Distribution, abundance and substrate versatility relationships in Chaetodontidae and Pommacanthidae.

Size: px
Start display at page:

Download "Distribution, abundance and substrate versatility relationships in Chaetodontidae and Pommacanthidae."

Transcription

1 1 Luke Hately-Broad BIO-162. Quarter. Marine Ecology Field Distribution, abundance and substrate versatility relationships in tidae and Pommacanthidae. Hately-Broad L School of Biological Sciences, University of East Anglia, Norwich NR4 7TJ, England.

2 2 Abstract: The distribution, abundance and feeding preferences of eight species of tidae and two species of Pomacanthidae were examined within a reef complex on the island of Moorea, French Polynesia. The reef complex was divided into four areas; fringe, fringe patch, crest patch and crest. In each area a ten minute abundance survey and five fifty meter habitat availability transects were conducted. The feeding preference of every individual seen in three hours was also recorded for each area. Species richness was found to increase from the fringe to the crest reef. Two species Centropyge flavissimus and citrinellus were found to have a generalist diet and were the most abundant species at all sites. Five species were found to feed mainly on live corals and so were more abundant in coral rich areas, these species were; lunula, lunulatus, ornatissimus, reticulates and unimaculatus. ephippium and vagabondis were found to feed mainly on and so were most abundant in areas with a high availability of. The Final species Centropyge bispinosus was only observed in crevices in Porites rus in the fringing reef. Key words: Abundance, Coral reef fish, Distribution, Habitat specialisation, Versatility. Introduction: Ecological versatility is defined by McNally (1995) as the degree to which organisms can fully exploit the available resources in their local environment. Within coral reef fish assemblage s species vary in terms of their resource versatility (Futuyma & Moreno 1988). The effect of this resource versatility on the distribution and abundance of organisms has received much theoretical attention (e.g. McNaughton &Wolf 197, Morris 1996). From this research it is suggested that generalists potentially will have a greater local abundance and distribution as they have access to more of the local resources. Where as specialists may be able to out compete generalists in the use of certain resources (Bean et al. 2). In terms of habitats used this means that generalist species should occur in a broad range of habitats, while specialist species will only be found in a few habitats (Bean et al. 2). Both of these extremes in resource versatility have associated costs and benefits, in terms of competition and resource availability. The theoretical relationships between the level of resource versatility and the distribution and

3 3 abundance of organisms, has only recently been tested in terrestrial ecosystems (Hughes ). Research on the effects of resource versatility in coral reef fish assemblages is very limited (Jones et al. 2). Coral reef fish communities are highly diverse and have representatives of the full spectrum of habitat versatility, from specialist species associated with only a few coral species to generalists which are found on most substrate types present on the reef (Munday & Jones 1998, Syms & Jones ). Many species of fish show habitat selection at settlement (Ormond et al. 1996) however the habitat usage of an individual may vary during its life cycle and this may be important in evaluating the processes affecting the distribution and abundance of adults. The habitat usage of adults has mainly been studied in speciose families such as gobies (Munday et al. 1997) and damselfishes (Meekan et al. 1997). Although studies that relate habitat versatility to distribution and abundance have been conducted for some families (Bean et al. 2), little research has been conducted to compare these relationships between different families, geographical areas or to relate the findings to the evolutionary age of the species concerned. The tidae are a very speciose family and it has been suggested that the reason for this may be the differentiations in diet found among the species. Allen et al 1998 placed all tidae species into five groups depending on their feeding types. These groups are those that feed on; hard corals, soft corals, small benthic invertebrates, zooplankton and omnivores. In this study I examine the potential relationships between substrate association, in terms of food preferences, and the distribution and abundance of coral reef fish species from two families found around the island of Moorea, French Polynesia. Ten species from the two families were examined tidae vagabondis (Linnaeus 1758), unimaculatus (Bloch 1787), lunula (Lacépède 13), citrinellus (Cuvier 1831), reticulatus (Cuvier 1831), lunulatus (Quoy & Gaimard 1824), ornatissimus (Cuvier 1831) and ephippium (Cuvier 1831). Pomacanthidae Centropyge flavissimus (Cuvier 1831) and Centropyge bispinosus (Günther 18). Naming follows that used in Allen et al (1998). I tested the following hypotheses: -Given equal habitat availability, species that feed on a wide variety of substrates will have a greater local abundance and distribution than species restricted to a few substrate types. -For generalist species food preferences will be related to food availability, and so will change between areas. -There will be significant differences in food preferences between species

4 4 To test these predictions the abundance and feeding preferences of each species was recorded in each of the four areas at the sample site, habitat availability was also recorded for each site. Materials and Methods: This Study was conducted in four areas at the public beach site (17º S. 149º 5 91 W) on the island of Moorea, French Polynesia during November and December 2. The areas were the fringe, fringe patch, crest patch and crest reefs (Figure 1). Figure 1: A, Map of Moorea (French Polynesia) showing the location of the sampling site; B, Schematic cross section of the study site showing the location of the four sampling areas. The fringe reef is dominated by Porites rus which occurs in large patches, in this area both macro and turf algae is common with some Porites lobata also present. The average depth is about 1 meter. The fringe patch reef contains all the substrate types listed bellow but is dominated by with P. lobata being the most common coral and an average depth of about 1.8 meters. In the crest patch is still the most common substrate with P. lobata being the dominant coral however the diversity of corals present here is higher than in the two previous areas this is the deepest site with an average depth of about 2.3

5 5 meters. The crest is the most coral rich of the four areas, P. lobata is still dominant but to a lesser extent and coverage is much reduced the average depth is about 1.5 meters (Figure2). The channel was not sampled as Bouchon-Navaro (1981) found no chaetodontidae present in this area during his survey and suggested that this was due to the strong currents and barren bottom found in this area. All observations were made by snorkling. In each of the four areas the habitat availability was recorded using five randomly positioned 5 meter transects, along which the substrate was recorded every 2.5 meters as:, dead coral,, macro algae, turf algae, Porites rus, Porites lobata, Pocillopora verrucosa and faveolata. The abundance of the species within each area was recorded as the number of individuals seen in ten minutes of swimming. For this the swimming speed was kept constant for each survey and only fish within two meters of the observer were recorded to eliminate bias from changes in visibility. Lastly feeding preferences were recorded for as many individuals of each species as could be found in three hours of searching. This involved recording the substrate the individual was first seen to feed on or pecked at, (from the substrate list for the transects). The data was analysed using Pearson Chi-squared tests and graphical techniques using SYSTAT 9 and Microsoft Excel for Windows. Results: 7 Percentage cover Figure 2: Bar graph showing the habitat availability in the four areas of the study site (Public Beach, Moorea, French Polynesia).

6 6 The diversity of the species studied is highest in the crest patch with 8 species and a total of 67 individuals being recorded here during the abundance surveys. The diversity of the crest and fringe patch reefs is similar even though this is not reflected in the number of species or total individuals found in these areas (Table 1). Table 1also shows that the fringe reef is the least diverse of the four zones even though the same number of species are found here as in the fringe patch with more individuals being present. Table 1: Showing the, total number of species and individuals and the diversity (calculated using the Shannon-Weaver index H = -_Pi logpi) for the study site (Public Beach, Moorea, French Polynesia). Total Number Total Number of Individuals of Species Diversity Fringe Fringepatch Crestpatch Crest Figure 3 shows the number of individuals of each species found in the four areas. C. flavissima is the domminant species in all four areas, C. citrinellus is the next most abundant on all four areas. C. bispinosus was not found in any areas during the abundance surveys but was found during the food preference surveys. C. lunula was not common in any of the areas but was most abundant in the crest patch and was also found in small numbers in the crest and fringe reefs but was absent from the fringe patch. C. lunulatus was also absent from the fringe patch, this species was quite abundant in all other areas with the most individuals being recorded from the crest patch. C. ornatissimus was only observed in the crest patch and crest reefs being most abundant in the later. C. reticulatus was also only found in the crest patch and crest reefs but was most abundant in the crest patch. C. ephippium was only found in the fringe patch and crest reefs. It was not common in either of these areas but more individuals were seen in fringe patch. C. unimaculatus was not found in the fringe reef area and was only represented by a few individuals in both the fringe patch and crest reefs, however in the crest patch this species is the third most abundant. C. vagabondis was found in small numbers in all areas with a peak in abundance in the fringe patch. In table 2 the results of the Pearson Chi-square tests, which tested for significant between habitat availability and feeding preferences, are presented. A significant value shows that the species in question, is in that area, actively seeking out a particular food type or types. This means that the species is not randomly feeding on any

7 7 45 Number of Individuals Centropyge bispinosus Centropyge flavissima lunula lunulatus ornatissimus reticulatus ephippium citrinellus unimaculatus vagabondis Figure 3: Bar graph showing the number of individuals of each species found in the four different areas at the sample site (Public Beach, Moorea, French Polynesia). substrate it comes across. Values that are not significant, are generally explained by the absence of that species from that particular area. There are three values that are not significant and the species does occur in that area. These are C. vagabondis in the crest patch and C. reticulates and C. ephippium in the crest reef. The reason for these values not being significant is an insufficient sample size. The bar graphs of feeding preferences are shown as figures 4-13 in the appendix, they show the percentage of the total feeding actions that each species used on the different substrates in the different areas. Figure 4 shows that C. bispinosus was only observed in the fringe patch reef and here it fed primarily on macro algae and some dead coral. Figures 5 & 11 show the feeding preferences for C. flavissima and C. citrinellus. Both of these species are generalists wit C. citrinellus feeding on all substrates in the fringe, fringe patch and crest patch. C. flavissima feeds on dead coral, macro algae P. lobata and P. rus in these areas. In the crest reef both species feed on M. faveolata. Five species feed mainly on live corals, these are C. lunula, C. lunulatus, C. ornatissimus, C. reticulatus, and C. unimaculatus, the graphs for these species are shown in figures 6, 7, 8, 9 & 12. C. lunula only feeds on P. lobata in the crest patch reef, whilst C. lunulatus feeds mainly on Porites sp in all areas and M. faveolata where it is available. C. ornatissimus feeds

8 8 Table 2: Showing the results from Pearson Chi-square tests between habitat availability and feeding preferences. + shows a significant value (P<.5), - shows a non-significant value (P>.5). Degrees of freedom were never more than 9 and were usually less. Species Fringe Fringe Patch Crest Patch Crest Centropyge bispinosus Centropyge flavissima lunula lunulatus ornatissimus reticulatus ephippium citrinellus unimaculatus vagabondis on P. rus in the fringe reef with P. lobata being favoured in the other areas, C. reticulates also feeds on P. rus but in the fringe patch rather than in the fringe, M. faveolata is the preferred food types in the crest patch and crest reefs. C. unimaculatus was only observed in the fringe patch, crest patch and crest reefs where it mainly feeds on M. faveolata, in the fringe patch and crest patch this is the sole food type whilst in the crest small amounts of other substrates are eaten. C. ephippium and C. vagabondis both feed mainly on dead coral, and rubble (Figures 1 & 13). C. ephippium favours dead coral in the fringe patch and crest patch reefs, however this is not fed on in the crest. In this area rubble is the dominant food type. Sand is the preffered food type of C. vagabondis in all areas, but in the fringe and fringe patch it displays a more generalist diet. Table 3: Showing the results from Pearson Chi-square tests between for feeding preferences between species. + shows a significant value (P<.5), - shows a non-significant value (P>.5) shows a test that was not run due to replication. Degrees of freedom were never more than 9 and were usually less.

9 9 Table 3 shows the results for Pearson Chi-square tests between for feeding preferences between species, this was done to see if there is significant differences in what different Centropyge bispinosus Centropyge flavissima lunula lunulatus ornatissimus reticulatus ephippium citrinellus unimaculatus vagabondis Centropyge bispinosus Centropyge flavissima lunula lunulatus ornatissimus reticulatus ephippium citrinellus unimaculatu s vagabondis species eat. Most species show significantly different diets from each other. The major exceptions are C. lunula which is not significantly different from C. flavissima, C. lunulatus, C. ornatissimus or C. reticulates. Also C. lunulatus is not significantly different from C. ornatissimus. Discussion: The finding that species richness increases from the fringe to the crest agrees with Bouchon-Navaro s (1981) findings that species richness of chaetodontidae increases across the same gradient and can probably be explained by increasing coral richness. The high abundances of chaetodontidae in the crest and crest patch also agree with his findings. The general increase in diversity from the fringe to the crest reefs, the decrease at the crest can be explained by the dominance of C. flavissima. Supports the idea that chaetodontidae communities are dependent on coral diversity and cover to maintain their diversity (Bouchon-Navaro 1981). The reason for this may be niche separation, this is that each species feeds on a specific range of food types and these are significantly different to those found for all other species, this would allow many species to exist with out competition but will only work if all the required food types are present. The results

10 1 in table 3 may support this idea as they show that most species have significantly different food preferences. The lack of significant differences between C. lunula and most other species is probably due to the low numbers of observations for the feeding preferences of this species as explained above. However Bell et al (1985) found that there was no relationship between coral cover and number of individuals. The results from the Pearson Chi-square tests for feeding preferences between species, shown in Table 3, show that there are significant differences in food preferences between the pommacanthidae and the chaetodontidae. However due to very few pommacanthidae species being recorded this question can not be fully addressed. Centropyge bispinosus This species was only observed in small numbers in the fringe reef, it was always seen in cracks in P. rus that were surrounded by turbinaria. It was only seen feeding on dead coral and macro algae around these cracks. This agrees with Allen et al s (1998) description of this species as being shy and never straying far from reef crevices, and may explain the low number of observations through individuals being missed during surveys. Centropyge flavissima This is the most abundant species in all the areas, and has the highest abundance at the crest reef followed by the crest patch then fringe, the lowest abundance was found in the fringe patch. This species was seen to be a generalist feeder, which fed on every substrate type in at least one of the areas. The results of the statistical analysis of food choice against habitat availability show that this species actively sought out specific food types and did not just eat the most abundant types. The fact that it fed on all substrates could be because it feeds on filamentous algae (Allen et al 1998), which may have been growing on the substrates. lunula Only a small number of observations were made for this species at the fringe, crest patch and crest sites during the abundance surveys but was only observed feeding on P. lobata four times in the crest patch reef. This was because even though it was found in the other areas during the food preference surveys, it was followed for thirty minutes and was not seen to feed. This can be explained by the fact that this species is supposed to forage mainly at night (Allen et al 1998). The low abundances agree with findings from other studies, as does its occurrence in all the areas (Bouchon-Navaro 1981). lunnulatus The fringe, crest patch and crest were the only areas where this species was recorded during the abundance surveys, however during the food preference surveys it was observed in all areas. This species fed mainly on live corals. In the fringe the preferred species was P. rus but this was probably due to it being the dominant coral species. In all four areas

11 11 this species fed on with this being the dominant food type in the fringe patch and crest patch, in the crest M. faveolata was the favoured food type. This usage of mainly live coral agrees with the fact that this species is supposed to feed only on live corals (Allen et al 1998). ornatissimus This species was absent rom the fringe reef but was found in the other three sites and had the highest abundance on the crest reef, however this species is never common any where. This species as stated in Allen et al (1998) was only observed to feed on live corals, particularly Porites sp. It also feeds on M. faveolata in the crest patch and crest reefs. reticulatus During the abundance surveys this species was only recorded from the crest patch and crest reefs, however whilst conducting the feeding preference surveys it was also recorded from the fringe patch but it was never recorded from the fringe. This species fed exclusively on P. rus in the fringe patch and preferred this food source on the crest reef, in the crest patch it fed mainly on M. faveolata and only fed on this food source on the crest patch and crest reefs These findings agree with the description of this species as feeding mainly on coral polyps (Allen et al 1998). ephippium Observations of this species were limited to a few individuals in the fringe patch and crest reefs. During the feeding preference surveys it was also recorded in the crest patch where it fed exclusively on dead coral, in the other two areas it also fed on rubble and. When doing this the species was probably feeding on benthic invertebrates and algae s which are recorded food sources for this species (Allen et al 1998). citrinellus This is the second most abundant species in all four areas. This finding agrees with the findings of other studies on Moorea that this species is one of the most abundant chaetodontidae (Bouchon-Navaro 1981). In the fringe, fringe patch and crest patch reefs this species fed on almost all substrate types showing a preference for P. rus and in the fringe, P. lobata and in the fringe patch and dead coral, and M. faveolata in the crest patch. In the crest this species fed on dead coral and P. rus but mainly M. faveolata. These findings of food preference agree with Allen et al s (1998) placing of this species in the omnivore feeding group. unimaculatus C. unimaculatus was found in the fringe patch, crest patch and crest reefs, in the first of these two zones this species fed exclusively on M. faveolata. In the crest M. faveolata was still fed on but P. rus was the preferred food type but in this area it also fed on dead

12 12 coral and rubble. This suggests that in Moorea etleast this species may have a more restricted diet than the omnivore one suggested in Allen et al (1998). vagabondis This species was recorded in small numbers from all four areas and was most abundant in the fringe and fringe patch reefs. It feeds on a wide variety of substrate types but preferentially fed on in all four areas with dead coral and rubble being important food sources in the fringe patch, crest patch and crest. In the fringe P. rus was an important food source but this was probably due to P. rus dominating the substrate availability so much. When feeding in this species is probably feeding on polychaete worms as reported in Allen et al (1998). In further research the results of this study will be related to other studies describing the feeding preferences and distributions of pommacanthidae and chaetodontidae both for the area studied and other geographical areas to examine the biogeographical repeatability of these findings. The results will also be analysed in light of the evolutionary age of the species to see if any relationships exist between the findings and this factor. Acknowledgements: I wish to thank Drs G. Bernardi and P. Raimondi for there help at all stages of this study. I also would like to thank all the staff of the C.R.I.O.B.E. research station for enabling me to conduct this study. I extend my thanks to B. Perlman, M. Readdie and J. Engel for their help in data collection. Appendix: Figures 4-13 show the relationships between the number of times a species fed on a particular substrate and how this changes between areas at the sample site Public Beach,

13 13 Moorea, French Polynesia. Centropyge bispinosus Figure 4: The relationship between the number of times C. bispinosus fed on a particular substrate and the variation in these numbers between areas. Centropyge flavissima Figure 5: The relationship between the number of times C. flavissima fed on a particular substrate and the variation in these numbers between areas.

14 14 lunula 1 Number of times fed on 1 Figure 6: The relationship between the number of times C. lunula fed on a particular substrate and the variation in these numbers between areas. lunulatus 1 Number of times fed on Figure 7: The relationship between the number of times C. lunulatus fed on a particular substrate and the variation in these numbers between areas.

15 15 ornatissimus 1 Number of times fed on 1 Figure 8: The relationship between the number of times C. ornatissimus fed on a particular substrate and the variation in these numbers between areas. reticulatus 1 Number of times fed on 1 Figure 9: The relationship between the number of times C. reticulates fed on a particular substrate and the variation in these numbers between areas.

16 16 ephippium 1 Number of times fed on 1 Figure 1: The relationship between the number of times C. ephippium fed on a particular substrate and the variation in these numbers between areas. citrinellus Number of times fed on Figure 11: The relationship between the number of times C. citrinellus fed on a particular substrate and the variation in these numbers between areas.

17 17 unimaculatus 1 Number of times fed on 1 Figure 12: The relationship between the number of times C. unimaculatus fed on a particular substrate and the variation in these numbers between areas. vagabondis Number of times fed on Figure 13: The relationship between the number of times C. vagabondis fed on a particular substrate and the variation in these numbers between areas.

18 18 References: Allen G.R., Steene R. & Allen M A Guide to Angelfishes and Butterflyfishes. Vanguard Press, Perth. Bean K., Jones G.P. & Caley M.J., 2. Relationships among distribution, abundance and microhabitat specialisation in a guild of coral reef triggerfish (family Balistidae). Mar Ecol Prog Ser. 233, Bell J., Harmelin-Vivien M. & Galzin R Large scale spatial variation in abundance of butterflyfishes (tidae) on Polynesian reefs. Proceedings of the Fifth International Coral Reef Congress, Tahiti, 1985, Vol Bouchon-Navaro Y Quantitative distribution of the chaetodontidae on a reef of Moorea island (French Polynesia). J. exp. Mar. Biol. Ecol. 55, Futuyma D.J. & Moreno G., The evolution of ecological specialisation. Annu Rev Ecol Syst. 19, Hughes J.B.,. The scale of resource specialisation and the distribution and abundance of Lycaenid butterflies. Oecologia. 123, Jones G.P., Caley M.J. & Munday P.L., 2. Rarity in coral reef fish communities. In: Sale P.F. (ed) Coral reef fishes: dynamics and diversity in a complex ecosystem. Academic Press, San Diego,p McNally R.C., Ecological versatility and community University Press. Cambridge. ecology. Cambridge McNaughton S.J. & Wolf L.L., 197. Dominance and the niche in ecological systems. Science. 167, Meekan M.G., Steven A.D.L. & Fortin M.J., Spatial patterns in the distribution of damselfishes on a fringing coral reef. Coral Reefs. 14, Morris D.A., Coexistence of specialist and generalist rodents via habitat selection. Ecology. 77,

19 19 Munday P.L. & Jones G.P., The ecological implications of small body size among coral-reef fishes. Oceanogr Mar Biol Annu Rev. 36, Munday P.L., Caley J.M. & Jones G.P., Bi-directional sex change in a coral reef dwelling goby. Behav Ecol Sociobiol. 43, Ormond R.F.G., Roberts J.M., & Jan R.Q., Behavioural differences in microhabitat use by damselfishes (Pomacentridae): implications for coral reef fish biodiversity. J Exp Mar Biol Ecol. 2, Syms C. & Jones G.P.,. Disturbance, habitat structure and the dynamics of a coral reef fish community. Ecology. 81,

ESM: S1: Table of colour patterns and ecological traits, their definitions, measures used and possible values

ESM: S1: Table of colour patterns and ecological traits, their definitions, measures used and possible values ESM: S1: Table of colour patterns and ecological traits, their definitions, measures used and possible values Morphology Ecology Social behavior Trait Definition Measures Values Spot Roughly circular marking,

More information

Influence of dietary specialization and resource availability on geographical variation in abundance of butterflyfish

Influence of dietary specialization and resource availability on geographical variation in abundance of butterflyfish Influence of dietary specialization and resource availability on geographical variation in abundance of butterflyfish Rebecca J. Lawton & Morgan S. Pratchett ARC Centre of Excellence for Coral Reef Studies,

More information

Spatial variation in distribution of fish species can be attributed to many different factors

Spatial variation in distribution of fish species can be attributed to many different factors Ben Perlman Rikke Kvist Preisler Site fidelity, coral type fidelity and coral type preference for the Humbug Damselfish, Dascyllus aruanus Abstract This study took place in the lagoon in front of Public

More information

This file is part of the following reference: Access to this file is available from:

This file is part of the following reference: Access to this file is available from: ResearchOnline@JCU This file is part of the following reference: Pratchett, Morgan S. (2001) Dynamics of outbreak populations of crown-of-throns starfish (Acanthaster planci L.), and their effects on coral

More information

Effects of resource availability on the competitive behaviour of butterflyfishes (Chaetodontidae)

Effects of resource availability on the competitive behaviour of butterflyfishes (Chaetodontidae) Effects of resource availability on the competitive behaviour of butterflyfishes (Chaetodontidae) Michael L. BERUMEN 1, 2 * and Morgan S. PRATCHETT 1 1 Centre for Coral Reef Biodiversity, School of Marine

More information

Biological and physical correlates of settlement and survival for a coral reef fish, Pomacentrus amboinensis (Pomacentridae)

Biological and physical correlates of settlement and survival for a coral reef fish, Pomacentrus amboinensis (Pomacentridae) Biological and physical correlates of settlement and survival for a coral reef fish, Pomacentrus amboinensis (Pomacentridae) Mark I. McCORMICK* and Andrew S. HOEY School of Marine Biology and Aquaculture,

More information

FEEDING PREFERENCES OF THE CUSHION STAR CULCITA NOVAEGUINEAE IN THE PRESENCE OF THE CROWN OF THORNS STARFISH ACANTHASTER PLANCI

FEEDING PREFERENCES OF THE CUSHION STAR CULCITA NOVAEGUINEAE IN THE PRESENCE OF THE CROWN OF THORNS STARFISH ACANTHASTER PLANCI FEEDING PREFERENCES OF THE CUSHION STAR CULCITA NOVAEGUINEAE IN THE PRESENCE OF THE CROWN OF THORNS STARFISH ACANTHASTER PLANCI JENNIFER BELL Environmental Science Policy and Management, University of

More information

Calvi, Corsica. Brittany Boyd. University of California Santa Cruz, STARESO Underwater and Oceanography Research Station

Calvi, Corsica. Brittany Boyd. University of California Santa Cruz, STARESO Underwater and Oceanography Research Station Halocynthia papillosa association with other sessile marine invertebrates in Calvi, Corsica Brittany Boyd University of California Santa Cruz, STARESO Underwater and Oceanography Research Station ABSTRACT

More information

Population Regulation of Coral Reef Fishes. Final Report of 2007 Research Authorization. Sally J. Holbrook and Russell J. Schmitt

Population Regulation of Coral Reef Fishes. Final Report of 2007 Research Authorization. Sally J. Holbrook and Russell J. Schmitt Population Regulation of Coral Reef Fishes Final Report of 2007 Research Authorization Sally J. Holbrook and Russell J. Schmitt Marine Science Institute and Department of Ecology, Evolution and Marine

More information

Questions from reading and discussion section (1-3 will be on exam)- 5 or 10 points each

Questions from reading and discussion section (1-3 will be on exam)- 5 or 10 points each 2017 Mock Exam - Marine Ecology 108; page 1 The concepts and questions on the exam will come from the terms and questions listed below except there may be new questions from lecture and readings from remaining

More information

Influence of corallivory, competition, and habitat structure on coral community shifts

Influence of corallivory, competition, and habitat structure on coral community shifts Ecology, 92(10), 2011, pp. 1959 1971 Ó 2011 by the Ecological Society of America Influence of corallivory, competition, and habitat structure on coral community shifts HUNTER S. LENIHAN, 1,2,4 SALLY J.

More information

Community Structure. Community An assemblage of all the populations interacting in an area

Community Structure. Community An assemblage of all the populations interacting in an area Community Structure Community An assemblage of all the populations interacting in an area Community Ecology The ecological community is the set of plant and animal species that occupy an area Questions

More information

RELATING BEHAVIOR TO HABITAT: SOLUTIONS TO THE FOURTH-CORNER PROBLEM

RELATING BEHAVIOR TO HABITAT: SOLUTIONS TO THE FOURTH-CORNER PROBLEM Ecology, 78(2), 997, pp. 547 562 997 by the Ecological Society of America RELATING BEHAVIOR TO HABITAT: SOLUTIONS TO THE FOURTH-CORNER ROBLEM IERRE LEGENDRE, RENÉ GALZIN, 2,4 AND MIREILLE L. HARMELIN-VIVIEN

More information

Habitat selection and aggression as determinants of spatial segregation among damsel sh on a coral reef

Habitat selection and aggression as determinants of spatial segregation among damsel sh on a coral reef Coral Reefs 2001) 20: 289±298 DOI 10.1007/s003380100173 REPORT L.K. Bay á G.P. Jones á M.I. McCormick Habitat selection and aggression as determinants of spatial segregation among damsel sh on a coral

More information

Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level

Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level www.xtremepapers.com Cambridge International Examinations Cambridge International Advanced Subsidiary and Advanced Level *5788967979* MARINE SCIENCE 9693/01 Paper 1 AS Structured Questions May/June 2015

More information

SEA URCHINS ON THE MOVE: DISTRIBUTION CHANGE OF ECHINOMETRA IN MO OREA, FRENCH POLYNESIA

SEA URCHINS ON THE MOVE: DISTRIBUTION CHANGE OF ECHINOMETRA IN MO OREA, FRENCH POLYNESIA SEA URCHINS ON THE MOVE: DISTRIBUTION CHANGE OF ECHINOMETRA IN MO OREA, FRENCH POLYNESIA MARIA D. ZIZKA Integrative Biology, University of California, Berkeley, California 94720 USA Abstract. The island

More information

Kamalo, Molokai 21 o N 156 o W

Kamalo, Molokai 21 o N 156 o W Kamalo, Molokai 21 o 02.496 N 156 o 53.837 W Management Status: Open access Area Description: Wide coastal plain with muddy sand beach shoreline. Residential area. Inner reef flat silty sand. Outer flat

More information

LOCAL RETENTION OF PRODUCTION IN MARINE POPULATIONS: EVIDENCE, MECHANISMS, AND CONSEQUENCES. Robert R. Warner and Robert K. Cowen

LOCAL RETENTION OF PRODUCTION IN MARINE POPULATIONS: EVIDENCE, MECHANISMS, AND CONSEQUENCES. Robert R. Warner and Robert K. Cowen BULLETIN OF MARINE SCIENCE, 70(1) SUPPL.: 245 249, 2002 LOCAL RETENTION OF PRODUCTION IN MARINE POPULATIONS: EVIDENCE, MECHANISMS, AND CONSEQUENCES Robert R. Warner and Robert K. Cowen A major unanswered

More information

Community Interactions. Community An assemblage of all the populations interacting in an area

Community Interactions. Community An assemblage of all the populations interacting in an area Community Interactions Community An assemblage of all the populations interacting in an area Populations are affected by: Available living space habitat Resource Availability niche Species interactions

More information

Does habitat availability determine geographical-scale abundances of coral-dwelling fishes?

Does habitat availability determine geographical-scale abundances of coral-dwelling fishes? Coral Reefs (2002) 21:105 116 DOI 10.1007/s00338-001-0200-y REPORT P.L. Munday Does habitat availability determine geographical-scale abundances of coral-dwelling fishes? Received: 22 March 2001 / Accepted:

More information

Coral Bleaching and the Effect of Disturbances on the Damselfish Community on Lizard Island, Australia

Coral Bleaching and the Effect of Disturbances on the Damselfish Community on Lizard Island, Australia SIT Graduate Institute/SIT Study Abroad SIT Digital Collections Independent Study Project (ISP) Collection SIT Study Abroad Winter 2017 Coral Bleaching and the Effect of Disturbances on the Damselfish

More information

"The Relationship Between Seagrass Cover and Species- richness of Invertebrates"

The Relationship Between Seagrass Cover and Species- richness of Invertebrates "The Relationship Between Seagrass Cover and Species- richness of Invertebrates" SCIE 2204: Marine Systems The Cottesloe Marine Ecosystem Research Project 2014 By Baronie Shaw, K., Bortoloso, T., Cargill,

More information

GENERAL ECOLOGY STUDY NOTES

GENERAL ECOLOGY STUDY NOTES 1.0 INTRODUCTION GENERAL ECOLOGY STUDY NOTES A community is made up of populations of different organisms living together in a unit environment. The manner in which these organisms relate together for

More information

Ecology. How the World Works

Ecology. How the World Works Ecology How the World Works Ecology is the study of interactions between living organisms and other living organisms and non living resources that they interact with. Levels of Organization Organism- a

More information

The Balance of Nature and Human Impact, ed. Klaus Rohde. Published by Cambridge University Press. Cambridge University Press 2013.

The Balance of Nature and Human Impact, ed. Klaus Rohde. Published by Cambridge University Press. Cambridge University Press 2013. Introduction Klaus Rohde It is obvious that nature is undergoing rapid changes as a result of human activities such as industry, agriculture, travel, fisheries, urbanization, etc. What effects do these

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

Current controversies in Marine Ecology with an emphasis on Coral reef systems. Niche Diversification Hypothesis Assumptions:

Current controversies in Marine Ecology with an emphasis on Coral reef systems. Niche Diversification Hypothesis Assumptions: Current controversies in Marine Ecology with an emphasis on Coral reef systems Open vs closed populations (already Discussed) The extent and importance of larval dispersal Maintenance of Diversity Equilibrial

More information

Edwin A. Hernández-Delgado*

Edwin A. Hernández-Delgado* Long-term Coral Reef Ecological Change Monitoring Program of the Luis Peña Channel Marine Fishery Reserve, Culebra Island, Puerto Rico: I. Status of the coral reef epibenthic communities (1997-2002). Edwin

More information

Settlement Patterns of Dascyllus flavicaudus and D. aruanus on Pocillopora spp.

Settlement Patterns of Dascyllus flavicaudus and D. aruanus on Pocillopora spp. Settlement Patterns of Dascyllus flavicaudus and D. aruanus on Pocillopora spp. Moira Decima and Holly Kindsvater Abstract Settlement patterns of two Dascyllus species provide insight into the relationship

More information

This file is part of the following reference: Access to this file is available from:

This file is part of the following reference: Access to this file is available from: ResearchOnline@JCU This file is part of the following reference: Berumen, Michael Lee (2006) Influence of resource availability on lifehistory traits in coral-feeding butterflyfishes (Pisces: Chaetodontidae).

More information

Measuring Structural Complexity on Coral Reefs

Measuring Structural Complexity on Coral Reefs Diving For Science In: 2007 Pollock Proceedings NW, Godfrey Of JM, The eds. American Diving for Science Academy 2007. Of Underwater Sciences Proceedings of the American Academy of Underwater Sciences 26

More information

The use of specialisation indices to predict vulnerability of. coral-feeding butterflyfishes to environmental change

The use of specialisation indices to predict vulnerability of. coral-feeding butterflyfishes to environmental change The use of specialisation indices to predict vulnerability of coral-feeding butterflyfishes to environmental change Rebecca J. Lawton a,d, Morgan S. Pratchett a, Michael L. Berumen b,c. a ARC Centre of

More information

Current controversies in Marine Ecology with an emphasis on Coral reef systems

Current controversies in Marine Ecology with an emphasis on Coral reef systems Current controversies in Marine Ecology with an emphasis on Coral reef systems Open vs closed populations (already discussed) The extent and importance of larval dispersal Maintenance of Diversity Equilibrial

More information

Coral-seaweed interactions and the implications for resilience of coral reefs Roberta M Bonaldo

Coral-seaweed interactions and the implications for resilience of coral reefs Roberta M Bonaldo 1 Coral-seaweed interactions and the implications for resilience of coral reefs Roberta M Bonaldo Introduction On coral reefs, coral-seaweed competition is one of the primary determinants of benthic community

More information

Biological survey of species diversity of sea grass beds in selected sites of southern Sri-Lanka.

Biological survey of species diversity of sea grass beds in selected sites of southern Sri-Lanka. Biological survey of species diversity of sea grass beds in selected sites of southern Sri-Lanka. Hikkaduwa,Weligama,Polhena. Harishcandra K.A.D.A.T FS/2006/010 Introduction. 1.What are Sea grasses? 2.Distribution

More information

Aggregations on larger scales. Metapopulation. Definition: A group of interconnected subpopulations Sources and Sinks

Aggregations on larger scales. Metapopulation. Definition: A group of interconnected subpopulations Sources and Sinks Aggregations on larger scales. Metapopulation Definition: A group of interconnected subpopulations Sources and Sinks Metapopulation - interconnected group of subpopulations sink source McKillup and McKillup

More information

Honors Biology Ecology Concept List

Honors Biology Ecology Concept List 1. For each pair of terms, explain how the meanings of the terms differ. a. mutualism and commensalism b. parasitism and predation c. species richness and species diversity d. primary succession and secondary

More information

Ch20_Ecology, community & ecosystems

Ch20_Ecology, community & ecosystems Community Ecology Populations of different species living in the same place NICHE The sum of all the different use of abiotic resources in the habitat by s given species what the organism does what is

More information

Community Ecology Bio 147/247 Species Richness 3: Diversity& Abundance Deeper Meanings of Biodiversity Speci es and Functional Groups

Community Ecology Bio 147/247 Species Richness 3: Diversity& Abundance Deeper Meanings of Biodiversity Speci es and Functional Groups Community Ecology Bio 147/247 Species Richness 3: Diversity& Abundance Deeper Meanings of Biodiversity Speci es and Functional Groups The main Qs for today are: 1. How many species are there in a community?

More information

Coral reef monitoring at Reunion island (Western Indian Ocean) using the GCRMN method

Coral reef monitoring at Reunion island (Western Indian Ocean) using the GCRMN method Proceedings 9 th International Coral Reef Symposium, Bali, Indonesia 23-27 October 2000, Vol. 2 Coral reef monitoring at Reunion island (Western Indian Ocean) using the GCRMN method P. Chabanet 1, L. Bigot

More information

BIOS 6150: Ecology Dr. Stephen Malcolm, Department of Biological Sciences

BIOS 6150: Ecology Dr. Stephen Malcolm, Department of Biological Sciences BIOS 6150: Ecology Dr. Stephen Malcolm, Department of Biological Sciences Week 14: Roles of competition, predation & disturbance in community structure. Lecture summary: (A) Competition: Pattern vs process.

More information

Alligator mississippiensis.

Alligator mississippiensis. Alligator mississippiensis http://www.birdsasart.com/bn201.htm Core Case Study: Why Should We Care about the American Alligator? Largest reptile in North America 1930s: Hunters and poachers Importance

More information

BZ471, Steam Biology & Ecology Exam

BZ471, Steam Biology & Ecology Exam BZ471, Eam1, p.1 BZ471, Steam Biology & Ecology Eam Name Multiple choice When benthic organisms enter the water column with a regular diel periodicity: a) catastrophic drift b) behavioral drift c) constant

More information

Treasure Coast Science Scope and Sequence

Treasure Coast Science Scope and Sequence Course: Marine Science I Honors Course Code: 2002510 Quarter: 3 Topic(s) of Study: Marine Organisms and Ecosystems Bodies of Knowledge: Nature of Science and Life Science Standard(s): 1: The Practice of

More information

VI) Population and Community Stability. VI) Population and Community Stability. I. Background / questions - refer back to succession

VI) Population and Community Stability. VI) Population and Community Stability. I. Background / questions - refer back to succession VI) Population and Community Stability I. Background / questions - refer back to succession A) Do marine communities trend toward climax states? B) Is there a single climax state? C) At climax, are populations

More information

History and meaning of the word Ecology A. Definition 1. Oikos, ology - the study of the house - the place we live

History and meaning of the word Ecology A. Definition 1. Oikos, ology - the study of the house - the place we live History and meaning of the word Ecology. Definition 1. Oikos, ology - the study of the house - the place we live. Etymology - origin and development of the the word 1. Earliest - Haeckel (1869) - comprehensive

More information

Stability Of Specialists Feeding On A Generalist

Stability Of Specialists Feeding On A Generalist Stability Of Specialists Feeding On A Generalist Tomoyuki Sakata, Kei-ichi Tainaka, Yu Ito and Jin Yoshimura Department of Systems Engineering, Shizuoka University Abstract The investigation of ecosystem

More information

VI) Population and Community Stability. VI) Population and Community Stability

VI) Population and Community Stability. VI) Population and Community Stability VI) Population and Community Stability I. Background / questions - refer back to succession A) Do marine communities trend toward climax states? B) Is there a single climax state? C) At climax, are populations

More information

FUNCTIONAL BIODIVERSITY OF MARINE SOFT BOTTOM POLYCHETES IN TWO MEDITERRANEAN COASTAL AREAS

FUNCTIONAL BIODIVERSITY OF MARINE SOFT BOTTOM POLYCHETES IN TWO MEDITERRANEAN COASTAL AREAS 1 Nasi F., 1 Auriemma R., 1 Cibic T., 1 Del Negro P., 2 Bonsdorff E., 2 Nordström M. C. 1 Istituto Nazionale di Oceanografia e Geofisica Sperimentale (OGS), Sezione Oceanografia, Trieste, Italy 2 Åbo Akademi

More information

Weekly summary of Tropic101x as posted by student Lucia_Agudelo

Weekly summary of Tropic101x as posted by student Lucia_Agudelo Weekly summary of Tropic101x as posted by student Lucia_Agudelo With minor grammatical and content edits by Tropic101x team Summary of Week 6 FIELD METHODS LECTURE 6.1.1 Being able to measure the distribution,

More information

BIOS 569: Practicum in Field Biology. Impact of DOC in the Zooplankton Community Composition. Amarilis Silva Rodriguez. Advisor: Patrick Kelly

BIOS 569: Practicum in Field Biology. Impact of DOC in the Zooplankton Community Composition. Amarilis Silva Rodriguez. Advisor: Patrick Kelly BIOS 569: Practicum in Field Biology Impact of DOC in the Zooplankton Community Composition Amarilis Silva Rodriguez Advisor: Patrick Kelly 2013 Abstract: Dissolved organic carbon (DOC) plays an important

More information

Rocky Intertidal Ecology -- part II The development of experimental ecology. Connell and the experimental revolution

Rocky Intertidal Ecology -- part II The development of experimental ecology. Connell and the experimental revolution Rocky Intertidal Ecology -- part II The development of experimental ecology I. Intertidal Zonation, part II 1. Follow ups on Connell 2. Predation 3. Exceptions II. Horizontal Distribution 1. Variation

More information

Ecosystem change: an example Ecosystem change: an example

Ecosystem change: an example Ecosystem change: an example 5/13/13 Community = An assemblage of populations (species) in a particular area or habitat. Here is part of a community in the grassland of the Serengetti. Trophic downgrading of planet Earth: What escapes

More information

AP Environmental Science I. Unit 1-2: Biodiversity & Evolution

AP Environmental Science I. Unit 1-2: Biodiversity & Evolution NOTE/STUDY GUIDE: Unit 1-2, Biodiversity & Evolution AP Environmental Science I, Mr. Doc Miller, M.Ed. North Central High School Name: ID#: NORTH CENTRAL HIGH SCHOOL NOTE & STUDY GUIDE AP Environmental

More information

Talks are generally led by the keepers and may vary between different staff members. We will adapt this talk according to the age of students.

Talks are generally led by the keepers and may vary between different staff members. We will adapt this talk according to the age of students. Key Stage 3 & Key Stage 4 HABITATS & ADAPTATIONS General points about this talk: Talks generally last 30-40 minutes and take place out in the Park in all weathers; please ensure that your pupils wear suitable

More information

Changing feeding preferences of butterflyfishes following coral bleaching

Changing feeding preferences of butterflyfishes following coral bleaching Changing feeding preferences of butterflyfishes following coral bleaching Chiara Pisapia 1, Andrew J. Cole 1, Morgan S. Pratchett 1 1 ARC Centre of Excellence for Coral Reef Studies, James Cook University,

More information

Project 1.3.1: Improved knowledge of biota, habitats and risks. Project Leader: Dr Mick Haywood, CSIRO Division of Marine and Atmospheric Research

Project 1.3.1: Improved knowledge of biota, habitats and risks. Project Leader: Dr Mick Haywood, CSIRO Division of Marine and Atmospheric Research Marine and Tropical Sciences Research Facility (MTSRF) June 2007 Milestone Report Project 1.3.1: Improved knowledge of biota, habitats and risks Project Leader: Dr Mick Haywood, CSIRO Division of Marine

More information

Sea Urchin Predation in Misali Island Marine Park

Sea Urchin Predation in Misali Island Marine Park SIT Graduate Institute/SIT Study Abroad DigitalCollections@SIT Independent Study Project (ISP) Collection SIT Study Abroad 4-1-2006 Sea Urchin Predation in Misali Island Marine Park Nicole Esclamado SIT

More information

4. Ecology and Population Biology

4. Ecology and Population Biology 4. Ecology and Population Biology 4.1 Ecology and The Energy Cycle 4.2 Ecological Cycles 4.3 Population Growth and Models 4.4 Population Growth and Limiting Factors 4.5 Community Structure and Biogeography

More information

Outline. - Background of coastal and marine conservation - Species distribution modeling (SDM) - Reserve selection analysis. - Results & discussion

Outline. - Background of coastal and marine conservation - Species distribution modeling (SDM) - Reserve selection analysis. - Results & discussion Application of GIS for data preparation and modeling for coastal and marine conservation planning in Madagascar Rija Rajaonson Technical Assistant, REBIOMA Wildlife Conservation Society Madagascar Outline

More information

Yakın Doğu Üniversitesi Mimarlık Fakültesi Peyzaj Mimarlığı Bölümü. PM 317 Human and Environment Assoc. Prof. Dr. Salih GÜCEL

Yakın Doğu Üniversitesi Mimarlık Fakültesi Peyzaj Mimarlığı Bölümü. PM 317 Human and Environment Assoc. Prof. Dr. Salih GÜCEL Yakın Doğu Üniversitesi Mimarlık Fakültesi Peyzaj Mimarlığı Bölümü PM 317 Human and Environment Assoc. Prof. Dr. Salih GÜCEL Ecology & Ecosystems Principles of Ecology Ecology is the study of the interactions

More information

A population is a group of individuals of the same species, living in a shared space at a specific point in time.

A population is a group of individuals of the same species, living in a shared space at a specific point in time. A population is a group of individuals of the same species, living in a shared space at a specific point in time. A population size refers to the number of individuals in a population. Increase Decrease

More information

Community Ecology Feral cat populations can be damaging to ecosystems.

Community Ecology Feral cat populations can be damaging to ecosystems. Community Ecology Feral cat populations can be damaging to ecosystems. Why? Photo Credit: http://www.flickr.com/photos/daveograve/4562537127/ Concept of the Community Community = assemblage of populations

More information

Coral Disease and Community Structure throughout the Northwestern Hawaiian Islands. Kailey Pascoe

Coral Disease and Community Structure throughout the Northwestern Hawaiian Islands. Kailey Pascoe Coral Disease and Community Structure throughout the Northwestern Hawaiian Islands Kailey Pascoe Marine Science Department University of Hawai i at Hilo Advisors Dr. Steven Colbert Marine Science Department

More information

Larvae. Juvenile. Adult. Bipartite life cycle of benthic marine fishes with pelagic larvae. Pelagic Environment. settlement.

Larvae. Juvenile. Adult. Bipartite life cycle of benthic marine fishes with pelagic larvae. Pelagic Environment. settlement. 13 - Marine Ecology Bipartite life cycle of benthic marine fishes with pelagic larvae Larvae survive, grow, develop, disperse reproduce Pelagic Environment Benthic Environment settlement Adult Juvenile

More information

Effects to Communities & Ecosystems

Effects to Communities & Ecosystems Biology 5868 Ecotoxicology Effects to Communities & Ecosystems April 18, 2007 Definitions Ecological Community an assemblage of populations living in a prescribed area or physical habitat [It is] the living

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

Gary G. Mittelbach Michigan State University

Gary G. Mittelbach Michigan State University Community Ecology Gary G. Mittelbach Michigan State University Sinauer Associates, Inc. Publishers Sunderland, Massachusetts U.S.A. Brief Table of Contents 1 Community Ecology s Roots 1 PART I The Big

More information

Biophysical assessment of reefs in Keppel Bay: a baseline study (April 2007)

Biophysical assessment of reefs in Keppel Bay: a baseline study (April 2007) Contents INTRODUCTION...5 METHODS...6 SURVEY SITES AND HABITAT TYPES...7 SURVEY RESULTS...10 ACKNOWLEDGEMENTS...33 REFERENCES...34 APPENDIX A. COORDINATES OF SITES SURVEYED...35 4 Introduction The Keppel

More information

Population Study Survey of Acanthaster planci, the Crown-of-Thorns starfish on the Northwest Coast Moorea, French Polynesia

Population Study Survey of Acanthaster planci, the Crown-of-Thorns starfish on the Northwest Coast Moorea, French Polynesia Population Study Survey of Acanthaster planci, the Crown-of-Thorns starfish on the Northwest Coast Moorea, French Polynesia Casey Clark & Benjamin Weitzman Abstract: Outbreaks of Acanthaster planci, the

More information

Guard crabs alleviate deleterious effects of vermetid snails on a branching coral

Guard crabs alleviate deleterious effects of vermetid snails on a branching coral Guard crabs alleviate deleterious effects of vermetid snails on a branching coral Coral Reefs Journal of the International Society for Reef Studies ISSN 0722-4028 Volume 29 Number 4 Coral Reefs (2010)

More information

Chapter 54: Community Ecology

Chapter 54: Community Ecology AP Biology Guided Reading Name Chapter 54: Community Ecology Overview 1. What does community ecology explore? Concept 54.1 Community interactions are classified by whether they help, harm, or have no effect

More information

Half Hollow Hills High School AP Biology

Half Hollow Hills High School AP Biology Chapter 53 Community Ecology Essential questions What factors structure a community? What species & how many are present in a community? In what way do the populations interact? What roles do species play

More information

The factors together:

The factors together: Biotic Interactions 8.11A DESCRIBE PRODUCER/CONSUMER, PREDATOR/PREY AND PARASITE/HOST RELATIONSHIPS AS THEY OCCUR IN FOOD WEBS WITHIN MARINE, FRESHWATER AND TERRESTRIAL ECOSYSTEMS Biotic These are the

More information

This file is part of the following reference: Access to this file is available from:

This file is part of the following reference: Access to this file is available from: This file is part of the following reference: Srinivasan, Maya (2006) Recruitment in time and space: the dynamics and distributions of reef fish populations on a low latitude coral reef. PhD thesis, James

More information

ENVE203 Environmental Engineering Ecology (Nov 19, 2012)

ENVE203 Environmental Engineering Ecology (Nov 19, 2012) ENVE203 Environmental Engineering Ecology (Nov 19, 2012) Elif Soyer Biological Communities COMPETITION Occurs when 2 or more individuals attempt to use an essential common resource such as food, water,

More information

Ecological mapping using satellite imagery: an Abu Dhabi case study Middle East Geospatial Forum 16 th February 2015

Ecological mapping using satellite imagery: an Abu Dhabi case study Middle East Geospatial Forum 16 th February 2015 Ecological mapping using satellite imagery: an Abu Dhabi case study Middle East Geospatial Forum 16 th February 2015 Richard Flemmings rf@proteusgeo.com About Proteus Formed in UAE 2011 We specialise in

More information

Chapter 3. Table of Contents. Section 1 Community Ecology. Section 2 Terrestrial Biomes & Aquatic Ecosystems

Chapter 3. Table of Contents. Section 1 Community Ecology. Section 2 Terrestrial Biomes & Aquatic Ecosystems Communities, Biomes, and Ecosystems Table of Contents Section 1 Community Ecology Section 2 Terrestrial Biomes & Section 1 Community Ecology Evolution in Communities Interactions Among Species Some interactions

More information

Responses of temperate mobile. macroinvertebrates to reef habitat. structure and protection from fishing. Timothy John Alexander, B.Sc.

Responses of temperate mobile. macroinvertebrates to reef habitat. structure and protection from fishing. Timothy John Alexander, B.Sc. Responses of temperate mobile macroinvertebrates to reef habitat structure and protection from fishing Timothy John Alexander, B.Sc. (Hons) Submitted in fulfilment of the requirements for the degree of

More information

Resources. Visual Concepts. Chapter Presentation. Copyright by Holt, Rinehart and Winston. All rights reserved.

Resources. Visual Concepts. Chapter Presentation. Copyright by Holt, Rinehart and Winston. All rights reserved. Chapter Presentation Visual Concepts Transparencies Standardized Test Prep Biological Table of Contents Section 1 How Organisms Interact in Section 2 How Competition Shapes Section 1 How Organisms Interact

More information

EnSt 110 Exam II (Sp06) Multiple Choice. Select the best answer. One only. 2 points each

EnSt 110 Exam II (Sp06) Multiple Choice. Select the best answer. One only. 2 points each Name: 1 EnSt 110 Exam II (Sp06) This test is worth 100 points; you have approximately 90 minutes. Multiple Choice. Select the best answer. One only. 2 points each 1) An ecosystem consists of A) a physical

More information

OPTIMAL FORAGING MODELS

OPTIMAL FORAGING MODELS 26 OPTIMAL FORAGING MODELS In collaboration with David N. Bonter Objectives Develop a spreadsheet model of foraging choices among two prey types, prey 1 and prey 2. Determine the conditions in which individuals

More information

Community Ecology. PowerPoint Lecture Presentations for Biology Eighth Edition Neil Campbell and Jane Reece

Community Ecology. PowerPoint Lecture Presentations for Biology Eighth Edition Neil Campbell and Jane Reece Chapter 54 Community Ecology PowerPoint Lecture Presentations for Biology Eighth Edition Neil Campbell and Jane Reece Lectures by Chris Romero, updated by Erin Barley with contributions from Joan Sharp

More information

HOMEWORK PACKET UNIT 2A. Part I: Introduction to Ecology

HOMEWORK PACKET UNIT 2A. Part I: Introduction to Ecology CP Biology Name Date Period HOMEWORK PACKET UNIT 2A Part I: Introduction to Ecology Name Class Date 3.1 What Is Ecology? Studying Our Living Planet 1. What is ecology? 2. What does the biosphere contain?

More information

Ecology +Biology. Baker-2015

Ecology +Biology. Baker-2015 Ecology +Biology Baker-2015 Ecology is the scientific study of interactions among organisms and between organisms and their physical environment. Eco meaning home, and ology meaning the study of. Thus

More information

Your web browser (Safari 7) is out of date. For more security, comfort and the best experience on this site: Update your browser Ignore

Your web browser (Safari 7) is out of date. For more security, comfort and the best experience on this site: Update your browser Ignore Your web browser (Safari 7) is out of date. For more security, comfort and the best experience on this site: Update your browser Ignore Activitydevelop PRO TECTING THE MARIANA TRENCH Why is it important

More information

Habitat and mutualism affect the distribution and abundance of a shrimp-associated goby

Habitat and mutualism affect the distribution and abundance of a shrimp-associated goby CSIRO PUBLISHING www.publish.csiro.au/journals/mfr Marine and Freshwater Research,,, Habitat and mutualism affect the distribution and abundance of a shrimp-associated goby A. R. Thompson Department of

More information

Biodiversity Classwork Classwork #1

Biodiversity Classwork Classwork #1 Biodiversity Classwork Classwork #1 1. What is biodiversity? 2. In the boxes below, create two ecosystems: one with low biodiversity and one with high biodiversity. Explain the difference. Biodiversity

More information

Biosphere Biome Ecosystem Community Population Organism

Biosphere Biome Ecosystem Community Population Organism Ecology ecology - The study of living things and how they relate to their environment Levels of Organization in Ecology organism lowest level one living thing population collection of organisms of the

More information

IV. Distribution and Abundance of Acropora Corals

IV. Distribution and Abundance of Acropora Corals IV. Distribution and Abundance of Acropora Corals Background The declines in abundance of two of the principal Caribbean reef-building corals, staghorn coral (Acropora cervicornis) and elkhorn coral (A.

More information

Chapter 04 Lecture Outline

Chapter 04 Lecture Outline Chapter 04 Lecture Outline William P. Cunningham University of Minnesota Mary Ann Cunningham Vassar College Copyright The McGraw-Hill Companies, Inc. Permission required for reproduction or display. 1

More information

Chapter 6 Population and Community Ecology. Thursday, October 19, 17

Chapter 6 Population and Community Ecology. Thursday, October 19, 17 Chapter 6 Population and Community Ecology Module 18 The Abundance and Distribution of After reading this module you should be able to explain how nature exists at several levels of complexity. discuss

More information

Possibilities of LIDAR in the shallow waters of the Baltic Sea and it s application for habitat modeling

Possibilities of LIDAR in the shallow waters of the Baltic Sea and it s application for habitat modeling Possibilities of LIDAR in the shallow waters of the Baltic Sea and it s application for habitat modeling Michael Haldin Natural Heritage Services / Metsähallitus Markku Viitasalo SYKE BACKGROUND LIDAR

More information

Resource Partitioning and Why It Matters

Resource Partitioning and Why It Matters Resource Partitioning and Why It Matters By: John N. Griffin (Department of Zoology, University of Florida) & Brian R. Silliman (Department of Zoology, University of Florida) 2011 Nature Education Citation:

More information

Marine Conservation Potential for Pearl Farming

Marine Conservation Potential for Pearl Farming Marine Conservation Potential for Pearl Farming 2014. Marine Pollution Bulletin, 78(20), 43-50. SPECIAL THANKS: Jacques Branellec, JEWELMER National Geographic Waitt Foundation Josh Humbert, KAMOKA PEARLS

More information

Chapter 1. General Introduction. Abstract

Chapter 1. General Introduction. Abstract General Abstract An investigation has been carried out in various islands of Lakshadweep Archipelago to assess the status of coral reefs and distribution pattern of butterflyfishes during 2008 to 2012.

More information

COMPETITIVE COEXISTENCE OF CORAL-DWELLING FISHES: THE LOTTERY HYPOTHESIS REVISITED PHILIP L. MUNDAY 1

COMPETITIVE COEXISTENCE OF CORAL-DWELLING FISHES: THE LOTTERY HYPOTHESIS REVISITED PHILIP L. MUNDAY 1 Ecology, 85(3), 2004, pp. 623 628 2004 by the Ecological Society of America COMPETITIVE COEXISTENCE OF CORAL-DWELLING FISHES: THE LOTTERY HYPOTHESIS REVISITED PHILIP L. MUNDAY 1 Centre for Coral Reef Biodiversity

More information

Unit 8: Ecology Guided Reading Questions (60 pts total)

Unit 8: Ecology Guided Reading Questions (60 pts total) AP Biology Biology, Campbell and Reece, 10th Edition Adapted from chapter reading guides originally created by Lynn Miriello Name: Unit 8: Ecology Guided Reading Questions (60 pts total) Chapter 51 Animal

More information

Relationships Within Ecosystems

Relationships Within Ecosystems Content Vocabulary LESSON 2 Directions: Each of the sentences below is false. Make the sentence true by replacing the underlined word with a term from the list below. Write your changes on the lines provided.

More information

Microhabitat characteristics of Stegastes planifrons and S. adustus territories

Microhabitat characteristics of Stegastes planifrons and S. adustus territories Microhabitat characteristics of Stegastes planifrons and S. adustus territories Charlotte Dromard, Yolande Bouchon-Navaro, Sébastien Cordonnier, Mireille Harmelin-Vivien, Claude Bouchon To cite this version:

More information