Abstract
Ectotherms, such as insects, experience non-constant temperatures in nature. Daily mean temperatures can be derived from the daily maximum and minimum temperatures. However, the converse is not true and environments with the same mean temperature can exhibit very different diurnal temperate ranges. Here we apply a degree-day model for development of the grape berry moth (Paralobesia viteana, a significant vineyard pest in the northeastern USA) to investigate how different diurnal temperature range conditions can influence degree-day accumulation and, hence, insect life history. We first consider changes in diurnal temperature range independent of changes in mean temperatures. We then investigate grape berry moth life history under potential climate change conditions, increasing mean temperature via variable patterns of change to diurnal temperature range. We predict that diurnal temperature range change can substantially alter insect life history. Altering diurnal temperature range independent of the mean temperature can affect development rate and voltinism, with the magnitude of the effects dependent on whether changes occur to the daily minimum temperature (Tmin), daily maximum temperature (Tmax), or both. Allowing for an increase in mean temperature produces more marked effects on life history but, again, the patterns and magnitude depend on the nature of the change to diurnal temperature range together with the starting conditions in the local environment. The study highlights the importance of characterizing the influence of diurnal temperature range in addition to mean temperature alone.
Introduction
Climate warming is expected to influence the dynamics and distribution of terrestrial ectotherms, such as insects, because their physiology and ecology are strongly dependent on ambient temperature [1–8]. While research has focused on the potential effects of changes in mean temperature at relatively coarse temporal scales (e.g. seasonal or yearly mean temperature) [6], recent studies have demonstrated that temperature variation at much finer scales can also influence insect life history [9–14]. These studies have highlighted the importance of considering diurnal temperature range (DTR thereafter) along with mean daily temperature in order to fully understand the consequences of climate change.
DTR is the range between daily maximum (Tmax) and minimum temperature (Tmin). How DTR is likely to change under current climate change projections is not clear [15–16]. There is evidence to suggest that Tmax will increase while Tmin decreases, or that Tmax will increase at a faster pace than Tmin, in both cases increasing the DTR [17–18]. On the other hand, there is also evidence to support greater increases in Tmin relative to Tmax, resulting in smaller DTRs [19–22]. Given these contrasting scenarios, there is a need to comprehensively and systematically investigate how changes in DTR could impact insect life history.
We use the grape berry moth (Paralobesia viteana Clemens, Lepidoptera: Tortricidae) as a model organism. P. viteana is a significant vineyard pest in the United States, and its life history has been well characterized [23–28]. In this study, we first demonstrate how degree-day accumulation changes under the same mean temperature with various DTR conditions. We then contrast how key aspects P. viteana life history (i.e. voltinism and mean emergence/eclosion time from pupa in each generation) change under the same mean temperature but with various DTR conditions using a published degree-day model for P. viteana [28]. Finally, we demonstrate and contrast how P. viteana life history changes under the same increased mean temperature with various DTR conditions and assess the implications of climate change on insect life history.
Materials and Methods
Diurnal Temperature Range (DTR) Change and Degree Day Accumulation
The diurnal temperature profile could be extrapolated accurately from daily maximum and minimum temperature as well as photoperiod using a modified sine curve model [29–30]. DTR was defined as the difference between daily maximum temperature (Tmax) and minimum temperature (Tmin). The degree-day accumulated in a given day was defined as the total heat unit accumulated (the area under the temperature curve) above the developmental threshold (Tbase) of the insect over the entire day, where Tbase was estimated from a linear regression of development rate against temperature [31]. Consequently, using mean temperature (Tmean) alone without considering the DTR could yield a different degree-day accumulation. More specifically, if Tmean was less than Tbase, then the insect accumulated zero degree-days in that day when a degree day model without DTR information is used; while if DTR was included, the insect accumulated some heat units, given that the daily maximum temperature (Tmax) is above Tbase. In general, the degree-day accumulation in the given time period (e.g. a day) was computed as the area of the actual temperature curve above the Tbase (base development temperature threshold). If Tbase was above Tmax (daily maximum temperature), then the degree-day accumulation was zero and there was no effect from the DTR. Similarly, if Tbase was below Tmin (daily minimum temperature), there was no effect from considering DTR when estimating degree-day accumulation, because the degree-day accumulation was always Tmean-Tbase (assuming Tmean, daily mean temperature, remained the same). Hence, DTR was an important factor for estimating degree-day accumulations when Tbase fell between Tmax and Tmin. The Tmax and Tmin (and also latitude information of the site) were used to extrapolate hourly temperature profile in a day based on the modified sine-curve method [29–30]. In each day, the starting diurnal temperature profile was constructed from 10-year averaged (starting) Tmax and Tmin (Tmax and Tmin were both averaged from 10 observations to eliminate any potential outlier temperatures) under the same Tmean with different DTR conditions.
To simulate various DTR change conditions, we used a parameter k to adjust the DTR while keeping the daily mean temperature the same as the current condition (i.e., the DTR using the modified sine curve applied to observed Tmax and Tmin, see below). The new daily maximum temperature (T’max) was computed as the starting Tmax plus a fraction of the starting daily mean temperature (kTmean). Similarly the altered daily minimum temperature (T’min) was the starting Tmin minus the same fraction of the starting daily mean temperature (kTmean). The difference between new DTR and current DTR is 2kTmean.
We allowed k to vary from −0.4 to 0.4 with 0.1 increments, hence there were a total of nine conditions (one with the current k = 0, plus eight with a DTR change when k≠0). When the same k is applied to Tmin and Tmax, the DTR changes but Tmean is held constant. Four conditions represent an increasing DTR (when k>0) and four conditions represent a decreasing DTR (k<0). For instance, k = 0.1 results in 1°C increase in Tmax and a simultaneously 1°C decrease in Tmin (assuming Tmean = 10°C, with a total of 2°C change of DTR), and k = 0.4 yields a 4°C increase in Tmax with 4°C decrease in Tmin (with 8°C change of DTR); in both cases Tmean = 10°C. Daily maximum and minimum temperatures from 2001 to 2010 in Erie, Pennsylvania (42.13°N, 80.09°W, in the Lake Erie coastal plain) and Stuarts Draft, Virginia (38.03°N, 79.03°W, in the Blue Ridge Mountains valley), both locations of major grape production in the USA and with P. viteana infestation, were acquired from National Oceanic and Atmospheric Administration, USA. In general, both locations had similar annual mean temperature (10.17°C and 9.86°C for Erie and Stuarts Draft, respectively), with Stuarts Draft experiencing colder winters and earlier springs (and larger annually temperature fluctuations). Their latitudes were used to calculate photoperiod, another major environmental factor that determined the moth’s life history. Unlike temperature, photoperiod in the same calendar day at a given location did not change from year to year. Tmax and Tmin for each day were averaged across these 10 years, adjusted by the method mentioned above to simulate various DTR conditions, and used to calculate degree-day accumulations. Although the annual mean temperature only had minor fluctuations for both locations in the recent 10 years (±1°C), the temperature range could change more than 3°C during the same period. The degree-day differences under these conditions in these two locations at selected days of the year were computed and compared.
Grape Berry Moth Life History Change under the Same Mean Temperature Conditions (with Various DTRs)
The Grape Berry Moth (Paralobesia vetiana Clemens) is a significant vineyard pest in the U.S. Its life history has been comprehensively studied. The processes of diapause termination, development from egg-to-adult under non-diapausing conditions, and diapause induction have been modeled as function of temperature and photoperiod [23–26]. The base developmental threshold temperature for P. viteana (Tbase) was reported as 8.4°C [24,26] and the simulation started from day 1 in the year (Jan. 1st) through the end of the year (Dec. 31st). The life history of P. viteana is determined by the complicated nonlinear interaction between temperature and photoperiod. During spring, overwintering pupae from the previous year (the 1st generation) broke diapause and emerged by accumulating about 210 degree-days (DD) on average, starting from Jan. 1st, and laid eggs. The successive generations (from 2nd generation and thereafter) required an average of 484 DD to complete the entire life history (from egg to larva, pupa, and until reproductively mature adult, under non-diapause condition). Diapause was mediated by photoperiod (and not temperature) experienced by the egg after summer solstice. If an individual was determined to diapause then the larva developed to pupa stage only and not to further adult stage in current year, and consequently did not count as a complete generation in current year. A more detailed complete life history individual-based simulation model was developed and validated [28] and provided as S1 Appendix, and all the codes were written in R [32].
We applied this modeling framework for P. viteana [28] and contrasted modeled output for the eight conditions reflecting DTR changes to the output without a change in DTR (where k = 0, defined as the current condition). We ran the P. viteana life history simulation at Erie, PA and Stuarts Draft, VA under various DTR change conditions described in the previous section (a total of 9 conditions including the current condition) and reported the mean voltinism (number of generations per year, averaged from 1,000 simulations), mean adult emergence time of each generation, and duration of each generation, for each of these conditions. The pairwise differences of emergence time among the 9 conditions in each generation (2 through 4) were tested by the Tukey honest significance difference (HSD) analysis. The number of generation was regressed against the DTRs (k value) to test whether the slope was significantly different from 0. The mean durations of each generation were also regressed against the DTRs (k value). The detailed modeling and calculation of P. viteana voltinism is provided in S1 Appendix.
Grape Berry Moth Life History Change under Increasing Mean Temperature Conditions (with Various DTRs)
As shown in the results, P. viteana life history changed substantially under changing DTR conditions even when Tmean remained the same (Tables 1 and 2). Next we investigated how changing DTR along with changing Tmean has the further potential impact on insect life history. Similar to the previous approach, we now used two parameters, k 1 and k 2, to modify Tmin and Tmax, respectively. The modified daily minimum temperature (T’min) and maximum temperature (T’max) were computed as below, with change in mean temperature approximately 0.5(k 1-k 2) Tmean and change of DTR as −(k 1 +k 2) Tmean; consequently, change in mean temperature is not independent from change of DTR:
Thus, positive k 1 values lead to higher nighttime temperatures (higher Tmin), but negative k 2 values leads to higher daytime temperatures (higher Tmax).
Table 1. Degree-day Accumulation at Different Locations in Different Days in a Year under Same Mean Temperature with Various DTR Conditions.
| Day 50 | Day 100 | Day 150 | Day 200 | |||||
|---|---|---|---|---|---|---|---|---|
| k | Erie | Stuarts | Erie | Stuarts | Erie | Stuarts | Erie | Stuarts |
| −0.4 | 0 | 0 | 0 | 0.33 | 10.06 | 7.22 | 15.10 | 7.41 |
| −0.3 | 0 | 0 | 0 | 0.53 | 10.16 | 7.31 | 15.32 | 7.50 |
| −0.2 | 0 | 0 | 0 | 0.74 | 10.22 | 7.40 | 15.48 | 7.59 |
| −0.1 | 0.09 | 0 | 0 | 0.96 | 10.43 | 7.50 | 15.62 | 7.68 |
| 0 | 0.23 | 0 | 0 | 1.18 | 10.54 | 7.61 | 15.70 | 7.77 |
| 0.1 | 0.39 | 0 | 0 | 1.39 | 10.63 | 7.80 | 15.95 | 7.89 |
| 0.2 | 0.55 | 0 | 0 | 1.61 | 10.86 | 8.11 | 16.11 | 8.07 |
| 0.3 | 0.72 | 0 | 0 | 1.83 | 10.95 | 8.50 | 16.21 | 8.37 |
| 0.4 | 0.90 | 0 | 0.02 | 2.04 | 11.15 | 8.94 | 16.48 | 8.77 |
Note: Stuarts stands for Stuart Draft, VA, in the table. At a given day and location, it is almost consistent that larger DTR (larger k value) is related to more degree-day accumulation, even when the mean temperature remains the same. For non-leap years, day 50 is Feb 19, day 100 is Apr 10, day 150 is May 30, and day 200 is Jul 19.
Table 2. Mean Duration (Days) of Each Generation at Different Locations under the Same Mean Temperature with Various DTR Conditions.
| 2nd Generation | 3rd Generation | 4th Generation | ||||
|---|---|---|---|---|---|---|
| k | Erie | Stuarts | Erie | Stuarts | Erie | Stuarts |
| −0.4 | 44.94 | 50.83 | 37.27 | 37.38 | 30.85 | 39.45 |
| −0.3 | 44.53 | 50.66 | 37.26 | 37.48 | 32.22 | 40.89 |
| −0.2 | 44.16 | 50.60 | 37.11 | 37.60 | 31.04 | 39.66 |
| −0.1 | 43.69 | 50.38 | 37.03 | 38.04 | 29.35 | 36.17 |
| 0 | 43.43 | 49.81 | 36.78 | 37.78 | 28.69 | 33.95 |
| 0.1 | 43.36 | 49.48 | 36.64 | 37.56 | 28.60 | 34.18 |
| 0.2 | 43.04 | 49.50 | 36.44 | 37.74 | 27.83 | 34.56 |
| 0.3 | 42.79 | 49.11 | 36.21 | 37.31 | 27.04 | 30.42 |
| 0.4 | 42.28 | 49.19 | 35.89 | 37.13 | 27.36 | 27.25 |
Note: Stuarts stands for Stuart Draft, VA in the table. There is consistent trend for larger DTRs (larger k values) to result in shorter generation durations for both locations, and this trend is more obvious in the 4th generation at Stuarts Draft, VA. 1st generation is excluded because it is not a complete generation in the current year (i.e. it is the overwintering generation from last year). k = 0 represents current condition (see S1 Appendix).
It had been estimated that the annual mean surface temperature will increase by 2–6°C by the end of the 21st century [20,22]. To begin, we comprehensively assigned both k 1 and k 2 to change from −0.4 to 0.4 (with 0.1 increment, so both k 1 and k 2 had 9 values, thus 81 conditions bracketed the full range of k 1 and k 2 values) to bracket this maximum potential increase (and also the maximum decrease—although not likely to occur in the near future, we show it as a demonstration of the influence of DTR on insect life history). We constructed a new daily temperature profile, ran the simulation model, and computed the potential number of generations under a total of these 81 climate change conditions.
Next, we investigated the life history change more realistically for Erie and Stuarts Draft. The annual mean temperature at both locations was approximately 10°C. It was estimated that under mild climate change conditions, Erie would expect an increase of 2°C in mean temperature [28]. However, there was no further deterministic estimation for Stuarts Draft, VA of expected daily mean temperature change under future climates, or any estimate on DTR change for both locations [33–35]. We assumed a minimum change (2°C) as the amplitude of Tmean increment in Stuarts Draft, which was the same estimate for Erie, for the end of the 21st century [20,22]. There were multiple configurations of k 1 and k 2 that achieve an incremental change of 2°C in Tmean: k 1 to change from 0 to 0.4 while k 2 to change from −0.4 to 0 simultaneously (both with 0.1 increment/decrement). Thus, a total of five possible conditions (out of all 81 combinations of climate change) could result in the desired Tmean increment, with DTR change as +4, +2, 0, −2, −4°C, respectively. We ran the simulation again and report not only the mean voltinism per year but also generation durations of 2nd to 4th generations at each location. The quantitative influence of both DTR change and Tmean change on P. viteana phenology was tested by a two-factor analysis of variance (ANOVA). Both k 1 and k 2 were considered as fixed effect and the interaction between k 1 and k 2 was also included. The model was specified as
where μ k1k2 represented phenology observations (number of generation, each generation duration) and for each k 1 and k 2 combination, there were 100 replications (i.e. 100 simulations per combination), μ was the overall mean, α k1 and β k2 were effects from k 1 and k 2 respectively, α β k1k2 was the interaction effect, and ε was a random error.
Results
Diurnal Temperature Range (DTR) Change and Degree Day Accumulation
An example of degree-day accumulation was shown in Fig. 1 for two different locations (Erie, Pennsylvania, and Stuarts Draft, Virginia, USA) on day 100 (Apr. 10 under non-leap year condition). When k<0 (decreasing DTR conditions, left two panels in Fig. 1), there was no degree-day accumulation during day 100 at Erie, and degree-day accumulation decreased at Stuarts Draft when k was smaller (more negative, indicating smaller DTR). When k>0 (increasing DTR conditions, right two panels in Fig. 1), there was a small amount of degree-day accumulation when k = 0.4 in Erie (largest DTR condition, and no degree-day accumulation when k<0.4). In Stuarts Draft, however, there was substantially more degree-day accumulation under larger k value conditions (larger DTR). A more comprehensive degree-day accumulation result under the same Tmean with various DTR conditions on selected days of the year (day 50, 100, 150, and 200; Feb 10, Apr 10, May 30, and Jul 19 under non-leap year conditions) for both locations were presented in Table 1. When Tmax was below Tbase for P. viteana (8.4°C) before summer solstice (approximately day 50 in Stuarts Draft and day 100 in Erie), there was no degree-day accumulation in any of the 9 DTR conditions. Around and after summer solstice, while Tmean remained the same at each location in a given day under these 9 DTR conditions, the actual degree-day accumulations varied substantially. For example, on day 100 at Stuarts Draft, VA, the degree-day accumulation in the largest DTR condition (k = 0.4) was 500% more than that in the least DTR condition (k = −0.4). Different locations (essentially different latitudes, which were also influential on diurnal temperature profile along with DTR33) and different days in the year (seasonality) also influenced degree-day accumulation (Table 1). Consequently, it was not surprising that these differences were able to further impact P. viteana life history (see below).
Fig 1. Degree-Days Accumulation at Erie PA and Stuarts Draft VA under the Same Mean with Various DTR Change Conditions.
Note: Upper panels: Erie, PA; lower panels: Stuarts Draft, VA. Left panels: decreased DTR conditions (k<0); right panels: increased DTR conditions (k>0). With same mean temperature, the larger the DTR, the more degree-days can be accumulated in a day.
Grape Berry Moth Life History under the Same Mean Temperature Conditions with Various DTRs
First we assessed the differences of mean adult emergence date (for generation 1 through 4) between various DTR conditions (k≠0) versus the current condition (k = 0), when the mean temperature remained the same in each day for all of these conditions (k 1 = k 2). The results are presented in Fig. 2 (upper panels: Erie, PA; lower panels: Stuarts Draft, VA). When k was negative (a smaller than current DTR as k<0), the mean emergence date was usually later than current condition (Fig. 2, positive values along Y-axis indicates delayed emergence dates compared to the current condition). This increased number of days to achieve emergence due to changing DTR conditions was consistently larger for the fourth generation than the previous generations, although the pattern of increase with respect to generation differed among locations. When k was positive (a larger DTR), the mean emergence date was usually earlier for both locations (Fig. 2, negative values along Y-axis indicated advancing emergence dates compared to the current condition).
Fig 2. Change in P. viteana Mean Emergence Date for Four Generations under Same Mean with Various DTR Change Conditions.

Note: Upper panels: Erie, PA; lower panels: Stuarts Draft, VA. Different colors indicate different k values (see figure legends). The error bars indicate standard errors. Positive numbers in y-axis indicate later emergence date (differences in emergence dates comparing to current k = 0 condition) while negative numbers indicate earlier emregence date. The difference among all DTR conditions are more obvious at the 4th generation than earlier generations.
The mean number of generations increased in a highly significant linear relationship against k for both locations ((Fig. 3, p<0.01 from regression results), with Erie and Stuarts Draft experiencing an additional 0.15 and 0.10 generations per year under the largest DTR condition (k = 0.4). Our interpretation of P. viteana voltinism, which defines adults that emerge from overwintering pupae as the first generation, and methods for defining mean voltinism from the realized distribution, are described in S1 Appendix.
Fig 3. Number of Generations of P. viteana under Same Mean with Various DTR Change Conditions.
Note: The dots represnet mean number of generations (voltinism) with error bars represent standard errors. The lines represent linear regression of voltinism against k values for both locations. The slopes of both regression lines are highly significant (p<0.01), indicating a strong increasing trend of voltinism with larger DTRs.
The pairwise differences in mean emergence dates among the nine conditions are highly significant (p<0.01 from Tukey HSD results) for all the four generations and both locations, with the only exception occurring between the k = −0.4 and k = −0.3 conditions in the 4th generation (p = 0.38 and p = 0.15 for Erie and Stuarts Draft, respectively). Thus the emergence dates differ significantly when DTR changed. Mean duration of each generation is summarized in Table 2 for the 9 conditions at both locations. First generation was excluded because it was the overwintering generation from the previous year. Second through fourth generation were counted as complete (egg-to-adult) generations in the current year. A small number of 5th generation P. viteana did exist, but because of an insufficient number (usually <10), they were also excluded. Regression results indicated consistently highly significant (p<0.01) decreasing relationship between DTR and generation duration (i.e. larger DTR was able to shorten generation duration significantly) for all three complete generations in both locations. However the duration of earlier generations (second and third generation) had smaller differences (about 2 days between smallest and largest DTRs), comparing to later generation (about 12 days in Stuarts Draft). This was due to the relatively cooler weather before summer. A simplified explanation for such spatial difference was that Stuarts Draft had larger seasonal temperature fluctuations, and its summer was warmer than Erie, hence the later generations (especially the 4th generation) developed much faster than Erie.
In summary, increasing DTR led to both advancing the mean emergence date and shortening the generation duration (hence increasing the voltinism), even as Tmean was held constant.
Grape Berry Moth Life History Change under Increasing Mean Temperature Conditions (with Various DTRs)
Statistical results of the effects of DTR and Tmean changes (through combination of all potential k 1 and k 2 values) were obtained from the two-way ANOVA with interaction. Both k 1 and k 2 had highly significant (p<0.01) influence on number of generations and mean emergence time for the 2nd through 4th generation for both locations. The interaction between k 1 and k 2 also highly significantly (p<0.01) influence these outputs, with the only exception of the number of generations in Erie (p = 0.09). Thus DTR and Tmean changes through combination of k 1 and k 2 can significantly alter P. viteana phenology.
Next, a systematic view of how number of generations of P. viteana would change under comprehensive climate change conditions is shown in Fig. 4 for Erie and Stuarts Draft, respectively. Current mean voltinism of P. viteana is about 3 generations per year at both Erie and Stuarts Draft [28]. Under some extreme climate change scenarios, such as k 1 = 0.4 and k 2 = −0.4 simultaneously (resulting in 4°C increase in Tmean and no DTR change—equivalent to shifting the entire diurnal temperature profile, such as the solid black curve in Fig. 1, 4°C upward along the Y-axis), there would be almost 5 generations per year on average, and a few 6th generation P. viteana adults would be expected as well (see Fig. 3).
Fig 4. Number of Generations of P. viteana under Various DTR Change Conditions in Erie, PA and Stuarts Draft, VA.

Note: Upper panel for Erie and lower panel for Stuarts Draft. T’min = Tmin+k 1*Tmean and T’max = Tmax-k 2*Tmean. A total of 81 conditions (9 k 1×9 k 2) are plotted. Cooler color (more blue) indicates lower number of generations and warmer color (more red) indicates higher number of generations. The scales and ranges of color key are the same for Erie and Stuarts Draft, and are directly comparable.
The blocks occupying the main diagonal (Fig. 4, from top-left to bottom-right) represent holding the mean temperature conditions the same as in current conditions (a total of 9 blocks where k 1 = k 2), which is the special case discussed above. In general, the blocks above the main diagonal are associated with increasing mean temperature conditions, and their warmer colors (compared with the diagonal blocks) indicate an increase in voltinism. Similarly the blocks below the main diagonal were linked with decreasing mean temperature conditions. Although decreasing mean temperatures are unlikely, and are not discussed in this study, they are shown for demonstration purposes. Furthermore, the blocks that are in parallel with the main diagonal have the same increased mean temperature (than current condition) but with different DTRs. For example, all five conditions from k 1 = 0/k 2 = −0.4 to k 1 = 0.4/k 2 = 0, in parallel with the main diagonal, represent a 2°C increase in Tmean for both locations, but with various DTRs. There was a consistent pattern for the same mean temperature conditions (blocks in parallel with main diagonal, regardless if the mean increased or decreased compared to the current condition): larger DTR conditions (towards bottom-right corner) was associated with larger voltinism, for both locations (Fig. 3).
Mild climate change scenarios, such as a 2°C increase in Tmean, would impose substantial change in P. viteana life history between the current condition (k 1 = k 2 = 0) and projected conditions (Table 3). For example the number of generations increased from 3 (current condition) to approximately 3.7 in Erie, and from 2.9 to 3.5 in Stuarts Draft. Our results indicated that a rarely seen 4th generation of P. viteana under current climate condition would become a common occurrence by the end of this century. The duration of each generation was also significantly shortened (Table 3).
Table 3. Comparison of Number of Generations, Duration of 2nd-4th Generations under Various Climate Change Conditions at Erie, PA and Stuarts Draft, VA.
| k 1 | k 2 | No. of Generations | Duration of 2nd Gen. | Duration of 3rd Gen. | Duration of 4th Gen. | ||||
|---|---|---|---|---|---|---|---|---|---|
| 0 | 0 | Erie | Stuarts | Erie | Stuarts | Erie | Stuarts | Erie | Stuarts |
| 0 | 0 | 3.00 | 2.87 | 43.43 | 49.82 | 36.78 | 37.78 | 28.69 | 33.95 |
| 0 | −0.4 | 3.65 | 3.38 | 34.80 | 44.68 | 30.46 | 30.86 | 24.59 | 23.19 |
| 0.1 | −0.3 | 3.67 | 3.42 | 34.83 | 44.61 | 30.36 | 30.67 | 24.58 | 22.96 |
| 0.2 | −0.2 | 3.70 | 3.45 | 34.81 | 44.54 | 30.15 | 30.51 | 24.44 | 22.31 |
| 0.3 | −0.1 | 3.74 | 3.49 | 34.82 | 44.43 | 29.89 | 30.42 | 24.60 | 21.96 |
| 0.4 | 0 | 3.77 | 3.53 | 34.96 | 44.22 | 29.74 | 30.21 | 24.53 | 21.81 |
Note: Stuarts stands for Stuart Draft, VA in the table. Annual mean temperature increased by 2°C in rows 2 through 5, but is achieved through different changes in the DTR. A positive k 1 increases the Tmin. A negative k 2 indicates a rising Tmax. There is substantial change in mean number of generations and duration of each generation compared to the current condition (row 1, k 1 = k 2 = 0). Different DTRs also change these life history variables, even with the same 2°C increase in mean temperature. The decimal of number of generations results from taking the average of 1,000 simulations, and the number of generation in each simulation is a discrete integer number.
Additionally, we also observed a noticeable difference of P. viteana voltinism (and generation duration) among the five different DTR conditions within the same increasing mean temperature scenario (2°C increment in Tmean, from k 1 = 0/k 2 = −0.4 to k 1 = 0.4/k 2 = 0, in parallel with the main diagonal in Fig. 4). All these conditions resulted in the same 2°C Tmean increment but yielded different P. viteana life histories, such as the number of generations, and mean emergence time (Table 3 and Fig. 4), for both locations. The voltinism difference between the smallest (k 1 = 0.4/k 2 = 0) and largest (k 1 = 0/k 2 = −0.4) DTR conditions was about 0.15 generation per year for both locations, similar to the results obtained under the same mean temperature condition. However, the additional 0.15 generations was on top of the 0.5–0.6 increase in number of generations due to changes in mean temperature. The most profound differences were observed in the 4th generation duration in Stuarts Draft (Table 3, last column), where the duration shortened for more than 10 days compared with current conditions, and the largest DTR condition had almost 2 days shorter duration than the smallest DTR condition, while the difference among different DTR conditions in both locations for the 2nd and 3rd generations were all less than 1 day. This result also coincided with the results in previous section (Table 2), where the 4th generation duration had a12-day variability in Stuarts Draft even when Tmean was held constant. This demonstrates that temperature changes in Stuarts Draft are due to larger DTR, which accelerated the development of the later generation P. viteana, especially under larger DTR conditions.
Discussion
The results of this study demonstrate that changing DTR (with the same or increasing Tmean) can substantially change degree-day accumulation and hence, insect life history. The exact patterns depend on the nature of the changes, with effects differing depending on whether there is variation in Tmax, Tmin or both. Using a previously published degree-day approach we show changes in DTR could impact voltinism, mean generation duration and emergence date above and beyond effects of changes in mean temperatures alone. Indeed, even just altering DTR without altering mean temperature can lead to substantial changes in life history. The effects differ subtly between our study locations indicating interactions with the baseline mean temperature, DTR and photoperiod. The absolute changes in voltinism due to the influence of DTR are small (e.g. 0.10–0.15 generations per year) but because of the ‘compound interest’ effect of population growth, such changes might still have important ecological or economic implications. Interactions with other biotic factors (e.g. phenology shift of host plants and ectotherm predators) could further complicate the life history projection, thus the results of this model still needs validation in the field.
In this study we used 10-year averaged daily temperature data and assumed the DTR change amplitude to be the same across the year. This approach tends to smooth out some extreme conditions. However, extreme climate events (such as abnormally high and low temperatures) [15–16] are expected to increase under future climate change [20,22,36–37] and could well have ecological effects above and beyond the influence of average changes in DTR. Exposure to temperatures above critical maximum temperatures or upper lethal limits, for example, could have dramatic effects on population dynamics, even if the events are rare [38–39].
Our current analysis ignores the potential for local thermal adaptation, which could occur already between populations, or might evolve in the future due to more extreme natural selection under climate change [37,40]. Local adaptation, which could impact base development thresholds or total degree-day accumulation requirements, for example, would alter the response to environmental temperature. How this would affect population dynamics and pest damage is unclear; the nature and extent of local thermal adaptation remains poorly characterized in many systems [40–41]. Similarly, for the grape berry moth, the termination of development is determined by a photoperiod-induced diapause. While photoperiod is fixed for a given day and latitude (i.e. is not going to change in the same way temperature might) local populations could adjust their response to photoperiod in different environments. The Asian tiger mosquito, for example, has shown adaptive evolution of photoperiodic response during invasion and range expansion across a climate gradient in the US [42]. It is possible that P. viteana might have similar adaptations to optimize its life history in different environmental contexts as well [27].
In summary, our approach uses a basic degree-day model for insect development. Degree-day models are widely used to predict crop, pest and disease emergence and to inform control strategies [28,30,43]. Many of these models do not explicitly include the influence of DTR (at least not in the way we have incorporated it here). Further, many ecological studies exploring possible effects of climate change consider changes in mean temperatures alone. The current study adds to a growing body of literature indicating the need to better quantify the influence of DTR in addition to mean temperatures.
Supporting Information
(DOCX)
Data Availability
All relevant data are within the paper and its Supporting Information files.
Funding Statement
These authors have no support or funding to report.
References
- 1. Allen J. A Modified Sine Wave Method for Calculating Degree Days. Environ Entomol. 2011;5:388–396. [Google Scholar]
- 2. Logan J, Wollkind D, Hoyt S, Tanigoshi L. An analytic model for description of temperature dependent rate phenomena in arthropods. Environ Entomol. 1976;5: 1133–1140. [Google Scholar]
- 3. Taylor F. Ecology and the evolution of physiological time in insects. Am Nat. 1981;117: 1–23. [Google Scholar]
- 4. Lowry W, Lowry P. Fundamentals of Biometeorology. Oregon: Peavine Publications;1989. [Google Scholar]
- 5. Liu S, Zhang G, Zhu J. Influence of temperature variation on rate of development in insects: analysis of case studies from entomological literature. Ann Entomol Soc Am. 1995;88: 107–119. [Google Scholar]
- 6. Deutsch CA, Tewksbury JJ, Huey RB, Sheldon KS, Ghalambor CK, Haak DC, et al. Impact of climate warming on terrestrial ectotherms across latitude. Proc Nat Acad Sci USA. 2008;105: 6668–6672. 10.1073/pnas.0709472105 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7. Folguera G, Bastias DA, Bozinovic F. Impact of experimental thermal amplitude on ectotherm performance: adaptation to climate change variability? Comp Biochem Physiol A. 2009;154: 389–393. 10.1016/j.cbpa.2009.07.008 [DOI] [PubMed] [Google Scholar]
- 8. Folguera G, Bastias DA, Caers J, Rojas JM, Piulachs MD, Belles X, et al. An experimental test of the role of environmental temperature variability on ecto-therm molecular, physiological and life-history traits: implications for global warming. Comp Biochem Physiol A. 2011;159: 242–246. 10.1016/j.cbpa.2011.03.002 [DOI] [PubMed] [Google Scholar]
- 9. Paaijmans KP, Blanford S, Bell AS, Blanford JI, Read AF, Thomas MB. Influence of climate on malaria transmission depends on daily temperature variation. Proc Nat Acad Sci USA. 2010;107: 15135–15139. 10.1073/pnas.1006422107 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10. Paaijmans KP, Heinig RL, Seliga RA, Blanford JI, Blanford S, Murdock CC, et al. Temperature variation makes ectotherms more sensitive to climate change. Glob Change Biol. 2013;19: 2373–2380. 10.1111/gcb.12240 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11. Lambrechts L, Paaijmans K, Fansiri T, Carrington LB, Kramer LD, Thomas MB, et al. Impact of daily temperature fluctuations on dengue virus transmission by Aedes aegypti . Proc Nat Acad Sci USA. 2011;108: 7460–7465. 10.1073/pnas.1101377108 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12. Terblanche J, Nyamukondiwa C, Kleynhans E. Thermal variability alters climatic stress resistance and plastic responses in a globally invasive pest, the Mediterranean fruit fly (Ceratitis capitata). Entomol Exp Appl. 2010;137: 304–315. [Google Scholar]
- 13. Bozinovic F, Bastias DA, Boher F, Clavijo-Baquet S, Estay SA, Angilletta MJ. The mean and variance of environmental temperature interact to determine physiological tolerance and fitness. Physiol Biochem Zool. 2010;84: 543–552. [DOI] [PubMed] [Google Scholar]
- 14. Blanford JI, Blanford S, Crane RG, Mann ME, Paaijmans KP, Schriber KV, et al. Implications of temperature variation for malaria parasite development across Africa. Nature Sci Rep. 2013;3:1300. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15. Eastering DR, Horton B, Jones PD, Peterson TC, Karl TR, Parker DE, et al. Maximum and minimum temperature trends for the globe. Science. 1997;277: 364–367. [Google Scholar]
- 16. Eastering DR, Meehl GA, Parmesan C, Changnon SA, Karl TR, Mearns LO. Climate extremes: observations, modelling, and impacts. Science. 2000;289: 2068–2074. [DOI] [PubMed] [Google Scholar]
- 17. Travis D. Contrails reduce daily temperature range. Nature. 2002;418: 601 [DOI] [PubMed] [Google Scholar]
- 18. Travis D. Regional variations in U.S. diurnal temperature range for the 11–14 September 2001 aircraft groundings: evidence of jet contrail influence on climate. J Climate. 2004;17: 1123–1134. [Google Scholar]
- 19.Wild M, Ohmura A, Makowski K. Impact of global dimming and brightening on global warming. Geophysic Res Lett 34. 2007. Available: http://onlinelibrary.wiley.com/doi/10.1029/2006GL028031/abstract. Accessed 20 August 2014.
- 20.Intergoverment Panel of Climate Change (IPCC). IPCC Fourth Assessment Report: Climate Change AR4. 2007. Available: http://www.ipcc.ch/pdf/assessment-report/ar4/syr/ar4_syr.pdf. Accessed 20 August 2014.
- 21.Hong G, Yang P, Minnis P, Hu Y, North G. Do contrails significantly reduce daily temperature range? Geophysic Res Lett 35. 2008. Available: http://geotest.tamu.edu/userfiles/229/Hong.etal.GRL.08.pdf. Accessed 20 August 2014.
- 22. Letcher M. Climate Change: Observed impacts on planet earth Oxford: Elsevier; 2009. [Google Scholar]
- 23. Nagarkatti S, Tobin PC, Saunders MC. Diapause induction in the grape berry moth (Lepidoptera: Tortricidae). Environ Entomol. 2001;30: 540–544. [DOI] [PubMed] [Google Scholar]
- 24. Tobin PC, Nagarkatti S, Saunders MC. Modeling Development in Grape Berry Moth (Lepidoptera: Tortricidae). Environ Entomol. 2001;30: 692–699. [Google Scholar]
- 25. Tobin PC, Nagarkatti S, Saunders MC. Diapause Maintenance and Termination in Grape Berry Moth (Lepidoptera: Tortricidae). Environ Entomol. 2002;31: 708–713. [Google Scholar]
- 26. Tobin PC, Nagarkatti S, Saunders MC. Phenology of Grape Berry Moth (Lepidoptera: Tortricidae) in Cultivated Grape at Selected Geographic Locations. Environ Entomol. 2003;32: 340–346. [Google Scholar]
- 27. Tobin PC, Nagarkatti S, Saunders MC. Historical and projected interactions between climate change and voltinism in a multivoltine insect species. Glob Change Biol. 2008;14: 951–957. [Google Scholar]
- 28. Chen S, Fleischer SJ, Tobin PC, Saunders MC. Projecting insect voltinism under high and low greenhouse gas emission conditions. Environ Entomol. 2011;40: 505–515. 10.1603/EN10099 [DOI] [PubMed] [Google Scholar]
- 29. Forsythe W, Rykielm E, Stahl R, Wu H, Schoolfiel R. A model comparison for daylength as a function of latitude and day of a year. Ecol Model. 1995;80: 87–95. [Google Scholar]
- 30. Chen S, Blanford JI, Fleischer SJ, Saunders MC, Thomas MB. Estimating West Nile virus transmission period in Pennsylvania using an optimized degree-day model. Vector Borne Zoonotic Dis. 2013;13: 489–497. 10.1089/vbz.2012.1094 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31. Wiese A, Binning L. Calculating the threshold temperature of development for weeds. Weed Sci 1987;35: 177–179. [Google Scholar]
- 32. R Core Development Team. R: A Language and Environment for Statistical Computing. Austria: R Foundation for Statistical Computing; 2013. 10.3758/s13428-013-0330-5 [DOI] [Google Scholar]
- 33.Union of Concerned Scientists. Climate Change in the US Northeast: Climate Impact Assessment; 2011. Available: http://www.climatechoices.org/assets/documents/climatechoices/confronting-climate-change-in-the-u-s-northeast.pdf. Accessed 20 August 2014.
- 34.Pennsylvania Department of Environmental Protection. Pennsylvania Final Climate Change Action Plan; 2009. Available: http://www.dcnr.state.pa.us/cs/groups/public/documents/document/dcnr_001957.pdf. Accessed 20 August 2014.
- 35.Virginia Office of Inspector General. Review of VA’s Programs for Addressing Climate Change; 2013. Available: http://www.va.gov/oig/pubs/VAOIG-13-01846-235.pdf. Accessed 20 August 2014.
- 36. Meehl GA, Karl T, Easterling DR, Changnon S, Pielke R, Chanong D, et al. An introduction to trends in extreme weather and climate events: observations, socioeconomic impacts, terrestrial ecological impacts, and model projections. Bull Am Meteorol Soc. 2000;81: 413–416. [Google Scholar]
- 37. Shein KA, Todey DP, Akyuz FA, Angel JR, Kearns TM, Zdrojewski JL. Revisiting the Statewide Climate Extremes for the United States: Evaluating Existing Extremes, Archived Data, and New Observations. Bull Am Meteorol Soc. 2013;94: 393–402. [Google Scholar]
- 38. Ribeiro P, Camacho A, Navas C. Considerations for assessing maximum critical temperatures in small ectothermic animals: insights from leaf-cutting ants. PLOS ONE. 2012;7: e32083 10.1371/journal.pone.0032083 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39. Carrington LB, Armijos MV, Lambrechts L, Barker CM, Scott TW. Effects of fluctuating daily temperatures at critical thermal extremes on Aedes aegypti life history traits. PLOS ONE. 2013;8: e58824 10.1371/journal.pone.0058824 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40. Hoffman AA, Sgro CM. Climate change and evolutionary adaptation. Nature. 2011;470: 479–485. 10.1038/nature09670 [DOI] [PubMed] [Google Scholar]
- 41. Sternberg ED, Thomas MB. Local adaptation to temperature and the implications for vector-borne diseases. Trends Parasitol. 2014;30: 115–122. 10.1016/j.pt.2013.12.010 [DOI] [PubMed] [Google Scholar]
- 42. Urbanski J, Mogi M, O’Donnell D, DeCotiis M, Toma T, Armbruster P. Rapid adaptive evolution of photoperiodic response during invasion and range expansion across a climate gradient. Am Nat. 2012;179: 490–500. 10.1086/664709 [DOI] [PubMed] [Google Scholar]
- 43. Lafferty K. The ecology of climate change and infectious diseases. Ecology. 2009;90: 888–900. [DOI] [PubMed] [Google Scholar]
Associated Data
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Supplementary Materials
(DOCX)
Data Availability Statement
All relevant data are within the paper and its Supporting Information files.


