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Effect of temperature on the development of the aquatic stages of Anopheles gambiae sensu stricto (Diptera: Culicidae)

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Global warming may affect the future pattern of many arthropod-borne diseases, yet the relationship between temperature and development has been poorly described for many key vectors. Here the development of the aquatic stages of Africa's principal malaria vector, Anopheles gambiae s.s. Giles, is described at different temperatures. Development time from egg to adult was measured under laboratory conditions at constant temperatures between 10 and 40 degrees C. Rate of development from one immature stage to the next increased at higher temperatures to a peak around 28 degrees C and then declined. Adult development rate was greatest between 28 and 32 degrees C, although adult emergence was highest between 22 and 26 degrees C. No adults emerged below 18 degrees C or above 34 degrees C. Non-linear models were used to describe the relationship between developmental rate and temperature, which could be used for developing process-based models of malaria transmission. The utility of these findings is demonstrated by showing that a map where the climate is suitable for the development of aquatic stages of A. gambiae s.s. corresponded closely with the best map of malaria risk currently available for Africa.
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Bulletin of Entomological Research (2003) 93, 375–381 DOI 10.1079/BER2003259
Effect of temperature on the development
of the aquatic stages of Anopheles gambiae
sensu stricto (Diptera: Culicidae)
M.N. Bayoh and S.W. Lindsay*
School of Biological and Biomedical Sciences, University of Durham,
Science Laboratories, Durham, DH1 3LE, UK
Abstract
Global warming may affect the future pattern of many arthropod-borne
diseases, yet the relationship between temperature and development has been
poorly described for many key vectors. Here the development of the aquatic stages
of Africa‘s principal malaria vector, Anopheles gambiae s.s. Giles, is described at
different temperatures. Development time from egg to adult was measured under
laboratory conditions at constant temperatures between 10 and 40°C. Rate of
development from one immature stage to the next increased at higher
temperatures to a peak around 28°C and then declined. Adult development rate
was greatest between 28 and 32°C, although adult emergence was highest between
22 and 26°C. No adults emerged below 18°C or above 34°C. Non-linear models
were used to describe the relationship between developmental rate and
temperature, which could be used for developing process-based models of malaria
transmission. The utility of these findings is demonstrated by showing that a map
where the climate is suitable for the development of aquatic stages of A. gambiae
s.s. corresponded closely with the best map of malaria risk currently available for
Africa.
Introduction
Estimating the potential impact of climate change on
malaria transmission has generated a great deal of interest
due, in part, to the concern that this debilitating disease may
emerge or re-emerge in many parts of the world (Bradley,
1993; Sutherst et al., 1995; Lindsay & Birley, 1996; Martens,
1998; Craig et al., 1999; Rogers & Randolph, 2000; Kovats et
al., 2001). There is a consensus amongst these scientists that
changes in the weather can affect malaria transmission, but
it is uncertain whether any changes in recent malaria
patterns are related to long-term changes in climate. With
the availability of detailed environmental data sets and
increased computing power, modelling climate change and
malaria transmission has never been easier. However, some
of the basic insect data on which process-based models are
constructed, such as vector survival and human-biting rate,
are lacking or poorly derived, raising concerns about the
accuracy of future scenarios.
The rate at which new individuals are produced is one
of the key factors that determine the growth rate of insect
populations. This rate is critically dependent on the
growth characteristics of immature stages, which is
governed by temperature, where food is not limiting
(Lassiter et al., 1995). The influence of temperature on
these stages has been studied in a number of different
species of mosquitoes (Diptera: Culicidae), including
Anopheles quadrimaculatus Say (Huffaker, 1944), Aedes
aegypti Linnaeus (Bar-Zeev, 1958; Tun-Lin et al., 2000),
Culex and Anopheles species (Shelton, 1973), Toxorhynchites
brevipaplis Theobald (Trips, 1972) and Wyeomyia smithii
Coquillett (Bradshaw, 1980), but not in detail in
*Author for correspondence
Fax: +44 (0)191 374 1179
E-mail: S.W.Lindsay@durham.ac.uk
anophelines (Bradshaw, 1980). In general, within the limits
of a lower development threshold and an upper lethal
temperature, the aquatic stages of mosquitoes develop
faster as temperature increases (Brust, 1967; Hagstrum &
Workman; 1971; Lyimo & Takken, 1993). The shortening of
aquatic life is important since it will increase adult
turnover, with consequences for increased vector biting
rates and disease transmission (Garett-Jones, 1964).
Importantly, the production of adult mosquitoes is not
directly proportional to the rate of development of the
aquatic stages since at temperatures that result in the fastest
rate of development, fewer adults are produced. Similarly, at
low temperatures, few adults may be produced in the field,
due to the drying up of breeding habitat, or a reduction in
numbers from predation or disease pathogens (Speight et al.,
1999), although evidence for this is rare.
Various temperature driven development models have
been used to predict the time of insect development. Where
temperatures fluctuate during the day, hourly rates can be
accumulated and converted to daily rates and then
converted to development times. A common approach is to
use the linear portion of the development rate versus
temperature curve to calculate development time, by
summing the number of thermal units (degree-hours or
degree-days) contributed at each temperature (Baskerville
& Emin, 1969; Abrami, 1972; Sevacherian et al., 1977). This
method is convenient as it requires minimal data for
formulation, it is simple to calculate and is often accurate
(Eckenrode & Chapman, 1972; Ali Niazee, 1976). However,
it is valid only over intermediate temperatures and the
threshold temperatures below or above which development
ceases are often determined by extrapolation. As a result,
the number of degree-days required for complete
development is often too low at temperatures near the
lower threshold and too high at temperatures near or above
the optimum (Howe, 1967). Several other models involving
the use of exponential equations, second and third degree
polynomials, logistic equations, modified sigmoid
equations have been developed and used with varying
degrees of success (Wagner et al., 1984).
Despite the enormous medical importance of Anopheles
gambiae Giles, the chief vector of malaria in Africa, the
relationship between temperature and their development is
poorly understood. One of the few published references is
the work of Jepson and others from Mauritius (Jepson et al.,
1947). This work describes development at mean
temperatures between 23 and 32°C at 11, markedly different,
natural-breeding sites. There were also large daily
differences in temperature between sites, varying from 4 to
12°C. This is important since developmental rates of
organisms depend both on the mean temperature and the
frequency and magnitude of any fluctuations around the
mean (Cossins & Bowler, 1987; Liu; 1990). Lyimo and
colleagues (Lyimo et al., 1992) investigated the effect of
temperature on A. gambiae development rate, but also at a
narrow temperature range (24–30°C). The aim of the present
study was to produce a mathematical expression for the
relationship between A. gambiae s.s. development rates over
a wider temperature range (10–40°C) in order to quantify
adult production at these temperatures. Maximum and
minimum thresholds for adult emergence were used to
produce a distribution map for mosquito suitability based
on climate and this was compared with the distribution of
malaria across Africa.
Materials and methods
Insect cultures
Stocks of the 16CSS strain of A. gambiae s.s., originally
from Lagos, were maintained at 26°C (± 1°C), 80% relative
humidity (± 10%) and a 12:12 h light and dark regime.
Immature stages were reared at constant temperatures
ranging from 10 to 40°C (± 1°C), with 2°C increments, under
a 12:12h light and dark regime in programmable growth
chambers (LMS cooled incubators, S.H. Scientific, UK).
Water temperature was monitored using data loggers (Tiny
Talk II, Gemini, UK, with ± 0.5°C accuracy).
Egg development
Approximately 200 adult female mosquitoes were fed on
defibrinated horse blood (Oxoid, UK) in order to produce
eggs. Sixty eggs, less than one day old, were added to 1 l of
48-h-old tap water in plastic bowls, 15 cm × 10 cm × 8 cm, in
volume. Bowls were lined with No. 1 Whatman filter paper
to prevent eggs adhering to the sides of the plastic bowl and
drying out. Each bowl was housed in an environmental
chamber at a constant temperature. Hatched larvae were
counted and removed daily until no further instars were
seen. This procedure was repeated four times for each set
temperature (five in total).
Larva and pupa development
Thirty, 2-day-old larvae from each egg tray were
dispensed into larval bowls containing 1 l of tap water and
100 ml of rearing medium. Larval bowls were the same as
the egg bowls, but without filter paper. Rearing medium
was produced by placing five whole grass plants (Festuca
spp.) with soil attached to the roots in 4 l of tap water for
48 h. Bacteria produced from the grass served as starting
food for the first instar larvae. Feeding with solid food
commenced 24 h after the hatched larvae were placed in the
rearing medium. About 10 mg of tropical fish food
(Tetramin
®
, Germany), ground into a fine powder, was
provided for each larval bowl daily. Dead larvae or pupae
were removed each day and the rearing medium replaced
every two days to prevent scum formation and the
accumulation of metabolites toxic to the insects. Larvae were
counted daily and categorized according to instar stages
(WHO, 1975).
Statistical analysis
Development time was recorded as the duration of
development of 50% of individuals for the immature stages,
and as mean emergence times for adults, in days. The rate of
development was described as the sum of the inverse of the
development times for each individual expressed as an
average. The Jonckheere-Terpstra and the Kruskal-Wallis
non-parametric tests in SPSS (Version 10.0 for Windows,
SPSS Inc., Chicago) statistical package were used,
respectively, to compare between group (temperature
regimes) and within group differences in mean development
times, while Chi-square statistics was used to compare the
number of adults produced. For between-group
comparisons, the null hypothesis that the distribution of
development times does not differ among the temperature
levels was tested against the alternative that as the
376 M.N. Bayoh and S.W. Lindsay
temperature increases, the magnitude of the response
increases. Because the alternative hypothesis is ordered, the
Jonckheere-Terpstra is more appropriate than the Kruskal-
Wallis test. The software TableCurve
®
2D version 4.0 for
Windows was used to fit curves to the data for overall
development rate and temperature and for rates of the instar
stages and temperature. SigmaPlot 2001 software was used
to produce three-dimensional surfaces describing adult
emergence times and the number of adults emerging at the
different temperatures.
Mapping
An environmental database for Africa, the spatial charac-
terization tool (SCT) (Corbett & O‘Brien, 1997), operating
within a geographical information system (GIS, arc/info
Version 7.2; ESRI, Redlands, California), was used to
generate mosquito suitability maps for Africa using data
produced from this study.
Results
There were no significant differences, at the 5% level, in
adult emergence times and number of adults of A. gambiae
produced at the different replicates within each temperature
regime, thus all five replicates were combined for further
analysis. Mean emergence times as well as proportions
developing into adults differed between temperature
regimes (Jonckheere-Terpstra Test Statistic = 22104.5 and Chi
square test statistic = 94.4 respectively, P < 0.001 in both
cases). The mean duration from egg to adult and the
percentage of adults produced at the various constant
temperatures are shown in table 1. Less than 50% of pupae
developed into adults at 30 and 32°C, with most deaths
(> 80%) occurring at pupation. The proportion of larvae
becoming adults was similar between 20 and 28°C (χ
2
= 2.81,
ns).
Overall, the rate of development increased at higher
temperatures for each immature stage. However, as the life
stages advanced, the lower temperature threshold for
development increased while the upper temperature
Temperature and larval development of A. gambiae 377
0
5
10
15
20
25
10 16 22 28 34
Temperature (°C)
Development time (days)
0
5
10
15
20
25
10 16 22 28 34 40
Temperature (°C)
Development time (days)
Fig. 1. Development times of the aquatic stages of Anopheles
gambiae s.s. at different temperatures.
, Egg; –, first instar;
,
second instar;
, third instar; , fourth instar;
, pupa.
Fig. 2. Development times of the aquatic stages of Anopheles
gambiae s.s. at different temperatures based on the equation D =
a+b/(1+(t/c)
d
).
, Egg; –, first instar;
, second instar;
, third
instar; , fourth instar;
, pupa.
Table 1. Development time of Anopheles gambiae s.s. and proportion of adults
produced at different constant temperatures.
Temperature
Time to adult (days) No. adults produced
(°C) Mean (± 95% CI) H P % χ
2
P
16 None None
18 23.3 (22.2–23.5) 1.427 0.839 42.0 1.841 0.765
20 20.4 (19.5–20.2) 7.139 0.129 70.0 8.476 0.076
22 17.5 (16.7–17.6) 4.571 0.334 76.0 1.175 0.882
24 13.5 (13.6–14.3) 3.592 0.464 78.7 2.424 0.658
26 11.5 (11.2–11.9) 5.817 0.213 72.7 0.128 0.998
28 9.8 (9.4–10.0) 4.858 0.302 66.0 7.010 0.135
30 10.0 (9.8–10.5) 5.918 0.205 27.3 1.073 0.899
32 10.2 (10.0–10.4) 2.274 0.685 34.7 4.538 0.338
34 None None
Overall 22104.5 <0.001 94.418 <0.001
H = Kruskal-Wallis Test Statistics, n = 5 for each temperature; for overall time to adult
data Jonckheere-Terpstra Test Statistic reported n = 8 for all temperatures; CI =
confidence interval.
threshold decreased (fig. 1). Adults emerged only between
16 and 34°C. There was no development of first instar larvae
at 10, 12 and 40
o
C. Larval development at 14 and 38°C
ceased at the second instar stage with immediate death at
38°C but prolonged life at 14°C. Similarly, development at 16
and 34° ceased at the fourth stage with prolonged duration
of life at 16°C.
Smooth curves were fitted along data points for
development times of each stage across the temperatures
(fig. 2) and all fitted the expression
D = a + b/(1 + (t/c)
d
)
where D = development time, t = temperature, and a, b, c
and d are coefficients for the fit which differ for each
immature stage and are presented in table 2.
Optimal temperatures for adult development ranged
from 28 to 32°C and for adult production from 22 to 26°C.
The peaks for development and adult production relative to
temperature were out of phase (fig. 3).
The relationship between overall development rate (R)
and temperature (t) is best described by the non-linear
expression
R = a + bt + ce
t
+ de-
t
where a = 0.050, b = 0.005, c = 2.139E-16, d = 281357.656
(goodness of fit, r
2
= 0.99 and F = 243.2).
A linear degree-day model was obtained by substituting
for temperature in the equation suggested by Craig and
others (Craig et al., 1999) and overlaid with predicted rates
from this study (fig. 4). There was a close resemblance
between the two models over the projected linear area
depicted by our model, except at temperature extremes.
The relationship between temperature, adult emergence
times and number of larvae surviving to adults was displayed
on a 3D surface (fig. 5). The period of adult emergence was
narrow for all temperatures while the number of adults
emerging peaked at the moderate temperatures.
378 M.N. Bayoh and S.W. Lindsay
Stages a b c d r
2
Fit SE F-value
Egg 48.549 970.200 12.096 4.839 0.98 16.623 135.876
First instar 131.322 988.156 14.134 5.425 0.97 28.816 114.707
Second instar 210.666 7430.194 9.402 4.658 0.97 35.324 82.633
Third instar 317.494 56199.178 7.038 5.174 0.98 43.781 96.438
Fourth instar 390.236 662.094 20.742 8.946 0.99 17.054 278.261
Pupa 410.863 991.391 19.759 6.827 0.99 22.046 234.515
Table 2. Coefficients of the curve fit D = a + b/(1 + (t/c)
d
), which describes the
relationship between temperature and the stage specific development times of
Anopheles gambiae s.s. immature stages.
0
0.02
0.04
0.06
0.08
0.10
0.12
16 20 24 28 32
Temperature (°C)
Development rate (days
–1
)
0
20
40
60
80
100
Adults (%)
0
0.04
0.08
0.12
0.16
0.20
12 18 24 30 36 42
Temperature °C
Development rate (days
–1
)
Temperature (°C)
Time (days)
No. adults
40
30
20
10
0
5
10
15
20
25
30
18
20
22
24
26
28
30
Fig. 3. Development rate of Anopheles gambiae s.s. ( ) and
percentage developing to adults (
) at different tempera-
tures.
Fig. 4. Comparison of a linear degree-day model (
) of
relationship between temperature and development rate of
Anopheles gambiae mosquitoes (Craig et al., 1999) with the non-
linear model produced from this study (
).
Fig. 5. A three-dimensional view of the influence of temperature
on adult Anopheles gambiae s.s. emergence times and numbers
produced.
The climate suitability map for A. gambiae s.s. was based
on areas in Africa where the mean temperature ranged from
a minimum of 15°C to a maximum of 35°C and rainfall was
higher than 350 mm during the wettest five months of the
year. Since the sensitivity of the growth chambers was ±1°C,
the temperature range for larval development was adjusted
to include this factor. Thus 15°C was used as the lower limit
and 35°C for the upper limit, rather than the 16 and 34°C
thresholds determined directly from the present
experiments. The rainfall criteria employed were based on
suggestions for stable malaria made by Craig and others,
that 80 mm rain for five months was sufficient but 60 mm
rain for five months was not (Craig et al., 1999). It was
assumed that the amount of rainfall needed for malaria fell
between these two values and took the average value of
350 mm was taken for the five wettest months of the year.
The map generated by the temperature requirements for A.
gambiae s.s. larval development where rainfall is not limiting,
approximately highlighted the areas known for stable
malaria and was very similar to the MARA/ARMA malaria
distribution map (fig. 6).
Discussion
The development of the aquatic stages of A. gambiae s.s.
increases with temperature between a lower and upper
threshold. The overall relationship between development
rate and temperature is non-linear and is made up of three
parts. Firstly, there is a non-linear increase in development
rate from zero development at a low temperature threshold,
in this case 16°C. Secondly, there is a temperature where the
rate begins to increase proportionally with temperature,
between 22 and 28°C. Finally, after the optimum
temperature is approached there is a rapid non-linear
decline to no development at an upper lethal temperature, in
this instance, 34°C. This trend has also been reported for
other insects (Logan et al., 1976; Briere & Pracros, 1998;
Petavy et al., 2001). The difference between the widely used
linear model of development versus time and the
polynomials used in this study was apparent when the
curves were superimposed. There is no upper bound for
development in the linear model but in the non-linear
polynomials upper and lower limits were imposed,
reflecting better the relationship between temperature and
development in which such continuous extreme
temperatures would not naturally support life.
Despite the fact that the duration of larval development
reduced with increased temperature, care must be taken
when incorporating these relationships in malaria
transmission models. As shown by this work, the
proportion of larvae that develop into adults reduced at
higher temperatures. Holometabolous insects, such as
mosquitoes, must attain a certain critical mass during larval
development before they can pupate (Clements, 1992). The
potential attainable mass decreases with increasing
temperature (Chambers & Klowden, 1990) and at higher
temperatures, when development occurs quickly, many
individuals may not accumulate sufficient mass for
eclosion. At these high temperatures, most fourth instar
larvae died during pupation or pupae failed to emerge into
adults. The physiological explanation for why few adults
emerged is unclear. One possibility could be that when
developing at a rapid rate, the organism may be unable to
keep up with the accompanying nutrient intake,
metabolism or accumulation (Korochkina et al., 1997)
required for the complex physiological process in the
change from fourth instar to pupa (Lassiter et al., 1995), and
as a result fails to develop. In field situations, such
physiological activities may well occur when temperatures
drop later in the day and the adults emerge in the early
evening (Shute, 1956). Inhibition of further development
also occurred at low temperatures, probably because of the
low metabolic rate experienced and the inability of the
aquatic stages to accumulate the required mass for
moulting. When Jalil (1971) placed the four different larval
stages of Aedes triseriatus Say at 6–8°C, he observed that
although they were all active, moulting did not take place.
However, they did moult and complete their development
when returned to 25°C. This indicates that cold
temperatures act as an inhibitor by which larvae are held
back at a moulting barrier. However, larvae exposed to 38°C
did not complete development when they were transferred
Temperature and larval development of A. gambiae 379
Fig. 6. Distribution map for malaria in Africa generated by (a) the temperature restrictions shown by this
study and (b) the MARA/ARMA Project.
to 25°C, implying a possible cumulative injurious effect at
the high temperature which prevents further development.
A cautionary note should also be made to emphasize that
the data reported here refers to just one strain of A. gambiae,
and we cannot exclude the possibility that the impact of
temperature on development may vary between
populations. Such intraspecific variation has been recorded
for some insect species (e.g. Trimble & Lund, 1983; Stacey &
Fellowes, 2002), but not all (Tauber et al., 1987; Mogi, 1992;
Royer et al., 2001).
The present work suggests that development rate-
temperature models alone are not sufficient for estimating
adult production. For instance, though development rates at
30 and 32°C were high, the actual numbers of adults
produced at these temperatures were very low compared to
lower temperatures. Thus, the adult production rate should
be expressed in terms of not only time to adult but also
numbers surviving to adulthood.
The map generated using the temperature ranges for
larval development, and assuming rainfall is not limiting,
compared favourably with maps published using more
sophisticated techniques. This zone map of suitable larval
breeding sites was remarkably similar to the areas in the
MARA/ARMA map depicting stable malaria. The southern
limits coincided with areas of greater than 50% stability
including north-eastern Namibia, northern and eastern
Zimbabwe, Lesotho and northern South Africa including the
east coast. Also, in the distribution maps produced by
Lindsay and others (Lindsay et al., 1998), all regions with a
probability of A. gambiae s.s. greater than 10% fell within the
areas depicted by the larval map. This is evidence that
climate is a first order determinant of the distribution and
abundance of species.
The development of processed-based models for
predicting the future spread or retreat of mosquito vectors
requires not only an understanding of the temperature
dependence of the development and survival of the aquatic
stages, but also an appreciation of how climate affects adult
mosquito survival and reproduction. Such mathematical
models could be developed for measuring future changes in
the distribution of this vector in Africa and identify areas of
the world that could support this vector if it were
accidentally introduced.
Acknowledgements
M.N. Bayoh was supported for this work by a
Commonwealth Scholarship. The authors thank Professor
Ken Bowler and two anonymous referees for their helpful
suggestions and we are also grateful to Ms Barbara Sawyers
and Professor Chris Curtis for providing us with the 16C
strain of Anopheles gambiae sensu stricto.
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© CAB International, 2003
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The Behavioural
Ecology of Parasites
Edited by E E Lewis, Virginia Polytechnic Institute and
State University, J F Campbell, US Department of
Agriculture, Kansas, and M V K Sukhdeo, Rutgers
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ISBN 0 85199 615 9
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... In MGDrivE 3, as in MGDrivE 2, the carrying capacity of the environment for larvae is a function of recent rainfall, and a mathematical relationship from White et al. [31] is used to translate local rainfall data to larval carrying capacity; however, in this example, we capture broad variations in the rainfall profile of São Tomé and Príncipe using the umbrella [30] package in R, using a shapefile of the national administrative boundary and a three-year timeframe for rainfall data (Fig 2). Otherwise, the life history module mirrors that of MGDrivE 2, including mean-variance relationships describing development times of the juvenile life stages [36]. For the purpose of this demonstration, and to emphasize the novel epidemiological component of MGDrivE 3, the island of São Tomé was treated as a single randomly mixing population. ...
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Novel mosquito genetic control tools, such as CRISPR-based gene drives, hold great promise in reducing the global burden of vector-borne diseases. As these technologies advance through the research and development pipeline, there is a growing need for modeling frameworks incorporating increasing levels of entomological and epidemiological detail in order to address questions regarding logistics and biosafety. Epidemiological predictions are becoming increasingly relevant to the development of target product profiles and the design of field trials and interventions, while entomological surveillance is becoming increasingly important to regulation and biosafety. We present MGDrivE 3 (Mosquito Gene Drive Explorer 3), a new version of a previously-developed framework, MGDrivE 2, that investigates the spatial population dynamics of mosquito genetic control systems and their epidemiological implications. The new framework incorporates three major developments: i) a decoupled sampling algorithm allowing the vector portion of the MGDrivE framework to be paired with a more detailed epidemiological framework, ii) a version of the Imperial College London malaria transmission model, which incorporates age structure, various forms of immunity, and human and vector interventions, and iii) a surveillance module that tracks mosquitoes captured by traps throughout the simulation. Example MGDrivE 3 simulations are presented demonstrating the application of the framework to a CRISPR-based homing gene drive linked to dual disease-refractory genes and their potential to interrupt local malaria transmission. Simulations are also presented demonstrating surveillance of such a system by a network of mosquito traps. MGDrivE 3 is freely available as an open-source R package on CRAN (https://cran.r-project.org/package=MGDrivE2) (version 2.1.0), and extensive examples and vignettes are provided. We intend the software to aid in understanding of human health impacts and biosafety of mosquito genetic control tools, and continue to iterate per feedback from the genetic control community.
... These could cause upsurge in the transmission or spread of vector-borne disease in temperate regions where vectors are available but parasite development controlled by existing temperature conditions (Martens, 1995). The proliferation of the Anopheline vector is enhanced as temperature rise with optimal larval growth at 28°C and optimal adult growth between 28°C and 32°C (Bayoh and Lindsay, 2003). ...
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... The first is defined as T w and accounts for the suitable heat accumulation for the development and is calculated as the cumulative degree-days in the 14 days before the sampling event setting with the lower thermal threshold at 18 ℃ and the upper thermal threshold at 30 °C. The second variable is defined as T h and accounts for the thermal stress due to high temperature; it is calculated in terms of the cumulated degree-days equal to or above a threshold of 32 ℃ [21]. The meteorological and derived variables used in the study are detailed in Table 1. ...
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... Increasing environmental temperature is, in turn, raising the body temperature of insects, and this phenomenon is more pronounced for species that inhabit the tropics [2][3][4]. This is particularly the case for mosquitoes that transmit disease [5,6]; at higher temperatures the rate of development is faster [7][8][9][10], the metabolic rate is higher [2,11], the body size is smaller [12,13], and the lifespan is shorter [7,9,14]. ...
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... In general, an increase in water temperature will result in faster development of aquatic stages but will reduce the size of emerging adults [27,36]. ...
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... The transmission of malaria is influenced by environmental factors that render it highly responsive to shifts in climate patterns. Research focusing on the ramifications of climate change on malaria transmission underscores that even minor fluctuations in temperature or rainfall can trigger a rapid upsurge in disease propagation [3]. Moreover, rainfall plays a pivotal role in the proliferation of malaria by fostering suitable breeding sites for mosquito larvae and facilitating the expansion of mosquito populations [4]. ...
Article
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In sub-Saharan Africa, temperatures are generally conducive to malaria transmission, and rainfall provides mosquitoes with optimal breeding conditions. The objective of this study is to assess the impact of future climate change on malaria transmission in West Africa using community-based vector-borne disease models, TRIeste (VECTRI). This VECTRI model, based on bias-corrected data from the Phase 6 Coupled Model Intercomparison Project (CMIP6), was used to simulate malaria parameters, such as the entomological inoculation rate (EIR). Due to the lack of data on confirmed malaria cases throughout West Africa, we first validated the forced VECTRI model with CMIP6 data in Senegal. This comparative study between observed malaria data from the National Malaria Control Program in Senegal (Programme National de Lutte contre le Paludisme, PNLP, PNLP) and malaria simulation data with the VECTRI (EIR) model has shown the ability of the biological model to simulate malaria transmission in Senegal. We then used the VECTRI model to reproduce the historical characteristics of malaria in West Africa and quantify the projected changes with two Shared Socio-economic Pathways (SSPs). The method adopted consists of first studying the climate in West Africa for a historical period (1950–2014), then evaluating the performance of VECTRI to simulate malaria over the same period (1950–2014), and finally studying the impact of projected climate change on malaria in a future period (2015–2100) according to the ssp245 ssp585 scenario. The results showed that low-latitude (southern) regions with abundant rainfall are the areas most affected by malaria transmission. Two transmission peaks are observed in June and October, with a period of high transmission extending from May to November. In contrast to regions with high latitudes in the north, semi-arid zones experience a relatively brief transmission period that occurs between August, September, and October, with the peak observed in September. Regarding projections based on the ssp585 scenario, the results indicate that, in general, malaria prevalence will gradually decrease in West Africa in the distant future. But the period of high transmission will tend to expand in the future. In addition, the shift of malaria prevalence from already affected areas to more suitable areas due to climate change is observed. Similar results were also observed with the ssp245 scenario regarding the projection of malaria prevalence. In contrast, the ssp245 scenario predicts an increase in malaria prevalence in the distant future, while the ssp585 scenario predicts a decrease. These findings are valuable for decision makers in developing public health initiatives in West Africa to mitigate the impact of this disease in the region in the context of climate change. Keywords: climate change; malaria; VECTRI; West Africa; bias-corrected CMIP6
... As a result, temperature changes can significantly influence disease transmission, mosquito lifespan, and vectorial competence [37,45]. Additionally, temperature sensitivity varies throughout mosquito stages, with the juvenile stage's dependency significantly impacting adult recruitment and abundance while resulting in nonlinear population responses [46][47][48]. Since only 1-10% of mosquito larvae make it to the adult stage [49], tackling the larval stage presents a viable way of controlling mosquito population dynamics. ...
Chapter
The impacts of climate change are increasingly evident, with unpredictable weather events and changing ecological conditions creating favorable environments for disease-carrying vectors such as mosquitoes and ticks. This chapter delves into the importance of surveillance strategies in monitoring the spread of vector-borne diseases as a measure of resilience. By synthesizing current knowledge, the chapter explores key aspects of surveillance, including the monitoring of human cases, the identification of pathogen species, the distribution and behavior of vectors, and the influence of climatic and environmental factors. It also examines the effectiveness of control measures in mitigating the spread of these diseases. Additionally, the chapter considers the social and economic impact of vector-borne diseases, highlighting the need for proactive surveillance and response systems. By understanding these factors, the chapter provides valuable insights into the development of resilient healthcare infrastructure. Conceptual frameworks are presented to guide the design and modeling of surveillance systems, helping policymakers and healthcare professionals develop effective strategies to mitigate the impact of vector-borne diseases and enhance community resilience. Overall, this chapter emphasizes the importance of surveillance as a fundamental component of disease management and resilience-building efforts in the face of climate change.
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Chrysopa oculata (Neuroptera) from 5 widespread localities (S Canada to montane Mexico) exhibited remarkable similarities in their thermal requirements for nondiapause development. Lower thermal thresholds varied by only 1.2oC, and the degree-days required for total preimaginal development differed among the populations by approx 85od. Despite the similarities among populations, results suggest that the thermal requirements for development are genetically variable. However, 2 factors may limit the geographical expression of this variation: 1) the multivoltine life cycle could result in seasonal oscillations in the magnitude and projection of directional selection on the non-diapuase thermal responses, and/or 2) the thermal thresholds for development and the rates of development above the thresholds may be functionally correlated and constrained in their evolution. Males from all populations emerged slightly but consistently earlier than females. Temperature did not affect sex ratio or survival, other than at 15.6oC where mortality was significantly increased.-from Authors
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The relationship between temperature and stem elongation has been investigated for representative herbaceous plants sampled from populations of seven species which were growing under semi-natural conditions in the Botanical Garden of the University of Padua (Italy). The growth of the floral stem was measured for the following species: Galanthus nivalis L., Corydalis cava Schw. et Krt., Anemone nemorosa l., Symphytum tuberosum L., Symphytum tuberosum L., Allium ursinum L., Aegopodium podagraria L., and Campanula rapunculoides L. Official records of daily maximum and minimum air temperatures have been elaborated by means of a new method of temperature summation. This method takes into consideration the concept that plants possess a range of sensitivity to temperature between maximum and minimum thresholds and that there is an optimal temperature for each stage of development. Data for stem elongation have been optimized (using the technique of best fit) as a function of a logistic curve which may represent growth under ideal conditions. Differences between the logistic curve and the real curve of growth may be related to the amount of deviation of values for environmental factors form optimal values. The temperature ranges between 0@? C and 30@? C which gave the best correlations with stem elongation have been calculated for the entire period of this process of growth. The average between the two thresholds on each day has been considered as the optimum mean temperature for that day. The optimum mean temperature increases from the start of the process to ripening, with the exception of a period just before flowering when all plants seem to require lower daily temperatures. The results of this analysis have also indicated that unknown factors other than temperature are affecting stem elongation.
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Linear regression analysis was used to estimate the developmental threshold, t 0, and thermal constant, K, for all preadult stages of two laboratory colonies of the mosquito Toxorhynchites rutilus septentrionalis (Dyar and Knab). The colonies originated from Newark, Delaware and Lake Charles, Louisiana. The physiological and ecological significance of the within- and the between-population differences in the slopes of the regressions,t 0's and K's, are discussed.
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Development time decreased with each increase in rearing temperature in Aedes vexans, A. nigromaculis, and Culiseta inornata until the optimum survival temperature was reached. The optimum survival temperature for A. vexans was 26.5 °C, for A. nigromaculis 21 °C, and for C. inornata 21 °C. Dry weight gain per hour in female larvae was greater than in male larvae in all three species, at all temperatures. There was a significant reduction in weight in each larval instar, pupal, and adult stage, with each 5.5 °C increase in rearing temperature. Times to larval–pupal ecdysis and pupal–adult ecdysis were the same for males and females of A. nigromaculis at all developmental temperatures tested. Time to larval–pupal ecdysis and pupal–adult ecdysis in A. vexans and C. inornata occurred 1 to several days later in females, depending upon the developmental temperature. In all three species the duration of the fourth instar was longest and the specific weight gain greatest.
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Effects of temperature on egg, larval, and pupal developmental times of the grape berry moth, Lobesia botrana Dennis & Schiffermüller, were examined at several constant temperatures ranging from 8 to 34°C by 2°C increments, with a relative humidity of 65% and a photoperiod of 16:8 (L:D) h. Optimal temperatures for development ranged from 28 to 30°C. The lower and upper limits occurred between 8 and 12°C and between 32 and 34°C, respectively. The experimental conditions covering the complete temperature range for each stage allowed us to apply the data to 5 published equations describing the effect of constant temperatures on developmental rates of various insects. Criteria of choice from the literature were used to evaluate models and to select the most suitable equation for each developmental stage of L. botrana.
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Cone screen traps baited with cruciferous material were used in conjunction with thermal-unit accumulations to distinguish generations of Hylemya brassicae (Bouché), adults in the field. The emergence pattern from overwintering puparia was reflected in succeeding generations. In 5 years, the air thermal-unit accumulations (day-degrees) for the spring emergence of flies varied from 290 to 365 (with a developmental zero of 43°F) depending on weather and soil variations. Later generations required a mean accumulation of 1176 thermal units. Using this information, it is estimated that predictions of cabbage maggot adult emergences could be made as an aid to the timing of foliar sprays.
Article
Lygus bugs, Lygus hesperus Knight and L. elisus Van Duzee, are major pests of cotton in the San Joaquin Valley, California. A simple method of heat accumulation is described which utilizes only daily maximum and minimum temperatures. The procedure is used to predict the time when 50-70% of the lygus bug nymph population in safflower is in the 3rd-5th stages. This critical stage is reached upon accumulating ca. 16,000 degree days, beginning Apr. 1 and using 52°F (11.1°C) as a developmental threshold. This enables growers to apply a single areawide insecticide treatment to their safflower fields before the Lygus begin to disperse to other crops. This treatment largely eliminates the Lygus threat to cotton on the west side of the San Joaquin Valley.