Skip Navigation

This Article
Right arrow Abstract Freely available
Right arrow FREE Full Text (PDF) Freely available
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Email this article to a friend
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Add to My Personal Archive
Right arrow Download to citation manager
Right arrow Search for citing articles in:
ISI Web of Science (42)
Right arrowRequest Permissions
Google Scholar
Right arrow Articles by Grostal, P.
Right arrow Articles by Dicke, M.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Grostal, P.
Right arrow Articles by Dicke, M.
Social Bookmarking
 Add to CiteULike   Add to Connotea   Add to Del.icio.us  
What's this?

Behavioral Ecology Vol. 10 No. 4: 422-427
© 1999 International Society for Behavioral Ecology

Direct and indirect cues of predation risk influence behavior and reproduction of prey: a case for acarine interactions

Paul Grostal and Marcel Dicke

Laboratory of Entomology, Wageningen Agricultural University, PO Box 8031, 6700 EH Wageningen, The Netherlands

Address correspondence to M. Dicke. E-mail: marcel.dicke{at}users.ento.wau.nl

Received 17 June 1998; revised 16 September 1998; accepted 22 December 1998.


    ABSTRACT
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
Little is known about the flow of chemical information from higher to lower levels within the animal food chain. However, this information may determine the behavior and distribution of many animals (e.g., that of potential prey) when exposed to direct and indirect cues of predation risk. We used herbivorous spider mites, Tetranychus urticae Koch (Tetranychidae) as a model to examine the foraging and oviposition decisions that prey make when exposed to these cues. We conducted laboratory tests to determine if the previous presence of predators (direct cues) on leaf discs or the presence of injured conspecifics (indirect cues) alters the distribution of adults and eggs of T. urticae. When given a choice, after 24 h, fewer adults and eggs were found on leaf discs that had previously contained specialist spider mite predators, Phytoseiulus persimilis Athias-Henriot (Phytoseiidae), than on discs unexposed to predators. Also, more T. urticae emigrated from predator-exposed discs than from unexposed discs or from those that had previously contained nonpredatory mites (Tyrophagus putrescentiae, Acaridae). Finally, fewer T. urticae foraged and laid eggs on predator-exposed discs or on those with artificially damaged conspecifics (eggs or dead adults) than on discs with intact conspecifics. Tetranychus urticae probably recognizes infochemicals (kairomones) from its predators or cues from injured spider mites and consequently avoids feeding or ovipositing in areas exposed to these cues. Recognition and avoidance of kairomones from specialist predators by this prey are likely to be hereditary, but avoidance of injured conspecifics may be an adaptation to avoid predators that are not inherently recognized. We discuss the behavioral and ecological implications of our findings.

Key words: arthropods, infochemicals, kairomone, mites, Phytoseiulus persimilis, predator, Tetranychus urticae.


    INTRODUCTION
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
The foraging behavior of animals is shaped by energetic costs and by the risk from natural enemies (Krebs and Davies, 1987Go). However, for the fitness of an organism, the failure to detect natural enemies is usually more detrimental than, say, the failure to detect food (Lima and Dill, 1990Go). An animal under strong selective pressure by higher trophic levels will benefit from early detection of its enemies and from consequent avoidance of a potentially lethal confrontation.

Many prey species evolved chemical senses (e.g., olfaction, taste) for detecting their predators. Cues of predator presence may be direct [e.g., chemicals (kairomones); Dicke and Sabelis, 1992Go] emitted by the predators (e.g., Jedrzejewski et al., 1993Go; Kriesch and Dicke, 1997Go; Nolte et al., 1994Go), or indirect [e.g., information from disturbed/injured (alarm pheromones) or dead conspecifics; Chivers et al., 1996Go; Janssen, 1998Go; Janssen et al., 1997Go; Pijanowska, 1997Go; Rittschof and Hazlett, 1997Go; Vadas et al., 1994Go].

When exposed to cues from predators or from injured conspecifics, many animals have been shown to display defensive or evasive behavior. For example, Daphnia magna respond to cues from crushed conspecifics by migrating down the water column and forming small aggregations, a behavior that was shown to reduce predation by fish (Pijanowska, 1997Go). Geckos (Coleonyx brevis) exhibit a defensive tail display when exposed to skin odors of snake predators (Dial and Schwenk, 1996Go). Snowshoe hares (Lepus americanus) and voles (Clethrionomys glareolus, Microtus agrestis) may avoid predation by reducing their feeding and breeding activity when perceiving predator infochemicals (Koskela and Ylönen, 1995Go; Sullivan and Crump, 1986Go; Ylönen and Ronkainen, 1994Go). In fact, this type of response prompted attempts to use predator products to reduce feeding damage by various mammal pests (Coulston et al., 1993Go; Engelhart and Muller-Schwarze, 1995Go; Sullivan et al., 1991Go; Woolhouse and Morgan, 1995Go; Zimmerling and Zimmerling, 1996Go). Finally, fruit flies (Rhagoletis basiola, Tephritidae) were observed to delay oviposition when exposed to chemical information from their egg parasitoids (Hoffmeister and Roitberg, 1997Go). The different responses of prey to predator infochemicals may depend on the relative risk posed by a predator species (Marko and Palmer, 1991Go; Vadas et al., 1994Go), familiarity of prey with the chemical (Chivers and Smith, 1994Go; Dickman, 1992Go; Mathis et al., 1996Go), and the predator avoidance strategy of the prey (Lima and Dill, 1990Go; Malmqvist, 1992Go; Vadas et al., 1994Go).

In this study, we used two-spotted spider mites, Tetranychus urticae Koch and predatory mites, Phytoseiulus persimilis Athias-Henriot, as a model system to observe the foraging and oviposition of a herbivore when exposed to information about the potential risk of predation. Tetranychus urticae are small, polyphagous mites (approximately 0.8 mm long; Sabelis, 1981Go) that commonly infest commercial crops worldwide. They feed on the contents of leaf cells and lay up to 20 eggs per day throughout their foraging area (Sabelis, 1981Go; Tomczyk and Kropczynska, 1985Go). Specialist phytoseiid predators, such as P. persimilis, are the most effective natural enemies of T. urticae (Sabelis, 1985Go). Phytoseiulus persimilis feed on all stages of the spider mite by piercing their prey with their mouthparts, and are capable of exterminating entire populations of spider mites (Sabelis and van der Meer, 1986Go).

We used the predators and the herbivores to test four hypotheses: (1) previous exposure of leaves to predators reduces oviposition by the spider mites, (2) when given a choice, T. urticae avoids foraging or ovipositing on leaves previously exposed to predators, (3) more spider mites emigrate from leaves exposed to predators than from leaves exposed to nonpredatory mites or from unexposed leaves, and (4) the spider mites avoid foraging and ovipositing on leaves that contain artificially damaged conspecifics.


    MATERIALS AND METHODS
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
Plants and mites
All experiments were conducted in a laboratory at 22°±2°C. For each experiment, we used discs (1 cm diam) cut from young, fully expanded leaves of lima bean (Phaseolus lunatus L.). Tetranychus urticae were reared on lima bean leaves and P. persimilis were reared on leaves that were infested by the spider mites. The mite colonies were maintained in a greenhouse (20°-30°C, 50-80% relative humidity). During experiments, we handled all mites and their eggs with fine brushes, using separate brushes for different mite species. For each trial, all open petri dishes or containers that housed the mites were placed in deep plastic trays, which were then covered with large sheets of paper to minimize air currents.

Reactions of T. urticae to previous predator presence
Exposure of leaf discs to predators
We used leaf discs that were either previously exposed to predators or unexposed (clean). To obtain exposed discs, we introduced six adult female P. persimilis and left the mites for 24 h (Kriesch and Dicke, 1997Go). To prevent predators from escaping, we placed the discs on water and left them floating in open petri dishes. Approximately 2 h before each experiment commenced, all predators and their eggs (if any were laid) were removed from the leaves. Unexposed discs were also floating on water for 24 h, but without predators.

Oviposition
Predator-exposed and unexposed discs (n = 70) were placed separately on moist cotton wool in open petri dishes (one disc per dish). The moist substrate kept the leaf tissue fresh for the duration of the test and prevented the spider mites from leaving the discs. We placed one randomly selected adult female T. urticae on every disc. After 24 h, we counted the number of eggs laid by the spider mites in both treatments.

Choice
In this experiment, spider mites were offered a choice between two discs: one predator exposed and one unexposed (clean). Thus, each petri dish (n = 32) contained a level sheet of moist cotton wool, on which we placed two leaf discs connected by a flat, T-shaped bridge (2.5 cm wide; Figure 1A). The bridges were cut from a transparent acetate sheet. The position of the discs relative to one another (left/right) was randomized in each petri dish. We then released six adult female T. urticae at the base of the T-bridge (see Figure 1A). After 24 h we counted the number of spider mite adults and eggs on each disc.



View larger version (16K):
[in this window]
[in a new window]
 
Figure 1

Experimental setups for choice and migration experiments, showing (A) two leaf discs connected by a T-shaped bridge. T. urticae were placed at the base of the bridge. (B) Two leaf discs connected by a straight bridge (actual bridge length = 13 cm). Six adult T. urticae were placed on the treatment discs (predator-exposed, fungivore-exposed, unexposed). C = control, T = treatment (placement of T and C discs relative to each other, i.e., left / right, was random).

 

Migration
We tested if spider mites will leave their initial food source and search for other leaves if the original source had been exposed to predators. We also examined if the spider mites have a similar response to leaves exposed to other, nonpredatory mites or to unexposed leaves.

We placed two leaf discs, connected by a straight acetate bridge (13 cm long, Figure 1B) on moist cotton wool sheeting in open plastic containers (10x17 cm). Three setups were used, each consisting of 35 replicates of the following disc pairs: (1) one predator exposed and one control (freshly cut, clean), (2) one fungivore exposed and one control, and (3) one unexposed and one control.

Both unexposed and control discs were clean (i.e., no initial contact with mites). However, unexposed discs had been floating on water for 24 h (as in previous experiments), but control discs were cut from fresh leaves < 3 h before the trial. Cutting fresh discs reduced preparation time and controlled for the effect of floating the cut tissue (unexposed discs) for 24 h. Fungivorous mites consisted of Tyrophagus putrescentiae (reared by Koppert Biological Systems B.V., Berkel-Rodenrijs, The Netherlands). To obtain fungivore-exposed discs, 10 adult Tyrophagus females were placed on each disc, but predator-exposed discs were treated as in the previous experiments (6 P. persimilis per disc). The leaf discs were then left floating on water for 24 h. Fungivores were initially released in higher numbers than the predators because they were more likely to escape from the discs; at the end of 24 h, an average of five predators and five fungivores were retained per disc.

We removed all predators, fungivores, and their eggs from exposed discs before introducing the spider mites. We then placed six adult female T. urticae on each predator-exposed (treatment 1), fungivore-exposed (treatment 2), and unexposed disc (treatment 3). No mites were placed on the control (freshly cut) discs. After 24 h we compared the distribution of mites and of their eggs on the treatment and control discs.

Reactions of T. urticae to damaged conspecifics
Damaged adults
Pairs of leaf discs, connected by a T-shaped bridge (as in Figure 1A), were placed on wet cotton wool in each petri dish. Three treatments were used, in each of which spider mites were offered a choice between two discs: (1) one with pierced adult spider mites and one without mites (control), (2) one with intact, dead adults and one without mites (control), and (3) one with pierced and one with intact, dead adults (control).

We used 40 replicates for each treatment. In treatments that included T. urticae (either pierced or intact), six adult females were immersed in liquid nitrogen and thawed before being haphazardly placed on each disc. The mites were killed by freezing to avoid interference with the experimental animals. After placing the dead mites on discs, we pierced the individuals in treatments 1 and 3 with a fine needle, partially spilling their hemolymph. Finally, six live T. urticae females were released at the base of the bridge (similarly to Figure 1A). After 24 h, we checked the distribution of the live mites and of their eggs in each treatment.

Damaged eggs
We used paired leaf discs connected by T-bridges on wet cotton wool, as in the previous experiment. However, this time, the following disc pairs were used: (1) one with pierced eggs of T. urticae and one without eggs (control), (2) one with intact eggs and one without eggs (control), and (3) one with pierced eggs and one with intact eggs (control).

Where included, 10 recently laid (not frozen) eggs were haphazardly placed on each leaf disc. We pierced the eggs in treatments 1 and 3 with a fine needle. Six live spider mites were then released on the base of the bridge and monitored as for the previous experiment. Each treatment had 40 replicates.

Statistical analysis
In the oviposition experiment, we used ANOVA to compare the mean number of eggs per disc that T. urticae laid on predator-exposed and on unexposed discs. In the migration trial, we calculated the proportion of mites and of eggs (out of the total number on both discs) found on the control disc [i.e., Eggscontrol/ (Eggscontrol + Eggstreatment)] for each replicate. We then normalized the data by transformation with arcsin square root and compared means for the three treatments with ANOVA. For all choice experiments (reaction to predators, to damaged adults and to damaged eggs), we calculated the proportion of spider mites and their eggs found on the control discs. We then used a t test within each treatment to determine if the proportions of mites and eggs on control (out of the total number on both discs) significantly differed from 0.5. Data for all experiments were checked for normality prior to the analyses.


    RESULTS
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
Reactions of T. urticae to previous predator presence
Oviposition
Exposure of leaf discs to predators did not have a significant effect on oviposition by T. urticae (ANOVA: F1,138 = 1.65; p =.202). After 24 h, the spider mites laid an average of 3.5 (± 0.2 SE) eggs per disc on predator-exposed discs and 4.0 (± 0.3 SE) eggs per disc on unexposed discs.

Choice
When released on a T-bridge that connected predator-exposed and unexposed leaf discs, the distribution of the spider mites and their eggs significantly differed from a random (50: 50) distribution: 72 ± 6% of the adults (t = 4.07, p =.0001) and 63±6% of their eggs (t = 2.26, p =.028) were found on unexposed leaf discs after 24 h (Figure 2).



View larger version (22K):
[in this window]
[in a new window]
 
Figure 2

Relative proportions (mean + SE) of adults and eggs of T. urticae found on treatment (previously exposed to P. persimilis) and control (unexposed) leaf discs. Pairs of control and treatment discs were joined by T-shaped bridges. Six adult spider mites were released at the base of each bridge and monitored after 24 h. *.05 > p >.01; ***p <.001.

 

Migration
When T. urticae were released on predator-exposed discs, after 24 h we found most of the mites and their eggs on the control, clean discs, 13 cm away (Figure 3). However, when the spider mites were released on fungivore-exposed and unexposed discs, more mites and more eggs were found on the treatment discs than on the control (Figure 3). The proportions of adult T. urticae and of their eggs found on control discs showed an overall difference among the three treatments (ANOVA, adults: F2,100 = 7.37, p =.001; eggs: F2,100 = 9.51, p <.001), although mite distribution on fungivore-exposed and clean discs did not clearly differ (Figure 3). Two replicates in the fungivore treatment were accidentally disturbed during the experiment and thus were excluded from the analysis.



View larger version (27K):
[in this window]
[in a new window]
 
Figure 3

Relative proportions (mean + SE) of adults and eggs of T. urticae found on control (clean) and treatment leaf discs, after 24 h. Six adult spider mites were released on treatment discs, which were (1) exposed to predators (P. persimilis), (2) exposed to fungivores (T. putrescentiae), or (3) clean (unexposed). The treatment and control discs were connected by straight, 13-cm long bridges.

 

Reactions of T. urticae to damaged conspecifics
Damaged adults
When T. urticae were offered a choice between discs with pierced conspecifics and clean discs (control), most adults foraged (t = 7.52, p <.001) and most eggs were laid (t = 9.59, p <.001) on the control (Figure 4). Similarly, more spider mites (t = 3.88, p <.001) and their eggs (t = 3.19, p =.002) were found on clean leaf discs (control) than on discs that contained intact conspecifics (Figure 4). However, when offered discs with pierced versus those with intact (but dead) conspecifics, most adults (t = 3.04, p =.003) and most eggs (t = 2.17, p =.033) were found on the disc with intact mites (control; Figure 4).



View larger version (26K):
[in this window]
[in a new window]
 
Figure 4

Relative proportions (mean + SE) of adults and eggs of T. urticae found on control and treatment leaf discs, after a choice between (1) discs with pierced adult conspecifics (treatment) and clean discs (control); (2) discs with intact (but dead) adult conspecifics (treatment) and clean discs (control); and (3) discs with pierced adults (treatment) and discs with intact adults (control). Pairs of treatment and control discs were connected by T-shaped bridges. Six spider mites were released at the base of the bridge 24 h before data collection. *.05 > p >.01; **.01 > p >.001; ***p <.001.

 

Damaged eggs
When we offered T. urticae a choice between clean discs and those with pierced eggs, more eggs were laid on clean discs (t = 2.56, p =.012), but the preference of adults for clean discs was marginally insignificant (t = 1.69, p =.094; Figure 5). There was no clear preference in foraging (t = - 0.80, p =.425) or oviposition (t = 0.99, p =.323) when mites were put on bridges that connected clean discs and those with intact eggs (Figure 5). Nevertheless, we found more adults (t = 3.66, p <.001) and more eggs (t = 3.10, p =.003) on discs with intact eggs than on those with pierced eggs (Figure 5).



View larger version (26K):
[in this window]
[in a new window]
 
Figure 5

Relative proportions (mean + SE) of adults and eggs of T. urticae found on control and treatment leaf discs after a choice between (1) discs with pierced spider mite eggs (treatment) and clean discs (control); (2) discs with intact spider mite eggs (treatment) and clean discs (control); and (3) discs with pierced eggs (treatment) and discs with whole eggs (control). Pairs of treatment and control discs were connected with T-shaped bridges. Six spider mites were released at the base of the bridge 24 h before data collection. ns, not significant; *.05 > p >.01; **.01 > p >.001; ***p <.001.

 


    DISCUSSION
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
The fitness of potential prey is favored when the prey forage and reproduce in areas that offer a minimal risk of predation. Chemical detection may be an important mechanism of risk assessment by prey (Tollrian and Harvell, 1999Go), but little is known about the ecological and evolutionary consequences of this phenomenon. Our experiments show that, when given a choice, T. urticae avoids foraging and ovipositing on leaves that had been previously exposed to predators. Interestingly, the spider mites also left a potential food source and traveled a considerable distance (equivalent to about 163 body lengths) in search of other food if the original source had been exposed to P. persimilis. In contrast, without predator exposure, most of the prey remained and oviposited on their initial feeding arena. This distribution effect is consistent with studies of other prey (e.g., Jedrzejewski and Jedrzejewska, 1990Go; Utne and Bacchi, 1997Go).

In our experiments, each replicate consisted of a group of six spider mites that may have influenced each other's distribution. The effect of conspecifics on the distribution of individuals has been little studied for spider mites (but see Bernstein, 1984Go; Pallini et al., 1997Go). However, spider mite populations often reach high densities in the field, and they can relocate in groups (Rabbinge, 1985Go). Consequently, our use of six individuals per replicate is likely in the field scenario and is consistent with previous studies of migration by group-living prey (e.g., Malmqvist, 1992Go; Pallini et al., 1997Go; Pijanowska, 1997Go).

Many species of prey react to kairomones contained in the feces or other secretions of their predators (Buchanan-Smith et al., 1993Go; Coulston et al., 1993Go; Dial and Schwenk, 1996Go), and the spider mites are probably no exception (Kriesch and Dicke, 1997Go). Learning through previous exposure to chemical cues also may play a role in the response of the herbivores (see Takabayashi et al., 1994Go), similar to behavior shown by vertebrate prey (Chivers and Smith, 1994Go; Brown and Smith, 1996Go, Mathis et al., 1996Go).

The chemicals that affect T. urticae are probably nonvolatile (Kriesch and Dicke, 1997Go), but their origin or nature is still unknown. For example, the prey may recognize and avoid protein-derived metabolites that are common among many predatory animals (Nolte et al., 1994Go). If so, the mites should also react to nonspecialist or allopatric predator species. Alternatively, the spider mites could react exclusively to traces of conspecific alarm pheromones carried by the predators and spread on the exposed discs. However, this is unlikely, as infochemicals from predatory mites that were fed on alternative (insect) prey also triggered an avoidance reaction among T. urticae (Grostal and Dicke, in preparation).

A variety of animals can distinguish cues of their predators from those of nonpredatory animals (Appelberg et al., 1993Go; Buchanan-Smith et al., 1993Go; Cooper, 1990Go; Jedrzejewski et al., 1993Go; Kelly and Cory, 1987Go; Sullivan, 1986Go; Ward et al., 1996Go). In our experiments T. urticae did not avoid leaves exposed to fungivorous mites. Perhaps the spider mites distinguish infochemicals of their predators from those of other, harmless species. Alternatively, the spider mites could avoid areas with a wide range of foreign chemicals, but the amount of kairomones deposited by T. putrescentiae differs from that deposited by equal numbers of P. persimilis. T. urticae have been shown to avoid leaf discs on which predator exposure per unit area was three times lower (five P. persimilis on 2-cm diam discs; Kriesch and Dicke, 1997Go) than in our experiments (six P. persimilis on 1-cm diam discs). The response of the spider mites to infochemicals of mite species from a broader range of feeding groups is currently being investigated (Grostal and Dicke, in preparation).

Unfavorable habitat conditions may suppress the fecundity of some species even after mating (Ohgushi, 1996Go; Plotkin et al., 1997Go), but little is known about whether predation risk can have a similar effect. Although T. urticae preferred to lay more eggs in areas that were relatively safe from predators, their oviposition on single, isolated discs was not suppressed by exposure to cues from P. persimilis, at least over 24 h. However, if the avoidance of predators incurs a significant energetic cost (e.g., searching for alternative sites or reduced feeding) or stress to the prey, size of adults and their oviposition may be reduced in the long term. Conversely, energetic and reproductive demands may incur trade-offs in predator avoidance (e.g., more frequent mating in spite of a correspondingly higher risk of predation) (Brown and Smith, 1996Go; Lima and Dill, 1990Go). These trade-offs remain unknown for terrestrial arthropods and should be examined in the future.

Some animals show defensive responses to indirect cues of predator risk (i.e., to information from damaged or alarmed conspecifics) (Chivers et al., 1996Go; Janssen, 1998Go; Janssen et al., 1997Go; Pickett et al., 1992Go; Pijanowska, 1997Go; Rittschof and Hazlett, 1997Go; Vadas et al., 1994Go). The reaction to indirect indications of threat is probably an adaptation to avoid nonspecialist predators, or ones that are not inherently recognized by the prey (Chivers and Smith, 1994Go; Engelhart and Muller-Schwarze, 1995Go; Mathis et al., 1996Go). Also, injured conspecifics probably provide an earlier warning about predation risk than do predator products (e.g. feces), which could be deposited after the attack on prey. In our experiments, spider mites avoided leaves with damaged conspecifics (both eggs and adults), consistent with several studies of other animals (Chivers et al., 1996Go; Pijanowska, 1997Go; Vadas et al., 1994Go). Interestingly, we also observed T. urticae to prefer empty leaves to those that contained dead (frozen) adults. We offer three hypotheses to explain this behavior. First, the spider mites may recognize dead conspecifics and consequently avoid feeding arenas that show high conspecific mortality. Second, the mites may choose areas that are free of potential competitors, (i.e., leaves without other spider mites) (Dicke, 1986Go; but see Pallini et al., 1997Go). Third, the dead animals may constitute an obstacle to feeding, and live adults may choose to forage on more exposed leaf surfaces.

Most animals have a range of specialist and nonspecialist predators. However, the specificity and intensity of prey response to different types of predator remains little studied. Our results suggest that animals as simple as mites can have direct (predator cues) and indirect (prey cues) means of assessing predation risk. Whether the combination of cues from predators with those from damaged conspecifics has a synergistic effect on mite defenses or whether these cues affect the mites at a community level remains to be shown.


    REFERENCES
 TOP
 ABSTRACT
 INTRODUCTION
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 REFERENCES
 
Appelberg M, Soderback B, Odelstrom T, 1993. Predator detection and perception of predation risk in the crayfish Astacus astacus L. Nord J Fresh Res 68:55-62.

Bernstein C, 1984. Prey and predator emigration responses in the acarine system Tetranychus urticae-Phytoseiulus persimilis. Oecologia 61:134-142.

Brown GE, Smith RJF, 1996. Foraging tradeoffs in fathead minnows (Pimephales promelas, Osteighthyes, Cyprinidae): acquired predator recognition in the absence of an alarm response.Ethology 102:776-785.

Buchanan-Smith HM, Anderson DA, Ryan CW, 1993. Responses of cotton-top tamarins (Saguinus oedipus) to faecal scents of predators and non-predators. Anim Welf 2 (1): 17-32.

Chivers DP, Kiesecker JM, Anderson MT, Wildy EL, Blaustein AR,1996 . Avoidance response of a terrestrial salamander (Ambystoma macrodactyllum) to chemical alarm cues. J Chem Ecol 22:1709-1716.

Chivers DP, Smith RJF, 1994. The role of experience and chemical alarm signalling in predator recognition by fathead minnows, Pimephales promelas. J Fish Biol 44:272-285.

Cooper WE Jr, 1990. Chemical detection of predators by a lizard, the broad-headed skink (Eumeces laticeps). J Exp Zool 256:162-167.

Coulston S, Stoddart DM, Crump DR, 1993. Use of predator odors to protect chick-peas from predation by laboratory and wild mice. J Chem Ecol 19:607-612.

Dial BE, Schwenk K, 1996. Olfaction and predator detection in Coleonyx brevis (Squamata, Eublepharidae), with comments on the functional significance of buccal pulsing in geckos. J Exp Zool 276:415-424.

Dicke M, 1986. Volatile spider-mite pheromone and host-plant kairomone, involved in spaced-out gregariousness in the spider mite Tetranychus urticae. Physiol Entomol 11:251-262.

Dicke M, Sabelis MW, 1992. Costs and benefits of chemical information conveyance: proximate and ultimate factors. In:Insect chemical ecology: an evolutionary approach (Roitberg BD, Isman MB, eds). New York, Chapman & Hall;122 -155.

Dickman CR, 1992. Predation and habitat shift in the house mouse, Mus domesticus. Ecology 73:313-322.

Engelhart A, Muller-Schwarze D, 1995. Responses of beaver (Castor canadiensis Kuhl) to predator chemicals. J Chem Ecol 21:1349-1364.

Hoffmeister TS, Roitberg BD, 1997. Counterespionage in an insect herbivore-parasitoid system. Naturwiss 84:1-3.

Janssen A, 1998. Avoidance of competition and predation in arthropod food webs (PhD dissertation). Amsterdam: University of Amsterdam.

Janssen A, Bruin J, Jacobs G, Schraag R, Sabelis MW,1997 . Predators use volatiles to avoid prey patches with conspecifics. J Anim Ecol 66:223-232

Jedrzejewski W, Jedrzejewska B. 1990. Effect of a predator's visit on the spatial distribution of bank voles: experiments with weasels. Can J Zool 68:660-666.

Jedrzejewski W, Rychlik L, Jedrzejewska B, 1993. Responses of bank voles to odors of seven species of predators: experimental data and their relevance to natural predator-vole relationships.Oikos 68:251 -257.

Kelly PM, Cory JS, 1987. Operculum closing as a defense against predatory leeches in four British freshwater prosobranch snails. Hydrobiology 144:121-124.

Koskela E, Ylönen H,1995 . Suppressed breeding in the field vole (Microtus agrestis): an adaptation to cyclically flucuating predation risk.Behav Ecol 6:311-315.[Abstract/Free Full Text]

Krebs JR, Davies NB, 1987. An introduction to behavioural ecology. Oxford: Blackwell Scientific.

Kriesch S, Dicke M, 1997. Avoidance of predatory mites by the two-spotted spider mite Tetranychus urticae: the role of infochemicals. Proc Exp Appl Entomol 8:121-126.

Lima SL, Dill LM, 1990. Behavioral decisions made under the risk of predation: a review and prospectus. Can J Zool 68:619-640.

Malmqvist B, 1992. Stream grazer responses to predator odour: an experimental study. Nord J Fresh Res 67:27-34.

Marko PB, Palmer AR, 1991. Responses of a rocky shore gastropod to the effluents of predatory and non-predatory crabs: avoidance and attraction. Biol Bull (Woods Hole) 181:363-370.[Abstract]

Mathis A, Chivers DP, Smith RJF, 1996. Cultural transmission of predator recognition in fishes: intraspecific and interspecific learning. Anim Behav 51:185-201.

Nolte DI, Mason JR, Epple G, Aronov E, Campbell DL,1994 . Why are predator urines aversive to prey? J Chem Ecol 20:1505-1516.

Ohgushi T, 1996. A reproductive tradeoff in an herbivorous lady beetle: egg resorption and female survival.Oecologia 106:345-351.

Pallini A, Janssen A, Sabelis MW, 1997. Odour-mediated responses of phytophagous mites to conspecific and heterospecific competitors.Oecologia 110:179-185.

Pickett JA, Wadhams LJ, Woodcock CM, Hardie J, 1992. The chemical ecology of aphids. Annu Rev Entomol 37:67-90.[Web of Science]

Pijanowska J, 1997. Alarm signals in Daphnia?Oecologia 112:12-16.

Plotkin PT, Rostal DC, Byles RA, Owens DW, 1997. Reproductive and developmental synchrony in female Lepidochelys olivacea. J Herpetol 31:17-22.

Rabbinge R, 1985. Aspects of damage assessment. In:Spider mites, their biology, natural enemies and control , vol. 1B (Helle W, Sabelis MW, eds). Amsterdam: Elsevier;261 -272.

Rittschof D, Hazlett BA, 1997. Behavioural responses of hermit crabs to shell cues, predator haemolymph and body odour. J Mar Biol Assoc 77:737-751.

Sabelis MW, 1981. Biological control of two-spotted spider mites using phytoseiid predators. Part 1: Modelling the predator-prey interaction at the individual level (PhD dissertation). Wageningen, the Netherlands: Wageningen Agricultural University.

Sabelis MW, 1985. Predation on spider mites. In:Spider mites, their biology, natural enemies and control , vol. 1B (Helle W, Sabelis MW, eds). Amsterdam: Elsevier;103 -130.

Sabelis MW, van der Meer J, 1986. Local dynamics of the interaction between predatory mites and two-spotted spider mites. In:Dynamics of physiologically structured populations (Metz JAJ, Diekman O, eds), Springer lecture notes in biomathematics 68. New York: Springer-Verlag, 322-343.

Sullivan T P, 1986. Influence of wolverine (Gulo gulo) odor on feeding behavior of snowshoe hares (Lepus americanus). J Mammal 67:385-388.

Sullivan TP, Crump DR, 1986. Feeding response of snowshoe hares (Lepus americanus) to volatile constituents of red fox (Vulpes vulpes) urine. J Chem Ecol 12:729-739.

Sullivan TP, Jin ZH, Li HL, Wang SC, 1991. Control of vole populations in young pine plantations in northeast China. Forest Chron 67:43-47.

Takabayashi J, Dicke M, Posthumus MA, 1994. Volatile herbivore-induced terpenoids in plant-mite interactions: variation caused by biotic and abiotic factors. J Chem Ecol 20:1329-1354.

Tollrian R, Harvell CD (eds), 1999. The ecology and evolution of inducible defenses. Princeton, New Jersey: Princeton University Press.

Tomczyk A, Kropczynska D, 1985. Effects on the host plant. In: Spider mites, their biology, natural enemies and control, vol. 1A (Helle W, Sabelis MW, eds). Amsterdam: Elsevier; 317-329.

Utne ACW, Bacchi B, 1997. The influence of visual and chemical stimuli from cod Gadus morhua on the distribution of the two spotted goby Gobiusculus flavescens (Fabricius).Sarsia 82:129-135.

Vadas RL Sr, Burrows MT, Hughes RN, 1994. Foraging strategies of dogwhelks, Nucella lapillus (L.): interacting effects of age, diet and chemical cues to the threat of predation.Oecologia 100:439-450.

Ward JF, MacDonald DW, Doncaster CP, Mauget C, 1996. Physiological response of the European hedgehog to predator and nonpredator odour. Physiol Behav 60:1469-1472.[Medline]

Woolhouse AD, Morgan DR, 1995. An evaluation of repellents to suppress browsing by possums. J Chem Ecol 21:1571-1583.

Ylönen H, Ronkainen H,1994 . Breeding suppression in the bank vole as antipredatory adaptation in a predictable environment. Ecol Evol 8:658-666.

Zimmerling TN, Zimmerling LM, 1996. A comparison of the effectiveness of predator odor and plant antifeedant in deterring small mammal feeding damage on lodgepole pine seedlings. J Chem Ecol 22:2123-2132.


Add to CiteULike CiteULike   Add to Connotea Connotea   Add to Del.icio.us Del.icio.us    What's this?


This article has been cited by other articles:


Home page
Behav EcolHome page
S. A. Juliano and M. E. Gravel
Predation and the evolution of prey behavior: an experiment with tree hole mosquitoes
Behav. Ecol., May 1, 2002; 13(3): 301 - 311.
[Abstract] [Full Text] [PDF]


Home page
Behav EcolHome page
M. H. Persons, S. E. Walker, and A. L. Rypstra
Fitness costs and benefits of antipredator behavior mediated by chemotactile cues in the wolf spider Pardosa milvina (Araneae: Lycosidae)
Behav. Ecol., May 1, 2002; 13(3): 386 - 392.
[Abstract] [Full Text] [PDF]


This Article
Right arrow Abstract Freely available
Right arrow FREE Full Text (PDF) Freely available
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Services
Right arrow Email this article to a friend
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Alert me to new issues of the journal
Right arrow Add to My Personal Archive
Right arrow Download to citation manager
Right arrow Search for citing articles in:
ISI Web of Science (42)
Right arrowRequest Permissions
Google Scholar
Right arrow Articles by Grostal, P.
Right arrow Articles by Dicke, M.
Right arrow Search for Related Content
PubMed
Right arrow Articles by Grostal, P.
Right arrow Articles by Dicke, M.
Social Bookmarking
 Add to CiteULike   Add to Connotea   Add to Del.icio.us  
What's this?