Visit larger displays but probe proportionally fewer

Size: px
Start display at page:

Download "Visit larger displays but probe proportionally fewer"

Transcription

1 Functional Ecology 2002 Visit larger displays but probe proportionally fewer Blackwell Science, Ltd flowers: counterintuitive behaviour of nectar-collecting bumble bees achieves an ideal free distribution K. OHASHI* and T. YAHARA *Biological Institute, Graduate School of Science, Tohoku University, Sendai , Japan, and Department of Biology, Faculty of Science, Kyushu University, Fukuoka , Japan Summary 1. Patterns of pollinator responses to variation in floral display size have significance for pollen flow among plants. Here we test a theoretical model for explaining such patterns by simultaneously assessing bumble bee behaviour and nectar availability in two native stands of Cirsium purpuratum with different spatial densities. 2. A bumble bee (Bombus diversus) foraging on a plant remembered and avoided only one or two flower heads that it had probed before, so that the flower-head revisitation rate increased as it stayed longer on a plant. Moreover, the revisitation rate increased less rapidly on larger displays. 3. The number of heads probed per plant increased less than proportionally with display size, and this increase was smaller at higher plant density. This pattern is consistent with our expectation that a bee leaves a plant when the cost of flower-head revisitation exceeds that of interplant movement. However, bees left plants slightly earlier than predicted. 4. As predicted, the visitation rate of bees per plant showed a decelerated increase with floral display size, and this increase was greater at higher plant density. 5. As a result of these complementary changes in the number of heads probed per plant and visitation rate per plant across plant densities, nectar rewards per head were equalized among displays (an ideal free distribution was achieved). Key-words: Bombus, floral display size, foraging behaviour, flower revisitation, ideal free distribution, plant pollinator interaction Functional Ecology (2002) Ecological Society Introduction Plants within a population often vary considerably in the numbers of open flowers (Willson & Price 1977; Pleasants & Zimmerman 1990). Variation in floral display size causes two types of pollinator response which can influence pollen dispersal. First, larger floral displays attract more pollinators per unit time (Dreisig 1995; Klinkhamer & de Jong 1990; Klinkhamer, de Jong & Bruyn 1989; Ohara & Higashi 1994; Ohashi & Yahara 1998; Robertson & Macnair 1995; Thomson 1988). This increased attractiveness promotes increased pollen receipt or removal, or potential mate diversity (Harder & Barrett 1996). Second, the number of flowers that individual pollinators probe per plant within a foraging bout also increases with floral display size (Geber 1985; Harder & Barrett 1995; Klinkhamer Author to whom correspondence should be addressed. kohashi@zoo.utoronto.ca Present address: Department of Zoology, University of Toronto, 25 Harbord St, Toronto, ON M5S 3G5, Canada. et al. 1989; Robertson 1992), which increases selfpollination among flowers on the same plant (geitonogamy; de Jong, Waser & Klinkhamer 1993; Richards 1986). Thus the relation of plant fitness to floral display size depends on the details of the two types of pollinator responses. In order to predict how pollinators respond to variation in floral display size, we developed a theoretical model based on considerations of optimal foraging (Ohashi & Yahara 1999). First, we considered a situation in which a pollinator foraging on a plant is increasingly likely to revisit previously probed flowers until the cost of flower revisitation exceeds that of moving to another plant. Such behaviour results in the number of flowers probed per plant increasing less than proportionally with the size of floral display. Next, based on previous empirical studies (Dreisig 1995; Robertson & Macnair 1995), we assumed that pollinators distribute themselves on displays of different size according to an ideal free distribution so that they can gain equal nectar rewards per flower. Given this behaviour, the rate at which individual plants receive pollinator visits 492

2 493 Nectar-collecting bumble bees achieve an ideal free distribution increases in a decelerating manner with the size of their floral display. Our model (Ohashi & Yahara 1999; Ohashi & Yahara 2001) made unique predictions concerning the effects of plant density on the two types of pollinator response to variation in floral display size. First, the number of flowers probed per plant should increase less strongly with floral display size at higher plant density. Although some authors have argued that a pollinator probes a smaller proportion of flowers as plant density increases (Cibula & Zimmerman 1984; Cresswell 1997; Heinrich 1979; Klinkhamer & de Jong 1990; Zimmerman 1981), they did not address the effect of plant density on the functional relation between the number of flowers probed per plant and floral display size. Second, visitation rate per plant should increase more strongly with display size at higher plant density. Although we found that a few previous observations on changes in pollinator behaviour across plant densities were consistent with our predictions (Klinkhamer & de Jong 1990; Klinkhamer et al. 1989), these studies did not test their findings statistically, nor did they investigate whether gain per flower was equalized among different-sized displays. In this paper we assess the effects of plant density on the responses of bumble bee behaviour in two native stands of Cirsium purpuratum (Maxim.) Matsum. First, we quantified the revisitation rate of bees to flower heads as a function of the number of previously probed flower heads on a plant, and the relative cost of interplant movement at each density. Incorporating these estimates into the model, we predicted the number of flower heads probed per plant in relation to floral display size, and compared it with observed behaviour. Second, we compared the relations between floral display size and the number of flower heads probed per plant, the visitation rate per plant, and the visitation rate per head in high- and low-density areas. Finally, we quantified nectar productivity and standing crops per head at each density to assess whether bees gain equal average nectar rewards per head regardless of variation in floral display size. We ask the following questions: (i) Is a bee increasingly likely to revisit flower heads as it stays longer on a plant, and is the increase smaller on larger displays? (ii) Is the increase in the number of flower heads probed per plant with floral display size smaller at higher plant density? (iii) Is the increase in visitation rate per plant with floral display size greater at higher plant density? (iv) Is the average visitation rate per head on each plant balanced by the per-head nectar productivity of the plant, irrespective of its floral display size? (v) Can the relationship between the number of flower heads probed by a bumble bee per plant and floral display size (number of flowering heads per plant) be quantitatively predicted by the model? EXPECTATIONS We first outline our model (Ohashi & Yahara 1999; Ohashi & Yahara 2001). We initially predicted the number of flowers probed by a pollinator before leaving a plant when display size is invariable. We considered a nectar-collecting pollinator making sequential decisions while foraging on a plant, and choosing between staying on the current plant or moving to another. This formulation may differ from well-known ratemaximizing models (e.g. marginal value theorem ; Charnov 1976). We chose this approach because of its expandability; it holds even when display size is variable, so long as pollinators visitation rate per flower is proportional to nectar productivity per flower (see below). In contrast, rate-maximizing models essentially require a condition that the forager randomly encounters each patch, which is rarely fulfilled in nature. Because plants are distributed as discrete patches, for a pollinator moving to another plant is more costly than moving within a plant. We incorporated this effect into the model by defining the discounting rate for moving to another plant (k) as k = [(flight time between flowers within a plant) + (handling time per flower)]/[(flight time between plants) + (handling time per flower)] eqn 1 In addition, we assumed that a pollinator remembers probing a maximum of m flowers on a plant and avoids revisiting them, but arbitrarily chooses among the remaining (F m) flowers where F is the size of floral display. Hence the flower revisitation rate (r) will increase linearly with the position of the flower in a visit sequence (t) (Fig. 1a). That is, r = (t m 1)/(F m) (t > m) r = 0 (t m) eqn 2 Because revisited flowers yield little or no nectar, this will cause a gradual decrease in the rate of energy gain per flower with increasing t. We refer to such a decrease in the rate of energy gain as patch depression (originally termed depression by Charnov, Orians & Hyatt 1976). Assuming that nectar productivity per flower is constant, we predicted the number of flowers that a pollinator will probe before leaving a plant as t c = (1 k)f + mk (F > m) t c = F (F m) eqn 3 where t c is the number of flowers probed per plant (for further details see Ohashi & Yahara 1999; Ohashi & Yahara 2001). The predicted pattern is shown in Fig. 1(b). The number of flowers probed per plant (t c ) increases with floral display size (F). When k < 1, the increase in t c is slower than the increase in F. At higher plant density, the increase in t c with increasing F is smaller. Next, we expanded the model for variable display sizes by considering visitation rate per plant as a combined response of many pollinators (Ohashi & Yahara 1999; Ohashi & Yahara 2001). We assumed that pollinators

3 494 K. Ohashi & T. Yahara Flower revisitation rate (a) Small display Large display m + 1 t c s t c 1 Flower sequence (t) No. of flowers probed per plant (t c ) (b) Low density High density m Floral display size (F) Visitation rate per plant (V p ) V f 1 k h V f 1 k l V f (c) High density Low density m Floral display size (F) Fig. 1. Predictions of Ohashi & Yahara s model (Ohashi & Yahara 1999; Ohashi & Yahara 2001). (a) Relationship between flower revisitation rate, r = (t m 1)/(F m) and the position of a flower in a sequence (t). Dashed line represents marginal level of revisitation for leaving a plant. The number of flowers probed on small and large displays is denoted as t c s and t c l, respectively. (b) Relationship between number of flowers probed per plant (t c ) and floral display size (F) at high and low plant densities. (c) Relationship between pollinator visitation rate per plant (V p ) and floral display size (F ) when visitation rate per flower (V f ) is equal between high and low plant densities. The discounting rate for interplant movement (equation 1) at high and low density is denoted as k h and k l, respectively. distribute themselves on plants varying in display size according to Fretwell & Lucas s (1970) theorem of the ideal free distribution (IFD): the average visitation rate per flower to be directly proportional to its nectar productivity. This is the simplest case of the IFD (continuous input model; Parker & Sutherland 1986), which is often consistent with observed pollinator behaviour (Dreisig 1995; Robertson & Macnair 1995). Then the relationship between the visitation rate per plant (V p ) and floral display size (F ) was predicted as V p = V f F/[(1 k)f + mk] (F > m) V p = V f (F m) eqn 4 where V f is constant (for further details see Ohashi & Yahara 1999; Ohashi & Yahara 2001). The predicted pattern is shown in Fig. 1(c). Pollinator visitation rate per plant (V p ) increases in a decelerating manner with floral display size (F ), which counterbalances the decline in t c /F on larger displays. At higher plant density, the increase in V p with increasing F is greater. These predictions largely depend on the assumptions that the pollinator s memory size is a constant that is smaller than display size, that nectar productivity per flower is equal among displays, and that pollinators distribute themselves on plants according to an IFD. To test our model, therefore, the assumptions and the predicted patterns should be supported empirically. Therefore we investigated the foraging behaviour of bumble bees and nectar distribution among plants in dense and sparse stands of C. purpuratum. Materials and methods ORGANISMS AND STUDY SITE Cirsium purpuratum is a herbaceous perennial that inhabits flood plains or volcanic barrens in the Kanto and Central Districts of mainland Japan. It produces large, purple, nodding flower heads ( florets per head) on several erect flowering stalks that elongate from a basal rosette. All florets within a flower head are hermaphroditic and protandrous. The number of flowering heads provides a practical measure of floral display size for a C. purpuratum plant (Ohashi & Yahara 1998). We studied C. purpuratum on a floodplain along the Kinu River ( 800 m), Tochigi Prefecture, Japan. During 1997 and 1998, main blooming occurred from September to October. Floral display size varied from one to 35 heads per plant, and 78 5% of plants had fewer than five flower heads. The most frequent pollinators were the bumble bee, Bombus diversus Smith. In addition, Bombus honshuensis Tkalcu, Bombus consobrinus wittenburgi Vogt and Bombus hypocrita Pèrez also visited C. purpuratum, but only rarely. The other rare visitors of C. purpuratum have been described elsewhere (Ohashi & Yahara 1998). Cirsium flowers offer nectar and pollen, but most bees do not actively collect pollen in the sense of manipulating the anthers. Thus we considered nectar to be the primary reward. For several reasons, the Cirsium Bombus system seems particularly appropriate for testing our model. (i) Flower heads are irregularly distributed in three-dimensional space within a plant, so that flower-head revisitation by bees is more likely than if heads had a regular distribution. (ii) Individual plants are dispersed so that each plant represents a distinct patch. (iii) Plants receive frequent visits by bees, so we could record numerous sequences of flower-head visitation on each plant. (iv) Bumble bees appear to compete extensively for nectar, and the visitation rate per head is almost equal among different-sized displays, suggesting an IFD (Ohashi & Yahara 1998). BUMBLE-BEE RESPONSES TO FLORAL DISPLAY SIZE During early September 1997 and 1998, we selected two areas with different spatial densities at our site. In the high-density area, mean distance to the nearest two neighbours was 1 48 m (n = 18, SE = 0 11) in 1997 and

4 495 Nectar-collecting bumble bees achieve an ideal free distribution 1 31 m (n = 22, SE = 0 13) in 1998; and in the low-density area, 10 2 m (n = 18, SE = 0 82) in 1997 and 8 15 m (n = 22, SE = 0 50) in These areas were separated by >50 m, so that few bees foraged in both areas. During each daily observation in 1997, we selected one or two pairs of one large plant (six to 16 flowering heads) and one small plant (one to three flowering heads) in each density area. For each plant we numbered flowering heads consecutively and observed them for 80 min, either directly or indirectly with 8 mm video cameras (Handycam CCD-TR250, Sony). For each plant we recorded the number of bees that visited, the number of flower heads probed per visit, and the sequence of flower heads probed during each visit. We repeated these 80 min observations three times a day for six focal plants, separated by 30 min intervals ( , and ), so that each focal plant was observed for 4 h. These daily observations were conducted at three separate times during the flowering season in 1997 (6 7, and September). We also recorded the date of anthesis of each head on 12 plants to describe flower-head age distribution within plants. In 1998 we conducted similar observations on 7 12, 14, 17 18, 20 22, 24, 26 27, September, and 2 October. For each daily observation we selected one or two plants in each density area and monitored their bee visits continuously for 6 h ( ). Because we primarily sought to collect data on flower-head revisitation during 1998, we did not always include large and small displays in pairs. Display size of focal plants ranged from eight to 18 heads. TIME COST OF FLIGHT WITHIN AND BETWEEN PLANTS To estimate the discounting rate for interplant movement (k), we timed inter- and intraplant bee flights, and the probing time of individual heads (time from landing until leaving a head) to 0 01 s with a digital stopwatch (ATC-1100, CASIO) in the high- and lowdensity areas. These measurements were repeated during the peak of pollinator activity ( ) on September STANDING CROP OF NECTAR SUGAR PER HEAD In parallel with monitoring bee visitation in 1997 (6 7, 9, 13 14, 16 and September), we selected a pair of displays (large, six to 13; small, two or three heads per plant) in each density area, and measured nectar standing crop in all flower heads on them. On each observation day we sampled nectar at 06.30, 08.20, and h. We roughly divided each head into inner, middle and outer florets, then picked five middle florets from each head with forceps. This influenced neither nectar productivity of other florets, nor bee visits to the head (K.O., unpublished results). Sampled Table 1. Variation in nectar production rate of florets due to differences in sexual stages (male, intermediate and female) and relative locations within a head (inner, middle and outer) among florets. Mean ± SE nectar sugar (sucrose) production rate (µg floret 1 h 1 ). Twelve heads were investigated in each case Sexual stage of florets Location of florets within a head Inner Middle Outer Male 23 5 ± ± ± 2 6 Intermediate 17 7 ± ± ± 3 1 Female 15 0 ± ± ± 3 0 Table 2. Variation in nectar production rate of florets due to differences in sexual stages (male, intermediate and female) and relative locations within a head (inner, middle and outer) among florets. A model I 3 3 factorial ANOVA Source df SS F P Position Stage Position stage Residual florets were placed in 1 5 ml microcentrifuge tubes and taken to the laboratory in a chilled airtight container. We also sampled five middle florets from each of 20 flower heads just after they had been probed by bees. In the laboratory, we collected floral nectar by inserting a 1 10 µl GELoader Tip (Eppendorf, Germany) into a floret and sucking up the nectar with a 5 ml syringe. We then flushed the tip with 3 5 µl distilled water and soaked it up with a rounded wick (6 mm diameter) of chromatography paper (Whatman 3MM Chr). We thus soaked up nectar from five florets with a wick and dried it at 37 C. Nectar of C. purpuratum primarily contains sucrose (>90% of solutes), so we measured the sucrose content of each sample. We dissolved the sugar in each wick in 20 µl distilled water, and quantified sucrose content with an automated enzyme electrode analyser (Biotec Analyzer M-110, Sakura Seiki Co. Ltd, Japan). Preliminary analysis showed that sucrose content in five middle florets correlated strongly with that in 25 randomly picked florets from the same head (n = 19, r = 0 91, P < ). NECTAR PRODUCTIVITY PER HEAD On 17 September 1997, we examined nectar sugar (sucrose) production rate of flower heads on differentsized displays of C. purpuratum. In the high- and lowdensity areas we selected 18 and 20 plants, respectively, with 1 19 flowering heads per plant. Nectar sugar production rate is highest when the flower is in the male phase, which does not vary among the locations within a head (Tables 1 and 2). To control for this effect of sexual stage, we selected one flower head on each plant which had just passed 3 4 days after anthesis,

5 496 K. Ohashi & T. Yahara and collected five middle, male-phase florets. After the first sampling at 1100 h, each focal head was bagged (2 mm mesh, vinylon 35%, polyester 65%) to allow nectar to accumulate until we sampled five additional florets at 1500 h. Sugar production rate was then determined as the difference between nectar contents before and after bagging. Nectar production over 4 h was much less than the maximum nectar capacity of florets (K.O., unpublished results). We also checked whether floret number per head varied with head number per plant. We randomly selected one flower head for each of 20 plants with different sizes of floral display (1 29 flowering heads per plant) and counted the total number of florets. DATA ANALYSIS Bumble bee behaviour within plants From observations of sequences of flower-head visits, we determined the extent to which bumble bees revisited flower heads as a function of the number of flower heads available on a plant and the number already visited by the bee during one visit. For each plant, we calculated the flower-head revisitation rate as r = R t /(R t + N t ), where R t and N t is the number of visit sequences in which the tth probing was a revisit and a non-revisit, respectively. We then estimated memory size (m) for each plant by fitting a linear function, r = b[t (m + 1)], to the observed relationship between the revisitation rate (r) and the position of a head in a sequence (t), where b and m are constants. Because the number of heads probed before leaving (the maximum t) varied among visit sequences, even on the same plant, the number of sequences including the tth probing (R t + N t ) decreased with increasing t. This would increase the variance of the calculated r with increasing t. Therefore, to estimate b and m as accurately as possible, we used the weighted least-squares method with 1/(R t + N t ) as the weight (Draper & Smith 1998). We also calculated the overall rate of flower-head revisitation for each plant as a ratio of the sum of the number of revisits to the sum of the number of visits over all flower heads on the plant: r o = ΣR t /Σ(R t + N t ) (t = 3, 4, ). Data on plants with fewer than three flower heads were omitted from these analyses. We estimated the discounting rate for interplant movement (k) using the observed values of time per head, flight time between heads, and flight time between plants. From the observed distribution of each parameter, we randomly selected one value and calculated the discounting rate (k) based on equation 1. We repeated this procedure times for each density area to estimate the mean k and its 95% confidence limits. We adopted such a Monte Carlo procedure because the average of a non-linear function of random variables differs from the function s value for averages of these variables (so-called fallacy of the averages ; Wagner 1969). We calculated the optimal number of flower heads probed per plant per bee (t c *) based on equation 3. Again, we carried out a Monte Carlo procedure involving randomly drawn input variables for each size of floral display. Values of m were drawn randomly from a truncated normal distribution (1 m) with the parametric mean and standard deviation based on observed values (see above), and k was calculated as described above (but 0 k 1). For both high- and low-density areas, the predicted t c * with its 95% confidence limits was compared to the observed t c for each display size. Bumble bee visitation rate per plant/head We previously found that the per-head and per-plant visitation rate on a given size of display fluctuated substantially from day to day (Ohashi & Yahara 1998). Therefore we calculated relative visitation rate per plant as (number of bee visits to focal plant)/(sum of number of bee visits to all observed plants on the same day) for each plant observed during 1997 and With regard to the number of flower heads probed per plant, we used mean data for each plant to avoid pseudoreplication due to repeated measurements on the same plant. For similar reasons, we calculated relative mean visitation rate per head for each plant as (mean number of bee visits per head on focal plant)/(sum of mean number of bee visits per head over all observed plants). We then related these three measures of bee behaviour with floral display size using linear or non-linear least-squares regressions with the polytope (simplex) method a numerical procedure that can be used to minimize a function with respect to a set of parameters (Nelder & Mead 1965; for a BASIC program see Nash & Walker- Smith 1987). Further, we performed ANCOVAs with either of the three measures of bee behaviour as the dependent variable, plant density (high or low) as the independent variable, and display size as the covariate. Prior to analyses, we logarithmically transformed the relative visitation rate per plant and the relative mean visitation rate per head to correct for lack of normality and/or inequality of variances (Sokal & Rohlf 1995). When the slopes of regression lines were not significant, we performed simple comparisons between the highand low-density area using Mann Whitney U-tests (we did not use log-transformed variables in such cases). When variances significantly differed between areas, we alternatively used tests for equality of medians (Sokal & Rohlf 1995) to avoid a type I and/or type II error due to heterogeneity of variances (Kasuya 2001). Nectar We performed an ANCOVA on sugar production rate with plant density (high or low) as the independent variable and display size as the covariate. We also performed a model I 3 3 factorial ANOVA with nectar standing crop as the dependent variable, floral

6 497 Nectar-collecting bumble bees achieve an ideal free distribution display size and plant density as the independent variables. Prior to these analyses, we logarithmically transformed the dependent variables to correct for lack of normality. Results BUMBLE BEE BEHAVIOUR The overall rate of flower-head revisitation by bumble bees on a plant (r o ) averaged (n = 24, SE = 0 002) at high density and (n = 27, SE = 0 009) at low density. At both densities, overall revisitation rate (r o ) increased with the size of floral display (F ) (high density: r o = F, n = 24, R 2 = 0 21, P = 0 024; low density: r o = F, n = 27, R 2 = 0 26, P = ), with a stronger increase at low density than high density (df = 1,47, F = 5 43, P = 0 024). For each plant, the likelihood of revisitation (r) increased linearly with the position of a head in a visit sequence after probing a few non-revisited heads (Fig. 2). The transition from no revisits to increasing revisits (t = m + 1) occurred after an average (±SE) of 3 0 ± 0 26 heads or 2 3 ± 0 23 heads in the high- and low-density areas, respectively. The risk of revisitation increased less rapidly with successive probings on large displays than on small displays (Fig. 2). The estimated slope of the regression line was negatively correlated with display size (high density: n = 24, Kendall s tau = 0 36, P = 0 015; low density: n = 27, Kendall s tau = 0 52, P = ). The estimated memory size (m) was marginally larger in the high- than in the low-density area (U = 219 0, P = 0 048, Mann Whitney U-test). On the other hand, the estimated memory size did not vary significantly with floral display size (high density: n = 24, r = 0 13, P = 0 55; low density: n = 27, r = 0 095, P = 0 64). Flight time between plants varied significantly between high and low densities (high density: n = 60, mean ± SE = 4 21 ± 0 28 s; low density: n = 49, mean ± SE = 7 43 ± 0 41 s; U = 522 5, P < , Mann Whitney U-test). On the other hand, no significant densitydependent difference was detected in time per head (U = , P = 0 40, Mann Whitney U-test; n = 99, mean ± SE = 27 8 ± 2 8 s) and in flight time between heads within plants (Fisher s exact probability = 0 098, test for equality of medians; n = 60, mean ± SE = 1 90 ± 1 2 s). In our Monte Carlo calculation, the mean k (±95% CL) was estimated as 0 88 ± 0 37 at high density and 0 76 ± 0 39 at low density. Bumble bees probed fewer heads per plant than expected, although the observed means always fell within the 95% confidence limits of the predictions (Fig. 3). Bees usually left a plant spontaneously, but interference by other pollinators (including bumble bees and other visitors) or vespid wasps caused about 12% of departures (data on 17 plants in 1998). The number of flower heads that bees probed per plant (t c ) increased linearly with, but less rapidly than, floral display size (Fig. 3). The slope of this relation in the Fig. 2. Relationships between the likelihood of revisitation (r) and the position of the head in a visit sequence (t). Bending point corresponds to (m + 1). (a) High density, data on small displays (, five plants with five to eight heads, bending point = 3 27, slope = 0 23, R 2 = 0 87, n = 6, P = ); large displays (, seven plants with heads, bending point = 3 35, slope = 0 068, R 2 = 0 94, n = 11, P < ). (b) Low density, data on small displays (, five plants with six to seven heads, bending point = 2 76, slope = 0 15, R 2 = 0 93, n = 8, P < ); large displays (, eight plants with heads per plant, bending point = 2 48, slope = 0 076, R 2 = 0 93, n = 11, P < ). Memory size (m) was also estimated for each plant using the same regression method (see text). low-density area was 2 3 (1997) or 3 0 times (1998) greater than in the high-density area (df = 1,32, F = 23 0, P < in 1997; df = 1,38, F = 8 76, P = in 1998). The relative visitation rate per plant increased in a decelerating manner with floral display size during 1997 (Fig. 4), but this pattern was not evident during 1998, when we observed few small displays. Visitation rate per plant increased more rapidly in both years and reached a higher maximum in the high- than in the low-density area (intercept: df = 1,33, F = 18 5, P = in 1997; df = 1,13, F = 34 4, P < in 1998; slope: df = 1,32, F = 0 55, P = 0 47 in 1997; df = 1,12, F = 0 044, P = 0 84 in 1998, ANCOVA for log-transformed dependent variable). During 1997, the average visitation rate per head per hour varied among plants from 0 84 to The relative mean visitation rates per head (V f ) at both densities did not vary significantly with floral display size (Fig. 5a; high density: n = 16, F = 2 00, P = 0 18;

7 498 K. Ohashi & T. Yahara Fig. 3. Observed and predicted relationships between number of flower heads probed per plant (t c, t c *) and floral display size (number of flowering heads per plant, F ). (a) Data in 1997: high density ( ), t c = F, R 2 = 0 91, n = 16, P < ; low density ( ): t c = F, R 2 = 0 84, n = 20, P < (b) Data in 1998: high density ( ), t c = F, R 2 = 0 51, n = 20, P = ; low density ( ), t c = F, R 2 = 0 51, n = 20, P = ). (c) Predicted mean t c * (high density, ; low density, ) and 95% CL (high density, dashed lines; low density, solid lines) for each F. low density: n = 20, F = 0 51, P = 0 49). We detected no significant difference in V f between the high- and the low-density area (U = 121 0, P = 0 21, Mann Whitney U-test). During 1998 the average visitation rate per head per hour varied among plants from 2 42 to The relative mean visitation rate per head (V f ) did not vary with floral display size (Fig. 5b; high density: n = 8, F = 0 30, P = 0 60; low density: n = 8, F = 0 039, P = 0 85), nor between the two areas (U = 31 0, P = 0 92, Mann Whitney U-test). Thus bumble bees utilized large and small displays equally in terms of average visitation rate per head. Within each plant, however, variation in visitation rate differed greatly among flower heads (CV = %, data on 21 plants in 1997). Fig. 4. Observed relationships between relative visitation rate per plant (V p ) and floral display size (number of flowering heads per plant, F ). (a) Data in 1997: high density ( ), V p = 0 13F/ ( F ), R 2 = 0 61, n = 16, P = ; low density ( ), V p = 0 19F/( F ), R 2 = 0 28, n = 20, P = (b) Data in 1998: high density ( ), V p = 0 067F/( F ), R 2 = 0 30, n = 8, P = 0 16; low density ( ), V p = 0 019F/( F ), R 2 = 0 15, n = 8, P = NECTAR AVAILABILITY Mean nectar sugar production rate of a flowering head (µg sucrose floret 1 h 1 ) did not vary with floral display size (Fig. 6). Furthermore, plants in the high- and lowdensity area produced equivalent amounts of nectar sugar (high density: n = 18, mean ± SE = 16 7 ± 2 1 µg floret 1 h 1 ; low density: n = 20, mean ± SE = 16 0 ± 1 5 µg floret 1 h 1 ; Fisher s exact probability = 0 63, test for equality of medians). In addition, the number of florets per head did not vary with floral display size (n = 20, r = 0 12, P = 0 63). Thus, irrespective of floral display size, C. purpuratum provided similar nectar rewards per head for pollinators. On each plant, however, there seemed to be some variation in nectar productivity among heads, derived from their asynchronous flowering (CV of flower-head age within a plant per day = %, data on 12 plants in 1997). Standing crop of nectar in flowering heads (n = 144 heads, mean ± SE = 16 9 ± 1 8 µg floret 1 ) varied neither with display size (df = 1,140, F = 0 60, P = 0 44)

8 499 Nectar-collecting bumble bees achieve an ideal free distribution Relative mean visitation rate per head (Vf) (a) (b) 1998 High density Low density No. of flowering heads per plant (F ) Fig. 5. Observed relationships between relative mean visitation rate per head (V f ) and floral display size (number of flowering heads per plant, F). Data in (a) 1997; (b) During both years and in both areas these variables were not significantly correlated with each other (see text). Fig. 6. Relationships between nectar productivity of a flowering head and floral display size (number of flowering heads per plant, F ). In both areas these variables were not significantly correlated with each other (see text). nor with plant density (df = 1,140, F = 0 14, P = 0 71). The interaction of the two independent variables was also non-significant (df = 1,140, F = 3 19, P = 0 076, model I 3 3 factorial ANOVA). On average, bumble bees left a head after removing about 80% of the initial crop (nectar sugar in a head just after probed: n = 20, mean ± SE = 3 03 ± 0 56 µg floret 1 ; nectar sugar in a randomly sampled head: n = 20, mean ± SE = 15 2 ± 2 0 µg floret 1 ; Fisher s exact probability = , test for equality of medians). Discussion FLOWER-HEAD REVISITATION AND MEMORY SIZE The estimated memory size of bumble bees was between one and two heads (Fig. 2). This suggests that bumble bees store spatial information on previously probed flower heads in spatial working memory (or short-term memory) with limited capacity and persistence. This appears to contradict the fact that bees often exhibit large long-term memory capacity for spatial information, such as the location of the nest and flower patches (Menzel et al. 1996). In nature, however, bees often probe hundreds of flowers successively during one foraging trip, in which case spatial working memory may be more efficient than long-term memory in terms of processing speed and flexibility. Honeybees also use spatial working memory to avoid flower revisitation instead of long-term memory (Brown & Demas 1994; Brown et al. 1997). It is unclear why bumble bees began revisiting previously probed heads slightly later on a plant in the high-density than in the low-density area. This may reflect some flexibility in bees foraging strategy in response to plant density. Otherwise, bees might use neighbouring plants as temporal signposts or landmarks in the high-density area. For example, Redmond & Plowright (1996) have reported that bumble bees avoid flower revisitation more efficiently when landmarks are available. As a consequence of this small memory size, the risk of flower-head revisitation increased linearly with the position of a head in a visit sequence after just two or three heads had been probed (Fig. 2). Because bees depleted the nectar in heads to 20% of the initial crop, our result indicates that increasing risk of flower-head revisitation caused a gradual decrease in the rate of gain per head (patch depression). This role of flower revisitation in patch depression has been poorly appreciated because bees seldom revisit flowers: 2 9% (Pyke 1979); 3 5% (Pyke 1982); 0 2 and 3 0% (Galen & Plowright 1985). However, we observed patch depression even though bees revisited 5 1% of the heads they probed. Several previous studies have also found that a pollinator is increasingly likely to revisit flowers as it stays longer on a plant or inflorescence (Pyke 1978; Pyke 1981; Pyke 1982; Redmond & Plowright 1996). Flower-head revisitation rate increased more slowly on larger displays (Fig. 2). This is simply because larger displays offer more flower heads from which to choose and relieve the risk of flower-head revisitation, as predicted in equation 2 and Fig. 1(a). Pyke (1982) also reported a similar result in bumble bees foraging on Aconitum columbianum (Table 14 of Pyke 1982). Previous authors have often considered the spatial gradient of nectar crops per flower as the cause of patch depression (Best & Bierzychudek 1982; Hodges 1981; Hodges 1985). However, as Pyke (1982) pointed out, spatial structuring of nectar crops alone cannot explain why pollinators

9 500 K. Ohashi & T. Yahara tend to be more tenacious on larger displays, because flowers on large displays often contain the same nectar distribution as those on small displays (Pyke 1978; Pyke 1982; Wolf & Hainsworth 1986; this study, but see Hodges 1985). We suggest therefore that the risk of flower revisitation, as well as nectar distribution pattern, is important in understanding pollinator behaviour on plants. RESPONSES TO VARIATION IN FLORAL DISPLAY SIZE AND PLANT DENSITY As has been observed repeatedly for other species (reviewed by Goulson 2000; Ohashi & Yahara 2001), the number of heads that bumble bees probed per plant increased less than proportionally with floral display size, so that the proportion of flower heads probed per bee (t c /F ) declined with display size (Fig. 3). This increase in the number of heads probed per plant was significantly slower in the high- than in the low-density area (Fig. 3). Ohashi & Yahara (1999) (see Fig. 1b) proposed that this change would result because bees decrease the marginal level of revisitation for leaving a plant (dashed line, Fig. 1a) at higher plant density, which reduces the difference in number of flower heads probed per plant between large and small displays (t c l t c s ). We also found that visitation rate per plant increased at a decelerating rate with floral display size (Fig. 4). A decelerating increase of visitation rate per plant with increasing display size has been reported in previous studies (reviewed by Iwasa, de Jong & Klinkhamer 1995; but see Andersson 1988; Ohara & Higashi 1994; Sih & Baltus 1987). As predicted, visitation rate per plant increased more strongly with increasing displays size at higher plant density (Fig. 4). The preference for visiting larger displays counterbalanced the decline in the proportion of flower heads probed by a bee on larger displays, so that the average visitation rate received per head did not vary with display size, irrespective of plant density (Figs 3 5). This strongly suggests that bees preferred to visit large displays because a decline in the proportion of heads probed per plant reduced the competition among bees on these plants. Because neither nectar production rate per head, nor head size (floret number per head), varied with floral display size of the plant, an equalization of the visitation rate per head means that bumble bees gained equal nectar rewards per head on all sizes of display they achieved an IFD. As a result of this, flower heads on large and small displays contained the same amounts of nectar crop. A few researchers have also proposed reliable evidence that nectar foragers approximate an IFD on plants. Delph & Lively (1992) found that perfect flowers on hermaphroditic plants of Hebe stricta had higher nectar productivity than pistillate flowers on female plants, but frequent pollinator visits to perfect flowers depleted nectar to the point where the two sexual morphs contained the same amounts of nectar crop. Dreisig (1995) found that foraging bumble bees achieved an IFD by visiting individual Anchusa officinalis and Viscaria vulgaris according to its nectar productivity and the proportion of flowers that a bee probed on that plant. Similarly, with regard to pollen foragers Robertson et al. (1999) reported that bumble bees responded to genetic variation in pollen quality (proportion of inviable pollen grains) among Mimulus guttatus plants by visiting the high-quality patch more often and by visiting more flowers within the patch. We do not emphasize that the distribution of bumble bees conformed strictly to an IFD. Some authors have noticed that the restrictive assumptions for the continuous input IFD model (see above) are often violated under natural conditions (Kennedy & Gray 1993; Milinski 1994). In addition, we found that the overall rate of flower-head revisitation (r o ) increased with display size, especially at low plant density. Ohashi & Yahara (1999) predicted that this would result because the ratio of m to t c declines with display size and plant density. If bees could detect these subtle differences in the rate of energy gain among plants and adjust their distributions to a complete IFD, the average visitation rate per head might have varied with display size. However, such effects seemed too small to affect actual bees visitation. Thus an equalization of the visitation rate per head among plants observed here can be regarded as a quasi-ifd. The strategies that individual bumble bees might use to achieve an IFD are still open to question. As Dreisig (1995) suggested, bees preferences for visiting large floral displays may partly explain the IFD. It should be noted, however, that the observed visitation rates per plant cannot be viewed simply as an amplified pattern of individual bees choice in relation to floral display size. Individual bumble bees frequently confine their foraging to small areas within a larger plant population, and they appear to overlap their foraging areas (Williams & Thomson 1998). Therefore a bee has to adjust the degree of overlap in its foraging area with others, while deciding how often it should visit each size of display. It has been suggested that bumble bees have some abilities needed for such complicated adjustments. For example, bees are known to fly longer distances after encountering lower rewards (area-restricted searching; reviewed by Motro & Shmida 1995). By adopting this rule while foraging along its own foraging route (trapline; Thomson 1996 and references therein), bees may efficiently reduce the spatio-temporal bias in nectar distribution. To clarify how these foraging patterns contribute to an IFD, a detailed description is required of individual bees behaviour and their use of space. QUANTITATIVE PREDICTIONS OF NUMBER OF FLOWER HEADS PROBED PER PLANT The predicted optimal number of flower heads probed per plant was generally larger than that observed

10 501 Nectar-collecting bumble bees achieve an ideal free distribution (Fig. 3). The most probable reason for this discrepancy is the variation in nectar productivity among heads within a plant. All available flower heads on a plant were used to quantify the size of floral display. However, flower age varied greatly among heads within a plant, so that this might result in a substantial variation in nectar productivity among heads. If bees probed older and less rewarding heads infrequently, as has been reported in other systems (Cruzan, Neal & Willson 1988; Gori 1989; Oberrath & Böhning-Gaese 1999), the realized mean number of heads probed per plant would be fewer than that predicted. Another possibility is the assumption of our model that the bees have complete information on nectar distributions within plants that information obtained while foraging on a plant is of no value for their decisionmaking. In nature, pollinators rarely have complete information and their environment is usually stochastic, so that they appear to use full or partial information gained at each flower to decide when to leave a plant; pollinators often leave a plant just after probing one or two flowers with little or no nectar (Hodges 1985; Pyke 1978; Pyke 1982; Thomson, Maddison & Plowright 1982). Such simple probabilistic rules may provide a practical method to approach a mathematical optimum in nature (see also Iwasa, Higashi & Yamamura 1981; McNamara & Houston 1980). We assumed complete information because our aim was simply to find an optimum plant departure, rather than patch-leaving rules that visitors actually follow. However, this difference might result in a quantitative discrepancy between expectation and observation. Conclusions Recent empirical research on plant pollinator interactions has identified a puzzling feature of pollinator behaviour in response to increasing display size pollinators visit larger displays more often, but leave a greater proportion of flowers behind on larger displays (Ohashi & Yahara 1999). The results obtained here strongly support our basic idea that this counterintuitive behaviour can be understood as an optimal strategy to avoid the risk of flower revisitation, and to utilize nectar in flowers left behind during one visit. By comparing different plant densities, we showed that these two types of pollinator behaviour interact with each other through the distribution of floral reward. These results suggest that decisions on patch choice and patch residence time should be considered inclusively when resource patches vary in size. Another novel finding of this study is that the reduction in plant density decreases pollinators preference for visiting larger displays, while it increases their tenacity on larger displays. Pollinators are said to alter their foraging behaviour in response to the decrease in plant density. First, pollinators may be attracted less strongly to plants growing at lower densities (Kunin 1997). Second, pollinators are more likely to behave as generalists on sparsely distributed plants (Kunin 1993). In addition to these population-level effects, we showed that pollinators respond to decreasing plant density by altering their behaviour on each size of display within populations. Such alterations may greatly affect pollen dispersal from plants with different size of displays (Harder & Barrett 1995; Rademaker & de Jong 1998). Our study suggests that observations on pollinator behaviour and/or pollen dispersal in relation to floral display size should be viewed with caution unless the effects of plant density are explicitly described. Acknowledgements We are grateful to many colleagues for contributions to the ideas herein; Drs L. F. Delph, L. D. Harder and A. W. Robertson for helpful comments on the manuscript; Dr E. Kasuya for writing BASIC programs and for help in statistical analyses; Dr O. Tadauchi for identification of bumble bee species; Drs K. Muraoka, M. Watanabe and S. Nawashiro for useful advice on nectar measurement; Y. Fujita, C. Kikuchi, M. Kinoshita, A. Konuma, K. Murayama, Y. Osone, S. Shiokawa and H. Taneda for patient help with field work; and K. Shibata, Dr M. Tateno and the other staff of the Nikko Botanical Garden for invaluable assistance throughout our field work. This work was partly supported by a fellowship (no. 1597) of The Japan Society for the Promotion of Science for Young Scientists. References Andersson, S. (1988) Size-dependent pollination efficiency in Anchusa officinalis (Boraginaceae): causes and consequences. Oecologia 76, Best, L.S. & Bierzychudek, P. (1982) Pollinator foraging on foxglove (Digitalis purpurea): a test of a new model. Evolution 36, Brown, M.F. & Demas, G.E. (1994) Evidence for spatial working memory in honeybees (Apis mellifera). Journal of Comparative Psychology 108, Brown, M.F., Moore, J.A., Brown, C.H. & Langheld, K.D. (1997) The existence and extent of spatial working memory ability in honeybees. Animal Learning and Behavior 25, Charnov, E.L. (1976) Optimal foraging, the marginal value theorem. Theoretical Population Biology 9, Charnov, E.L., Orians, G.H. & Hyatt, K. (1976) Ecological implications of resource depression. American Naturalist 110, Cibula, D.A. & Zimmerman, M. (1984) The effect of plant density on departure decisions: testing the marginal value theorem using bumblebees and Delphinium nelsonii. Oikos 43, Cresswell, J.E. (1997) Spatial heterogeneity, pollinator behaviour and pollinator-mediated gene flow: bumblebee movements in variously aggregated rows of oil-seed rape. Oikos 78, Cruzan, M.B., Neal, P.R. & Willson, M.F. (1988) Floral display in Phyla incisa: consequences for male and female reproductive success. Evolution 42, Delph, L.F. & Lively, C.M. (1992) Pollinator visitation, floral display, and nectar production of the sexual morphs of a gynodioecious shrub. Oikos 63,

11 502 K. Ohashi & T. Yahara Draper, N.R. & Smith, H. (1998) Applied Regression Analysis, 3rd edn. John Wiley & Sons, New York, NY. Dreisig, H. (1995) Ideal free distributions of nectar foraging bumblebees. Oikos 72, Fretwell, S.D. & Lucas, H.L. (1970) On territorial behavior and other factors influencing habitat distribution in birds. Acta Biotheoretica 19, Galen, C. & Plowright, R.C. (1985) The effects of nectar level and flower development on pollen carry over in inflorescences of fireweed (Epilobium angustifolium) (Onagraceae). Canadian Journal of Botany 63, Geber, M.A. (1985) The relationship of plant size to selfpollination in Mertensia cliata. Ecology 66, Gori, D.F. (1989) Floral color change in Lupinus argenteus (Fabaceae): why should plants advertise the location of unrewarding flowers to pollinators? Evolution 43, Goulson, D. (2000) Why do pollinators visit proportionally fewer flowers in large patches? Oikos 91, Harder, L.D. & Barrett, S.C.H. (1995) Mating cost of large floral displays in hermaphrodite plants. Nature 373, Harder, L.D. & Barrett, S.C.H. (1996) Ecology of geitonogamous pollination. Floral Biology (eds D. G. Lloyd & S. C. H. Barrett), pp Chapman & Hall, New York, NY. Heinrich, B. (1979) Resource heterogeneity and patterns of movement in foraging bumblebees. Oecologia 40, Hodges, C.M. (1981) Optimal foraging in bumblebees: hunting by expectation. Animal Behaviour 29, Hodges, C.M. (1985) Bumble bee foraging: energetic consequences of using a threshold departure rule. Ecology 66, Iwasa, Y., de Jong, T.J. & Klinkhamer, P.G.L. (1995) Why pollinators visit only a fraction of the open flowers on a plant: the plant s point of view. Journal of Evolutionary Biology 8, Iwasa, Y., Higashi, M. & Yamamura, N. (1981) Prey distribution as a factor determining the choice of optimal foraging strategy. American Naturalist 117, de Jong, T.J., Waser, N.M. & Klinkhamer, P.G.L. (1993) Geitonogamy: the neglected side of selfing. Trends in Ecology and Evolution 8, Kasuya, E. (2001) Mann Whitney U test when variances are unequal. Animal Behaviour 61 (1247), Kennedy, M. & Gray, R.D. (1993) Can ecological theory predict the distribution of foraging animals? Oikos 68, Klinkhamer, P.G. & de Jong, T.J. (1990) Effects of plant size, plant density, and sex differential nectar reward on pollinator visitation in the protandrous Echium vulgare (Boraginaceae). Oikos 57 (399), 405. Klinkhamer, P.G.L., de Jong, T.J. & Bruyn, G.-J. (1989) Plant size and pollinator visitation in Cynoglossum officinale. Oikos 54, Kunin, W.E. (1993) Sex and the single mustard: population density and pollinator behavior effects on seed-set. Ecology 74, Kunin, W.E. (1997) Population size and density effects in pollination: pollinator foraging and plant reproductive success in experimental arrays of Brassica kaber. Journal of Ecology 85, McNamara, J. & Houston, A. (1980) The application of statistical decision theory to animal behaviour. Journal of Theoretical Biology 85, Menzel, R., Geiger, K., Chittka, L., Joerges, J., Kunze, J. & Mueller, U. (1996) The knowledge base of bee navigation. Journal of Experimental Biology 199, Milinski, M. (1994) Ideal free theory predicts more than only input matching a critique of Kennedy and Gray s review. Oikos 71, Motro, U. & Shmida, A. (1995) Near far search: an evolutionarily stable foraging strategy. Journal of Theoretical Biology 173, Nash, J.C. & Walker-Smith, M. (1987) Nonlinear Parameter Estimation: An Integrated Sysytem in basic. Marcel Dekker, New York, NY. Nelder, J.A. & Mead, R. (1965) A simplex-method for function minimization. Computer Journal 7, Oberrath, R. & Böhning-Gaese, K. (1999) Floral color change and the attraction of insect pollinators in lungwort (Pulmonaria collina). Oecologia 121, Ohara, M. & Higashi, S. (1994) Effects of inflorescence size on visits from pollinators and seed set of Corydalis ambigua (Papaveraceae). Oecologia 98, Ohashi, K. & Yahara, T. (1998) Effects of variation in flower number on pollinator visits in Cirsium purpuratum (Asteraceae). American Journal of Botany 85, Ohashi, K. & Yahara, T. (1999) How long to stay on, and how often to visit a flowering plant? A model for foraging strategy when floral displays vary in size. Oikos 86, Ohashi, K. & Yahara, T. (2001) Behavioral responses of pollinators to variation in floral display size and their influences on the evolution of floral traits. Cognitive Ecology of Pollination (eds L. Chittka & J. D. Thomson), pp Cambridge University Press, New York, NY. Parker, G.A. & Sutherland, W.J. (1986) Ideal free distributions when individuals differ in competitive ability phenotypelimited ideal free models. Animal Behaviour 34, Pleasants, J.M. & Zimmerman, M. (1990) The effect of inflorescence size on pollinator visitation of Delphinium nelsonii and Aconitum columbianum. Collectanea Botanica 19, Pyke, G.H. (1978) Optimal foraging in hummingbirds: testing the marginal value theorem. American Zoologist 18, Pyke, G.H. (1979) Optimal foraging in bumblebees: rule of movement between flowers within inflorescences. Animal Behaviour 27, Pyke, G.H. (1981) Honeyeater foraging: a test of optimal foraging theory. Animal Behaviour 29 (878), 888. Pyke, G.H. (1982) Foraging in bumblebees: rule of departure from an inflorescence. Canadian Journal of Zoology 60, Rademaker, M.C.J. & de Jong, T.J. (1998) Effects of flower number on estimated pollen transfer in natural populations of three hermaphroditic species: an experiment with fluorescent dye. Journal of Evolutionary Biology 11, Redmond, D. & Plowright, C.M.S. (1996) Flower revisitation by foraging bumble bees: the effects of landmarks and floral arrangement. Journal of Apicultural Research 35, Richards, A.J. (1986) Plant Breeding Systems. George Allen & Unwin, London. Robertson, A.W. (1992) The relationship between floral display size, pollen carryover and geitonogamy in Myosotis colensoi (Kirk) Macbride (Boraginaceae). Biological Journal of the Linnean Society 46, Robertson, A.W. & Macnair, M.R. (1995) The effects of floral display size on pollinator service to individual flowers of Myosotis and Mimulus. Oikos 72, Robertson, A.W., Mountjoy, C., Faulkner, B.E., Roberts, M.V. & Macnair, M.R. (1999) Bumble bee selection of Mimulus guttatus flowers: the effects of pollen quality and reward depletion. Ecology 80, Sih, A. & Baltus, M.S. (1987) Patch size pollinator behavior and pollinator limitation in catnip. Ecology 68, Sokal, R.R. & Rohlf, F.J. (1995) Biometry, 3rd edn. W.H. Freeman, New York, NY. Thomson, J.D. (1988) Effects of variation in inflorescence size and floral rewards on the visitation rates of traplining pollinators of Aralia hispida. Evolutionary Ecology 2,

J. M. GRINDELAND,* N. SLETVOLD and R. A. IMS. Department of Biology, University of Oslo, PO Box 1066 Blindern, N-0316 Oslo, Norway

J. M. GRINDELAND,* N. SLETVOLD and R. A. IMS. Department of Biology, University of Oslo, PO Box 1066 Blindern, N-0316 Oslo, Norway Functional Ecology 2005 Effects of floral display size and plant density on pollinator Blackwell Publishing, Ltd. visitation rate in a natural population of Digitalis purpurea J. M. GRINDELAND,* N. SLETVOLD

More information

Department of Biological Science, University of Calgary, Alberta, Canada T2N 1N4

Department of Biological Science, University of Calgary, Alberta, Canada T2N 1N4 Functional Ecology 2006 Floral display size influences subsequent plant choice Blackwell Publishing Ltd by bumble bees H. S. ISHII Department of Biological Science, University of Calgary, Alberta, Canada

More information

האוניברסיטה העברית בירושלים

האוניברסיטה העברית בירושלים האוניברסיטה העברית בירושלים THE HEBREW UNIVERSITY OF JERUSALEM VARIABILITY IN NECTAR PRODUCTION AND YIELD, AND THEIR RELATION TO POLLINATOR VISITS, IN A MEDITERRANEAN SHRUB by TAMAR KEASAR, ADI SADEH and

More information

Variability in nectar production and standing crop, and their relation to pollinator visits in a Mediterranean shrub

Variability in nectar production and standing crop, and their relation to pollinator visits in a Mediterranean shrub Arthropod-Plant Interactions (2008) 2:117 DOI 10.1007/s11829-008-9040-9 ORIGINAL PAPER Variability in nectar production and standing crop, and their relation to pollinator visits in a Mediterranean shrub

More information

Biological Applications of Game Theory

Biological Applications of Game Theory Biological Applications of Game Theory Frank Thuijsman 1 st Joint China-Dutch Seminar on Game Theory and 4 th China Meeting on Game Theory and its Applications Presentation Outline Two examples of Biological

More information

Foraging by Male and Female Solitary Bees with Implications for Pollination

Foraging by Male and Female Solitary Bees with Implications for Pollination Journal of Insect Behavior, Vol. 19, No. 3, May 2006 ( C 2006) DOI: 10.1007/s10905-006-9030-7 Foraging by Male and Female Solitary Bees with Implications for Pollination Gidi Ne eman, 1,4 Ofrit Shavit,

More information

Does the Flower Constancy of Bumble Bees Reflect Foraging Economics?

Does the Flower Constancy of Bumble Bees Reflect Foraging Economics? Ethology 110, 793 805 (2004) Ó 2004 Blackwell Verlag, Berlin ISSN 0179 1613 Does the Flower Constancy of Bumble Bees Reflect Foraging Economics? Robert J. Gegear & James D. Thomson Department of Zoology,

More information

INVESTMENT AND ALLOCATION OF NECTAR PRODUCTION IN AN ANIMAL-POLLINATED PLANT

INVESTMENT AND ALLOCATION OF NECTAR PRODUCTION IN AN ANIMAL-POLLINATED PLANT INVESTMENT AND ALLOCATION OF NECTAR PRODUCTION IN AN ANIMAL-POLLINATED PLANT Jay M. Biernaskie B.Sc. Biological Sciences, University of Lethbridge 200 1 THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS

More information

removal in hermaphrodite flowers

removal in hermaphrodite flowers Functional Ecology 2003 Anther arrangement influences pollen deposition and Blackwell Publishing Ltd. removal in hermaphrodite flowers G. KUDO Graduate School of Environmental Earth Science, Hokkaido University,

More information

Bumble bee preference for flowers arranged on

Bumble bee preference for flowers arranged on Functional Ecology 2008, 22, 1027 1032 doi: 10.1111/j.1365-2435.2008.01473.x Bumble bee preference for flowers arranged on Blackwell Publishing Ltd a horizontal plane versus inclined planes T. T. Makino*

More information

Selfing rates in natural populations of Echium vulgare: a combined empirical and model approach

Selfing rates in natural populations of Echium vulgare: a combined empirical and model approach Functional Ecology 1999 ORIGINAL ARTICLE OA 000 EN Selfing rates in natural populations of Echium vulgare: a combined empirical and model approach M. C. J. RADEMAKER, T. J. DE JONG and E. VAN DER MEIJDEN

More information

Floral and inflorescence effects on variation in pollen. removal and seed production among six legume species. G. KUDO* and L. D.

Floral and inflorescence effects on variation in pollen. removal and seed production among six legume species. G. KUDO* and L. D. Functional Ecology 2005 Floral and inflorescence effects on variation in pollen Blackwell Publishing, Ltd. removal and seed production among six legume species G. KUDO* and L. D. HARDER *Graduate School

More information

Beyond floricentrism: The pollination function of inflorescences

Beyond floricentrism: The pollination function of inflorescences Blackwell Science, LtdOxford, UKPSBPlant Species Biology0913-557X2004 The Society for the Study of Species BiologyDecember 2004193137148Invited ArticlePOLLI- NATION FUNCTION OF INFLORESCENCESL. D. HARDER

More information

The spatial distribution of nonrewarding artificial flowers affects pollinator attraction

The spatial distribution of nonrewarding artificial flowers affects pollinator attraction ANIMAL BEHAVIOUR, 2000, 60, 639 646 doi:10.1006/anbe.2000.1484, available online at http://www.idealibrary.com on The spatial distribution of nonrewarding artificial flowers affects pollinator attraction

More information

Inflorescence architecture affects pollinator behaviour and mating success in Spiranthes sinensis (Orchidaceae)

Inflorescence architecture affects pollinator behaviour and mating success in Spiranthes sinensis (Orchidaceae) Research Inflorescence architecture affects pollinator behaviour and mating success in Spiranthes sinensis (Orchidaceae) Tatsunori Iwata 1, Osamu Nagasaki 2, Hiroshi S. Ishii 3 and Atushi Ushimaru 1 1

More information

Pollination Lab Bio 220 Ecology and Evolution Fall, 2016

Pollination Lab Bio 220 Ecology and Evolution Fall, 2016 Pollination Lab Bio 220 Ecology and Evolution Fall, 2016 Journal reading: Comparison of pollen transfer dynamics by multiple floral visitors: experiments with pollen and fluorescent dye Introduction: Flowers

More information

Community Involvement in Research Monitoring Pollinator Populations using Public Participation in Scientific Research

Community Involvement in Research Monitoring Pollinator Populations using Public Participation in Scientific Research Overview Community Involvement in Research Monitoring Pollinator Populations using Public Participation in Scientific Research Public Participation in Scientific Research (PPSR) is a concept adopted by

More information

Simulation of Floral Specialization in Bees

Simulation of Floral Specialization in Bees Simulation of Floral Specialization in Bees Dan Ashlock Mathematics Department Iowa State University Ames, Iowa 511 danwell@iastate.edu Jessica Oftelie Mathematics Department Iowa State University Ames,

More information

Oecologia. How and why do nectar-foraging bumblebees initiate movements between inflorescences of wild bergamot Monarda tistulosa (Lamiaceae)?

Oecologia. How and why do nectar-foraging bumblebees initiate movements between inflorescences of wild bergamot Monarda tistulosa (Lamiaceae)? Oecologia (1990) 82: 450-460 Oecologia 9 Springer-Verlag 1990 How and why do nectar-foraging bumblebees initiate movements between inflorescences of wild bergamot Monarda tistulosa (Lamiaceae)? James E.

More information

The use of conspecific and interspecific scent marks by foraging bumblebees and honeybees

The use of conspecific and interspecific scent marks by foraging bumblebees and honeybees ANIMAL BEHAVIOUR, 21, 62, 183 189 doi:1.16/anbe.21.1729, available online at http://www.idealibrary.com on The use of conspecific and interspecific scent marks by foraging bumblebees and honeybees JANE

More information

KAISA MUSTAJÄRVI, PIRKKO SIIKAMÄKI*, SAARA RYTKÖNEN and ANTTI LAMMI

KAISA MUSTAJÄRVI, PIRKKO SIIKAMÄKI*, SAARA RYTKÖNEN and ANTTI LAMMI Journal of Ecology 2001 Consequences of plant population size and density for Blackwell Science, Ltd plant pollinator interactions and plant performance KAISA MUSTAJÄRVI, PIRKKO SIIKAMÄKI*, SAARA RYTKÖNEN

More information

Patch departure rules in Bumblebees: evidence of a decremental motivational mechanism

Patch departure rules in Bumblebees: evidence of a decremental motivational mechanism Behav Ecol Sociobiol (2007) 61:1707 1715 DOI 10.1007/s00265-007-0402-6 ORIGINAL PAPER Patch departure rules in Bumblebees: evidence of a decremental motivational mechanism Diane Lefebvre & Jacqueline Pierre

More information

The ideal free distribution: an analysis of the perceptual limit model

The ideal free distribution: an analysis of the perceptual limit model Evolutionary Ecology Research, 2002, 4: 471 493 The ideal free distribution: an analysis of the perceptual limit model Edmund J. Collins,* Alasdair I. Houston and Alison Lang Centre for Behavioural Biology,

More information

In-hive pollen transfer between bees enhances cross-pollination of plants

In-hive pollen transfer between bees enhances cross-pollination of plants In-hive pollen transfer between bees enhances cross-pollination of plants J. Paalhaar, W.J. Boot, J.J.M. van der Steen* & J.N.M. Calis Laboratory of Entomology, Wageningen University, PO Box 803, 6700

More information

Behavior of Pollinators That Share Two Co- Flowering Wetland Plant Species

Behavior of Pollinators That Share Two Co- Flowering Wetland Plant Species The University of Akron IdeaExchange@UAkron Honors Research Projects The Dr. Gary B. and Pamela S. Williams Honors College Spring 2015 Behavior of Pollinators That Share Two Co- Flowering Wetland Plant

More information

RESEARCH NOTE: NECTAR CONTENT OF NEW ZEALAND HASS AVOCADO FLOWERS AT DIFFERENT FLORAL STAGES

RESEARCH NOTE: NECTAR CONTENT OF NEW ZEALAND HASS AVOCADO FLOWERS AT DIFFERENT FLORAL STAGES New Zealand Avocado Growers' Association Annual Research Report 2004. 4:25 31. RESEARCH NOTE: NECTAR CONTENT OF NEW ZEALAND HASS AVOCADO FLOWERS AT DIFFERENT FLORAL STAGES J. DIXON AND C. B. LAMOND Avocado

More information

Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and

Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere

More information

UNIVERSITY OF CALGARY. foraging by bumble bees. Paul A Simpson A THESIS SUBMITTED TO THE FACULTY OF GRADUATE STUDIES

UNIVERSITY OF CALGARY. foraging by bumble bees. Paul A Simpson A THESIS SUBMITTED TO THE FACULTY OF GRADUATE STUDIES UNIVERSITY OF CALGARY The effects of structured variation in nectar standing crop on currency choice and optimal foraging by bumble bees by Paul A Simpson A THESIS SUBMITTED TO THE FACULTY OF GRADUATE

More information

Experimental Design, Data, and Data Summary

Experimental Design, Data, and Data Summary Chapter Six Experimental Design, Data, and Data Summary Tests of Hypotheses Because science advances by tests of hypotheses, scientists spend much of their time devising ways to test hypotheses. There

More information

GENERAL CURRICULUM MULTI-SUBJECT SUBTEST

GENERAL CURRICULUM MULTI-SUBJECT SUBTEST GENERAL CURRICULUM MULTI-SUBJECT SUBTEST SUPPLEMENTAL SAMPLE OPEN-RESPONSE ITEM WITH SAMPLE RESPONSES AND ANALYSES NOTE: This sample open-response item is provided as a supplement to the Test Information

More information

PREDATOR AND PREY HABITAT SELECTION GAMES: THE EFFECTS OF HOW PREY BALANCE FORAGING AND PREDATION RISK

PREDATOR AND PREY HABITAT SELECTION GAMES: THE EFFECTS OF HOW PREY BALANCE FORAGING AND PREDATION RISK ISRAEL JOURNAL OF ZOOLOGY, Vol. 50, 2004, pp. 233 254 PREDATOR AND PREY HABITAT SELECTION GAMES: THE EFFECTS OF HOW PREY BALANCE FORAGING AND PREDATION RISK BARNEY LUTTBEG* AND ANDREW SIH Department of

More information

Stability Analyses of the 50/50 Sex Ratio Using Lattice Simulation

Stability Analyses of the 50/50 Sex Ratio Using Lattice Simulation Stability Analyses of the 50/50 Sex Ratio Using Lattice Simulation Y. Itoh, K. Tainaka and J. Yoshimura Department of Systems Engineering, Shizuoka University, 3-5-1 Johoku, Hamamatsu 432-8561 Japan Abstract:

More information

Chapter 24-Flowering Plant and Animal Coevolution

Chapter 24-Flowering Plant and Animal Coevolution Chapter 24-Flowering Plant and Animal Coevolution coevolutionary plant-animal associations alliances that have influenced the evoluton of both partners. These examples show that plants have acquired traits

More information

Flower Power!! Background knowledge material and dissection directions.

Flower Power!! Background knowledge material and dissection directions. Flower Power!! Background knowledge material and dissection directions. 96 Plant Dissection 3.2 Plants Essential Question: Why do plants have flowers? Questions: As you read the lab background, complete

More information

Reproductive ecology and conservation of the rare Dictamnus

Reproductive ecology and conservation of the rare Dictamnus Reproductive ecology and conservation of the rare Dictamnus Alessandro Fisogni, Martina Rossi, Giovanni Cristofolini & Marta Galloni Department of Experimental Evolutionary Biology, University of Bologna

More information

U.S. Fish & Wildlife Service. Attracting Pollinators to Your Garden

U.S. Fish & Wildlife Service. Attracting Pollinators to Your Garden U.S. Fish & Wildlife Service Attracting Pollinators to Your Garden Why are Pollinators Important? Pollinators are nearly as important as sunlight, soil and water to the reproductive success of over 75%

More information

Insect Size and Foraging Distances for Insects Visiting Eryngium yuccifolium. Final Report to Litzsinger Road Ecology Center. By: Valerie Slegesky

Insect Size and Foraging Distances for Insects Visiting Eryngium yuccifolium. Final Report to Litzsinger Road Ecology Center. By: Valerie Slegesky Insect Size and Foraging Distances for Insects Visiting Eryngium yuccifolium Final Report to Litzsinger Road Ecology Center By: Valerie Slegesky ----------------------------------------------------------------------------------------------------------------

More information

BUMBLE BEE SELECTION OF MIMULUS GUTTATUS FLOWERS: THE EFFECTS OF POLLEN QUALITY AND REWARD DEPLETION

BUMBLE BEE SELECTION OF MIMULUS GUTTATUS FLOWERS: THE EFFECTS OF POLLEN QUALITY AND REWARD DEPLETION Ecology, 80(8), 999, pp. 2594 2606 999 by the Ecological Society of America BUMBLE BEE SELECTION OF MIMULUS GUTTATUS FLOWERS: THE EFFECTS OF POLLEN QUALITY AND REWARD DEPLETION ALASTAIR W. ROBERTSON, CLAIRE

More information

Evolutionary Ecology of Social Interactions Among Plants

Evolutionary Ecology of Social Interactions Among Plants Evolutionary Ecology of Social Interactions Among Plants by Jay Michael Biernaskie A thesis submitted in conformity with the requirements for the degree of Doctor of Philosophy Ecology and Evolutionary

More information

Each copy of any part of a JSTOR transmission must contain the same copyright notice that appears on the screen or printed page of such transmission.

Each copy of any part of a JSTOR transmission must contain the same copyright notice that appears on the screen or printed page of such transmission. Bumblebee Response to Variation in Nectar Availability Author(s): John M. Pleasants Source: Ecology, Vol. 62, No. 6 (Dec., 1981), pp. 1648-1661 Published by: Ecological Society of America Stable URL: http://www.jstor.org/stable/1941519

More information

Plant hormones: a. produced in many parts of the plant b. have many functions

Plant hormones: a. produced in many parts of the plant b. have many functions Plant hormones: a. produced in many parts of the plant b. have many functions Illustrated with 4 plant hormones: Gibberellins Auxin Cytokinins Ethylene Gibberellins Gibberellins illustrate how plant hormones

More information

Sex, Bugs, and Pollen s Role

Sex, Bugs, and Pollen s Role Sex, Bugs, and Pollen s Role Principle of Plant Biology #4 Reproduction in flowering plants takes place sexually, resulting in the production of a seed. Reproduction can also occur via asexual reproduction.

More information

BIOL 305L Spring 2018 Laboratory Seven

BIOL 305L Spring 2018 Laboratory Seven Please print Full name clearly: BIOL 305L Spring 2018 Laboratory Seven Flowering and reproduction Introduction Flowers are not simple structures, and the diversity of flower shape, color, and fragrance

More information

Effects of fragmentation on pollen and gene flow in insect-pollinated plant populations Velterop, Odilia

Effects of fragmentation on pollen and gene flow in insect-pollinated plant populations Velterop, Odilia University of Groningen Effects of fragmentation on pollen and gene flow in insect-pollinated plant populations Velterop, Odilia IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's

More information

Overnight memory retention of foraging skills by bumblebees is imperfect

Overnight memory retention of foraging skills by bumblebees is imperfect Overnight memory retention of foraging skills by bumblebees is imperfect T. Keasar, U. Motro, Y. Shur and A. Shmida 1996 Animal Behavior 52:95-104 Anim. Behav., 1996, 52, 95 104 Overnight memory retention

More information

FLOWERS AND POLLINATION. This activity introduces the relationship between flower structures and pollination.

FLOWERS AND POLLINATION. This activity introduces the relationship between flower structures and pollination. FLOWERS AND POLLINATION This activity introduces the relationship between flower structures and pollination. Objectives for Exam #1 1. Identify flower structures and match those structures to specific

More information

Oecologia. Remote perception of floral nectar by bumblebees. Oecologia (Berlin) (1984) 64: Springer-Verlag 1984

Oecologia. Remote perception of floral nectar by bumblebees. Oecologia (Berlin) (1984) 64: Springer-Verlag 1984 Oecologia (Berlin) (1984) 64:232-240 Oecologia 9 Springer-Verlag 1984 Remote perception of floral nectar by bumblebees James H. Marden Department of Zoology, University of Vermont, Burlington, VT 05405,

More information

Natal versus breeding dispersal: Evolution in a model system

Natal versus breeding dispersal: Evolution in a model system Evolutionary Ecology Research, 1999, 1: 911 921 Natal versus breeding dispersal: Evolution in a model system Karin Johst 1 * and Roland Brandl 2 1 Centre for Environmental Research Leipzig-Halle Ltd, Department

More information

PhD/ MSc: Investigating handedness in flowers

PhD/ MSc: Investigating handedness in flowers PhD/ MSc: Investigating handedness in flowers Left handed Right handed Figure 1. Left and right handed morphs of Wachendorfia paniculata The primary function of flowers is to mediate the movement of pollen.

More information

of gynodioecious Thymus vulgaris L.

of gynodioecious Thymus vulgaris L. Journal of Ecology 2004 Temporal variation in sex allocation in hermaphrodites Blackwell Publishing, Ltd. of gynodioecious Thymus vulgaris L. BODIL K. EHLERS and JOHN D. THOMPSON Centre d Ecologie Fonctionelle

More information

6.1 Pollen-ovule ratios and Charnov s model

6.1 Pollen-ovule ratios and Charnov s model Chapter 6 Synthesis In this chapter I discuss the results obtained in chapters 2 to 5 and highlight the most important findings. Throughout this chapter, I point out which further approaches in studying

More information

Heredity.. An Introduction Unit 5: Seventh Grade

Heredity.. An Introduction Unit 5: Seventh Grade Heredity.. An Introduction Unit 5: Seventh Grade Why don t you look like a rhinoceros? The answer seems simple --- neither of your parents is a rhinoceros (I assume). But there is more to this answer than

More information

Case Studies in Ecology and Evolution

Case Studies in Ecology and Evolution 3 Non-random mating, Inbreeding and Population Structure. Jewelweed, Impatiens capensis, is a common woodland flower in the Eastern US. You may have seen the swollen seed pods that explosively pop when

More information

Does Individual Flower Density and Patch Level Conspecific Neighbor Density Affect Reproductive Success in a 'Golden Banner' Legume (FABACEAE)?

Does Individual Flower Density and Patch Level Conspecific Neighbor Density Affect Reproductive Success in a 'Golden Banner' Legume (FABACEAE)? University of Colorado, Boulder CU Scholar Undergraduate Honors Theses Honors Program Spring 2012 Does Individual Flower Density and Patch Level Conspecific Neighbor Density Affect Reproductive Success

More information

NGSS Example Bundles. Page 1 of 23

NGSS Example Bundles. Page 1 of 23 High School Conceptual Progressions Model III Bundle 2 Evolution of Life This is the second bundle of the High School Conceptual Progressions Model Course III. Each bundle has connections to the other

More information

What factors limit fruit production in the lowbush blueberry, Vaccinium angustifolium? Melissa Fulton and Linley Jesson University of New Brunswick

What factors limit fruit production in the lowbush blueberry, Vaccinium angustifolium? Melissa Fulton and Linley Jesson University of New Brunswick What factors limit fruit production in the lowbush blueberry, Vaccinium angustifolium? Melissa Fulton and Linley Jesson University of New Brunswick Barriers to fruit production Pollinator abundance -specialists

More information

Crowding in Brassica rapa. Deanna Hall

Crowding in Brassica rapa. Deanna Hall Crowding in Brassica rapa Deanna Hall Bio 493 March 24, 26 Crowding in Brassica rapa Deanna Hall Abstract Wisconsin Fast plants (Brassica rapa) were grown in four different densities of one, two, three

More information

Oilseed rape pollen dispersal by insect pollinators in agricultural landscape

Oilseed rape pollen dispersal by insect pollinators in agricultural landscape Oilseed rape pollen dispersal by insect pollinators in agricultural landscape R. Chifflet, B. Vaissière, A. Ricroch, E. Klein, C. Lavigne, J. Lecomte Good afternoon, my name is Rémy Chifflet and I am a

More information

Traplining in bumblebees (Bombus impatiens): a foraging strategy s ontogeny and the importance of spatial reference memory in short-range foraging

Traplining in bumblebees (Bombus impatiens): a foraging strategy s ontogeny and the importance of spatial reference memory in short-range foraging Oecologia (007) 151:719 730 DOI 10.1007/s0044-006-0607-9 BEHAVIORAL ECOLOGY Traplining in bumblebees (Bombus impatiens): a foraging strategy s ontogeny and the importance of spatial reference memory in

More information

Trapline foraging by bumble bees: V. Effects of experience and priority on competitive performance

Trapline foraging by bumble bees: V. Effects of experience and priority on competitive performance Behavioral Ecology doi:10.1093/beheco/arn048 Advance Access publication 30 May 2008 Trapline foraging by bumble bees: V. Effects of experience and priority on competitive performance Kazuharu Ohashi, a

More information

Bees: The most important pollinators

Bees: The most important pollinators Bees: The most important pollinators Bees are complete vegans: All food comes from plants Nectar and pollen from flowers What makes bees effective pollinators: One of the very few insect groups that purposefully

More information

Levels of Ecological Organization. Biotic and Abiotic Factors. Studying Ecology. Chapter 4 Population Ecology

Levels of Ecological Organization. Biotic and Abiotic Factors. Studying Ecology. Chapter 4 Population Ecology Chapter 4 Population Ecology Lesson 4.1 Studying Ecology Levels of Ecological Organization Biotic and Abiotic Factors The study of how organisms interact with each other and with their environments Scientists

More information

Chapter 4 Population Ecology

Chapter 4 Population Ecology Chapter 4 Population Ecology Lesson 4.1 Studying Ecology Levels of Ecological Organization The study of how organisms interact with each other and with their environments Scientists study ecology at various

More information

Lesson: Why a Butterfly Garden? Seeking Pollinator Certification for a Butterfly Garden

Lesson: Why a Butterfly Garden? Seeking Pollinator Certification for a Butterfly Garden Lesson: Why a Butterfly Garden? Seeking Pollinator Certification for a Butterfly Garden What is the primary threat to most endangered species? Why is our butterfly and pollinator population declining?

More information

Introduction to Genetics

Introduction to Genetics Introduction to Genetics The Work of Gregor Mendel B.1.21, B.1.22, B.1.29 Genetic Inheritance Heredity: the transmission of characteristics from parent to offspring The study of heredity in biology is

More information

EFFECTS OF FLORAL DISPLAY SIZE AND BIPARENTAL

EFFECTS OF FLORAL DISPLAY SIZE AND BIPARENTAL American Journal of Botany 94(10): 1696 1705. 2007. EFFECTS OF FLORAL DISPLAY SIZE AND BIPARENTAL INBREEDING ON OUTCROSSING RATES IN DELPHINIUM BARBEYI (RANUNCULACEAE) 1 CHARLES F. WILLIAMS 2 Department

More information

Optimal Foraging in Hummingbirds: Testing the Marginal Value Theorem

Optimal Foraging in Hummingbirds: Testing the Marginal Value Theorem AMER. Zooi... 18:739-752(1978). Optimal Foraging in Hummingbirds: Testing the Marginal Value Theorem GRAHAM H.PYKE Department of Biology, University of Utah, Salt Lake City, Utah 84112 SYNOPSIS. To a hummingbird,

More information

Ch16.xls. Wrap-up. Many of the analyses undertaken in biology are concerned with counts.

Ch16.xls. Wrap-up. Many of the analyses undertaken in biology are concerned with counts. Model Based Statistics in Biology. Part V. The Generalized Linear Model. Analysis of Count Data ReCap. Part I (Chapters 1,2,3,4), Part II (Ch 5, 6, 7) ReCap Part III (Ch 9, 10, 11), Part IV (Ch13, 14,

More information

Oikos. Appendix A1. o20830

Oikos. Appendix A1. o20830 1 Oikos o20830 Valdovinos, F. S., Moisset de Espanés, P., Flores, J. D. and Ramos-Jiliberto, R. 2013. Adaptive foraging allows the maintenance of biodiversity of pollination networks. Oikos 122: 907 917.

More information

The Evolution of Empty Flowers

The Evolution of Empty Flowers Z theor BioL (1986) 118, 253-258 The Evolution of Empty Flowers GRAHAM BELL Biology Department, McGill University, 1205 Avenue Dr. Penfield, Montreal, Quebec, Canada H3A 1B1 (Received 3 January 1985) This

More information

Diversity partitioning without statistical independence of alpha and beta

Diversity partitioning without statistical independence of alpha and beta 1964 Ecology, Vol. 91, No. 7 Ecology, 91(7), 2010, pp. 1964 1969 Ó 2010 by the Ecological Society of America Diversity partitioning without statistical independence of alpha and beta JOSEPH A. VEECH 1,3

More information

Presence of two types of flowers with respect to nectar sugar in two gregariously flowering species

Presence of two types of flowers with respect to nectar sugar in two gregariously flowering species Two types of fl owers with respect to nectar 769 Presence of two types of flowers with respect to nectar sugar in two gregariously flowering species CHAITALI ANAND, CHAITRALI UMRANIKAR, POOJA SHINTRE,

More information

INTERSPECIFIC COMPETITION FOR POLLINATION LOWERS SEED PRODUCTION AND OUTCROSSING IN MIMULUS RINGENS

INTERSPECIFIC COMPETITION FOR POLLINATION LOWERS SEED PRODUCTION AND OUTCROSSING IN MIMULUS RINGENS Ecology, 86(3), 2005, pp. 762 771 2005 by the Ecological Society of America INTERSPECIFIC COMPETITION FOR POLLINATION LOWERS SEED PRODUCTION AND OUTCROSSING IN MIMULUS RINGENS JOHN M. BELL, 1,3 JEFFREY

More information

COVARIANCE ANALYSIS. Rajender Parsad and V.K. Gupta I.A.S.R.I., Library Avenue, New Delhi

COVARIANCE ANALYSIS. Rajender Parsad and V.K. Gupta I.A.S.R.I., Library Avenue, New Delhi COVARIANCE ANALYSIS Rajender Parsad and V.K. Gupta I.A.S.R.I., Library Avenue, New Delhi - 110 012 1. Introduction It is well known that in designed experiments the ability to detect existing differences

More information

SUMMER NECTAR AND FLORAL SOURCES

SUMMER NECTAR AND FLORAL SOURCES Apiculture Factsheet Ministry of Agriculture http://www.al.gov.bc.ca/apiculture Factsheet #905 SUMMER NECTAR AND FLORAL SOURCES In some parts of British Columbia, a dearth period occurs following initial

More information

An assessment of Vicia faba and Trifolium pratense as forage crops for Bombus hortorum

An assessment of Vicia faba and Trifolium pratense as forage crops for Bombus hortorum An assessment of Vicia faba and Trifolium pratense as forage crops for Bombus hortorum B. BROWN* AND R. R. SCOTT Department of Entomology, P.O. Box 84, Lincoln University, New Zealand R. P. MACFARLANE

More information

Niche The sum of all interactions a species has with biotic/abiotic components of the environment N-dimensional hypervolume

Niche The sum of all interactions a species has with biotic/abiotic components of the environment N-dimensional hypervolume Niche The sum of all interactions a species has with biotic/abiotic components of the environment N-dimensional hypervolume Each dimension is a biotic or abiotic resource Ecomorphology Ecology (niche)

More information

California Fuchsia Onagraceae Evening Primrose Family Epilobium canum

California Fuchsia Onagraceae Evening Primrose Family Epilobium canum 6. California Fuchsia Onagraceae Evening Primrose Family Epilobium canum California Fuchsia, also known as Hummingbird Flower, Hummingbird Trumpet, and Firechalice, is a species of willowherb that is native

More information

COMPARISON OF FORAGING ACTIVITY BETWEEN MASON BEE OSMIA ORIENTALIS

COMPARISON OF FORAGING ACTIVITY BETWEEN MASON BEE OSMIA ORIENTALIS Volume 125, Number 5, March 2016 363 COMPARISON OF FORAGING ACTIVITY BETWEEN MASON BEE OSMIA ORIENTALIS (HYMENOPTERA: MEGACHILIDAE) AND HONYBEES FOR WILD RASP- BERRY RUBUS HIRSUTUS (ROSALES: ROSACEAE)

More information

Pollinator Adaptations

Pollinator Adaptations Adapted from: Life Lab Garden Pollinators unit Pollinator Adaptations Overview: Students will learn about pollinators and their adaptations, and match flowers to the kinds of pollinators they attract.

More information

How Does Pollination Work?

How Does Pollination Work? How Does Pollination Work? What is pollination? What is pollination? Pollination the transfer of pollen from the anther of one flower to the stigma of another flower Fertilization occurs when the male

More information

Do bumble bee queens choose nest sites to maximize foraging rate?

Do bumble bee queens choose nest sites to maximize foraging rate? 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 Do bumble bee queens choose nest sites to maximize foraging rate? -Testing models of nest site selection- Yukari Suzuki, Lina G. Kawaguchi,

More information

Plant Growth & Reproduction

Plant Growth & Reproduction Water loss (ml) Water loss (ml) Water loss (ml) Water loss (ml) 4/24/2014 Plant Growth & Reproduction BI 103 Plant-Animal Systems Turn in Homework #1 Lab Wed! (schedule change) 1.2 1 0.8 0.6 0.4 no wind

More information

POLLINATION IN VERBASCUM THAPSUS (SCROPHULARIACEAE):

POLLINATION IN VERBASCUM THAPSUS (SCROPHULARIACEAE): American Journal of Botany 85(11): 1618 1625. 1998. POLLINATION IN VERBASCUM THAPSUS (SCROPHULARIACEAE): THE ADVANTAGE OF BEING TALL 1 SARAH E. DONNELLY, CHRISTOPHER J. LORTIE, AND LONNIE W. AARSSEN 2

More information

14.1. KEY CONCEPT Every organism has a habitat and a niche. 38 Reinforcement Unit 5 Resource Book

14.1. KEY CONCEPT Every organism has a habitat and a niche. 38 Reinforcement Unit 5 Resource Book 14.1 HABITAT AND NICHE KEY CONCEPT Every organism has a habitat and a niche. A habitat is all of the living and nonliving factors in the area where an organism lives. For example, the habitat of a frog

More information

The Origin of Species

The Origin of Species LECTURE PRESENTATIONS For CAMPBELL BIOLOGY, NINTH EDITION Jane B. Reece, Lisa A. Urry, Michael L. Cain, Steven A. Wasserman, Peter V. Minorsky, Robert B. Jackson Chapter 24 The Origin of Species Lectures

More information

Optimal Translocation Strategies for Threatened Species

Optimal Translocation Strategies for Threatened Species Optimal Translocation Strategies for Threatened Species Rout, T. M., C. E. Hauser and H. P. Possingham The Ecology Centre, University of Queensland, E-Mail: s428598@student.uq.edu.au Keywords: threatened

More information

11-1 The Work of Gregor Mendel. The Work of Gregor Mendel

11-1 The Work of Gregor Mendel. The Work of Gregor Mendel 11-1 The Work of Gregor Mendel The Work of Gregor Mendel Gregor Mendel s Peas! Gregor Mendel s Peas Genetics is the scientific study of heredity. " Gregor Mendel was an Austrian monk. His work was important

More information

Habitat Enhancements to Support Bees: Agriculture to Urban Research. Neal Williams Department of Entomology

Habitat Enhancements to Support Bees: Agriculture to Urban Research. Neal Williams Department of Entomology Habitat Enhancements to Support Bees: Agriculture to Urban Research Neal Williams Department of Entomology nmwilliam@ucdavis.edu Overview Bees and pollination service for agriculture Threats to native

More information

Embryo selection, abortion and inbreeding depression. I. Cynoglossum officinale (Boraginaceae).

Embryo selection, abortion and inbreeding depression. I. Cynoglossum officinale (Boraginaceae). 6 Embryo selection, abortion and inbreeding depression. I. Cynoglossum officinale (Boraginaceae). Summary Selective abortion of embryos with low potential fitness later in life might free resources for

More information

L. G. KAWAGUCHI, K. OHASHI and Y. TOQUENAGA

L. G. KAWAGUCHI, K. OHASHI and Y. TOQUENAGA Functional Ecology 2006 Do bumble bees save time when choosing novel flowers by Blackwell Publishing Ltd following conspecifics? L. G. KAWAGUCHI, K. OHASHI and Y. TOQUENAGA Integrative Environmental Sciences,

More information

Nectar Sugar Concentration as a Measure of Pollination of Alfalfa (Medicago sativa L.)

Nectar Sugar Concentration as a Measure of Pollination of Alfalfa (Medicago sativa L.) Utah State University DigitalCommons@USU All PIRU Publications Pollinating Insects Research Unit 1962 Nectar Sugar Concentration as a Measure of Pollination of Alfalfa (Medicago sativa L.) William P. Nye

More information

Assessment Schedule 2013 Biology: Demonstrate understanding of the responses of plants and animals to their external environment (91603)

Assessment Schedule 2013 Biology: Demonstrate understanding of the responses of plants and animals to their external environment (91603) NCEA Level 3 Biology (91603) 2013 page 1 of 6 Assessment Schedule 2013 Biology: Demonstrate understanding of the responses of plants and animals to their external environment (91603) Assessment Criteria

More information

HABITAT SELECTION INTRODUCTION. Objectives

HABITAT SELECTION INTRODUCTION. Objectives 25 HABITAT SELECTION In collaboration with David N. Bonter Objectives Develop a spreadsheet model of ideal-free habitat selection. Compare the ideal-free and ideal-despotic habitat selection models. INTRODUCTION

More information

Risk-Sensitive Foraging in a Patch Departure Context: A Test with Worker Bumble Bees'

Risk-Sensitive Foraging in a Patch Departure Context: A Test with Worker Bumble Bees' AMER. ZOOL., 36:447-458 (1996) Risk-Sensitive Foraging in a Patch Departure Context: A Test with Worker Bumble Bees' RALPH V. CARTAR 2 AND MARK V. ABRAHAMS Department of Zoology, University of Manitoba,

More information

Ecology is studied at several levels

Ecology is studied at several levels Ecology is studied at several levels Ecology and evolution are tightly intertwined Biosphere = the total living things on Earth and the areas they inhabit Ecosystem = communities and the nonliving material

More information

Major questions of evolutionary genetics. Experimental tools of evolutionary genetics. Theoretical population genetics.

Major questions of evolutionary genetics. Experimental tools of evolutionary genetics. Theoretical population genetics. Evolutionary Genetics (for Encyclopedia of Biodiversity) Sergey Gavrilets Departments of Ecology and Evolutionary Biology and Mathematics, University of Tennessee, Knoxville, TN 37996-6 USA Evolutionary

More information

Stability with Inheritance in the Conditional Strategy

Stability with Inheritance in the Conditional Strategy J. theor. Biol. (1998) 192, 445 453 Stability with Inheritance in the Conditional Strategy MART R. GROSS* AND JOE REPKA * Department of Zoology, University of Toronto, 25Harbord Street, Toronto, Ontario,

More information

The upper limit for the exponent of Taylor s power law is a consequence of deterministic population growth

The upper limit for the exponent of Taylor s power law is a consequence of deterministic population growth Evolutionary Ecology Research, 2005, 7: 1213 1220 The upper limit for the exponent of Taylor s power law is a consequence of deterministic population growth Ford Ballantyne IV* Department of Biology, University

More information

Where in the world does your food come from?

Where in the world does your food come from? Pollinators come in all species, sizes, shapes and shades Where in the world does your food come from? Do you eat fruits? vegetables? nuts? seeds? grains? Where do you get them? Usually Mom or Dad go to

More information