2010 tracked the impact of insecticide-treated bed nets and artemisinin-based combination therapy and found that the incidence of malaria initially decreased, but increased again around 30 months after the distribution of bed nets [122, 123]. This resurgence in malaria was most pronounced in adults and children 10 years of age or older, rising from 33 % to 2007 to 63 % in 2010, which was attributed, at least in part, to reduced levels of acquired immunity [122, 123], consistent with observations from other studies in Kenya, The Gambia and Uganda [124,125,126,127].
One direct cause of potential harm arising from dsxFCRISPRh transgenics is worth some discussion, as it would not occur for non-nuclease expressing transgenic mosquitoes that have already progressed to field releases . Because gene drive is propagated by a DNA endonuclease expressed in dsxFCRISPRh transgenics, it creates the possibility for the occurrence of promiscuous off-target or retargeted mutations , which would then subsequently lead to potential phenotypes in transgenics that might cause harms to protection goals, such as increased vector competence for diseases (see Pathways 3, 25 and 41 in Figs. 5, 27 and 43, respectively). The Cas9 enzyme is highly specific and the gRNA can be designed using reference Anopheles genomes to prevent sequences identical to the target site at genomic locations other than the target site. Guide RNAs can also be designed to limit the potential for off-target or re-targeted effects. However, unintended nuclease-induced mutation could theoretically become common in two ways: the mutation might happen to increase the fitness of the mosquito and be positively selected for, or off-target cleavage might be at such a high rate that it leads to a correspondingly high frequency of mutation in the population. The former simply reflects the status quo in large field populations where the full range of possible mutations are naturally occurring and potentially being selected for. The latter would require high mutation rates that would be observable in the laboratory. Determining the propensity for off-target or re-targeted mutations in gene drive transgenics early in the development of a strain for field release is, therefore, yet another essential aspect of the ERA for population suppression gene drive.
Mechanisms by which the efficacy of population suppression gene drive could be lost were also considered (Fig. 1). In particular, the evolution of resistance to gene drive, for example via the emergence of second-site suppressors, could also lead to pleiotropic effects that are in themselves potential harms, such as increase increased insecticide resistance (Pathway 18 in Fig. 20), vector competence (Pathway 20 in Fig. 22) or environmental tolerance (Pathway 26 in Fig. 28). This would be analogous to the situation where mutations conferring insecticide resistance to An. gambiae can have pleiotropic effects on vectorial capacity for Plasmodium [128,129,130,131]. Nonetheless, insecticides remain a cornerstone of malaria vector control programmes, despite significant remaining uncertainties on physiological interactions between insecticide resistance and vector competence and their potential contributions to disease transmission [132,133,134,135].
Effects of potential harms
The effect of each potential harm was categorized as either direct (n = 30) or indirect (n = 16) (see Table 1). Pathways were also classified into eight broad categories of potentially harmful effects on protection goals. The largest two categories involved 26 pathways related to increases in disease transmission in humans (n = 13) or livestock (n = 13). The second largest category was reduced populations of valued species or ecosystem services (n = 8). The third largest category of potentially harmful effects involved increased toxicological effects and immune or allergic responses in humans (n = 5). Four other categories of potential harmful effects consisted of reduced water quality for humans, livestock or NTOs (n = 2), novel disease transmission in humans (n = 2) or livestock (n = 2), and increased toxicity in livestock (n = 1).
Exposure routes to potential harms
The most common exposure route in pathways was from biting (n = 26), in which cases dsxFCRISPRh heterozygous transgenics, but not homozygous transgenics, would provide the source of exposure. The potential for increased allergenicity in humans caused from exposure to transgenic mosquitoes via incidental inhalation or ingestion (Pathway 12 in Fig. 14; cf. ), which could occur from exposure to both homozygotes and heterozygotes, was also considered as plausible. The second most common exposure route to potential harms was from NTO consumption of the transgenic or changes in NTO consumption patterns caused by exposure to the transgenic (n = 6). The third most common exposure route was changes in predator-prey interactions (n = 3). Bio-accumulation of transgenic products or detritus and changes in competition were also routes of exposure for three potential harms each. Horizontal gene transfer, spread of transgenics beyond their geographic range and loss of immune system pre-exposure to pathogens were routes of exposure for two potential harms each.
Exposure levels leading to potential harms
The relationship between level of exposure leading to potential harms and success of the intervention is worth considering, as this will guide future considerations of the risks and benefits from environmental releases of dsxFCRISPRh transgenics. A minority of pathways (n = 4) could occur via allergic or immune system responses in individual humans exposed to potentially single transgenic mosquitoes or their body parts, and these could occur without any gene drive efficacy. Only 11 potential harms would be unrelated to the presence of the transgene in the environment and three, caused by off-target or retargeted mutations, could occur either due to the continued presence or subsequent absence of the transgene. However, for most potential harms to occur (n = 42), they would depend of the successful efficacy of the gene drive (Table 2).
The exposure level leading to the majority of potential harms (n = 35) would also be dependent on the absolute numbers of transgenics in the environment, where the greater the efficacy of population suppression, the less exposure there should be leading to potential harms. However, exposure levels leading to a minority of potential harms (n = 8) could increase with successful population suppression gene drive, such as in Pathways 6, 7, 27, 29, 30, 43, 45, and 46 shown in Figs. 8, 9, 29, 30, 43, 45, 47, and 48, respectively. These pathways could theoretically occur with any effective vector control tool that was relatively enduring and species specific, including pre-existing programmes based on insecticides or sterile insect technique (SIT) [122, 136]. In that sense, they represent plausible pathways to potential harm from successful malaria vector control, rather than from population suppression gene drive per se.
It is also important to recognize that any potential investigational release of a gene drive is first and foremost into a local environment with specific conditions which will vary from place to place and season to season . So it can also be expected that the performance of the gene drive, and its suppression of the population, will vary temporally and spatially. There may also be oscillations in effects from the gene drive, for example reflecting the impact of the dry season on the survival of transgenics in highly seasonal locations (Fig. 2). This also means that exposure to any potential harm caused by the gene drive may also vary temporally and spatially .
Risk hypotheses and experiments with widest impacts
Analysis of risk hypotheses and allied analysis plans revealed the experimental outputs that should provide the widest impact on testing of pathways and potential harms with the least levels of residual uncertainty. The most common theme amongst all risk hypotheses (in n = 14 pathways: 14, 20–25, 32, 36–41), that the transgenic would not transmit pathogens better than non-transgenics, can be informed by testing in the laboratory by assessments of vector competence and extrinsic incubation periods for a number specific representative pathogens. Data from such experimental evaluations can then further evaluated in the context of additional parameters relevant to vectorial capacity, to inform risk conclusions in subsequent stages of ERA. The second most common theme amongst risk hypotheses was that the transgenic was not toxic or allergenic (in n = 10 pathways: 1, 9, 11–13, 16, 17, 28, 31, 44), which can be tested initially from analysing bioinformatic and literature databases, supplemented by feeding studies in indicator species. The third most frequent theme in risk hypotheses involved fitness being unaffected in transgenics (in n = 10 pathways: 2, 3, 8, 10, 18, 25, 26, 34, 41, 42), which can be tested in small and large cage laboratory studies. The next most common theme in risk hypotheses was that transgenics did not bite more than non-transgenics (in n = 6 pathways: 19, 21, 22, 35, 37, 38). Rates of biting and probing can be assessed in the laboratory using a panel of artificial attractants. Finally, another common theme in risk hypotheses was that transgenic saliva did not differ from non-transgenic saliva (in n = 6 pathways: 11, 13, 15, 16, 31, 33), which can be tested via a variety of laboratory experiments that will assess levels of guide RNA, endogenous allergens, or RNA and proteins implicated in host defence responses.
Dismissed pathways to potential harm
The exercise which led to the development of the current set of plausible pathways to potential harm took place between July 2019 and October 2020. Over that period, several provisional pathways were developed that were ultimately excluded from this analysis as invalid or inconsequential . These included:
n = 5 pathways to loss of efficacy of population suppression gene drive from the suite of initial pathways considered, as it was agreed they did not directly result in potential harms to protection goals and therefore should not be included amongst the plausible pathways to potential harm;
n = 3 pathways related to transboundary movement as it was subsequently recognized that ERA does not formally include socio-economic or legal issues, such as the potential for transboundary movement of transgenics, despite these warranting further exploration in the context of gene drive organisms that are anticipated to cross national borders;
n = 1 pathway to potential harm that would be caused by vertical gene transfer (via hybridization) of the population suppression gene drive from An. gambiae to species outside the complex, as it was subsequently recognized that the most closely related species to those within the An. gambiae complex is An. christyi, but which is separated by circa 9 million years of evolution. The absence of observed gene flow between species of An. gambiae and An. christyi supports the lack of any significant hybridization between these species so that, for even less closely related species of Anopheles, hybridization is considered implausible. Moreover, in species of Anopheles more distantly related to An. gambiae than An. christyi, the guide RNA target DNA sequence of the dsxFCRISPRh transgene diverges from that found in An. gambiae;
n = 2 pathways leading to potential increases in disease transmission caused by increased transgenic larval mortality because it was based on the false assumption that population suppression would automatically lead to increased larval mortality and because it was ultimately considered biologically implausible as a potential route to increased disease transmission;
n = 6 pathways to potential harm to either human or animal health that would result in transmission of a novel pathogen caused by altered host-seeking behaviour in, or off-target mutations in, or extension in geographic range of, the transgenic. By contrast, pathways involving altered transgenic anatomy or physiology leading to the transmission of a novel pathogen were retained as plausible;
n = 6 pathways, which were eliminated when n = 12 pathways were combined together into n = 6 pathways at the request of peer reviewers to help identify more efficiently common risk hypotheses and key experiments that could interrogate the viability of a number of pathways to a low level of remaining uncertainty.
Limitations of this problem formulation exercise
The aim of this problem formulation exercise was to generate a comprehensive, if not exhaustive, set of plausible pathways to potential harm to previously defined protection goals from simulated field releases of the dsxFCRISPRh transgene in West Africa. Although based on the gene drive strain containing the dsxFCRISPRh transgene as described in Kyrou et al. , this work should also broadly be applicable to other similar CRISPR/Cas9-based population suppression gene drive strains targeting doublesex, for example those exploiting multiplexed guide RNAs (see Table 2). However, some of the pathways presented here may need to be re-examined on a case-by-case basis, depending on the strain under investigation and release protocol to be used. Indeed, new or altered pathways may also be identified as the scientific evidence base expands. These pathways are, therefore, likely to be revised and updated periodically, including with feedback from stakeholders and the wider scientific community.
Although the logical, stepwise process allows for the systematic identification of plausible pathways to potential harm, the strict linear format does not allow for branching pathways, parallel pathways or feedback loops. This may sometimes force the ‘shoehorning’ of parallel processes into a series of sequential events. The approach does, however, offer a transparent communication tool for the unbiased identification and description of pathways, potential harms and analysis plans.
Another difficulty encountered in this exercise was in defining the criteria for plausibility; pathways were considered plausible based on scientific and technical knowledge, but also based on expert judgement, introducing an element of subjectivity to the exercise . This situation is not unique to problem formulation, however, as expert elicitation in quantitative risk assessment, for example, also involves expert judgement .
The precise classification of TOs and NTOs may also evolve over time. Recently, membership of the An. gambiae complex has expanded with the addition of Anopheles fontenillei from Central Africa . Moreover, some species of the complex, are currently considered to be only minor vectors of malaria but are still TOs, so that one expected consequence of the intervention could be suppression of species that do not efficiently transmit disease. However, it may still be worthwhile to reduce the density of such vectors, notwithstanding them being inefficient at transmitting disease at present .
It could also be argued that many of the pathways identified here, although plausible, would not, in any event, be expected to occur because the potential harm would be identified during standard product development and result in the strain being eliminated from further advancement towards release. There are already regulatory precedents for the development and successful field release of transgenic mosquito strains [20, 138] so that increased vector competence, decreased insecticide sensitivity, broadened tolerances for abiotic conditions, or toxicity and allergenicity of transgenic products are all recognized as having the potential to contribute to harms to health and environmental protection goals. In that respect, many of the pathways identified here are not uniquely drawn from problem formulation. However, this problem formulation approach did help to unpick many of the more complex environmental and ecological pathways to potential harm that need to be further investigated in subsequent steps of ERA for population suppression gene drive. This exercise also allowed for the systematic definition of analysis plans and made the process of identifying and describing potential harms and their plausible pathways demonstrable, transparent and systematic, allowing for any potential for erroneous assumptions or unconscious bias to be challenged.
Next stages of ERA for population suppression gene drive
This analysis represents, to our knowledge, the first systematic and comprehensive identification of plausible pathways to potential harm using problem formulation for a specific gene drive organism. The exercise involved a systematic approach to identify (a) potential harms and exposure routes; (b) areas of uncertainty in our scientific understanding of plausible pathways to potential harms; and, (c) analysis plans to credibly assess pathways. Although superficially similar to fault tree analyses in some probabilistic risk assessment , the purpose of these pathways is not to assign probability to each step, but to inform the next stages of an ERA which will involve exposure and hazard characterization based largely on the outputs of analysis plans identified here. While protection goals were identified from published problem formulation exercises on gene drive conducted in Africa, assessment endpoints for most potential pathways to harm were not precisely defined, nor were limits of concern to those assessment endpoints established. These issues would have to be addressed in the immediate next steps of an ERA for population suppression gene drive.
Depending on the nature of the individual pathway, there are four possible outcomes in subsequent stages of ERA: (i) all hypotheses for a given pathway could be rejected in which case the pathway to harm would be considered valid; (ii) one or more hypotheses that nullify one or more individual steps in a pathway would cause the entire pathway to be rejected; (iii) evidence from a series of hypotheses may together produce sufficient ‘weight of evidence’ to indicate rejection of that pathway; or, (iv) evidence from a series of hypotheses may together produce sufficient weight of evidence to indicate acceptance of that pathway. For example, in Pathway 50, Potential toxicological effects of dsxFCRISPRh transgenics on NTOs could increase disease transmission in livestock, toxicology tests could be conducted on indicator species and the toxicity of transgenic proteins investigated in the literature and bioinformatically, mostly based on evidence from humans. Nonetheless, evidence from investigation of these evidence requirements should be sufficient to allowed informed decision-making about the potential for such a harm. Additionally, for any given risk hypothesis analysis plans should be tiered so that components likely to contribute most to informing the ERA and allied decision-making can be prioritized [47, 80]. Where a particular pathway is assessed to have the potential to lead to a harm to protection goals following further investigations and characterization of the risk in the ERA, risk mitigation options would need to be subsequently evaluated. It is possible that the unmanaged risk could be considered unacceptable by decision-makers, or they could deem a risk to be acceptable when taking into account the potential benefits of the intervention. It may also be possible to put in place risk management strategies that could be considered sufficiently robust by stakeholders to mitigate any identified risk from the intervention.
Building on a series of consultative workshops held in Africa that previously identified relevant environmental and health protection goals, eight potentially harmful effects of simulated field releases of the dsxFCRISPRh transgene in West Africa were identified. These were stratified into 46 plausible pathways that would be required for potential harms to occur. Most identified potential harms involved increased disease transmission, emphasizing the importance to subsequent stages of ERA of data assessing vectorial capacity in transgenics compared to non-transgenics. Although some of the pathways were based on considerations arising from anatomical alterations typically found in dsxFCRISPRh homozygotes, many pathways could be relevant to field releases of a range of other transgenic strains of mosquito. This analaysis revealed that the efficacy of population suppression caused by the dsxFCRISPRh transgene should itself have a direct impact on the majority of pathways. Mathematical modelling will therefore play an essential role in subsequent stages of ERA by clarifying the dynamics of this relationship between population suppression and reduction in exposure to specific potential harms [33,34,35, 139]. This investigation represents, to our knowledge, the first comprehensive identification of plausible pathways to potential harm using problem formulation for a specific gene drive transgene and organism, as well as a transparent communication tool that could inform a full range of future regulatory science studies, guide subsequent stages of ERA [33,34,35], and stimulate further, broader engagement on the use of population suppression gene drive to control malaria vectors in West Africa.
Availability of data and materials
Not applicable. All data and material is presented in the manuscript.
African Union Development Agency (AUDA) New Partnership for Africa’s Development (NEPAD)
Environmental risk assessment
Foundation for the National Institutes of Health
WHO. World malaria report 2020: 20 years of global progress and challenges. Geneva: World Health Organization; 2020.
AUDA-NEPAD. Gene Drives for Malaria Control and Elimination in Africa. 2018.
WHO. Evaluation of genetically modifed mosquitoes for the control of vector-borne diseases. Geneva: World Health Organization; 2020.
ESA (Entomological Society of America). Position Statement on the Importance of Continued Innovation in Gene Drive Technology. Ann Entomol Soc Am. 2020;113:486–7.
Wilson AL, Courtenay O, Kelly-Hope LA, Scott TW, Takken W, Torr SJ, et al. The importance of vector control for the control and elimination of vector-borne diseases. PLoS Negl Trop Dis. 2020;14:e0007831.
Burt A. Site-specific selfish genes as tools for the control and genetic engineering of natural populations. Proc Biol Sci. 2003;270:921–8.
Windbichler N, Menichelli M, Papathanos PA, Thyme SB, Li H, Ulge UY, et al. A synthetic homing endonuclease-based gene drive system in the human malaria mosquito. Nature. 2011;473:212–5.
Eckhoff PA, Wenger EA, Godfray HC, Burt A. Impact of mosquito gene drive on malaria elimination in a computational model with explicit spatial and temporal dynamics. Proc Natl Acad Sci USA. 2017;114:E255-E64.
Godfray HCJ, North A, Burt A. How driving endonuclease genes can be used to combat pests and disease vectors. BMC Biol. 2017;15:81.
Hamilton WD. Extraordinary sex ratios. A sex-ratio theory for sex linkage and inbreeding has new implications in cytogenetics and entomology. Science. 1967;156:477–88.
Curtis CF. Possible use of translocations to fix desirable genes in insect pest populations. Nature. 1968;218:368–9.
Burt A, Coulibaly M, Crisanti A, Diabate A, Kayondo JK. Gene drive to reduce malaria transmission in sub-Saharan Africa. J Resp Innovation. 2018;5(suppl 1):66–80.
Jinek M, Chylinski K, Fonfara I, Hauer M, Doudna JA, Charpentier E. A programmable dual-RNA-guided DNA endonuclease in adaptive bacterial immunity. Science. 2012;337:816–21.
Gantz VM, Jasinskiene N, Tatarenkova O, Fazekas A, Macias VM, Bier E, et al. Highly efficient Cas9-mediated gene drive for population modification of the malaria vector mosquito Anopheles stephensi. Proc Natl Acad Sci USA. 2015;112:E6736-43.
Gantz VM, Bier E. Genome editing. The mutagenic chain reaction: a method for converting heterozygous to homozygous mutations. Science. 2015;348:442–4.
Hammond A, Galizi R, Kyrou K, Simoni A, Siniscalchi C, Katsanos D, et al. A CRISPR-Cas9 gene drive system targeting female reproduction in the malaria mosquito vector Anopheles gambiae. Nat Biotechnol. 2016;34:78–83.
Kyrou K, Hammond AM, Galizi R, Kranjc N, Burt A, Beaghton AK, et al. A CRISPR-Cas9 gene drive targeting doublesex causes complete population suppression in caged Anopheles gambiae mosquitoes. Nat Biotechnol. 2018;36:1062–6.
Hammond AM, Galizi R. Gene drives to fight malaria: current state and future directions. Pathog Glob Health. 2018;111:412–23.
North AR, Burt A, Godfray HCJ. Modelling the suppression of a malaria vector using a CRISPR-Cas9 gene drive to reduce female fertility. BMC Biol. 2020;18:98.
Alphey L. Genetic control of mosquitoes. Annu Rev Entomol. 2014;59:205–24.
Deredec A, Godfray HC, Burt A. Requirements for effective malaria control with homing endonuclease genes. Proc Natl Acad Sci USA. 2011;108:E874-80.
Hartley S, Thizy D, Ledingham K, Coulibaly M, Diabate A, Dicko B, et al. Knowledge engagement in gene drive research for malaria control. PLoS Negl Trop Dis. 2019;13:e0007233.
OECD (Organization for Economic Cooperation and Development). Safety considerations for biotechnology: scale-up of crop plants. Paris: OECD; 1993.
WHO. Strategies for assessing the safety of foods produced by biotechnology: report of a joint FAO/WHO consultation. Geneva: World Health Organization; 1991.
EFSA. Guidance on the environmental risk assessment of genetically modified plants. EFSA J. 2010;8:1879.
EFSA. Guidance on the environmental risk assessment of genetically modified animals. EFSA J. 2013;11:3200.
EPA (US Environmental Protection Agency). Principles of environmental impact assessment review. Washington, D.C, 1998.
NASEM (National Academies of Sciences, Engineering, and Medicine). Gene Drives on the horizon: advancing science, navigating uncertainty, and aligning research with public values. Washington, DC: The National Academies Press; 2016. 230 p.
Costero-Saint Denis A, Leitner WW, Wali T, James S. Translational considerations of novel vector management approaches. PLoS Negl Trop Dis. 2016;10:e0004800.
James S, Collins FH, Welkhoff PA, Emerson C, Godfray HCJ, Gottlieb M, et al. Pathway to deployment of gene drive mosquitoes as a potential biocontrol tool for elimination of malaria in sub-Saharan Africa: recommendations of a Scientific Working Group. Am J Trop Med Hyg. 2018;98(6_Suppl):1–49.
Landis WG, Brown EA, Eikenbary S. An initial framework for the environmental risk assessment of synthetic biology-derived organisms with a focus on gene drives. In: Trump B, Cummings C, Kuzma J, Linkov I, eds. Synthetic Biology 2020: Frontiers in Risk Analysis and Governance. Risk, Systems and Decisions. p. 257–68.
Mitchell HJ, Bartsch D. Regulation of GM Organisms for Invasive Species Control. Front Bioeng Biotechnol. 2019;7:454.
Devos Y, Gallani B, Firbank LG. Stakeholder workshop “Problem formulation for the environmental risk assessment of gene drive modified insects”. EFSA Supporting Publications. 2020;17:3.
Devos Y, Bonsall MB, Nogué F, Paraskevopoulos K, Wimmer EA, Firbank LG. Outcome of a public consultation on the draft adequacy and sufficiency evaluation of existing EFSA guidelines for the molecular characterisation, environmental risk assessment and post-market environmental monitoring of genetically modified insects containing engineered gene drives. EFSA Supporting Publications. 2020;17:11.
Naegeli H, Bresson JL, Dalmay T, Dewhurst IC, Epstein MM, Guerche P, et al. Adequacy and sufficiency evaluation of existing EFSA guidelines for the molecular characterisation, environmental risk assessment and post-market environmental monitoring of genetically modified insects containing engineered gene drives. EFSA J. 2020;18:e06297.
Raybould A. Problem formulation and hypothesis testing for environmental risk assessments of genetically modified crops. Environ Biosafety Res. 2006;5:119–25.
Wolt JD, Keese P, Raybould A, Fitzpatrick JW, Burachik M, Gray A, et al. Problem formulation in the environmental risk assessment for genetically modified plants. Transgenic Res. 2010;19:425–36.
Garcia-Alonso M, Raybould A. Protection goals in environmental risk assessment: a practical approach. Transgenic Res. 2014;23:945–56.
Raybould A, Macdonald P. Policy-led comparative environmental risk assessment of genetically modified crops: testing for increased risk rather than profiling phenotypes leads to predictable and transparent decision-making. Front Bioeng Biotechnol. 2018;6:43.
WHO. Guidance framework for testing of genetically modified mosquitoes. Geneva: World Health Organization; 2014.
Devos Y, Craig W, Devlin RH, Ippolito A, Leggatt RA, Romeis J, et al. Using problem formulation for fit-for-purpose pre-market environmental risk assessments of regulated stressors. EFSA J. 2019;17 S1:e170708.
Raybould A, Holt K, Kimber I. Using problem formulation to clarify the meaning of weight of evidence and biological relevance in environmental risk assessments for genetically modified crops. GM Crops Food. 2019;10:63–76.
Romeis J, Collatz J, Glandorf DCM, Bonsall MB. The value of existing regulatory frameworks for the environmental risk assessment of agricultural pest control using gene drives. Environ Sci Policy. 2020;108:19–36.
David AS, Kaser JM, Morey AC, Roth AM, Andow DA. Release of genetically engineered insects: a framework to identify potential ecological effects. Ecol Evol. 2013;3:4000–15.
Roberts A, Andrade PP, Okumu F, Quemada H, Savadogo M, Singh JA, et al. Results from the Workshop “Problem Formulation for the Use of Gene Drive in Mosquitoes”. Am J Trop Med Hyg. 2017;96:530–3.
Teem JL, Ambali A, Glover B, Ouedraogo J, Makinde D, Roberts A. Problem formulation for gene drive mosquitoes designed to reduce malaria transmission in Africa: results from four regional consultations 2016–2018. Malar J. 2019;18:347.
Romeis J, Bartsch D, Bigler F, Candolfi MP, Gielkens MM, Hartley SE, et al. Assessment of risk of insect-resistant transgenic crops to nontarget arthropods. Nat Biotechnol. 2008;26:203–8.
Hunt RH, Coetzee M, Fettene M. The Anopheles gambiae complex: a new species from Ethiopia. Trans R Soc Trop Med Hyg. 1998;92:231–5.
Coetzee M, Hunt RH, Wilkerson R, Torre AD, Coulibaly MB, Besansky NJ. Anopheles coluzzii and Anopheles amharicus, new members of the Anopheles gambiae complex. Zootaxa. 2013;3619:246–74.
Davidson G. Anopheles gambiae complex. Nature. 1962;196:907-.
Coluzzi M, Sabatini A, Petrarca V, Di Deco MA. Chromosomal differentiation and adaptation to human environments in the Anopheles gambiae complex. Trans R Soc Trop Med Hyg. 1979;73:483–97.
Barron MG, Paupy C, Rahola N, Akone-Ella O, Ngangue MF, Wilson-Bahun TA, et al. A new species in the major malaria vector complex sheds light on reticulated species evolution. Sci Rep. 2019;9:14753.
Sinka ME, Bangs MJ, Manguin S, Rubio-Palis Y, Chareonviriyaphap T, Coetzee M, et al. A global map of dominant malaria vectors. Parasit Vectors. 2012;5:69.
Lobo NF, Laurent BS, Sikaala CH, Hamainza B, Chanda J, Chinula D, et al. Unexpected diversity of Anopheles species in Eastern Zambia: implications for evaluating vector behavior and interventions using molecular tools. Sci Rep. 2015;5:17952.
Killeen GF, Kiware SS, Okumu FO, Sinka ME, Moyes CL, Massey NC, et al. Going beyond personal protection against mosquito bites to eliminate malaria transmission: population suppression of malaria vectors that exploit both human and animal blood. BMJ Glob Health. 2017;2:e000198.
Chinula D, Hamainza B, Chizema E, Kavishe DR, Sikaala CH, Killeen GF. Proportional decline of Anopheles quadriannulatus and increased contribution of An. arabiensis to the An. gambiae complex following introduction of indoor residual spraying with pirimiphos-methyl: an observational, retrospective secondary analysis of pre-existing data from south-east Zambia. Parasit Vectors. 2018;11:544.
Diabate A, Dabire RK, Kim EH, Dalton R, Millogo N, Baldet T, et al. Larval development of the molecular forms of Anopheles gambiae (Diptera: Culicidae) in different habitats: a transplantation experiment. J Med Entomol. 2005;42:548–53.
Diabate A, Dabire RK, Heidenberger K, Crawford J, Lamp WO, Culler LE, et al. Evidence for divergent selection between the molecular forms of Anopheles gambiae: role of predation. BMC Evol Biol. 2008;8:5.
Epopa PS, Collins CM, North A, Millogo AA, Benedict MQ, Tripet F, et al. Seasonal malaria vector and transmission dynamics in western Burkina Faso. Malar J. 2019;18:113.
North AR, Burt A, Godfray HCJ. Modelling the potential of genetic control of malaria mosquitoes at national scale. BMC Biol. 2019;17:26.
White GB. Chromosomal evidence for natural interspecific hybridization by mosquitoes of the Anopheles gambiae complex. Nature. 1971;231:184–5.
Shidrawi GR. The distribution and seasonal prevalence of members of the Anopheles gambiae species complex (species A & B) in Garki District, Northern Nigeria. Geneva: World Health Organization; 1972.
White GB. Anopheles gambiae complex and disease transmission in Africa. Trans R Soc Trop Med Hyg. 1974;68:278–98.
Bryan JH. Observations on the member species of the Anopheles gambiae complex in The Gambia, West Africa. Trans R Soc Trop Med Hyg. 1979;73:463–6.
Thelwell NJ, Huisman RA, Harbach RE, Butlin RK. Evidence for mitochondrial introgression between Anopheles bwambae and Anopheles gambiae. Insect Mol Biol. 2000;9:203–10.
Costantini C, Ayala D, Guelbeogo WM, Pombi M, Some CY, Bassole IH, et al. Living at the edge: biogeographic patterns of habitat segregation conform to speciation by niche expansion in Anopheles gambiae. BMC Ecol. 2009;9:16.
Lee Y, Marsden CD, Norris LC, Collier TC, Main BJ, Fofana A, et al. Spatiotemporal dynamics of gene flow and hybrid fitness between the M and S forms of the malaria mosquito, Anopheles gambiae. Proc Natl Acad Sci USA. 2013;110:19854–9.
Weetman D, Steen K, Rippon EJ, Mawejje HD, Donnelly MJ, Wilding CS. Contemporary gene flow between wild An. gambiae s.s. and An. arabiensis. Parasit Vectors. 2014;7:345.
Neafsey DE, Lawniczak MKN, Park DJ, Redmond SN, Coulibaly MB, Traore SF, et al. SNP genotyping defines complex gene-flow boundaries among African malaria vector mosquitoes. Science. 2010;330:514–7.
Neafsey DE, Waterhouse RM, Abai MR, Aganezov SS, Alekseyev MA, Allen JE, et al. Mosquito genomics. Highly evolvable malaria vectors: the genomes of 16 Anopheles mosquitoes. Science. 2015;347:1258522.
Harbach RE. The phylogeny and classification of Anopheles. In: Manguin S, editor. Anopheles mosquitoes -. New insights into malaria vectors: IntechOpen; 2013.
Fontaine MC, Pease JB, Steele A, Waterhouse RM, Neafsey DE, Sharakhov IV, et al. Mosquito genomics. Extensive introgression in a malaria vector species complex revealed by phylogenomics. Science. 2015;347:1258524.
Irish SR, Kyalo D, Snow RW, Coetzee M. Updated list of Anopheles species (Diptera: Culicidae) by country in the Afrotropical Region and associated islands. Zootaxa. 2020;4747:401–49.
IRD (Institut de Recherche pour le Développement). GeCol Gestionnaire de Collections Biologiques. Arthropodes d’Intérêt Médical. Montpellier, France; 2020. https://arim.ird.fr/arim/#recherches/index/dico_taxons/.
Collins CM, Bonds JAS, Quinlan MM, Mumford JD. Effects of the removal or reduction in density of the malaria mosquito, Anopheles gambiae s.l., on interacting predators and competitors in local ecosystems. Med Vet Entomol. 2019;33:1–15.
Demont M, Stein AJ. Global value of GM rice: a review of expected agronomic and consumer benefits. Nat Biotechnol. 2013;30:426–36.
Hudson D, Richards R. Evaluation of the agronomic, environmental, economic, and coexistence impacts following the introduction of GM canola to Australia (2008–2010). AgBioForum. 2014;17:1–12.
Adenle AA, Morris EJ, Parayil G. Status of development, regulation and adoption of GM agriculture in Africa: views and positions of stakeholder groups. Food Policy. 2013;43:159–66.
Belay G, Kimani V, Wafula D. Harmonization of regional biosafety and regulatory services to remove future trade barriers in the COMESA Region. In: Wambugu F, Kamanga D, editors. Biotechnology in Africa: emergence, initiatives and future. Berlin: Springer; 2014. p. 207–22.
Raybould A, Cooper I. Tiered tests to assess the environmental risk of fitness changes in hybrids between transgenic crops and wild relatives: the example of virus resistant Brassica napus. Environ Biosafety Res. 2005;4:127–40.
CBD (Convention on Biological Diversity). National Biodiversity Strategies and Actions Plans. https://www.cbd.int/nbsap/.
IUCN (International Union for Conservation of Nature Red List of Threatened Species). http://www.iucnredlist.org/.
Target Malaria. Where we operate. https://targetmalaria.org/about-us/where-we-operate/.
Devos Y, Romeis J, Luttik R, Maggiore A, Perry JN, Schoonjans R, et al. Optimising environmental risk assessments: accounting for ecosystem services helps to translate broad policy protection goals into specific operational ones for environmental risk assessments. EMBO Rep. 2015;16:1060–3.
Nienstedt KM, Brock TC, van Wensem J, Montforts M, Hart A, Aagaard A, et al. Development of a framework based on an ecosystem services approach for deriving specific protection goals for environmental risk assessment of pesticides. Sci Total Environ. 2012;415:31–8.
EEA (European Environment Agency). The Common International Classification of Ecosystem Services (CICES). https://cices.eu/.
Sanvido O, Romeis J, Gathmann A, Gielkens M, Raybould A, Bigler F. Evaluating environmental risks of genetically modified crops: ecological harm criteria for regulatory decision-making. Environ Sci Policy. 2012;15:82–91.
Aron JL, May RM. The population dynamics of malaria. In: Abderson RM, editor. The population dynamics of infectious diseases: theory and applications. Boston: Spinger; 1982. pp. 139–79.
Koella JC. On the use of mathematical models of malaria transmission. Acta Trop. 1991;49:1–25.
Brady OJ, Godfray HC, Tatem AJ, Gething PW, Cohen JM, McKenzie FE, et al. Vectorial capacity and vector control: reconsidering sensitivity to parameters for malaria elimination. Trans R Soc Trop Med Hyg. 2016;110:107–17.
Kim D, Luk K, Wolfe SA, Kim JS. Evaluating and enhancing target specificity of gene-editing nucleases and deaminases. Annu Rev Biochem. 2019;88:191–220.
Scharenberg AM, Stoddard BL, Monnat RJ, Nolan A. Retargeting: an unrecognized consideration in endonuclease-based gene drive biology. bioRxiv. 2016:089946.
Garrood WT, Kranjc N, Petri K, Kim DY, Guo JA, Hammond AM, et al. Analysis of off-target effects in CRISPR-based gene drives in the human malaria mosquito. Proc Natl Acad Sci USA. 2020; in press.
Labun K, Montague TG, Gagnon JA, Thyme SB, Valen E. CHOPCHOP v2: a web tool for the next generation of CRISPR genome engineering. Nucleic Acids Res. 2016;44:W272-6.
EFSA. Scientific Opinion on the Guidance on the risk assessment of food and feed from genetically modified animals and animal health and welfare aspects. EFSA J. 2012;10:2501.
Tsai SQ, Zheng Z, Nguyen NT, Liebers M, Topkar VV, Thapar V, et al. GUIDE-seq enables genome-wide profiling of off-target cleavage by CRISPR-Cas nucleases. Nat Biotechnol. 2015;33:187–97.
Zuo E, Sun Y, Wei W, Yuan T, Ying W, Sun H, et al. Cytosine base editor generates substantial off-target single-nucleotide variants in mouse embryos. Science. 2019;364:289–92.
Courtier-Orgogozo V, Danchin A, Gouyon PH, Boëte C. Evaluating the probability of CRISPR-based gene drive contaminating another species. Evol Appl. 2020;13:1888–905.
Carballar-Lejarazu R, Ogaugwu C, Tushar T, Kelsey A, Pham TB, Murphy J, et al. Next-generation gene drive for population modification of the malaria vector mosquito, Anopheles gambiae. Proc Natl Acad Sci USA. 2020;117:22805–14.
Holt RA, Subramanian GM, Halpern A, Sutton GG, Charlab R, Nusskern DR, et al. The genome sequence of the malaria mosquito Anopheles gambiae. Science. 2002;298:129–49.
IHME (Institute for Health Metrics and Evaluation). Compare GBD. Seattle, WA: University of Washington; 2015. https://vizhub.healthdata.org/gbd-compare/.
James SL, Marshall JM, Christophides GK, Okumu FO, Nolan T. Toward the definition of efficacy and safety criteria for advancing gene drive-modified mosquitoes to field testing. Vector Borne Zoonotic Dis. 2020;20:237–51.
McGreevy PB, Bryan JH, Oothuman P, Kolstrup N. The lethal effects of the cibarial and pharyngeal armatures of mosquitoes on microfilariae. Trans R Soc Trop Med Hyg. 1978;72:361–8.
Amuzu H, Wilson MD, Boakye DA. Studies of Anopheles gambiae s.l (Diptera: Culicidae) exhibiting different vectorial capacities in lymphatic filariasis transmission in the Gomoa district, Ghana. Parasit Vectors. 2010;3:85.
Pi-Bansa S, Osei JHN, Frempong KK, Elhassan E, Akuoko OK, Agyemang D, et al. Potential factors influencing lymphatic filariasis transmission in “hotspot” and “control” areas in Ghana: the importance of vectors. Infect Dis Poverty. 2019;8:9.
Miles A, Harding NJ, Bottà G, Clarkson CS, Antão T, Kozak K, et al. Genetic diversity of the African malaria vector Anopheles gambiae. Nature. 2017;552:96–100.
Clarkson C. Genome variation and population structure among 1,142 mosquitoes of the African malaria vector species Anopheles gambiae and Anopheles coluzzii. Genome Res. 2020;30:1533–46.
Tsai SQ, Nguyen NT, Malagon-Lopez J, Topkar VV, Aryee MJ, Joung JK. CIRCLE-seq: a highly sensitive in vitro screen for genome-wide CRISPR-Cas9 nuclease off-targets. Nat Methods. 2017;14:607–14.
Holt RD, Bonsall MB. Apparent competition. Annu Rev Ecol Evol System. 2017;48:447–71.
Kennedy SR, Prost S, Overcast I, Rominger AJ, Gillespie RG, Krehenwinkel H. High-throughput sequencing for community analysis: the promise of DNA barcoding to uncover diversity, relatedness, abundances and interactions in spider communities. Dev Genes Evol. 2020;230:185–201.
Killeen GF, Seyoum A, Sikaala C, Zomboko AS, Gimnig JE, Govella NJ, et al. Eliminating malaria vectors. Parasit Vectors. 2013;6:172.
Pumpuni CB, Beier MS, Nataro JP, Guers LD, Davis JR. Plasmodium falciparum: inhibition of sporogonic development in Anopheles stephensi by gram-negative bacteria. Exp Parasitol. 1993;77:195–9.
Keene KM, Foy BD, Sanchez-Vargas I, Beaty BJ, Blair CD, Olson KE. RNA interference acts as a natural antiviral response to O’nyong-nyong virus (Alphavirus; Togaviridae) infection of Anopheles gambiae. Proc Natl Acad Sci USA. 2004;101:17240–5.
Dennison NJ, BenMarzouk-Hidalgo OJ, Dimopoulos G. MicroRNA-regulation of Anopheles gambiae immunity to Plasmodium falciparum infection and midgut microbiota. Dev Comp Immunol. 2015;49:170–8.
Carissimo G, Pain A, Belda E, Vernick KD. Highly focused transcriptional response of Anopheles coluzzii to O’nyong nyong arbovirus during the primary midgut infection. BMC Genom. 2018;19:526.
Carissimo G, Pondeville E, McFarlane M, Dietrich I, Mitri C, Bischoff E, et al. Antiviral immunity of Anopheles gambiae is highly compartmentalized, with distinct roles for RNA interference and gut microbiota. Proc Natl Acad Sci USA. 2015;112:E176-85.
Barreaux AMG, Stone CM, Barreaux P, Koella JC. The relationship between size and longevity of the malaria vector Anopheles gambiae (s.s.) depends on the larval environment. Parasit Vectors. 2018;11:485.
Godfray HC. Mosquito ecology and control of malaria. J Anim Ecol. 2013;82:15–25.
Gillies MT, Furlong M. An investigation into the behaviour of Anopheles parensis Gillies at Malindi on the Kenya coast. Bull Entomol Res. 1964;55:1–16.
Gillies MT, Smith A. The effect of a residual house-spraying campaign in East Africa on species balance in the Anopheles funestus group. The replacement of A. funestus Giles by A. rivulorum Leeson. Bull Entomol Res. 1960;51:243–52.
Pringle G. Malaria in the Pare area of Tanzania. 3. The course of malaria transmission since the suspension of an experimental programme of residual insecticide spraying. Trans R Soc Trop Med Hyg. 1967;61:69–79.
Trape J-F, Tall A, Diagne N, Ndiath O, Ly AB, Faye J, et al. Malaria morbidity and pyrethroid resistance after the introduction of insecticide-treated bednets and artemisinin-based combination therapies: a longitudinal study. Lancet Infect Dis. 2011;11:925–32.
Keating J, Eisele TP. Epidemiology of malaria morbidity after control scale-up. Lancet Infect Dis. 2011;11:891–2.
Snow RW, Omumbo JA, Lowe B, Molyneux CS, Obiero J-O, Palmer A, et al. Relation between severe malaria morbidity in children and level of Plasmodium falciparum transmission in Africa. Lancet. 1997;349:1650–4.
O’Meara WP, Bejon P, Mwangi TW, Okiro EA, Peshu N, Snow RW, et al. Effect of a fall in malaria transmission on morbidity and mortality in Kilifi, Kenya. Lancet. 2008;372:1555–62.
Njuguna P, Maitland K, Nyaguara A, Mwanga D, Mogeni P, Mturi N, et al. Observational study: 27 years of severe malaria surveillance in Kilifi, Kenya. BMC Med. 2019;17:124.
Kigozi SP, Kigozi RN, Epstein A, Mpimbaza A, Sserwanga A, Yeka A, et al. Rapid shifts in the age-specific burden of malaria following successful control interventions in four regions of Uganda. Malar J. 2020;19:128.
Alout H, Ndam NT, Sandeu MM, Djegbe I, Chandre F, Dabire RK, et al. Insecticide resistance alleles affect vector competence of Anopheles gambiae s.s. for Plasmodium falciparum field isolates. PLoS One. 2013;8:e63849.
Alout H, Dabire RK, Djogbenou LS, Abate L, Corbel V, Chandre F, et al. Interactive cost of Plasmodium infection and insecticide resistance in the malaria vector Anopheles gambiae. Sci Rep. 2016;6:29755.
Ndiath MO, Cailleau A, Diedhiou SM, Gaye A, Boudin C, Richard V, et al. Effects of the kdr resistance mutation on the susceptibility of wild Anopheles gambiae populations to Plasmodium falciparum: a hindrance for vector control. Malar J. 2014;13:340.
Tchouakui M, Chiang MC, Ndo C, Kuicheu CK, Amvongo-Adjia N, Wondji MJ, et al. A marker of glutathione S-transferase-mediated resistance to insecticides is associated with higher Plasmodium infection in the African malaria vector Anopheles funestus. Sci Rep. 2019;9:5772.
Viana M, Hughes A, Matthiopoulos J, Ranson H, Ferguson HM. Delayed mortality effects cut the malaria transmission potential of insecticide-resistant mosquitoes. Proc Natl Acad Sci USA. 2016;113:8975–80.
Thomas MB, Read AF. The threat (or not) of insecticide resistance for malaria control. Proc Natl Acad Sci USA. 2016;113:8900–2.
Alout H, Labbe P, Chandre F, Cohuet A. Malaria vector control still matters despite insecticide resistance. Trends Parasitol. 2017;33:610–8.
Minetti C, Ingham VA, Ranson H. Effects of insecticide resistance and exposure on Plasmodium development in Anopheles mosquitoes. Curr Opin Insect Sci. 2020;39:42–9.
Killeen GF. Characterizing, controlling and eliminating residual malaria transmission. Malar J. 2014;13:330.
Hayes KR, Hosack GR, Dana GV, Foster SD, Ford JH, Thresher R, et al. Identifying and detecting potentially adverse ecological outcomes associated with the release of gene-drive modified organisms. J Resp Innovation. 2018;5(suppl 1):139-S58.
Turner G, Beech C, Roda L. Means and ends of effective global risk assessments for genetic pest management. BMC Proc. 2018;12(Suppl 8):13.
Golnar AJ, Ruell E, Lloyd AL, Pepin KM. Embracing dynamic models for gene drive management. Trends Biotechnol. 2021;39:211–4.
Beaghton AK, Hammond A, Nolan T, Crisanti A, Burt A. Gene drive for population genetic control: non-functional resistance and parental effects. Proc Biol Sci. 2019;286:20191586.
Cantillo JF, Fernandez-Caldas E, Puerta L. Immunological aspects of the immune response induced by mosquito allergens. Int Arch Allergy Immunol. 2014;165:271–82.
Thirugnanasambantham K, Hairul-Islam VI, Saravanan S, Subasri S, Subastri A. Computational approach for identification of Anopheles gambiae miRNA involved in modulation of host immune response. Appl Biochem Biotechnol. 2013;170:281–91.
Arcà B, Colantoni A, Fiorillo C, Severini F, Benes V, Di Luca M, et al. MicroRNAs from saliva of anopheline mosquitoes mimic human endogenous miRNAs and may contribute to vector-host-pathogen interactions. Sci Rep. 2019;9:2955.
Bensaoud C, Hackenberg M, Kotsyfakis M. Noncoding RNAs in parasite-vector-host interactions. Trends Parasitol. 2019;35:715–24.
Cai Y. Immunostimulatory guide RNAs mediate potent antiviral response. bioRxiv. 2018:282558.
Kim S, Koo T, Jee HG, Cho HY, Lee G, Lim DG, et al. CRISPR RNAs trigger innate immune responses in human cells. Genome Res. 2018;28:367–73.
Wienert B, Shin J, Zelin E, Pestal K, Corn JE. In vitro-transcribed guide RNAs trigger an innate immune response via the RIG-I pathway. PLoS Biol. 2018;16:e2005840.
Teijaro JR. Type I interferons in viral control and immune regulation. Curr Opin Virol. 2016;16:31–40.
Dolo G, Briet OJ, Dao A, Traore SF, Bouare M, Sogoba N, et al. Malaria transmission in relation to rice cultivation in the irrigated Sahel of Mali. Acta Trop. 2004;89:147–59.
Diuk-Wasser MA, Sogoba N, Bagayoko M, Taylor CE, Dolo G, Toure MB, et al. Vector abundance and malaria transmission in rice-growing villages in Mali. Am J Trop Med Hyg. 2005;72:725–31.
Shapiro LLM, Whitehead SA, Thomas MB. Quantifying the effects of temperature on mosquito and parasite traits that determine the transmission potential of human malaria. PLoS Biol. 2017;15:e2003489.
Ghani AC, Sutherland CJ, Riley EM, Drakeley CJ, Griffin JT, Gosling RD, et al. Loss of population levels of immunity to malaria as a result of exposure-reducing interventions: consequences for interpretation of disease trends. PLoS One. 2009;4:e4383.
We thank Target Malaria colleagues Mamadou Coulibaly (Malaria Research and Training Center (MRTC), University of Sciences, Techniques and Technologies of Bamako, Mali), Jonathan Kayondo (Uganda Virus Research Institute (UVRI), Uganda), Andrea Beaghton, Federica Bernardini, Bhavin Kathri, Samantha O’Loughlin (Imperial College London, UK), Talya Hackett (Oxford University, UK), Ruth Mueller (Institute of Tropical Medicine, Belgium and Polo GGB, Italy), Tony Nolan (Liverpool School of Tropical Medicine, UK), Alekos Simoni (Polo GGB, Italy), Frederic Tripet (Keele University, UK), Mark Benedict, Ellen Dotson (Centres for Disease Control and Prevention, USA), and Raymond Monnat (University of Washington, USA) for comments on draft pathways,both anonymous peer reviewers of this article for their helpful comments and insights, and all the contributors to the gene drive problem formulation workshops organised by AUDA-NEPAD in Africa and the FNIH in the USA between 2016 and 2019 [45, 46].
The authors are either members (JBC, JDM, SF, GT, ARN, AB) of, or consultants (CB) to, the Target Malaria not-for-profit research consortium, which receives core funding from the Bill & Melinda Gates Foundation (Grant INV006610 Target Malaria Phase II) and from the Open Philanthropy Project Fund (Grant O-77157), an advised fund of Silicon Valley Community Foundation.
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JBC: Employment by Imperial College London in a position which is solely funded through a grant from the Bill & Melinda Gates Foundation, Member of Target Malaria not-for-profit research consortium; Travel grants from FNIH. JDM: Employment by Imperial College London; Member of Target Malaria not-for-profit research consortium; Research grants from Bill & Melinda Gates Foundation; Working Group and Hearing Expert for European Food Safety Authority; Travel grants from FNIH, World Health Organisation and International Atomic Energy Agency. SF: Employment by Imperial College London in a position which is solely funded through a grant from the Bill & Melinda Gates Foundation; Member of Target Malaria not-for-profit research consortium; Travel grants from FNIH. GT: Employment by Imperial College London in a position which is solely funded through a grant from the Bill & Melinda Gates Foundation, and was formerly funded solely through a grant from the Open Philanthropy Project Fund, an advised fund of Silicon Valley Community Foundation; Member of Target Malaria not-for-profit research consortium; Travel grants from FNIH; Former employee of Oxitec Ltd, an entity with commercial interests in genetic insect technologies. CB: Paid consultancy with Imperial College London, a partner in the Target Malaria non-for-profit research consortium; Former employee at Oxitec Ltd., an entity with commercial interests in genetic insect technologies, and shareholder in its parent company Intrexon Inc.; Member of the World Health Organisation Vector Control Advisory Group; Member of the International Society for Biosafety Research (ISBR); Member of ISBR program committee for 2019 conference, receiving an honorarium for attendance at the conference; Travel grants from FNIH. ARN: Employment by University of Oxford in a position which is solely funded through a grant from the Bill & Melinda Gates Foundation; Member of Target Malaria not-for-profit research consortium; Travel grants from FNIH. AB: Employment by Imperial College London; Principle Investigator of the Target Malaria not-for-profit research consortium, which receives core funding from the Bill & Melinda Gates Foundation and from the Open Philanthropy Project Fund, an advised fund of Silicon Valley Community Foundation.
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Connolly, J.B., Mumford, J.D., Fuchs, S. et al. Systematic identification of plausible pathways to potential harm via problem formulation for investigational releases of a population suppression gene drive to control the human malaria vector Anopheles gambiae in West Africa. Malar J 20, 170 (2021). https://0-doi-org.brum.beds.ac.uk/10.1186/s12936-021-03674-6
- Gene drive
- Population suppression gene drive
- Field release
- Vector control
- Problem formulation
- Pathways to harm
- Environmental risk assessment (ERA)