Bees are important pollinators of many wild plants and crops and play an important role in maintaining the balance between natural ecosystems and agroecosystems (Xie & An, 2014; Ollerton, 2017; Huang & An, 2018; Toni et al., 2018). According to the Food and Agriculture Organization (FAO), 90% of the food for 146 countries is provided by more than 100 crop varieties, seventy one of which require bee pollination (Klein et al., 2007). Bee pollination directly contributes to crops by increasing their yield and improving fruit quality (Rader et al., 2012; Fijen et al., 2018). Crop species have different attributes and differ in their degree of dependence on bee pollination (Ollerton, 2017; Toni et al., 2018). Bee pollination of oil crops significantly increase seed yield and oil yield, and cross-pollination can even significantly increase yields for self-compatible crops (Abrol & Shankar, 2012). Honeybees (
The tree peony (
Based on this information, we conducted systematic research on the foraging behavior of honeybees and bumblebees and their influence on the seed yield and oil quality of oil tree peony. This study was expected to answer the following questions: 1) What are the differences in the foraging behaviors and daily activities of honeybees and bumblebees? 2) Can increasing the number of pollinating bees increase the fruit and seed yields and oil quality of oil tree peony?
The experiment was carried out in 2017 at the peony base (N 34°38′30″, E 112°39′43″, 125.5 m above sea level) in the East Garden of the Yibin District, which is one of the largest oil tree peony gardens in Luoyang city. The oil tree peony cultivar planted there is ‘Fengdan’, with an area of more than 106.7 hm2. ‘Fengdan’ peony had entered the fruiting period and was eight years old. More than 3,000 plants were used for this experiment.
In March 2017, three equally sized pollination net houses were built parallelly in an east-west direction at the oil tree peony base of Luoyang's East Garden. The net houses were 45 m long from east to west, 8 m wide from north to south, 2.1 m in wall height and 3.2 m in ridge height. The nylon mesh was made of a polyethylene material with a hole 1 mm in diameter. Each house was evenly divided into three small net rooms (15 m×8 m×3.2 m). These rooms corresponded to different pollination methods, namely, honeybee pollination (HP), ground bumblebee (
Pollination net rooms built at the oil tree peony base. A. oil tree peony base; B. the net house for the bee pollination treatment (45 m×8 m), which is equally divided into three net rooms; C. the net house without pollinating insects; D. plane graph of the pollination experiment. FC, natural field control; HP, honeybee pollination; BP, ground bumblebee pollination; BC, blank control (without pollinating insects).
When the first peony flower in a pollination net room opened, honeybees or ground bumblebees were placed inside. Honeybees were placed in the middle of each net room, 120 cm from the ground. Because there are no nectary glands in peony flowers, a sugar feeder (50% sugar water) was placed in each honeybee and bumblebee hive, and a water feeder (drinking water) was placed near the beehive. The ground bumblebee hives were placed in the middle of each net room, 30 cm from the ground, and a water feeder (drinking water) was placed near the beehive. The sugar water and drinking water were regularly replenished and replaced.
To better understand the living habits of honeybees and ground bumblebees for possible application in crop pollination in the future, their foraging behaviors and daily activities were observed.
Between April 14 and 19, 2019, when oil tree peony entered the peak flowering period, the flower visiting behaviors of the bees were observed. Using a stopwatch, the visit interval, single-flower visit time, number of single-flower visits, number of visited flowers per minute and number of stigma contacts by honeybees and ground bumblebees were studied (He, Li, & Zhang, 2012).
The foraging behavior parameters were defined as follows. Visit interval refers to the time it takes for a bee to leave the flower and visit the flower again, including the time when the bee temporarily leaves the flower to carry pollen in the air over the flowers when visiting the same flower and the time from one flower visit to another. Single-flower visit time refers to the total time it takes for a bee that fells on a flower to leave the flower, that is, the sum of the time spent on a single visit and the time spent combing the pollen over the flower when the bee temporarily leaves the flower. The number of single-flower visits refers to the number of visits per flower by bees (He, Li, & Zhang, 2012; He et al., 2019). The number of visited flowers per minute refers to the number of flowers that each bee visited per minute. The stigma contact ratio refers to the percentage of stigma contacts per flower relative to the total number of single-flower visits.
From April 14 to 16 (three consecutive days) 2019, the daily activities of the honeybees and ground humblebees in the pollination net rooms were separately observed. Due to a large population of the honeybees, it was difficult to accurately count the numbers of bees that left the nest, returned to the nest and returned to the nest with pollen during the peak period of daily activities. According to literature (He et al., 2019), their daily activities were observed based on the number of bees that visited flowers. Specifically, in each of the three net rooms with honeybees, two 2 m×2 m sample plots were established, and thirty flowers in full bloom were labeled in each sample plot. From 6:00 to 19:00, the number of bees that visited the flowers in each plot within 10 min every 30 min was recorded. In the three net rooms with ground bumblebees, the numbers of bees that left the nest, returned to the nest and returned to the nest with pollen within 10 min every 30 min were counted (An et al., 2007). In the meantime, the temperature and relative humidity near the nest entrance of the honeybees and ground bumblebees were recorded during different time intervals with a hand-held meteorological instrument (Kestrel 3000).
In early August, the follicles of oil tree peony were harvested (most of the follicles were a golden color). During a single-fruit harvest, the picked fruit was wrapped in newspaper, the fruit follicles of each plant were placed in a single nylon mesh bag, and the follicles of each net were placed in a single woven mesh bag. In the laboratory, the fruit follicles were placed on a ventilated and transparent balcony and matured for approximately fifteen days. After the follicles naturally cracked, the number of fruits per plant, the number and weight of seeds per follicle, and the number and weight of seeds per plant from the different pollination treatments were determined. Finally, the seed yield under different pollination treatments was calculated.
The kernel percentage of peony seeds was determined by manual peeling, and 100 seeds were taken from each sample. This process was repeated three times.
The oil yield of peony seeds was determined by a supercritical CO2 extractor (HA220-50-06; Huaan, Nantong, China). The extraction conditions were as follows: extraction II: 40°C, 30 MPa; separation I: 40°C, 10 MPa; separation II: 35°C, 5 MPa; sample volume: 200 g; and sample material: peony kernel powder that passed through a sieve of 20–40 mesh per inch (approximately 0.42–0.84 mm).
The fatty acid content of peony seed oil was determined by gas chromatography (Agilent-7890, USA). The specific method followed GB 5009.168-2016 (2016) in the national food safety standards. Peony seed oil fatty acid content was determined by the Agricultural Products Quality Supervision and Inspection Center (Zhengzhou) of the Ministry of Agriculture.
Statistical analysis of the data was performed using SPSS 20.0. Graphs were produced using Origin 2018 software. The Pearson correlation method in SPSS 20.0 software was used to analyze the correlation between the number of single-flower visits and the number of stigma contacts for the honeybees and ground bumblebees on oil tree peony. Measurement data are presented as the mean ± standard error, and categorical data are expressed as percentages. Homogeneity of variances was tested using Levene's method. Independent t tests were used to compare the single-flower visit time, visit interval and number of visited flowers per minute between the honeybees and the ground bumblebees. The number of fruits per plant, number and weight of seeds per follicle, and number and weight of seeds per plant under different pollination treatments were compared using one-way analysis of variance (ANOVA) followed by a Bonferroni test. The kernel percentages, oil yield rates and compositions of seed oil for the different pollination treatments were compared using the nonparametric Kruskal-Wallis H method followed by a Dunn's multiple comparison test.
Honeybees and ground bumblebees showed significant differences in the number of flowers visited per minute (independent-samples t test, t=9.957, F=15.313, P<0.001) (Fig. 2A), single-flower visit time (t=−3.630, F=44.502, P<0.001) (Fig. 2B), flower visit interval (t=−9.072, F=104.792, P<0.001) (Fig. 2C), and number of single-flower visits (t=3.274, F=6.592, P=0.011) (Fig. 2D).
The foraging behavior parameters of honeybees and ground bumblebees on oil tree peony flowers.
A. number of flowers visited per minute. B. single-flower visit time. C. flower visit interval. D. number of single-flower visits.
Note: The data in the figure are the means ± standard errors. *P<0.05 and **P<0.001 according to an independent-samples t test.
The number of stigma contacts per flower by honeybees was 0–7, with an average of 0.92±1.32; the stigma contact ratio of honeybees was 7.70% (n=97). Furthermore, honeybees exhibited a significant correlation between the number of single-flower visits and the number of stigma contacts per flower (Pearson r=0.212, P=0.037). The number of stigma contacts per flower by ground bumblebees was 0–5, with an average of 1.84±1.06. The stigma contact ratio of ground bumblebees was 24.11% (n=63) (Fig. 3), and there was a significant correlation between the number of single-flower visits and the number of stigma contacts per flower (Pearson r=0.781, P<0.001). There was a significant difference in the stigma contact ratio between honeybees and ground bumblebees (independent-samples t test, t=−5.939, F=2.254, P <0.01) (Fig. 3).
The stigma contact ratios of honeybees and ground bumblebees. The upper limit of the rectangle is the 75th percentile of the data, the lower limit is the 25th percentile, and the middle line is the 50th percentile. The vertical length of the rectangle represents the quartile range, and the solid squares (points) are the observed values.
The daily activities of honeybees and ground bumblebees are shown in Fig. 4. Honeybees left the nest later than ground bumblebees (after 8:00 vs. after 6:00), and their homing time was earlier than that of ground bumblebees (before 17:30 vs. before 19:00). The peak period of visiting flowers for honeybees was 9:30–11:45, during which the number of visited flowers was approximately 57.72% of the total number of flowers visited during the day. Between 9:30 and 11:45, the temperature was 27–31°C, and the relative humidity was 41%–60% (Fig. 4A). The peak period of visiting flowers for ground bumblebees was 6:00–10:00, during which the number of visited flowers was approximately 59.43% of the total number of flowers visited during the day. During this period, the temperature was 16–27°C, and the relative humidity was 48%–70% (Fig. 4B).
The daily activity of honeybees (A) and ground bumblebees (B) on oil tree peony (the Y-axis on the left shows the number of flowers visited by honeybees, and the Y-axis on the right shows the air temperature in consecutive hours of observation)
The four pollination treatments showed significant differences in the number of fruits per plant (one-way ANOVA,
Effect of pollination by honeybees and ground bumblebees on the yield parameters and quality of oil tree peony (SE - standard error, n - number of samples)
Measurement index | Pollination without insects (mean±SE (n)) | Field plot (mean±SE (n)) | ||
---|---|---|---|---|
Number of fruits per plant | 11.23±0.30 (311)a | 10.51±0.27 (296)a | 9.61±0.46 (90)b | 10.95±0.50 (96)a |
Number of seeds per follicle | 36.44±0.55 (869)a | 24.99±0.62 (866)b | 15.92±0.36 (863)d | 18.88±0.35 (866)c |
Seed weight per follicle (g) | 8.90±0.25 (872)a | 7.45±0.24 (974)b | 4.69±0.10 (865)d | 5.25±0.14 (867)c |
Number of seeds per plant | 414.93±21.04 (98)a | 281.46±15.93 (95)b | 204.58±10.29 (90)c | 152.34±10.48 (97)c |
Seed weight per plant (g) | 102.42±5.91 (98)a | 75.57±4.13 (95)b | 45.06±3.03 (90)d | 57.30±2.96 (97)c |
Kernel percentage (%) | 66.92±0.002 (9)a | 66.47±0.001 (9)a | 66.13±0.002 (3)a | 65.59±0.002 (3)a |
Oil yield rate (%) | 22.03±0.25 (9)a | 21.72±0.33 (9)a | 20.67±0.60 (3)a | 21.10±0.31 (3)a |
The data in the same row followed by different letters are significantly different at the 0.05 level (one-way ANOVA followed by a Bonferroni test or nonparametric Kruskal-Wallis H analysis).
Palmitic acid, stearic acid, oleic acid, linoleic acid, α-linolenic acid, arachidic acid and arachidonic acid were detected as components of the peony seed oil. The unsaturated fatty acid content in peony seed oil was above 91%, and the relative α-linolenic acid content was as high as 43%. The compositions of peony seed oil for the different pollination treatments are summarized in Tab. 2. There were no significant differences in palmitic acid (χ2=3.167, P=0.367), stearic acid (χ2=6.514, P=0.089), oleic acid (χ2=5.227, P=0.156), linoleic acid (χ2=5.227, P=0.140), α-linolenic acid (χ2=6.649, P=0.084), or unsaturated fatty acid (χ2=4.006, P=0.261) content between the different pollination treatments.
Peony seed oil components (in %) obtained under different pollination treatments (mean±SE; SE – standard error)
Component | Pollination without insects | Field plot | ||
---|---|---|---|---|
Palmitic acid | 5.98±0.07a | 5.93±0.02a | 6.00±0.04a | 6.00±0.04a |
Stearic acid | 2.12±0.02a | 2.16±0.02a | 2.23±0.01a | 2.18±0.02a |
Oleinic acid | 22.9±0.15a | 23.4±0.02a | 23.4±0.00a | 23.9±0.10a |
Linoleic acid | 24.37±0.23a | 23.5±0.38a | 22.7±0.10a | 23.2±0.00a |
α-Linolenic acid | 43.97±0.39a | 44.37±0.09a | 44.3±0.10a | 44.2±0.00a |
Unsaturated fatty acids | 91.34±0.06a | 91.53±0.58a | 91.66±0.00a | 91.56±0.11a |
The data in the same row followed by different letters are significantly different at the 0.05 level (Kruskal-Wallis H analysis).
The activity of pollinators is affected by meteorological factors as well as physiological factors of the insects themselves. Temperature, humidity, and wind are key factors limiting bee feeding, and the effects of temperature on honeybee and ground bumblebee activity are greater than those of light, wind speed and other factors (Lee et al., 2016). Different bees display different pollination and pollen collection activities under different climatic conditions. Due to their weak phototaxis and low-temperature tolerance, ground bumblebees exhibit greater pollination activity than honeybees during periods of low temperature, rainfall and low light availability (An et al., 2007; Zhao et al., 2011; Lee et al., 2016). According to this study, ground bumblebees left the nest earlier than honeybees, and the peak activity of the former occurred between 6:00 and 10:00. Ground bumblebees are more tolerant than honeybees to low temperatures. When the temperature reached 29 °C in the morning, the number of ground bumblebees that left the nest for pollen collection greatly decreased. In contrast, honeybees left the nest after 8:00, with a peak activity period of 9:30–11:45. The results of this study suggested rather satisfactory complementary foraging behaviors. Oil tree peony has a short flowering period in early spring, when the temperature is low and the temperature difference between day and night is large. However, the effect of coapplying the two bee species for oil tree peony pollination remains to be explored.
The role of pollinators in the success of plant reproduction depends on their contribution to the number of pollen grains deposited on the stigmatic surface and subsequent increases in fruit or seed yield and quality. In general, pollinator efficiency consists of visit density and such visit effects as the pollen-carrying capacity and the number of pollen deposited on the stigma per contact (Xie & An, 2014). On apple (
The diversity and density of pollinators are factors that affect pollination efficiency (Sabbahi, DeOliveira, & Marceau, 2005; Atmowidi et al., 2007; Peña & Carabalí, 2018). At the time of alfalfa (
Pollination is essential for spermatophytes and is the process by which pollen is transferred from the anther of the stamen to the stigma of the pistil. The seed-setting rate or seeding rate is usually used as a proxy for pollination success (Delaplane et al., 2013). Bee pollination not only increases crop yield but also improves quality and increases market value (Bommarco, Marini, & Vaissière, 2012; Said, Inayatullah, & Ali, 2017; Stein et al., 2017). For crops that rely on pollinators, pollination is directly affected by pollinator abundance (Sabbahi, DeOliveira, & Marceau, 2005; Peña & Carabalí, 2018). ‘Fengdan’ is a cross-pollinated plant, and its self-pollination rate is low (Han et al., 2014; Si, 2016; He et al., 2019). In this study, honeybee pollination greatly increased the yield of oil tree peony. Specifically, honeybee pollination increased the seed yield of oil tree peony by 78.74%, and ground bumblebee pollination by 31.88%. However, the oil yield and fatty acid content of oil tree peony seeds were not significantly improved. In this study, honeybees and ground bumblebees were encouraged to pollinate oil tree peony by setting up a pollination net room. The results showed that the seed-setting rate of plants pollinated by honeybees and ground bumblebees was higher than that of plants in the control and under natural field conditions, indicating that the technique was effective for pollinating oil tree peony. However, how to apply honeybees and ground bumblebees to oil tree peony in the field requires further study.
In conclusion, both honeybees and ground bumblebees can effectively improve the seed and oil yields of oil tree peony. Honeybees and ground bumblebees generally show complementary foraging behaviors in terms of time. The results of this study may provide useful insight for improving the seed and oil yields of large-scale-planted oil tree peony in the field.