Open Access
How to translate text using browser tools
1 June 2012 Effect of Climate Change on Longevity and Reproduction of Sipha flava (Hemiptera: Aphididae)
Alexander Machado Auad, Marcy G. Fonseca, Tiago T. Resende, Ítalo S. C. P. Maddalena
Author Affiliations +
Abstract

This study examined effects of elevated CO2 alone and in combination with elevated temperature on plant-aphid interactions. CO2 levels in which the host plants were grown affected the durations of some nymphal stadia, but not the survivorship within each instar or of all nymphal instarS. Sipha flava (Forbes) (Hemiptera: Aphididae) adults kept under a constant high CO2 environment (500 ppm) and fed on plants grown under fluctuating CO2 levels (avg. 440 ppm) in a greenhouse had significantly greater longevity and greater reproduction than aphids fed on plants grown either under a constant high CO2 level (500 ppm) or under fluctuating CO2 levels (avg. 368 ppm). Nevertheless, no significant differences were observed in these biological parameters of S. flava that were kept individually in a greenhouse, regardless of the CO2 and temperatures under which the plants used to feed them were grown. However, populations of aphids kept and fed on plants grown in the greenhouse produced significantly more nymphs and adults than did those fed plants grown in a climate-controlled chamber under a constant high CO2 level (500 ppm). The combination of elevated CO2 and high temperature significantly decreased the duration of nymphal stadia, the longevity and reproductive success of S. flava but not nymphal survival. Adults produced fewer nymphs in an environment with elevated CO2 and high temperature than an environment with elevated CO2 and lower fluctuating temperatures. Based on these results, we concluded that S. flava populations will significantly decrease under future climatic conditions when both the concentration of atmospheric CO2 and temperature are projected to increase.

The yellow sugarcane aphid, first named Chaitophorus flavus Forbes, but later Sipha flava (Forbes) (Hemiptera: Aphididae) (Davis 1909), is yellow, 1.3–2.0 mm long, and has numerous long bristle-like hairs with dusky transverse markings on the dorsum (Blackman & Eastop 2000). Sipha flava has an extensive geographic range that includes all the Americas and Hawaii (Medina-Gaud et al. 1965; Kindler & Dalrymple 1999; Blackman & Eastop 2000). Sipha flava is not only a serious pest of sugarcane (Saccharum spp.; Poales: Poaceae) , but it infests corn, sorghum, wheat, and several other grasses (Webster 1990; Hentz & Nuessly 2004; Oliveira et al. 2010). Plant injury caused by this aphid is often severe and is associated with the release of an unidentified toxin followed by leaf chlorosis (Breen & Teetes 1986; Webster 1990).

In Brazil, elephant grass, Pennisetum purpureum (Schumach); Poales: Poaceae, is one of the most widely used grasses for dairy cattle forage, and is noted for high productivity and quality of forage (Xavier et al. 2001). However, production of this forage grass is being compromised by S. flava attack. Thus, studies on effects of S. flava on forage grasses such as P. purpureum are needed to develop effective management programs for the pest. Oliveira et al. (2009) evaluated effects of different temperatures on the development, survival, reproduction, life expectancy, and fertility tables of S. flava feeding on P. purpureum, and concluded that temperatures between 20 °C and 24 °C are most suitable for S. flava development and reproduction. Furthermore, this temperature range is appropriate for the insect to reach pest status in elephant grass. Increasing temperatures will directly affect development, survival, and abundance of aphids (Oliveira et al. 2009; Auad et al. 2009), and both elevated CO2 and increased temperatures affect insect herbivores indirectly by influencing host plant physiology and phytochemistry (Flynn et al. 2006).

By 2100 the world is projected to experience an approximate doubling of atmospheric CO2 concentrations to around 700 ppm accompanied by a 1.4–5.8 °C rise in mean global temperatures (Houghton et al. 2001), and CO2 concentrations may reach 770 ppm (IPCC 2007). These climatic changes would greatly alter relationships between plants and insects in areas of important agricultural production and elsewhere (Theurillat & Guisan 2001).

The effects of such elevated CO2 levels on plants, in turn, have been shown to affect the biology of herbivorous insects (Chen et al. 2005, 2007; Wu et al. 2006). Direct and indirect effects of elevated CO2 on herbivores should therefore be studied to better understand interactions between host plants and phytophagous insects under the CO2-enriched environments expected in the future (Yin et al. 2010).

Given the potentially large effect of S. flava on P. purpureum (Oliveira et al. 2010), it is important to understand how global climatic changes influences this aphid's ecology, and to determine whether future elevated CO2 levels and temperatures could enhance the destructiveness of this pest. To our knowledge, there has been no previous investigation on the effects of global climatic changes on this pest. Hence, we investigated effects of elevated CO2 alone and in combination with elevated temperature on the interactions of S. flava and one of its hosts, P. purpureum.

MATERIALS AND METHODS

Aphids

The Sipha flava aphids used in all experiments were obtained from a colony maintained in a greenhouse at the EMBRAPA Dairy Cattle Research Station, Juiz de Fora, Minas Gerais, Brazil. Adults were transferred to petri dishes (8.5 cm × 2 cm) containing one foliar disc of P. purpureum (8.5 cm diam) placed on a 1.0 cm-thick layer of 1% agar in order to keep the leaf disc turgid. Each petri dish was covered with organza secured with rubber bands, and it was maintained in a chamber at 25 ±1 °C, 70 ±10% RH and 14:10 h L:D to facilitate aphid reproduction.

To study the biology of S. flava individuals, the nymphs were ≤s24 h old and collected from these petri dishes with a fine-tipped paint brush. In each test the individual nymph was kept alone in a plastic container (2.5 × 2.5 cm) containing a foliar disc of P. purpureum placed on a layer of 1% agar, and the plastic container were covered with organza secured with a rubber band. The foliar disc was changed each 48 h to avoid degradation as a food resource. This technique was used because Oliveira et al. (2009) had successfully used it to study the biology of S. flava. To study S. flava population performance, 10 nymphs were placed on each P. purpureum plant (50 cm high) maintained in plastic cages (20 cm diam × 60 cm high) closed with a voile lid secured with a rubber band. In the present study, foliar discs and plants were obtained from environments with different CO2 levels, either constant or fluctuating.

Plant Growth Conditions

The host plant in all tests was P. purpureum, ‘Cameron de Piracicaba’, because this genotype is very suitable for the development of S. flava (Oliveira et al. 2010). P. purpureum cuttings were each planted in a 1.0-L pot with a plant growth substrate of soil/manure at the ratio 2:1 and kept in the following 3 growth environments: 1) a greenhouse (avg. 440 ppm; min 384 ppm and max 924 ppm of CO2), 2) a climate-controlled chamber with an almost constant CO2 level, i.e., a range of 500–550 ppm; henceforth referred to as 500 ppm, and 3) climate-controlled chamber with fluctuating CO2 levels (avg. 368 ppm; min 163 ppm and max 832 ppm of CO2). Each climatecontrolled growth chamber (2.5 × 2.20 × 2.80 m) was maintained at 25 ± 2 °C during the day, 20 ± 2 °C at night, 70 ± 10% RH and 14:10 h L:D. Conditions in the climate-controlled chamber with fluctuating CO2 levels and in the greenhouse were recorded with a HOBO U12 Temperature/ Relative Humidity/Light/External Data Logger - U12-012 (Onset Co., Pocasset, Massachusetts, USA). Conditions in the constant CO2 chamber were maintained with an automatic monitoring system, COEL HW 4200 (Manaus - Amazonas, Brazil) and an injection system using a CO2 cylinder to maintain the desired CO2 concentration. Fluctuating CO2 levels were recorded with a data logger every 2 min and the data were transferred to a computer using HOBOware® software (Onset Co., Pocasset, Massachusetts, USA). Thus we were able to maintain the desired CO2 concentration (avg. 368 ppm) during the experimental period. All plants were 74 d old when foliar discs were explanted. Despite the similar CO2 concentrations in the greenhouse and in the climate chambers, other abiotic factors fluctuated in the greenhouse (temperature 18 ± 5 °C and RH 74 ± 10 %), but these were kept almost constant in the climate-controlled chambers.

The CO2 concentrations used for the treatments with constant CO2 levels were selected based on predicted CO2 levels for the year 2100 by the Intergovernmental Panel on Climate Change (IPCC 2007), and treatments with fluctuating CO2 levels were selected according to those recorded in the greenhouse.

Experiments

In all the experiments, both plants and insects were contained either in a greenhouse with fluctuating CO2 concentrations, or in climate-controlled chambers either with relatively constant or variable CO2 concentrations. Insects in a climatecontrolled chamber were fed forage grown in the greenhouse, while insects in the greenhouse were fed on plants grown in a climate-controlled chamber with relatively constant CO2.

Experiment 1: Effects of Different CO2 Regimes on Sipha flava Individuals.

Experiment 1 had 2 parts. In Part I,3 treatments were applied with 50 individual nymphs per treatment. In Treatment #1 nymphs and forage grass were maintained in a climate-controlled chamber under a constant high CO2 level (500 ppm). In Treatment #2 both nymphs and forage grass were maintained in a climate-controlled chamber with fluctuating CO2 levels (avg. 368 ppm). In Treatment #3 nymphs were kept under a climate-controlled chamber at a constant high CO2 level (500 ppm), but were fed forage grass grown in the greenhouse with fluctuating CO2 levels (avg. 440 ppm).

In Part II, 2 treatments were applied with 50 individual nymphs per treatment. In Treatment #1 nymphs and forage grass plants were maintained in a greenhouse under fluctuating CO2 levels (avg. 440 ppm). In Treatment #2 nymphs were also maintained in a greenhouse under fluctuating CO2 levels (avg. 440 ppm), and fed on P. purpureum derived from a climate-controlled chamber under a constant high CO2 level (500 ppm).

The following parameters were evaluated and recorded daily for Experiment 1: the duration (days) of each nymphal stadium, percent survival of each nymphal instar, and the longevity (days) and reproductive capacity of adults.

Experiment 2: Effects of Different CO2 Regimes on Sipha flava Populations

Experiment 2 also had 2 parts, with each treatment the same as in Experiment 1. There were 20 replications per treatment, and each treatment within a replication involved 10 nymphs per plant. After 30 days, numbers of nymphs and adults were recorded. This 30 day-period was sufficient for approximately 4 generations to occur, according to Oliveira et al. (2009).

Experiment 3: Effects of Elevated CO2 and Temperature on Sipha flava

This experiment was conducted with a constant high CO2 level (500 ppm) in both treatments, moderate diurnally fluctuating temperatures in one treatment, and an elevated constant temperature in second treatment. The objective was to determine the effects of these conditions on the development, reproduction and longevity of S. flava. For each treatment, 50 S. flava individual nymphs were each kept in a plastic container (2.5 × 2.5 cm) containing a foliar disc of P. purpureum placed on a 1% agar layer, and the plastic container was covered with organza secured with a rubber band. Foliar discs were explanted from plants grown in a greenhouse with fluctuating CO2 levels (avg. 440 ppm), and the insects were maintained in a controlled-climate chamber with a constant high CO2 level (500 ppm), 28 ± 2 °C, 70% ± 10% RH, and 14:10 h L:D. Data from this experiment were compared to data from Treatment 3 of Experiment 1 (a constant high CO2 level (500 ppm), 25 ± 2 °C (day), and 20 ± 2 °C (night)). The following parameters were evaluated and recorded daily: duration of each nymphal stadium and of the entire nymphal phase, percent survival of each nymphal instar and of all nymphal instars, and longevity and reproductive capacity of the adults.

Statistical Analyses

The effects of CO2 on the performances of S. flava individuals (Experiment 1) and S. flava populations (Experiment 2) when insects and/ or plants were provided conditions in which only CO2 concentration varied (climate-controlled chambers) or in which all abiotic factors varied (greenhouse), and effects of elevated temperature on individual performance of S. flava under elevated CO2 levels (Experiment 3) were evaluated. In each experiment the data were subjected to an analysis of variance (ANOVA), and the means were compared with Tukey's test using Sisvar 5.1 software (Lavras, Minas Gerais, Brazil).

RESULTS

Experiment 1: Effects of Different CO2 Regimes on Sipha flava Individuals.

In experiment 1 Part I (Table 1), when nymphs and the plants were held under a constant high CO2 level (500 ppm) (Treatment 1), the duration of the third instar nymphs' development was prolonged compared to Treatment 2 (both nymphs and plants kept under fluctuating CO2 levels (avg. 368 ppm)), and Treatment 3 (nymphs under a constant high CO2 level (500 ppm), and plants under fluctuating CO2 levels (avg. 440 ppm)). However the stadia of the second and fourth instars were not significantly different between the treatments. When both first instar nymphs and plants were kept under fluctuating CO2 levels (avg. 368 ppm) (Treatment 2), the duration of the N1 stadium was shorter than when nymphs were kept under a constant high CO2 level (500 ppm) were fed on plants kept under fluctuating CO2 levels (avg. 440 ppm) (Treatment 3). Also when both nymphs and plants were kept under fluctuating CO2 levels (avg. 368 ppm) (Treatment 2), the duration of total period of nymphal development was shorter than that of nymphs fed on plants under a constant high CO2 level (500 ppm) (Treatment 1), or fed on plants under fluctuating CO2 levels (avg. 440 ppm) (Treatment 3). No significant differences occurred in the percent survival of nymphs in all 3 treatments (Table 1).

TABLE 1.

EXPERIMENT 1, PART I: DURATION OF EACH SIPHA FLAVA NYMPHAL STADIUM AND SURVIVAL OF EACH NYMPHAL INSTAR WHEN (1) NYMPHS AND FORAGE GRASS WERE MAINTAINED IN A CLIMATE-CONTROLLED CHAMBER WITH CONSTANT 500 PPM CO2 (TREATMENT 1); (2) NYMPHS AND FORAGE GRASS WERE MAINTAINED IN A CLIMATE-CONTROLLED CHAMBER WITH FLUCTUATING CO2 LEVELS - AVG. 368 PPM (TREATMENT 2), AND (3) NYMPHS WERE MAINTAINED IN A CLIMATE-CONTROLLED CHAMBER WITH CONSTANT 500 PPM CO2, BUT FED FORAGE GRASS GROWN IN A GREENHOUSE WITH FLUCTUATING CO2 LEVELS - AVG. 440 PPM (TREATMENT 3).

t01_433.gif

Aphids kept under a constant high CO2 level (500 ppm) environment (Fig. 1) and fed on plants from an environment with fluctuating CO2 levels (avg. 440 ppm) (Treatment #3) lived significantly longer and displayed a significantly greater reproductive capacity than aphids in a constant high CO2 level (500 ppm) environment and fed on plants also grown under a constant high CO2 level (500 ppm) environment (Treatment #1), as well as significantly longer than insects kept along with their food plants in an environment with fluctuating CO2 levels (avg. 368 ppm) (Treatment #2) (F = 26. 19; P = 0.0000). Hence, the results show that aphids fed on plants derived from a constant high CO2 level (500 ppm) environment and fluctuating CO2 levels (avg. 368 ppm) environment produced about half as many progeny as did the aphids kept in a constant high CO2 level (500 ppm) environment and fed on plants grown with fluctuating CO2 levels (avg. 440 ppm) (F = 42.48; P = 0.0000) (Fig. 1).

Fig. 1.

Effects of forage grown either under a constant high (500 ppm) CO2 level, or under lower but fluctuating CO2 levels on longevity (days) and reproductive capacity (number of nymphs) of Sipha flava held under the same CO2 regimes. Treatment 1: Both S. flava and forage grass were maintained in a climate-controlled chamber with constant high 500 ppm CO2 level. Treatment 2: Both S. flava and forage grass were maintained in a climatecontrolled chamber with fluctuating CO2 levels - avg. 368 ppm. Treatment 3: S. flava were maintained in a climatecontrolled chamber with constant 500 ppm of CO2, but the forage grass fed to them was grown in a greenhouse with fluctuating CO2 levels - avg. 440 ppm. Mean longevity values followed by different lower case letters were significantly different, as were mean values for reproductive capacity followed by different upper case letters based on ANOVA followed by the Tukey test.

f01_433.jpg

In Experiment 1, Part II (Table 2), the duration of the second nymphal stadium was significantly shorter when the aphids were kept under fluctuating CO2 levels (avg. 440 ppm) and fed on plants derived from a constant high CO2 level (500 ppm) environment (Treatment #2) than when both the aphids and their food plants were kept under fluctuating CO2 levels (avg. 440 ppm, Treatment 1). However, durations of the first, third and fourth instars, the overall nymphal period, and the survival of S. flava were not significantly affected regardless of the environment in which the plants were grown (Table 2). Moreover, no significant differences in longevity (F = 0.54; P = 0.463) or reproductive capacity (F = 2.95; P = 0.089) of S. flava occurred when the aphids were kept under fluctuating CO2 levels (avg. 440 ppm) regardless of the environment in which plants consumed by the insects were grown (Fig. 2).

Experiment 2: Effects of Different CO2 Regimes on Sipha flava Populations

The aphids kept under a constant high CO2 level (500 ppm) and fed on plants grown under fluctuating CO2 levels (avg. 440 ppm) (Treatment 3) produced significantly more nymphs (F = 5.23; P = 0.008) (Fig. 3A) and adults (F = 5.55; P = 0.006) (Fig. 3B) than did aphids kept together with their host plants under a constant high CO2 level (500 ppm) (Treatment 1), or when both aphids and host plants were kept under fluctuating CO2 levels (avg. 368 ppm) (Treatment 2).

Also aphids kept in the greenhouse and fed on plants grown in the greenhouse under fluctuating CO2 levels (avg. 440 ppm) produced significantly more nymphs (F = 10.78; P = 0.002) (Fig. 4A) and adults (F = 4.89; P = 0.03) (Fig. 4B) than did aphids also kept in a greenhouse but fed plants grown under a constant high CO2 level (500 ppm).

Experiment 3: Effects of Elevated CO2 and Temperature on Sipha flava

As shown in Table 3, the combination of a high temperature and a constant high CO2 level (500 ppm) significantly decreased the duration of the overall nymphal period, but not decrease nymphal survival. The durations of all of the nymphal stadia in an environment with a constant high CO2 level (500 ppm) and high temperature (28 ± 1 °C) were shorter than those in an environment with the same CO2 environment but lower diurnally fluctuating temperatures (25 ± 1 °C/20 ± 1 °C, day/night). Moreover, this combination of conditions drastically affected the longevity and reproductive capacity of S. flava (Fig. 5). Aphids exhibited shorter longevity when kept in an environment with elevated CO2 and elevated temperature (28 ± 1 °C) (Treatment 2) than when kept in the same CO2 environment but lower fluctuating temperatures (25 ± 1 °C/20 ± 1 °C, day/night) (Treatment 1) (F = 101.2; P = 0.000) (Fig. 5). These longevity results directly correlated with the reproductive capacity results in that aphids kept under a high CO2 environment (500 ppm) and a high temperature (28 ± 1 °C) produced far fewer nymphs than those kept in an environment with the same CO2 environment but lower diurnally fluctuating temperatures (25 ± 1 °C/20 ± 1°C, day/ night) (F = 135.6; P = 0.000) (Fig. 5).

TABLE 2.

EXPERIMENT 1, PART II: DURATION OF EACH SIPHA FLAVA NYMPHAL STADIUM AND SURVIVAL OF EACH NYMPHAL INSTAR WHEN (1) NYMPHS AND FORAGE GRASS PLANTS WERE MAINTAINED IN A GREENHOUSE WITH FLUCTUATING CO2 LEVELS AVG. OF 440 PPM (TREATMENT 1), AND (2) NYMPHS WERE MAINTAINED IN A GREENHOUSE WITH FLUCTUATING CO2 LEVELS - AVG. OF 440 PPM, BUT FED ON P. PURPUREUM DERIVED FROM A CLIMATE-CONTROLLED CHAMBER WITH CONSTANT 500 PPM CO2 (TREATMENT 2).

t02_433.gif

Fig. 2.

Effects of forage grass grown either under a constant high (500 ppm) CO2 level, or under fluctuating CO2 levels - avg. 440 ppm on longevity (days) and reproductive capacity (number of nymphs) Sipha flava under artificial conditions. Treatment 1: S. flava and forage grass were under fluctuating CO2 levels - avg. 440 ppm (greenhouse). Treatment 2: S. flava were maintained under fluctuating CO2 levels - avg. 440 ppm (greenhouse), but fed forage grass under a constant high (500 ppm) CO2 level (climate-controlled chamber). Mean longevity values followed by the same lower case letters were not significantly different, and neither were mean reproductive capacity values followed by the same upper case letters based on ANOVA and Tukey test.

f02_433.jpg

Fig. 3.

Reproductive performance of Sipha flava kept under constant and fluctuating CO2 environments. A) Upper panel - number of nymphs and B) Lower panel - number of adults. In Treatment 1, both S. flava and forage grass were kept under a constant high CO2 level (500 ppm) (climate-controlled chamber). In Treatment 2, both Sipha flava and forage grass were maintained under fluctuating CO2 levels (avg. 368 ppm) (climate-controlled chamber). In Treatment 3, S. flava were kept under a constant high CO2 level (500 ppm) (climate-controlled chamber), but fed forage grass grown under fluctuating CO2 levels (avg. 440 ppm) (greenhouse). Mean numbers of nymphs followed by the same lower case letter were not significantly different based on ANOVAS and Tukey tests; and likewise for mean numbers of adults.

f03_433.jpg

DISCUSSION

The effects of climate change on animal populations are of critical concern (Fleming & Volney 1995; Thomas et al. 2004). However, researchers are only beginning to investigate how insects respond to such changes (Mondor et al. 2005; Balanyá et al. 2006). Global climate change may alter ecosystem functioning and species interactions by promoting a shift in the geographical range of herbivores (Jepsen et al. 2008), by facilitating the spread new adventive and invasive species (e.g., Crow et al. 2008), and by altering the natural climatic control of herbivorous species (Jepsen et al. 2008).

Our results suggest that effects of elevated CO2 on S. flava mediated through one of its food plants may affect the fitness of this insect pest. We found that aphids kept either in a constant CO2 environment and fed plants grown in a greenhouse (fluctuating CO2 levels) had significantly greater longevity than aphids fed either plants kept under constant (500 ppm) CO2 or in a climate-controlled chamber with a fluctuating CO2 environment with a lower avg. CO2 concentration. However, no significant differences in the longevity or reproductive aspects of S. flava adults kept in a greenhouse were observed, regardless of the environment in which the plants were grown, hence other abiotic factors in the greenhouse such as higher light intensity may favor development of the insect. However, regarding reproduction in S. flava populations, aphids maintained in a greenhouse and fed on plants grown in a greenhouse produced significantly more progeny than did aphids consuming plants grown in a climatecontrolled chamber with constant high (500 ppm) CO2. These results suggest that our artificial CO2 regime changed the physiology of the plants, thereby affecting longevity and fecundity of S. flava feeding on these plants.

Fig. 4.

Effects of forage grown either under a constant high CO2 level (500 ppm), or under fluctuating CO2 levels (avg. 440 ppm) on the reproductive success of Sipha flava held under fluctuating CO2 levels (avg. 440 ppm). A) Upper panel - number of nymphs and B) Lower panel - number of adults. In Treatment 1, both S. fava and forage grass were maintained under fluctuating CO2 levels (avg. 440 ppm) (greenhouse). In Treatment 2, S. flava were maintained under fluctuating CO2 levels (avg. 440 ppm) (greenhouse), but the forage grass was grown under a constant high CO2 level (500 ppm) (climate-controlled chamber). Mean numbers of nymphs followed by the same lower case letter were not significantly different based on ANOVA and Tukey test; and likewise for mean numbers of adults.

f04_433.jpg

Plant tissues changes under altered climatecontrolled conditions affect food quality for herbivores and may in consequence alter the performance of herbivorous insects species (Zvereva & Kozlov 2006; Valkama et al. 2007). An explanation for this effect is that elevated CO2 tends to increase photosynthesis and plant biomass (Will & Ceuleman 1997), while it reduces host plant quality for herbivores because of increased foliar carbon and secondary organic compounds (Zvereva & Kozlov 2006; Stiling & Cornelissen 2007) and decreased availability of nitrogen (Lawler et al. 1997; Norby et al. 1999).

Many studies have investigated alterations in plant responses to elevated CO2 with respect to aphids (Hughes & Bazzaz 2001; Hunter 2001; Stacey & Fellowes 2002; Newman et al. 2003; Chen et al. 2004; Dermody et al. 2008; Mondor et al. 2010; Fu et al. 2010). Elevated CO2 results in larger, more architecturally complex Brassica oleracea L. (Brassicales: Brassicaceae) plants with a higher tissue carbon-to-nitrogen ratio. The aphids, Brevicoryne brassicae (L.) and Myzus persicae (Sulzer) (Aphididae), exhibited different responses to these changeS. Brevicoryne brassicae reared on plants grown in elevated CO2 were larger and accumulated more fat, whereas the corresponding traits of M. persicae do not change (Stacey & Fellowes 2002). Populations of corn rootworm (Diabrotica virgifera Leconte) (Chrysomelidae) adults and soybean aphids (Aphis glycines Matsumura) (Aphididae) increased on soybeans grown under elevated CO2 conditions (Dermody et al. 2008). Hughes et al. (2001) suggested that under future CO2 levels, the population of M. persicae will increase, populations of Acyrthosiphon pisum Harris (Aphididae) will decrease; and populations of Aphis nerii Boyer de Fonscolombe, Aphis oenotherae Oestlund, and Aulacorthum solani (Kaltenbach) (Hemiptera: Aphididae) will not be affected. O'Neill et al. (2010) predicted that an increase in the production of volatiles in soybeans grown under elevated CO2 will lead to larger herbivore outbreaks in the future.

Fig. 5.

Effects of temperature on longevity (days) and reproductive capacity (number of progeny) of Sipha flava. Both in Treatments 1 and 2, the forage grass used to feed the aphids was grown in a greenhouse under fluctuating CO2 levels (avg. 440 ppm). However, in Treatment 1, the aphids were kept under a constant CO2 level (500 ppm) (climate-controlled chamber ) and 25 ± 2 °C during the day and 20 ± 2 °C at night. In Treatment 2, the aphids were kept under a constant 28 ± 2 °C both day and night. Mean longevity values (days) followed by different lower case letters were significantly different as were the reproductive capacity values (numbers of progeny) followed by different upper case letters based on ANOVA and Tukey test.

f05_433.jpg

Differences in the population densities of aphids, especially in relation to CO2 elevation, vary with specific populations within a species; some populations will increase, decrease, or remain the same (Flynn et al. 2006). In our study, S. flava populations decreased when they were kept in a greenhouse and fed plants grown in either in a constant high (500 ppm) CO2 environment or in fluctuating (avg. 368 ppm) CO2 environmentS. Sipha flava populations also decreased when plants and insects were kept under a constant high (500 ppm) CO2 concentration at 28 °C. The longevity and fertility of S. flava adults were lower when they were kept in a high (500 ppm) CO2 concentration and a high temperature (28 °C) than when they were kept under the identical CO2 concentration but lower diurnally fluctuating temperatures (25 °C/20 °C, day/night). These simultaneous effects of elevated CO2 and temperature on aphids performance could also be a reflection of changes in plant chemistry.

Temperature elevation should not be overlooked when predicting the effects of climate change on plant - herbivore interactions (Newman 2004). Some authors concluded that temperature does not influence plant and herbivore responses to CO2 elevation (Williams et al. 2000), whereas others have shown strong interactive effects between CO2 and temperature (Johns & Hughes 2002; Johns et al. 2003). Flynn et al. (2006) showed that modifications of plant physiology under altered CO2 and temperature do not impair and may actually enhance Macrosiphum euphorbiae Thomas aphid populations.

Although the population of S. flava decreased under elevated CO2 and temperature conditions, additional studies should be performed to assess whether insects will increase consumption because of the poor food quality in an elevated CO2 - high temperature environment. According to Coviella et al. (2000) and Hunter (2001), insects consuming plants grown under elevated CO2 conditions exhibit increased consumption because of poor food quality of these plants.

Our results show that the population of S. flava decreased when fed on plants grown under the elevated CO2 conditions alone and in combination with high temperature. This result may be used to predict the future populations of this insect as the concentration of atmospheric CO2 continues to build.

TABLE 3.

EXPERIMENT 3: DURATION OF EACH NYMPHAL STADIUM AND SURVIVAL OF EACH NYMPHAL INSTAR WHEN COHORTS OF 50 NYMPHS WERE KEPT IN CLIMATE-CONTROLLED CHAMBERS WITH A CONSTANT CO2 LEVEL OF 500 PPM AND 2 DIFFERENT TEMPERATURE REGIMES. THESE NYMPHS WERE FED FORAGE GRASS GROWN IN A GREENHOUSE WITH FLUCTUATING CO2 LEVELS—AVG. OF 440 PPM. ONE CLIMATE-CONTROLLED CHAMBER WAS MAINTAINED 25 ± 1 °C DURING THE DAY AND 20 ± 1 °C DURING THE NIGHT (TREATMENT 1), WHILE ANOTHER WAS MAINTAINED AT 28 ± 1 °C BOTH DAY AND NIGHT (TREATMENT 2).

t03_433.gif

ACKNOWLEDGMENTS

We thank the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq, Brazil) and Fundação de Amparo à Pesquisa do Estado de Minas Gerais (FAPEMIG, Brazil) for supporting our research.

REFERENCES CITED

1.

A. M. Auad , S. O. Alves , C. A. Carvalho , D. M. Silva , T. T. Resende , and B. A. Veríssimo 2009. The impact of temperature on biological aspects and life table of Rhopalosiphum padi (Hemiptera: Aphididae) fed with signal grass. Florida Entomol. 92: 569–577. Google Scholar

2.

J. Balanyá , J. M. Oller , R. B. Huey , G. W. Gilchrist , and L. Serra 2006. Global genetic change tracks global climate warming in Drosophila subobscura. Science 313: 1773–1775. Google Scholar

3.

R. L. Blackman , and V. F. Eastop 2000. Aphids on the world's crops: an identification and information guide, 2nd ed. Wiley, Chichester, UK. Google Scholar

4.

J. P. Breen , and G. L. Teets 1986. Relationships of the yellow sugarcane aphid (Homoptera: Aphididae) density to sorghum damage. J. Econ. Entomol. 79: 1106–1110. Google Scholar

5.

F. J. Chen , G. E. Feng , and J. W. Su 2005. An improved open-top chamber for research on the effects of elevated CO2 on agricultural pests in the field. Chinese J. Ecol. 24: 585–590. Google Scholar

6.

F. J. Chen , G. Wu , M. N. Parajulee , and F. Ge 2007. Long-term impacts of elevated carbon dioxide and transgenic Bt cotton on performance and feeding of three generations of cotton bollworm. Entomol. Exp. Appl. 124: 27–35. Google Scholar

7.

F. J. Chen , G. Wu , and F. Ge 2004. Impacts of elevated CO2 on the population abundance and reproductive activity of the aphid Sitobion avenae Fabricius feeding on spring wheat. J. Appl. Entomol. 128: 723–730. Google Scholar

8.

C. E. Coviella , D. J. W. Morgan , and J. T. Trumble 2000. Interactions of elevated CO2 and nitrogen fertilization, effects on the production of Bacillus thuringiensis toxins in transgenic plants. Environ. Entomol. 29: 781–787. Google Scholar

9.

T. A. Crow , T. O. Crist , R. R. Parmenter , G. Belovsky , and A. E. Lugo 2008. The spread of invasive species and infectious disease as drivers of ecosystem change. Frontiers Ecol. Environ. 6: 238–246. Google Scholar

10.

J. J. Davis 1909. Biological studies on three species of Aphididae. Washington DC: US Department of Agriculture, Division of Entomol., Tech. Series No. 12, pt. 8, pp. 1–24. Google Scholar

11.

O. Dermody , B. F. O'Neill , A. R. Zangerl , M. R. Berenbaum , and E. H. Delucia 2008. Effects of elevated CO2 and O3 on leaf damage and insect abundance in a soybean agroecosystem. Arthropod-Plant Interactions 2: 125–135. Google Scholar

12.

R. A. Fleming , and W. J. A. Volney 1995. Effects of climate change on insect defoliator population processes in Canada's boreal forest: some plausible scenarios. Water Air Soil Pollution 82: 445–454. Google Scholar

13.

D. F. B. Flynn , E. A. Sudderth , and F. A. Bazzaz 2006. Effects of aphid herbivory on biomass and leaf-level physiology of Solanum dulcamara under elevated temperature and CO2. Environ. Expt. Bot. 56: 10–18. Google Scholar

14.

X. Fu , L. Ye , L. Kang , and F. Ge 2010. Elevated CO2 shifts the focus of tobacco plant defenses from cucumber mosaic virus to the green peach aphid. Plant Cell Environ. 33: 2056–2064. Google Scholar

15.

M. Hentz , and G. Nuessly 2004. Development, longevity, and fecundity of Sipha flava (Homoptera: Aphidae) feeding on Sorghum bicolor. Environ. Entomol. 33: 546–553. Google Scholar

16.

J. T. Houghton , Y. Ding , D. J. Griggs , M. Noguer , P. J. Van Der Linden , D. Xiaosu , K. Maskell , and C. A. Johnson [Eds.]. 2001. Climate Change 2001: The Scientific Basis. Cambridge Univ. Press, Cambridge, UK. Google Scholar

17.

L. Hughes , and F. A. Bazzaz 2001. Effects of elevated CO2 on five plant-aphid interactions. Entomol. Exp. Appl. 99: 87–96. Google Scholar

18.

M. D. Hunter 2001. Effects of elevated atmospheric carbon dioxide on insect-plant interactions. Agric. For. Entomol. 3: 153–159. Google Scholar

19.

IPCC (INTERGOVERNMENTAL PANEL ON CLIMATE CHANGE). 2007 Climate change 2007, the physical science basis. Summary for policy makers. Report of Working Group I of the Intergovernmental Panel on Climate Change) Cambridge Univer. Press, Cambridge, UK and New York. 996 pp. Google Scholar

20.

J. U. Jepsen , S. B. Hagen , R. A. Ims , and N. G. Yoccoz 2008. Climate change and outbreaks of the geometrids Operophtera brumata and Epirrita autumnata in subarctic birch forest: evidence of a recent outbreak range expansion. J. Animal Ecol. 77: 257–264. Google Scholar

21.

C. V. Johns , and A. Hughes 2002. Interactive effects of elevated CO2 and temperature on the leaf-miner Dialectica scalariella Zeller (Lepidoptera: Gracillariidae) in Paterson's Curse, Echium plantagineum (Boraginaceae). Glob. Change Biol. 8: 142–152. Google Scholar

22.

C. V. Johns , L. J. Beaumont , and L. Hughes 2003. Effects of elevated CO2 and temperature on development and consumption rates of Octotoma championi and O. scabripennis feeding on Lantana camara. Entomol. Exp. Appl. 108: 169–178. Google Scholar

23.

S. D. Kndler , and R. L. Darlrymple 1999 Relative susceptibility of cereals and pasture grasses to the yellow sugarcane aphid (Homoptera: Aphididae). J. Agric. Urban Entomol. 16: 113–122. Google Scholar

24.

I. R. Lawler , W. J. Foley , I. E. Woodrow , and S. J. Cork 1997. The effects of elevated CO2 atmospheres on the nutritional quality of Eucalyptus foliage and its interaction with soil nutrient and light availability. Oecologia 109: 59–68. Google Scholar

25.

S. Medina-Gaud , L. F. Martorell , and R. B. Robles 1965. Notes on the biology and control of the yellow aphid of sugarcane, Sipha flava (Forbes) in Puerto Rico. Proc. 12th Congress Int. Soc. Sugarcane Technol, San Juan, Puerto Rico, 28–III–10–VI: 1307–1320. Google Scholar

26.

E. B. Mondor , C. S. Awmack , and R. L. Llndroth 2010. Individual growth rates do not predict aphid population densities under altered atmospheric conditions. Agric. For. Entomol. 12: 293–299. Google Scholar

27.

E. B. Mondor , M. N. Tremblay , C. S. Awmack , and R. L. Lindroth 2005. Altered genotypic and phenotypic frequencies of aphid populations under enriched CO2 and O3 atmospheres. Glob. Change Biol. 11: 1990–1996. Google Scholar

28.

J. A. Newman 2004. Climate change and cereal aphids: the relative effects of increasing CO2 and temperature on aphid population dynamics. Glob. Change Biol. 10: 5–15. Google Scholar

29.

J. A. Newman , D. J. Gibson , A. J. Parsons , and J. H. M. Thornley 2003. How predictable are aphid population responses to elevated CO2? J. Animal Ecol. 72: 556–566. Google Scholar

30.

R. J. Norby , S. D. Wullschleger , C. A. Gunderson , D. W. Johnson , and R. Ceulemans 1999 Tree responses to rising CO2 in field experiments: implications for the future forest. Plant Cell Environ. 6: 683–714. Google Scholar

31.

B. F. O'Neill , A. R. Zangerl , E. H. Delucia , and M. R. Berenbaum 2010. Olfactory preferences of Popillia japônica, Vanessa cardui, and Aphis glycines for Glycine max grown under elevated CO2. Environ. Entomol. 39: 1291–1301. Google Scholar

32.

S. A. Oliveira , A. M. Auad , B. Souza , L. S. Souza , R. L. Amaral , and D. M. Silva 2009. Tabela de esperança de vida e de fertilidade de Sipha flava (Forbes) (Hemiptera, Aphididae) alimentado com capim-elefante em diferentes temperaturas. Rev. Brasileira Entomol. 53: 614–619. Google Scholar

33.

S. A. Oliveira , B. Souza , A. M. Auad , D. M. Silva , L. S. Souza , and C. A. Carvalho 2009. Desenvolvimento e reprodução de Sipha flava (Forbes) (Hemiptera: Aphididae) em diferentes temperaturas. Neotrop. Entomol. 38: 311–316. Google Scholar

34.

S. A. Oliveira , B. Souza , A. M. Auad , D. M. Silva , and C. A. Carvalho 2010. Biological responses of the Sipha flava (Forbes, 1884) (Hemiptera: Aphididae) fed with different elephant grass genotypes. Rev. Ciênc Agro. 41: 107–112. Google Scholar

35.

D. A. Stacey , and M. D. E. Fellowes 2002. Influence of elevated CO2 on interspecific interactions at higher trophic levels. Glob. Change Biol. 8: 668–678. Google Scholar

36.

P. Stiling , and T. Cornelissen 2007. How does elevated carbon dioxide (CO2) affect plant-herbivore interactions? A field experiment and meta-analysis of CO2 mediated changes on plant chemistry and herbivore performance. Glob. Change Biol. 13: 1–20. Google Scholar

37.

J. P. Theurillat , and A. Guisan 2001. Potential impact of climate change on vegetation in the European Alps: a review. Climate Change 50: 77–109. Google Scholar

38.

C. D. Thomas , A. Cameron , R. E. Green , M. Bakkenes , L. J. Beaumont , Y. C. Collingham, B. F. N. Erasmus , M. F. Siqueira , A. Grainger , L. Hannah , L. Hughes , B. Huntley , A. S. Van Jaarsveld , G. F Midgley, L. Miles , M. A. Ortega-Huerta , A. T. Peterson , O. L. Phillips , and S. E. Williams 2004. Extinction risk from climate change. Nature 427: 145–148. Google Scholar

39.

E. Valkama , J. Koricheva , and E. Oksanen 2007. Effects of elevated O3, alone and in combination with elevated CO2, on tree leaf chemistry and insect herbivore performance: a meta-analysis. Glob. Change Biol. 13: 184–201. Google Scholar

40.

J. A. Webster 1990. Yellow sugarcane aphid (Homoptera: Aphididae): detection and mechanisms of resistance among Ethiopian sorghum lines. J. Econ. Entomol. 83: 1053–1057. Google Scholar

41.

R. E. Will , and R. Ceulemans 1997. Effects of elevated CO2 concentration on photosynthesis, respiration and carbohydrate status of coppice Populus hybrids. Physiol. Plantarum 100: 933–939. Google Scholar

42.

R. S. Williams , R. J. Norby , and D. E. Lincoln 2000 Effects of elevated CO2 and temperature-grown red and sugar maple on gypsy moth performance. Glob. Change Biol. 6: 685–695. Google Scholar

43.

G. Wu , F. J. Chen , and F. Ge 2006. Responses of multiple generations of cotton bollworm Helicoverpa armigera Hübner, feeding on spring wheat, to elevated CO2. J. Appl. Entomol. 130: 2–9. Google Scholar

44.

D. F. Xavier , M. M. Carvalho , M. A. Botrel , V. P. Freitas , and R. S. Verneque 2001 Efeito do manejo pósplantio no estabelecimento de pastagens de capim elefante. R. Brasileira Zootec 30: 1200–1203. Google Scholar

45.

J. Yin , S. Yucheng , W. Gang , and G. Feng 2010. Effects of elevated CO2 associated with maize on multiple generations of the cotton bollworm, Helicoverpa armigera. Entomol. Exp. Appl. 136: 12–20. Google Scholar

46.

E. L. Zvereva , and M. V. Kozlov 2006. Consequences of simultaneous elevation of carbon dioxide and temperature for plant-herbivore interactions: a meta analysis. Glob. Change Biol. 12: 27–41. Google Scholar
Alexander Machado Auad, Marcy G. Fonseca, Tiago T. Resende, and Ítalo S. C. P. Maddalena "Effect of Climate Change on Longevity and Reproduction of Sipha flava (Hemiptera: Aphididae)," Florida Entomologist 95(2), 433-444, (1 June 2012). https://doi.org/10.1653/024.095.0227
Published: 1 June 2012
KEYWORDS
aphids
carbon dioxide
forage grass
temperature
Back to Top