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iForest - Biogeosciences and Forestry
vol. 8, pp. 207-213
Copyright © 2015 by the Italian Society of Silviculture and Forest Ecology
doi: 10.3832/ifor1185-008

Research Articles

Seed trait and rodent species determine seed dispersal and predation: evidences from semi-natural enclosures

Xianfeng Yi (1)Corresponding author, Zhenyu Wang (1), Changqu Liu (2), Guoqiang Liu (2)

Introduction 

Many plant species producing large-sized seeds rely substantially on animals for their seed dispersal ([18], [26], [46], [51], [39]). In the dispersal systems, animals depend on plant seeds as nutrition supplies for their survival, especially in food shortage periods, and future reproductive success ([53], [42]). Seed predators may also act as effective seed dispersers, provided that seeds are cached and not completely retrieved ([64], [32], [71]). Two kinds of seed hoarders can be distinguished according to their caching strategies: larder hoarders usually store food items in central caches; while scatter hoarders store food in spaced caches and invest little to defense stores and reduce pilferage ([53], [27]).

Seed dispersal can be affected by various properties of seeds (e.g., [38], [51], [33], [68]). Seed traits have been recognized as important factors affecting rodents’ final decision to manipulate food sources ([29], [68], [32]). Seed size ([37], [57], [60], [2], [4]), handling time ([28]), moisture content ([22]), energy and soluble carbohydrates ([29], [30], [58]), nutrients ([1], [25], [59]), secondary chemical compounds (e.g., tannins and other polyphenols - [49]), seed coat thickness ([68], [52]) as well as seed germination schedule ([60]) have been identified to show influences on seed removal and dispersal. Apart from the influence of seed traits, environmental factors such as habitat qualities and seasonal variations show great impacts on seed removal and dispersal ([23], [31], [54], [36]).

Sympatric rodent species often differ greatly for instance in body size, tooth morphology, and nutrition requirement, and they may differ in affecting seed fates in the field (e.g., [30], [40]). Large-sized rodent species may have strong abilities of opening hard seeds, defending food caches or predation, which may affect their seed hoarding strategies. It suggests that larder-hoarding is often adopted by dominant or stronger animals because they can defend their larders ([9]), while scatter-hoarding is generally considered as a strategy of subordinate animals to minimize the risk of catastrophic loss of hoarded food ([35], [44]). Therefore, body size of small rodents may be another important factor in affecting hoarding strategies (e.g., scatter- vs. larder-hoarding). Previous field studies usually evaluated the interaction between seeds and rodents at community levels, as it is impossible to evaluate the role of a single rodent species in seed dispersal of various tree species. Therefore, it is hard to discriminate specific behavioral response of one given rodent species to certain seed traits when selecting seeds ([41], [68]). Although seed trait plays an important role in determining the formation of mutualism and predation interactions among multiple tree and animal species ([68], [32], [55]), the effects of both seed and rodent traits on seed dispersal and predation have been not well evaluated ([8]).

The purpose of this study is to investigate how three sympatric rodent species with different body sizes affect seed dispersal and seed fates of five sympatric tree species in semi-natural enclosures in northeastern China. We predicted that: (1) thick-coated seeds will be removed more slowly than seeds with thin coat because thick coat usually increase the time for rodents to eat seeds ([68]); (2) thick-coated seeds will be less likely eaten in situ but more likely eaten after removal according to the handling-time hypothesis; (3) more seeds with high caloric value will be hoarded by rodents according to the optimal forage theory ([45]); (4) large-sized rodent species will eat more seeds in situ, while rodents with small size tend to eat seeds after removal; (5) large-sized rodents will larder-hoard more seeds than small-sized ones, while rodents with small size will scatter-hoard more seeds than large-sized rodents due to their lower ability to defend larders ([34], [44]).

Materials and methods 

Study site

This study was conducted in the Dongfanghong Forestry Center (average elevation 750 m, located at 46° 50′ to 46° 59′ N, 128° 57′ to 129° 17′ E) in the Dailing district, Yichun city, Heilongjiang Province, north-eastern China. The climate of the experimental site is dominated by the north temperate zonal monsoon with severe and long winters and short summers. The annual average temperature is 1.4 °C with maximum at 37 °C and minimum at -40 °C. Average annual precipitation averages at 660 mm, with 80% of annual precipitation falls between May and September ([65]).

Experimental enclosures

Sixteen separate semi-natural enclosures (10 × 10 × 2.5 m) were constructed in an open area at the edge of the forests. The enclosures were built using bricks about 2.5 m above and 0.5 m below the ground. The walls of the enclosures were smoothed to prevent escape of small rodents. Grasses commonly found in the forests were distributed with an average coverage of 60%, while trees and shrubs were removed to prevent rodents from escaping by climbing. To prevent avian predators from entering the enclosures, the enclosures were covered with plastic nets on the top. An artificial nest constructed of bricks (H × W × L = 20 × 15 × 30 cm) and a plastic water bowl were placed at one corner of the enclosure to allow animals to rest and drink freely. A seed station of 0.5 m2 was established at the center of each enclosure.

Tested rodent species

The dominant rodent species in the study site are Apodemus peninsulae (Rodentia, Muridae), Clethtionomys rufocanus (Rodentia, Cricetidae) and Tamias sibiricus (Rodentia, Sciuridae). They were chosen for the present experiments because their significant role in the dispersal of large seeds of local tree species ([65]). A. peninsulae and C. rufocanus are small nocturnal species, while T. sibiricus is a larger diurnal rodent. T. sibiricus mainly scatter-hoards but occasionally larder-hoards seeds of local tree species, while A. peninsulae behaves differently, mainly larder-hoarding but sometimes scatter-hoarding seeds. Another nocturnal species, C. rufocanus, is pure seed predator and only larder-hoards seeds of local tree species.

During seed fall in early September 2010, steel frame live traps with a size of 9 × 10 × 25 cm (H × W × L), baited with peanuts and some carrots, were placed in the forests with a 5 m interval along four transects at 9:00 a.m. for animal trapping. We checked the traps every three hours to ensure safety of the captured rodents. All traps were removed at 6:00 p.m. and re-placed next day. Trapping stopped in bad-weather days, such as heavy rain. The target animals captured in each visit were transported by car to the laboratory housing room within no more than 30 minutes. In the laboratory, the animals were individually kept in steel frame cages (H × W × L: 40 × 50 × 90 cm) at outdoors conditions (15-25 °C, 14h of daylight). They were provided with carrots, peanuts, tree seeds and water ad libitum. No animal died during trapping and laboratory rearing. The Dailing Forestry Bureau of the Heilongjiang Province issued permits for the experimental animal trapping. Our behavioral trials and housing procedures were approved by the College of Agriculture, Henan University of Science and Technology. Four days after the experiments, all animals were released where they were captured.

Experimental seeds

The seeds of the five sympatric plant species Juglans mandshurica, Quercus mongolica, Pinus koraiensis, Corylus mandshurica and C. heterophylla were tested (Tab. 1). In the study region, C. mandshurica and C. heterophylla are dominant shrub species, while P. koraiensis, Q. mongolica and J. mandshurica are dominant tree species. Seeds of these five tree species were reported to be dispersed and predated by T. sibiricus, A. peninsulae, and C. rufocanus ([47]). Seeds of J. mandshurica are rich in fat and have the largest size and the thickest coat. C. heterophylla produces seeds of medium size and thick coat, while Q. mongolica produces medium-sized acorns with thinnest seed coat, low nutrition level and high level of tannins. C. mandshurica and P. koraiensis have the smallest seeds with thin coat and high nutrition level. During seed fall, seeds of the five species were collected from the ground under 10-15 trees. Thirty seeds of each tree species were randomly selected for the measurement of physical traits (seed mass, seed length, seed width and coat thickness by using electric vernier caliper and precision scale). Ninety seeds of each tree species were dried at 60 °C for 48 hours. The whole kernel of each seed was carefully collected and weighed. Then, thirty kernels of each species were mixed up into a sample for nutrition analyses, therefore a total of three samples were collected. Concentrations of crude protein, crude fat, crude starch and tannin of the seeds were measured by the Cereal Quality Supervision and Testing Centre, Ministry of Agriculture, China (No. 12 Southern Zhongguancun Road, Haidian District, Beijing). The caloric values of seeds were calculated by the average gross energy equivalents of protein, fat, and carbohydrates. Yang & Xiao ([61]) have calculated the corresponding values for the three organic matters, i.e., 17.2 kJ/g, 38.9 KJ/g, and 17.2 kJ/g, respectively. Caloric value per seed was calculated using mean kernel mass × caloric value of seeds ([68]). The caloric values per seed and per gram kernel were used to reflect the nutritional values of tree species. Seeds were then labeled with plastic tags according to Yi et al. ([67]) with minor modifications. A hole (0.3 mm in diameter) was drilled through the seed coat of each seed, without damaging the cotyledon and the embryo. A flexible plastic tag (2.5 × 3.5 cm, < 0.3 g) was tied through the hole in each seed using a thin 10 cm-long steel thread.

Tab. 1 - Morphological and nutritional traits of the five seed species (mean ± SD). These seeds were the same as those in the removal experiments. (*): Data are drawn from Yi & Zhang ([65]), Yi et al. ([67]), and Yang et al. ([62]).

Assessment of seed selection and dispersal by rodents

Trapped animals were starved for 12 hours before being moved in the enclosures. At 7:00 a.m. one animal was singly introduced in each enclosure to test seed removal, seed predation and hoarding. Nine adult individuals of A. peninsulae (5 females, 4 males, body mass: 26.83 ± 5.64 g, mean ± SD), 7 C. rufocanus (3 females, 4 males, body mass 33.38 ± 3.57 g) and 7 T. sibiricus (3 females, 4 males, body mass: 104.80 ± 9.25 g) were randomly selected for the seed removal experiments. Ten intact tagged seeds of each tree species were supplied to each individual only once. The tagged seeds in the enclosures were checked in the morning (7:00 a.m.) and afternoon (16:00 p.m.) daily in the following 3 days (81 hours). The seed removal rate by small rodents was reflected by the proportions of intact seed remaining at the seed stations. Scatter-hoarded seeds were located easily because the attached tags are usually left on the ground after being buried by rodents.

Data analysis

Statistical Package for the Social Sciences (SPSS 16.0) was used for data analyses. Cox regression was used to identify difference in seed removal rates of the five seed species at seed stations. Two-way ANOVA was used to test the effects of plant and rodent species on the number of seeds remained at seed stations (IIS), eaten in situ (EIS), intact after removal (IAR), eaten after removal (EAR), scatter-hoarded (SH) and larder-hoarded (LH), respectively.

Results 

Seed removal rate according to plant species

Seed removal rate by A. peninsulae was marginally different among the five tested plant species (Wald = 9.34, df = 4, P = 0.053), following the order: P. koraiensis > Q. mongolica > C. mandshurica > C. heterophylla > J. mandshurica (Fig. 1A, Fig. 2A). As in A. peninsulae, also T. sibiricus showed significant differences in seed removal rates among the plant species (Wald = 19.01, df = 4, P = 0.001 - Fig. 1B, Fig. 2B). Finally, significant differences between plant species in seed removal rates were found in C. rufocanus (Wald = 20.73, df = 4, P < 0.001 - Fig. 1C), but with a different preference order: Q. mongolica > P. koraiensis > C. mandshurica > C. heterophylla > J. mandshurica.

Fig. 1 - Seed removal of five sympatric seed species from seed stations by individual of each rodent species in semi-natural enclosures. (A): Apodemus peninsulae (n = 9); (B): Tamias sibiricus (n = 7); (C): Clethrionomys rufocanus (n = 7). Data are expressed as mean ± SE.
Fig. 2 - Seed fates of five sympatric seed species manipulated by individual of each rodent species in semi-natural enclosures. (A): Apodemus peninsulae (n = 9); (B): Tamias sibiricus (n = 7); (C): Clethrionomys rufocanus (n = 7). (IIS): intact in situ; (EIS): eaten in situ; (EAR): eaten after removal; (IAR): intact after removal; (SH): scatter-hoarded; (LH): larder-hoarded. Data are expressed as mean ± SE.

Seed fates according to plant species

More seeds of P. koraiensis and Q. mongolica were removed from seed stations than those of C. mandshurica, C. heterophylla and J. mandshurica (F = 99.639, df = 4, P < 0.001- Fig. 2, Tab. 2, Tab. 3). EIS and EAR seeds were significantly affected by seed species (EIS: F = 40.224, df = 4, P < 0.001; EAR: F = 22.124, df = 4, P < 0.001), with seeds of Q. mongolica, with the thinnest coat, showing the highest EIS and EAR rates (Tab. 2). Seeds of P. koraiensis were instead more likely to be scatter-hoarded than the other four seed species (F = 8.18, df = 4, P < 0.001). Larder-hoarding was also affected by seed species, i.e., small rodents larder-hoarded more seeds of P. koraiensis and J. mandshurica than those of Q. mongolica, C. mandshurica and C. heterophylla (Fig. 2, Tab. 2, Tab. 3), indicating that seeds with high caloric value were more likely to be hoarded by rodents.

Tab. 2 - The effects of seed and rodent species on seed fates of the five sympatric tree species. Data are seed numbers and expressed as mean ± SD. Different letters in the same column indicate significant difference at P < 0.05 among seed or rodent species. Seed fates in the table were defined as: intact in situ (IIS), eaten in situ (EIS); eaten after removal (EAR), intact after removal (on surface - IAR), scatter-hoarded (SH) and larder-hoarded (LH).
Tab. 3 - Two-way ANOVA summary of seed fates correlated with seed and rodent species.

Seed fates according to rodent species

The three rodent species showed significantly different manipulations of seeds in term of total number of seeds remaining at seed stations (F = 166.92, df = 2, P < 0.001); more seeds were left by C. rufocanus than by A. peninsulae and T. sibiricus, respectively (all P < 0.001 - Fig. 2, Tab. 2, Tab. 3). T. sibiricus, with large body size, ate more seeds at seed stations than small-sized A. peninsulae and medium-sized C. rufocanus (F = 487.36, df = 2, P < 0.001). However, more seeds were eaten after removal (EAR) by A. peninsulae than by C. rufocanus and T. sibiricus (F = 104.64, df = 2, P < 0.001). T. sibiricus and A. peninsulae scatter-hoarded more seeds than C. rufocanus (F = 6.53, df = 2, P < 0.001). Finally, more seeds were larder-hoarded by A. peninsulae and C. rufocanus than by T. sibiricus (F = 46.03, df = 2, P < 0.001 - Fig. 2, Tab. 2, Tab. 3).

Correlation between seed traits and seed fates

Regression of the proportion of IIS vs. seed coat thickness indicated that seed species with thick coat were more likely to be left at seed stations (r = 0.909, P < 0.05 - Tab. 4). No significant relationship was found between the proportion of EIS and seed coat thickness (r = -0.827, P = 0.084); however, the proportion of EIS was negatively correlated with the caloric value of seeds (r = -0.942, P < 0.05). We also found that the proportion of EAR was negatively correlated with both coat thickness and caloric value of seeds (r = -0.905, P < 0.05; r = -0.892, P < 0.05, respectively). Seed caloric value was positively and marginally correlated with the proportion of larder-hoarded seeds (r = 0.876, P = 0.051), but not with scatter-hoarded seeds (r = 0.499, P > 0.05).

Tab. 4 - Linear regression results between seed fates and seed traits. Seed fates in the table were defined as: intact in situ (IIS), eaten in situ (EIS); eaten after removal (EAR), intact after removal (on surface) (IAR), scatter-hoarded (SH) and larder-hoarded (LH).

Discussion 

High level of defense (e.g., thick seed coat) to predators usually reduces seed removal rates from seed stations by seed dispersers ([68]). Our results support the first prediction suggesting that thick-coated seeds are removed more slowly than thin-coated seeds by small rodents because they may require greater efforts to handle. Rodents have to spend more time to eat seeds with thick coat, which may increase predation risk ([20]); selecting thin-coated seeds may reflect their feeding strategies. Previous studies suggest that large-sized seeds are more likely to be cached by rodents ([56], [57], [59], [5]). In the three investigated rodent species, we fail to detect any apparent relationship between seed mass/size and number of seeds eaten or hoarded. More Q. mongolica acorns, the richest in tannins, were eaten either in situ or after removal than those of the other four plant species, inconsistent with the high tannin hypothesis ([49]). This suggests that tannin contents in seeds are unimportant in determining seed hoarding by rodents in our study region ([70]). Early germinating Q. mongolica acorns were eaten instantly rather than hoarded, in agreement with the perishability hypothesis ([16], [50], [60]). We propose that in Q. mongolica instant consuming rather than acorn caching is probably related to their higher perishability ([48], [15], [51]). A seed coat thinner than those of other seed species might be an alternative explanation for instant consumption of Q. mongolica acorns by small rodents. Therefore, the effect of seed mass and tannin on seed fates might be masked by other prominent seed traits, e.g., seed coat ([43]). The significant and negative correlations between seed removal rates and seed coat thickness reflect the crucial role of seed coat in determining seed selection and seed dispersal ([68]).

No significant relationship was found between seed coat thickness and the proportion of EIS. Our second prediction that thick-coated seeds are less likely to be eaten in situ but more likely to be eaten after removal is not fully demonstrated in this study. Although feeding thick-coated seeds after moving them away would be a safer way to prevent rodents from predation risk ([20]), our results show a significant and negative relationship between the proportion of EAR and seed coat thickness. These results indicate that seeds with extreme thick coat (e.g., J. mandshurica) prevent small rodents to disperse and eat them, generally reflecting the negative effect of thick seed coat on seed dispersal ([68]).

Also the prediction that seeds with high caloric value are more hoarded by rodents is verified in this study. Seeds of P. koraiensis and J. mandshurica with high caloric value were more likely to be larder-hoarded, but less likely to be eaten by small rodents, in agreement with previous observations reporting that small rodents prefer to cache seeds with high nutritional value ([11], [12], [3], [10]). The significant and positive relationship between the proportion of larder-hoarded seeds and the caloric value of seeds also indicates the important role of energy reserves in seeds in determining food hoarding by animals ([26]). More seeds of P. koraiensis were scatter-hoarded than those of J. mandshurica, although the latter shows higher caloric value per seed, reflecting the trade-offs between nutrition rewards and efforts in handling the thick coat of J. mandshurica seeds.

Animals with different body size may display different seed disposal abilities, and therefore show different preferences for seeds with contrasting traits ([40], [68]). In our study, the large T. sibiricus ate more seeds in situ, while the medium-small A. peninsulae and C. rufocanus ate more seeds after removing them to safe places (e.g., corners and nests), supporting our fourth prediction. Actually, body size cannot always indicate seed handling ability, as T. sibiricus refuse to select seeds of J. mandshurica.

Larder-hoarding animals usually store food in their nests and invest more efforts to defend them, while scatter-hoarders bury one or several seeds in dispersed caches and space them far apart ([27]). Although it has been suggested that scatter-hoarding is due to poor ability of animals defending food caches ([34], [44]), A. peninsulae and C. rufocanus, with small body mass, larder-hoarded more seeds than T. sibiricus did, while T. sibiricus scatter-hoarded more seeds than A. peninsulae and C. rufocanus. Contrasting with the last prediction, our results suggest that body size is not linked with the evolution of food hoarding strategies (scatter-hoarding and larder-hoarding). Caching strategies may represent trade-offs between cache defense maximization and cache pilferage minimization ([24], [14], [9]).

We acknowledge that many environmental factors may influence seed selection, seed removal and dispersal, and ultimately seed fates in the field ([17], [19], [13], [36]). Although the same-sized enclosures have been applied to investigate caching behavior of chipmunks and other rodent species ([69], [6], [7], [21]), the semi-natural enclosures cannot completely mimic the field conditions. Lack of competition and unnatural presentation of seeds are supposed to alter the behavior of rodents in the enclosures. Although previous studies show that the average dispersal distances of seeds of P. koraiensis, C. mandshurica, C. heterophylla, and J. mandshurica are less than 4 m in the field ([66], [65], [63]), the enclosures may not be large enough to allow the expression of rodents’ desired seed dispersal range.

Our results shed light on the interaction and coevolution between rodents and plants bearing large seeds. On one hand, plants need to increase seed size and nutrition contents to attract potential dispersers. On the other hand, plants have to avoid predation through developing various physical and chemical defense systems ([49], [68]). Trade-offs between attractive and defensive traits of plants regulates dispersers’ decision to remove, consume, and hoard seeds. From the animal’s point of view, trade-offs between costs and rewards of manipulating seeds may shape their different abilities of handling, consuming, and hoarding a seed. Thus, the interactions between plant seeds and rodents are often complex and diffuse at community level. The combined effects of seeds and rodents appear to play an important role in determining seed dispersal and predation in the seed-rodent dispersal system.

Acknowledgments 

Funding for this study was partially supported by the National Natural Science Foundation of China (No. 31470113), the State Key Laboratory of Integrated Management of Pest Insects and Rodents (ChineseIPM1404), and the Program for New Century Excellent Talents in University (NCET-12-0693).

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Yi X, Wang Z, Liu C, Liu G (2015).
Seed trait and rodent species determine seed dispersal and predation: evidences from semi-natural enclosures
iForest - Biogeosciences and Forestry 8: 207-213. - doi: 10.3832/ifor1185-008
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Paper ID# ifor1185-008
Title Seed trait and rodent species determine seed dispersal and predation: evidences from semi-natural enclosures
Authors Yi X, Wang Z, Liu C, Liu G
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