Abstract
Vector-borne diseases, among them leishmaniasis, cause more than 700,000 deaths annually. The lack of an effective vaccination and the increasing resistance of sand flies to insecticides require the urgent development of innovative approaches to contain the disease. The use of engineered bacteria that express anti-parasite molecules (paratransgenesis) shows much promise. However, a challenge for implementation of this strategy is to devise means to introduce modified bacteria into sand flies in the field. In this study, we use rodent food bait as a delivery strategy to introduce two mCherry-fluorescent bacteria, Serratia AS1 and Enterobacter cloacae, into adult sand flies in field settings. Bacteria-infected food was provided to Rhombomys opimus rodents. These bacteria transiently pass through the rodent alimentary tract and are delivered to larval habitats with the rodent feces. The feces are ingested by sand fly larvae and, in the case of Serratia AS1, are trans-stadially transmitted to adults. This is the first report of targeting delivery of Serratia AS1 in a paratransgenic system to control transmission of leishmaniasis under field condition. This novel strategy shows promise for delivering transgenic bacteria to Leishmania vectors in the field.
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Introduction
Leishmaniasis is caused by parasites of the genus Leishmania. These parasites are transmitted by the bite of female phlebotomine sand flies of the genus Phlebotomus in the Old World and Lutzomyia in the New World1,2. Three basic manifestations of the illness are cutaneous, mucocutaneous, and visceral. Skin ulcers are characteristic of the cutaneous form, whereas mouth, nose, and skin ulcers are characteristics of the mucocutaneous type. The visceral form manifests by fever, low red blood cell count, and enlarged spleen and liver. Skin symptoms may occur after the initial visceral leishmaniasis in the form of Post Kala-azar dermal leishmaniasis (PKDL). More than 20 different species of Leishmania are responsible for human infections2,3,4.
A total of 97 out of 200 nations and territories are endemic for leishmaniasis. Leishmaniasis is widespread, from deserts of western Asia and the Middle East to the rainforests of Central and South America. With 700,000 to 1 million new cases annually, it may affect as many as 12 million people worldwide3,4.
Human leishmaniasis has two main means of transmission: (i) from animal reservoirs in case of zoonotic1,5 and (ii) transmission from person to person in case of anthroponotic leishmaniasis1,6,7. Wild or domestic animals, such as hyrax, dogs, foxes, wolves, and rodents may serve as reservoirs for zoonotic leishmaniasis.
Because of the complexity of biological and epidemiological conditions of transmission, that includes human or animal reservoirs, a variety of parasites and sand fly vectors, disease control requires a combination of strategies1,5,8. Developing vector insecticide resistance and parasite resistance to drugs are hampering the fight of parasite infection and treatment. These limitations point to the need for the development of novel and more effective strategies that impact minimum environmental effects3,9,10,11.
Paratransgenesis, consisting of engineering symbionts to produce anti-pathogen molecules, shows promise for combating pathogen transmission by insect vectors. Some examples are listed in Table 1. Of note, paratransgenesis is compatible with other control methods39. One of the most important challenges in paratransgenesis is to find a robust delivery system to introduce the engineered symbiont to vectors in the field. In endemic foci of ZCL in Iran, the Leishmania-carrying sand flies prefer to lay their eggs in reservoir rodent dwellings. Sand flies larvae feed on rodent’s feces in their nests, in depths of 1–2 m below the earth’s surface. We hypothesized that if these feces were contaminated with bacteria, they could be transmitted to larvae, and in case of Serratia As1, be further transmitted from larvae to adults40.
Recently, two bacteria, Serratia AS1 and Enterobacter cloacae have been evaluated as paratransgenesis candidates against vector-born disease18,20,21,22,23,41,42. In this study we tested rodent food bait containing Serratia AS1 or E. cloacae as a delivery method to adult sand flies, using laboratory and field conditions.
Materials and methods
Study area
Our research was conducted on a site that will henceforth be referred to as the “field site”, located in the Isfahan Province at 33° 44′ 59.3′′ N 51° 59′ 59.9′′ E with altitude of 981 m above sea level. The province is known as one of the most important leishmaniasis foci, in the country. It is located about 6 km north of Badroud City and is 2.3 km to the closest village (Fig. 1). Phlebotomus papatasi is the dominant and the main sand fly vector species in this region. Rodents used for experiments were collected in this location. Sherman traps were used to capture alive Rhombomys opimus (Muridae: Gerbillinae) which is the dominant and the most important reservoir in the region.
Establishment of transgenic bacteria expressing mCherry fluorescent protein
Serratia AS1-mCherry a facultative aerobic, Gram-negative, rod-shaped bacterium belonging to the Enterobacteriaceae family was a gift from Prof. Jacobs-Lorena from the Department of Molecular Microbiology and Immunology, Malaria Research Institute, Johns Hopkins Bloomberg School of Public Health. It was generated by integration of a pBAM2 plasmid carrying a mCherry fluorescent protein gene23,41. The plasmid was constructed by replacing a beta-lactamase (ApR) gene of the plasmid pBAM1 with expression cassette43. pBAM2-mCherry was transformed into both bacteria (Serratia AS1 and E. cloacae) using heat shock method44. Enterobacter cloacae subsp. dissolvens, a rod-shaped, gram-negative bacterium belonging to the family Enterobacteriaceae was isolated from microflora of Ph. papatasi from a zoonotic cutaneous leishmaniasis area in Isfahan, central Iran45. The transformed bacteria were cultured on Luria–Bertani (LB) agar plate containing the apramycin (80 µg/ml) antibiotics for about 16 h, after that single colony of mCherry-fluorescent bacteria was isolated and cultured on LB agar at 28 and 37 °C for Serratia AS1 and E. cloacae respectively. Stocks of bacteria were prepared and stored in – 80 °C for further use. In all the lab and field experiments, besides observation of fluorescence protein, a selective LB medium containing the apramycin (80 µg/ml) antibiotics was used thoroughly. The transformed bacteria and sand fly specimens fed on the transformed bacteria were used as a positive and the wild type bacteria and wild sand flies not fed on the transformed bacteria were used as negative controls.
Preparing bacterial suspension
The transformed bacteria were cultured in LB broth at 28 °C for Serratia and 37 °C for E. cloacae in shaking incubator until reaching OD600 = 1 (109 cell per ml), then cells were harvested by centrifugation (3000×g, 10 min), washed twice in sterile phosphate-buffered saline (PBS), and resuspended in 5% (w/v) sterile sucrose solution to obtain 109 cells/ml. The bacterial suspensions were used for our experiments.
Gastrointestinal transit time in R. opimus
To perform the test of whether the bacteria can pass through rodents alimentary and its speed, nine female, non-pregnant, 200–300 g weight of R. opimus (great gerbil) were selected randomly from the animal unit in Isfahan Health Research Station, and divided into 3 groups of three rodents each. There were no exclusion criteria except sex. The first and second groups were offered food infected by the modified E. cloacae subsp. dissolvens and Serratia AS1 expressing cherry-fluorescent respectively, and the third group was used as control. A mix of 10 g pellets (parsfeed®, consisting of wheat straw, sodium chloride, maize, fish meal, whey powder, soybean dehulled, dicalcium phosphate, soybean oil, corn, calcium carbonate and yeasts) and 10 g carrots (as a source of water) were coated with 1 ml bacteria suspension (109 cell per ml suspension per gram of food) and given to the treatment groups; the same amount of food without bacteria was available to the control group. Rodents were then transferred to disinfected solitary cages. Their fecal samples were collected every 2 h and 0.1 g of each fecal sample was homogenized in 900 µL of PBS, serial dilutions were plated on LB agar medium and then fluorescent colonies were counted. The whole process was repeated 3 times. The sixth author was aware of the group allocation, and then the rest of experiment was followed blindly by first author. All the animals were healthy and normal at the end of the experiment.
Stability of bacteria in R. opimus feces
Rodent stool samples that were positive for transgenic bacteria were divided into two parts and stored at 24 °C to evaluate bacterial stability. One part was stored in 1.5 ml plastic closed-lid micro tube and another part in open-lid micro tube. Bacteria were assayed daily using serial dilution on LB agar medium and CFUs were counted.
Stability of bacteria in R. opimus food
Experiments were conducted to determine bacteria stability when added to rodent food in laboratory (26 °C, 25% RH) and field conditions (Minimum temperature: 39.5 °C and Maximum 51 °C, with 11.5–19.6% RH). Colony-forming units (CFUs) in rodent food containing 109 bacteria/gram of food were determined by daily sampling for 12 consecutive days. Sampling was carried out as follows: 0.1 g food was removed and was added to 900 µl of sterile PBS buffer and serially diluted. A total of 100 µl was cultured in LB agar plates and bacteria CFUs per gram of food were calculated.
Vivarium setup
The semi-field enclosure (hereafter, vivarium) was built using scaffold frameworks measuring 15 × 6 × 2.5 m. The framework was fully covered with fine-mesh (400 holes/cm2) cotton mosquito net to prevent sand fly escape. The interior was divided into two equal parts accessible via zipper doors, each part for one of the bacteria. For protecting the net from wild animals, green plastic shade net was used all around the enclosure (Fig. 2). The vivarium's position was carefully chosen to include naturally populated by high numbers of wild sand flies, three separate wild R. opimus colonies, and at least five shrubs of the area's dominant vegetation, Haloxylon persicum, on either side of it. Using mosquito net allows the vivarium to have the exact same temperature, sunlight and air circulation of the surrounding environment.
Adult sand fly bacterial acquisition via larval diet
Laboratory tests
For conducting this section of our test, using a hand aspirator, live sand flies were captured and transferred to sand fly insectary of School of Public Health, Tehran University of Medical Sciences. Sand flies were fed on the blood of BALB/c mice. After feeding blood-engorged females with few males were moved to oviposition pots which were lined with plaster of Paris and covered with fine mesh net. They were fed with honey solution (50%) and saturated sucrose. After oviposition and death of adult sand flies, the remnants were removed, and pots were maintained at 26 ± 2 °C and 72 ± 10% relative humidity. Pots were checked daily for hatched eggs. The larvae were fed by powdered diet consisting of rabbit food (pellet) and rabbit excrement46 laced with the two bacteria (1ml suspension containing 109 cells per 1 gr larval food). Adult sand flies which emerged from these pots were divided into three groups (1) intact specimens without sugar or blood meal (2) fed on sugar meal and (3) fed on both sugar and blood of BALB/c mouse. After 24 h the sand flies were chilled to death, homogenized, and cultivated on LB Agar media after being surface sterilization with 70% alcohol. The specimens were washed by PBS and the washout was used as negative control to ensure that bacteria were not getting transmitted mechanically.
Field tests
As mentioned, chambers were set up where rodents and sand flies naturally occur. Bacteria were prepared the same way as for laboratory tests. The food consisting of pellets and carrots coated with bacteria (1ml suspension containing 109 cells per gram of food), were provided to rodents in a separate chamber for each bacterium. Wheat (50 g) was added to the food as a mean to prevent rodents to leave the vivarium, as this is their main food source in natural conditions. About 20 g of fresh food contaminated with the bacteria were supplied for each rodent burrow every day. Ten days after starting to feed the rodents on the bacteria, sand flies that emerged from larvae that fed on the rodent feces, were captured at regular interval every three to four days and transferred into individual cages. The flies were frozen 24 h after blood feeding on mice and after being surface cleaned with PBS and sterilized with 70% alcohol, they were homogenized in 100 µl PBS and plated on LB agar media. To confirm sand fly’s surface sterilization, the captured sand flies were washed with PBS and then the washed PBS was plated for the fluorescent bacteria, and in case of infection to the bacteria, that specimen was discarded from analysis.
Statistics
Significance of bacteria relative abundance between samples was analyzed using the Mann–Whitney U test. Means were compared using Student’s t test. SPSS version 27 was used for all statistics. p < 0.05 was considered statistically significant.
Ethics approval
The protocols were conducted in this study followed the guidelines of the institutional ethical committee (School of Public Health & Allied Medical Sciences- Tehran University of Medical Sciences, SPH-TUMS). The protocols were approved by Biomedical Research Ethics Committee of SPH-TUMS under registry IR.TUMS.SPH.REC.1399.243. We confirm the study is reported here was performed in accordance with ARRIVE guidelines.
Results
We tested the introduction of fluorescent Serratia As1 and E. cloacae subsp. dissolvens into adult sand flies by feeding rodents with food containing the bacteria and exposing sand fly larvae to their feces.
Recording of gastrointestinal transit time in R. opimus
Fluorescent Serratia As1 and E. cloacae dissolvens were fed to R. opimus and bacteria number in their feces was measured at different times. The peak number for Serratia AS1 bacteria was at 4 h after bacteria feeding, while for E. cloacae bacteria peaked at 8 h after feeding (Fig. 3). No bacteria were found after 14 h.
Survival of bacteria in close/open lid
This test was conducted to mimic natural situation of faeces and their bacteria in the depth of rodent burrows as close lid and ground surface as open lid. We found that both bacteria are more stable under a closed lid environment. Serratia AS1 is less stable than E. cloacae, and the latter can be detected in cultures for a longer period of time (open lid: 19 versus 8, close lid: 7 versus 6 days) (Fig. 4). Also, the abundance of E. cloacae (e.g., at maximum point with 9.3 × 108 CFUs/g feces) was several folds higher than Serratia AS1 (at maximum point 3 × 106 CFUs/g feces).
Survival of bacteria on R. opimus’s diet
Both bacteria were detected in the food up to day 12 in the laboratory and only up to day 4 in the field (Fig. 5). No bacteria were found after the last time points shown in the figure.
Transstadial transmission
Laboratory tests
Sand fly larvae were fed with a powdered diet, consisting of rabbit food and rabbit excrement, laced with the two bacteria. A total of 50 emerged adult sand flies (20 males and 30 females) were tested for transstadial transmission of Serratia AS1 from the larvae. We found that six out of 20 males (30%) harbored 3–7 CFUs respectively. Out of the 30 females, five were tested immediately after emergence, without sugar feeding, and were negative for Serratia AS1-mCherry. The 25 remaining females were fed on sugar and 18 of them succeeded to feed on blood. Three out of seven sugar-fed female flies were positive for Serratia AS1-mCherry with 16–27 CFUs. Eleven out of the 18 blood-fed sand flies were positive for Serratia AS1-mCherry, with 1100 to 2150 CFUs colonies at 24 h post blood feeding. Altogether, 20 out of 50 (40.0%) of sand flies were positive for the bacterium in laboratory experiments. As for E. cloacae, we found only one positive fly (out of 50 tested) carrying 226 CFUs 24 h post blood feeding.
Field tests
Ten days after starting to feed the rodents on the bacteria, sand flies that emerged from the rodent burrows were captured at regular interval every three-four days and transferred to individual cages. A total of 515 Ph. papatasi adult flies were captured from two vivariums. From one vivarium containing three rodent colonies (each colony contains about 7 animals and was considered as one replicate) that were fed with E. cloacae, 249 sand flies (87 males, 162 females) were captured; from the other vivarium containing three rodent colonies that were fed with Serratia AS1, 266 sand flies (108 males, 158 females) were captured. Sampling was performed at regular (3–4 days) interval. Of the 418 (out of 515) flies that were caught during the first 20 days, none was positive for either of the two bacteria. Sand flies positive for Serratia AS1 first appeared on day 21 post feeding of the rodents with food containing the modified bacteria. Additional positive flies were also found on days 24, 35, and 41. A total of 12 (six males and six females) out of 97 (12.4%) of the sand flies captured from day 21 to day 41 were positive for the Serratia AS1-mCherry bacterium (Fig. 6A). The numbers of the bacterium colonies in the gut of sand flies ranged from 40 to 300 CFUs per specimen with a mean of 167.9 CFUs (Fig. 6B). Only one female sand fly specimen that had been captured on day 24 was infected with E. cloacae-mCherry and contained 10 CFUs. These results indicate that Serratia AS1can be transferred transstadially in Ph. papatasi sand flies in natural conditions, while E. cloacae transfer is very rare.
Discussion
We showed that Serratia AS1-mCherry can be introduced to Ph. papatasi larvae and then to adults via R. opimus feces as a source of infection. The Serratia added to the wild R. opimus food (carrot or pellet) passes through the rodent digestive tract and is then excreted with the feces in the hidden nests where sand fly larvae breed. The temperature and RH in the depth of nest is respectively much cooler and higher than outside of rodent burrows which are in favor of bacterial survival, as we showed that high temperature and low RH have a big effect on the survival of bacteria on rodent food. The bacteria ingested by the larvae are then transstadially transmitted to the pupae and adult sand flies. We found that, in adult sand flies carrying transgenic bacteria expressing defensin, the development of Leishmania parasites is inhibited18. Transstadial transmission of Serratia AS1 has also been reported in An. gambiae, An. stephensi, and Culex pipiens mosquitoes21,22,23.
We found that Serratia AS1 can be introduced to both adult male and female sand flies. It has been shown that some bacteria such as Serratia AS1 can be transmitted horizontally during copulation (venereal transmission)20,23,47,48,49,50, and we have previously shown that Serratia AS1 is transmitted venereal from Ph. papatasi males to females51. Venereal transmission of Serratia AS1 facilitates introduction of the bacteria into sand fly populations. In addition, it provides potential use of non-vector and harmless male sand flies as a delivery route for genetically modified Serratia AS1 producing anti-Leishmania effector molecules. We note that Serratia AS1 can be transmitted for three An. stephensi generations20; it will be of interest to determine for how many sand fly generations this bacterium can persist.
Sand flies harboring Serratia first appeared 21 days post-feeding of rodents on food baits containing the fluorescent bacteria. From days 10 through 18, 98 adult sand flies were captured, none of which were positive for the bacteria. The first positive flies were observed on day 21. This time gap (first 20 days) agrees with the sand fly life cycle, which takes about 20 days for development from third/forth instar larvae to adults52,53. Flies that were positive on days 35 or 41 post-feeding of rodent on food baits probably represent the smaller larvae (1st–2nd stage) which needed more time to develop to adults.
We investigated the stability of the two modified bacteria when added to the rodent food under field and laboratory conditions. We found that there is a sharp decline in bacterial numbers of both E. cloacae and Serratia AS1 on rodent food, but that a considerable number of viable bacteria (more than 200,000 CFUs per ml of food suspension for both bacteria) remained until day four under field conditions. However, no bacteria were found after four days, indicating that it is necessary to replace food baits with fresh baits every four days. This loss may be caused, at least in part, by the loss of the plasmid encoding the fluorescent protein, as was found to be the case for Anopheles mosquitoes20.
We have conducted an open/closed lid experiment to mimic the natural situation of feces and their bacteria in the depth of rodent burrows as close lid and ground surface as open lid. Although, this experiment in some way mimics the natural situation particularly in case of temperature and RH, however, a more detailed and precise experiment is needed to measure the environment parameters such as oxygen concentration (or air composition), humidity, and temperature in these two different filed environments.
In this study, the bacteria were administered to the rodents via food (pellet and carrots), which is high in fiber, is an easy and practical delivery system, and is like the R. opimus diet in nature. Moreover, we observed that the two bacteria cannot colonize the R. opimus alimentary canal and only transiently pass through it, being egested with the feces. We detected both bacteria in the feces for 14h after feeding, with a peak at 4 h for Serratia AS1, and 8h for E. cloacae. This agrees with the findings of Padmanabhan et al.54 who showed that it takes 6–8 h for activated charcoal to reach the colon and fecal pellet. The mean number of excreted bacteria for those peak hours was 311,000 bacteria (CFU) for Serratia AS1 and 874,000 for E. cloacae.
Adult sand flies may pick up bacteria from at least one of the following three sources: plant saps during sugar feeding, animal host skin while taking a blood meal, or transstadially, where bacteria are transmitted from larvae to adult55,56,57. For the paratransgenesis approach against pathogens, understanding bacterial acquisition routes is crucial, since it indicates how best to introduce transgenic bacteria to vectors in field conditions. In this study, we found that E. cloacae could not be transmitted transstadially to adult sand flies. Although it has been shown that wild or modified E. cloacae has the potential to be used in control of insects58,59 or to block parasite transmission in mosquitoes and sand fly vectors18,42,43, this bacterium cannot be transmitted via the transstadial route17. Thus, alternative delivery of this bacterium needs to be explored, using other routes, including sugar baits and animal host skin23,58,59.
In this study we observed the negative result of bacteria detection in adults immediately after emergence, prior to the intake of sugar or blood. It is known that the quantity of bacteria pass from larvae to adult stage will diminish strongly and reach to few to no bacteria in the midgut during metamorphosis because huge physiological and biochemical variations, involving the larval immune system and loss of the peritrophic membrane due to the midgut enzymes’ activities41,60,61,62,63,64,65.
Safety and non-pathogenic of the modified bacteria to other organisms including humans, animals, and harmless or beneficial insects are some important prerequisites before releasing the transformed bacteria in nature. The requirements for using engineered bacteria for paratransgenesis have been reviewed by Ratcliffe et al. 202266. There are some studies assuring some of these requirements for safety of Serratia AS1 before released into the environment. For example, Huang et al.20 showed lack of horizontal gene transfer in An. stephensi infected with fluorescent Serratia. These authors demonstrated a self-limiting event for the modified Serratia because the bacteria had lost the plasmids used for transforming returning to the wild type after three generations of mosquitoes. However, concerns about the possible pathogenicity of the modified Serratia towards animals and humans must be considered since there is a report on opportunistic pathogenicity of Serratia in humans67, even though the pathogenic bacteria belonging to S. marcescens which is not the same as the Serratia bacteria isolated from insect41 and used in this study.
In this study we showed that under the desert conditions in summertime when the temperature was maximum and RH was minimum in the vivarium, 12% of emerging adults were infected. We suggest that if the bacteria apply from the beginning of sand fly seasonal activity and repeated throughout the spring, summer, and early autumn, this rate will be increased since the environment condition in spring and autumn is milder and support the bacteria survival. This method can be used to control ZCL in Iran and neighboring countries with the same or similar rodent reservoir hosts and vector that share the same microhabitat, where infected food can be easily delivered. These reservoir rodents are reported in central and south Asia from Uzbekistan, Kyrgyzstan, Kazakhstan, Turkmenistan, Tajikistan, Pakistan, Iran, Afghanistan, to southern Mongolia, and north-western China68,69,70,71,72,73,74,75,76. However, it would be challenging to apply this method to more complex or less well-known transmission cycles, e.g., in tropical forests of South and Central America where different wild and synanthropic rodents are reservoirs of American cutaneous leishmaniasis (ACL)77.
In summary, we show that transgenic Serratia AS1 bacteria can be introduced into sand flies utilizing rodents as carrier, a delivery strategy that may be used in the field (Fig. 7). Other delivery systems that directly target adult sand flies, including sugar baits and animal host skin may complement this approach.
Data availability
All the data are available and presented in the text.
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Acknowledgements
Research was supported by Elite Researcher Grant Committee under award number 989593 from the National Institutes for Medical Research Development (NIMAD), Tehran, Iran. Also, this study was supported by the Tehran University of Medical Sciences, Iran, Grant number 48901. The manuscript was edited for English language by the ICGEB Editing Service (manuscripts@icgeb.org).
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M.G., M.A.O. involved in conceptualization, A.A.A., K.A. performed Formal analysis, M.A.O. helped for Funding acquisition, M.G., M.K., A.Z.R., B.Y., M.H.A., R.J., M.A., and L.S. did Methodology and Data curation, M.G., M.K., A.Z.R., B.Y., M.H.A., R.J., M.A., L.S., and K.A. performed Investigation, M.A.O. and A.A.A. provide Resources, Supervised the project, and Wrote, reviewed and edited the manuscript, M.A.O. did Project administration, M.G.: Wrote the original draft. All authors reviewed the manuscript.
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Ghassemi, M., Akhavan, A.A., Zahraei-Ramazani, A. et al. Rodents as vehicle for delivery of transgenic bacteria to make paratransgenic sand fly vectors of cutaneous leishmaniasis in field condition. Sci Rep 13, 14912 (2023). https://doi.org/10.1038/s41598-023-41526-2
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DOI: https://doi.org/10.1038/s41598-023-41526-2
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