scholarly journals The Ecology of Sponges at Palmyra Atoll: Variability, Introduced Species and their Potential Direct and Indirect Impacts

2021 ◽  
Author(s):  
◽  
Ingrid Sally Sigrid Knapp

<p>Anthropogenic pressures, direct and indirect, have left no coral reef untouched. Those that remain in a near-pristine condition are remote islands and atolls removed from the majority of direct impacts, but even these are still subjected to the pressures of global climate change to which they are demonstrating a higher resilience than those which are already severely compromised. These near-pristine systems should be protected, managed and studied to better understand how they function and hopefully ensure the future of coral reefs. Unfortunately a number of the remote atolls and islands in the Pacific were modified or used by the US military during WWII, which altered these systems in unknown ways and threatened their surrounding reefs. Palmyra Atoll in the Central Pacific for example had its lagoons dredged and blocked to create more landmass for building, along with the creation of a channel through the reef to allow boat access into the lagoons making them susceptible to introduced species. Fortunately the surrounding reefs at Palmyra are still in a near-pristine condition with high densities of scleractinian corals, however the lagoon fauna is now predominantly sponges. Sponges in high enough densities can have considerable impacts on semi-enclosed bodies of water through their high filtering capabilities and could even threaten native species through competition if they were to extend onto non-lagoon reefs. Therefore, the broad aim of this thesis was to understand the ecology of the sponges in the lagoons at Palmyra and determine their potential impacts on the atoll directly and indirectly. To answer these questions I collected sponge assemblage data across the lagoons at both shallow and deep depths and sampled those species found on the reefs, which were surprisingly entirely different from the lagoon species. I then modelled a suite of environmental predictors to ascertain whether environmental conditions might be maintaining the sponges in the lagoon. To further examine whether the sponges were capable of extending onto the reef I also looked at larval recruitment patterns and assessed the temporal stability with semi-permanent quadrats. The initial surveys revealed the presence of at least two introduced species: Haliclona caerulea (Hechtel 1965) and Gelliodes fibrosa (Wilson 1925). Molecular tools were then employed to confirm the identification and attempt to ascertain the introduction pathway of H. caerulea. Finally, to assess the potential impact of the sponges on the water column I calculated the filtration rates of all the morphologies in the lagoon and extrapolated to the time required to clear all the available water in the lagoon as well as the removal rates of dissolved organic carbon and oxygen.  Overall the lagoons appear to have undergone a phase-shift from a coral to sponge dominated system. However, the direct threat of the sponges extending onto the adjacent near-pristine reef currently seems negligible as they appear to be relatively “stable” (sponge mortality and recruitment are in equilibrium) and maintained in the lagoons by the environmental conditions, despite larval production. Sponge diversity changed over depths but the total number of species was consistent with other atoll systems despite the military modifications, with the most prominent sponge being a Hawaiian endemic species: Iotrochota protea (de Laubenfels 1950). The introduction of H. caerulea, a Caribbean sponge is thought to have occurred to Palmyra via Hawaiʻi; however, the molecular data also revealed further cryptic speciation at both the species and order levels, suggesting greater species diversity at Palmyra than previously believed. Finally, the indirect impacts of the sponges on the water column also appear to be small and with limited future risks to the reef organisms, as recruitment and mortality are currently in equilibrium and therefore unlikely to increase dramatically in percentage cover. Globally sponges can play important functional roles in semi-enclosed bodies of water and in summary, despite the sponges being the most dominant fauna on the hard substrate in the lagoons, they appear to pose little threat to the atoll and the adjacent reefs either directly or indirectly despite the confirmed introduction of non-endemic species. However, it must be noted that the time since the modification (70 years) is not that long in an evolutionary sense, so the sponges may still have the potential to extend onto the reef, particularly if there are any dramatic changes to the environmental conditions on the outer reefs. Therefore, to detect whether the sponges are extending onto the reef I propose, as a future management tool, the use of I. protea as an indicator species. The use of multidisciplinary approaches to answer important ecological questions with respect to the potential for sponges to have negative impacts on the nonlagoon reefs proved to be essential in understanding whether the modifications to the lagoons and the subsequent dominance of sponges could be threatening one of the last few remaining near-pristine reef systems in the world.</p>

2021 ◽  
Author(s):  
◽  
Ingrid Sally Sigrid Knapp

<p>Anthropogenic pressures, direct and indirect, have left no coral reef untouched. Those that remain in a near-pristine condition are remote islands and atolls removed from the majority of direct impacts, but even these are still subjected to the pressures of global climate change to which they are demonstrating a higher resilience than those which are already severely compromised. These near-pristine systems should be protected, managed and studied to better understand how they function and hopefully ensure the future of coral reefs. Unfortunately a number of the remote atolls and islands in the Pacific were modified or used by the US military during WWII, which altered these systems in unknown ways and threatened their surrounding reefs. Palmyra Atoll in the Central Pacific for example had its lagoons dredged and blocked to create more landmass for building, along with the creation of a channel through the reef to allow boat access into the lagoons making them susceptible to introduced species. Fortunately the surrounding reefs at Palmyra are still in a near-pristine condition with high densities of scleractinian corals, however the lagoon fauna is now predominantly sponges. Sponges in high enough densities can have considerable impacts on semi-enclosed bodies of water through their high filtering capabilities and could even threaten native species through competition if they were to extend onto non-lagoon reefs. Therefore, the broad aim of this thesis was to understand the ecology of the sponges in the lagoons at Palmyra and determine their potential impacts on the atoll directly and indirectly. To answer these questions I collected sponge assemblage data across the lagoons at both shallow and deep depths and sampled those species found on the reefs, which were surprisingly entirely different from the lagoon species. I then modelled a suite of environmental predictors to ascertain whether environmental conditions might be maintaining the sponges in the lagoon. To further examine whether the sponges were capable of extending onto the reef I also looked at larval recruitment patterns and assessed the temporal stability with semi-permanent quadrats. The initial surveys revealed the presence of at least two introduced species: Haliclona caerulea (Hechtel 1965) and Gelliodes fibrosa (Wilson 1925). Molecular tools were then employed to confirm the identification and attempt to ascertain the introduction pathway of H. caerulea. Finally, to assess the potential impact of the sponges on the water column I calculated the filtration rates of all the morphologies in the lagoon and extrapolated to the time required to clear all the available water in the lagoon as well as the removal rates of dissolved organic carbon and oxygen.  Overall the lagoons appear to have undergone a phase-shift from a coral to sponge dominated system. However, the direct threat of the sponges extending onto the adjacent near-pristine reef currently seems negligible as they appear to be relatively “stable” (sponge mortality and recruitment are in equilibrium) and maintained in the lagoons by the environmental conditions, despite larval production. Sponge diversity changed over depths but the total number of species was consistent with other atoll systems despite the military modifications, with the most prominent sponge being a Hawaiian endemic species: Iotrochota protea (de Laubenfels 1950). The introduction of H. caerulea, a Caribbean sponge is thought to have occurred to Palmyra via Hawaiʻi; however, the molecular data also revealed further cryptic speciation at both the species and order levels, suggesting greater species diversity at Palmyra than previously believed. Finally, the indirect impacts of the sponges on the water column also appear to be small and with limited future risks to the reef organisms, as recruitment and mortality are currently in equilibrium and therefore unlikely to increase dramatically in percentage cover. Globally sponges can play important functional roles in semi-enclosed bodies of water and in summary, despite the sponges being the most dominant fauna on the hard substrate in the lagoons, they appear to pose little threat to the atoll and the adjacent reefs either directly or indirectly despite the confirmed introduction of non-endemic species. However, it must be noted that the time since the modification (70 years) is not that long in an evolutionary sense, so the sponges may still have the potential to extend onto the reef, particularly if there are any dramatic changes to the environmental conditions on the outer reefs. Therefore, to detect whether the sponges are extending onto the reef I propose, as a future management tool, the use of I. protea as an indicator species. The use of multidisciplinary approaches to answer important ecological questions with respect to the potential for sponges to have negative impacts on the nonlagoon reefs proved to be essential in understanding whether the modifications to the lagoons and the subsequent dominance of sponges could be threatening one of the last few remaining near-pristine reef systems in the world.</p>


2010 ◽  
Vol 26 (3) ◽  
pp. 347-350 ◽  
Author(s):  
Jannie Fries Linnebjerg ◽  
Dennis M. Hansen ◽  
Nancy Bunbury ◽  
Jens M. Olesen

Disruption of ecosystems is one of the biggest threats posed by invasive species (Mack et al. 2000). Thus, one of the most important challenges is to understand the impact of exotic species on native species and habitats (e.g. Jones 2008). The probability that entire ‘invasive communities’ will develop increases as more species establish in new areas (Bourgeois et al. 2005). For example, introduced species may act in concert, facilitating one another's invasion, and increasing the likelihood of successful establishment, spread and impact. Simberloff & Von Holle (1999) introduced the term ‘invasional meltdown’ for this process, which has received widespread attention since (e.g. O'Dowd 2003, Richardson et al. 2000, Simberloff 2006). Positive interactions among introduced species are relatively common, but few have been studied in detail (Traveset & Richardson 2006). Examples include introduced insects and birds that pollinate and disperse exotic plants, thereby facilitating the spread of these species into non-invaded habitats (Goulson 2003, Mandon-Dalger et al. 2004, Simberloff & Von Holle 1999). From a more general ecological perspective, the study of interactions involving introduced and invasive species can contribute to our knowledge of ecological processes – for example, community assembly and indirect interactions.


2021 ◽  
Vol 41 (3) ◽  
pp. 358-366
Author(s):  
Peter B. Banks

Distinguishing between whether a species is alien or native can be problematic, especially for introduced species that are long-established in new areas outside of their natural range. Transport by humans is the criterion for alien status used by many definitions, whereas arbitrary time since arrival to a location is often used to define native status. Here I propose an eco-evolutionary approach to distinguish between alien and native status and use this to resolve uncertainty in the status of the dingo in Australia. Dingoes were transported to mainland Australia by humans, but more than 4000 years ago, and dingoes now interbreed with feral domestic dogs. Legally, this mix of events has the dingo classified as native in some jurisdictions and alien in others. I suggest that native status for introduced species should be based on (1) whether the species has evolved in their new environment; (2) whether local species recognise and respond to them as they do towards deep endemic native species, and; (3) whether their impacts benchmark against those of a native species or are exaggerated like those of other alien species. Dingoes are behaviourally, reproductively and morphologically different to close ancestors from south-east Asia, and this difference has a genetic basis indicative of evolution in Australia. There is abundant evidence that native prey species on mainland Australia recognise and respond to them as a dangerous predator, which they are. But there is strong evidence that dingo impacts on prey are not exaggerated, with effect sizes from mensurative experiments similar to those of experiments on native predators rather than alien predators. These three lines of evidence suggest dingoes should be considered native to mainland Australia. I suggest this eco-evolutionary approach to defining native status can be helpful in resolving the often-heated debates about when an alien species becomes native.


2011 ◽  
Vol 25 (2) ◽  
pp. 346-362
Author(s):  
Edson Luís de Carvalho Soares ◽  
Márcia Vignoli-Silva ◽  
Lilian Auler Mentz

This work consists of a taxonomic synopsis of the genera of Solanaceae in Rio Grande do Sul state, Brazil. Solanaceae is represented by 28 genera in this state: Acnistus Schott, Athenaea Sendtn., Aureliana Sendtn., Bouchetia Dunal, Browalia L., Brugmansia Pers., Brunfelsia L., Calibrachoa La Llave & Lex., Capsicum L., Cestrum L., Datura L., Dyssochroma Miers, Grabowskia Schltdl., Jaborosa Juss., Lycianthes (Dunal) Hassl., Melananthus Walp., Nicandra Adans., Nicotiana L., Nierembergia Ruiz & Pav., Petunia Juss., Physalis L., Salpichroa Miers, Schwenckia L., Sessea Ruiz & Pav., Solandra Sw., Solanum L. (including Cyphomandra Sendtn. and Lycopersicon Mill.), Streptosolen Miers and Vassobia Rusby. Of these, 23 consist of native species , while five are represented exclusively by introduced species. The total number of species is 149, of which 118 are native and 31 are introduced (adventitious or cultivated). An identification key for genera, and also comments on the most relevant taxonomic characters of each one are presented, plus comments on the species that occur in Rio Grande do Sul state.


2010 ◽  
Vol 58 (spe3) ◽  
pp. 23-28 ◽  
Author(s):  
Rosana M. Rocha ◽  
Leonardo C. Cangussu ◽  
Mariana P. Braga

Artificial substrates in and near ports and marinas commonly have many non-indigenous species and are the first stepping stone for the establishment of bioinvasors. Substrate movement influences fouling communities and so understanding of how species assemblages are related to specific substrate conditions is crucial as a management tool. Here we describe the species assemblage of the community after six months of development on granite plates in Paranaguá Bay. Species richness was similar in the two treatments, with 12 species on floating (constant depth) plates and 15 on stationary (variable depth) plates. However, species composition differed, with the community on floating plates being dominated by the native bivalve Mytella charruana (66.1 ± 5.5% cover) and that on stationary plates dominated by the barnacles Fistulobalanus citerosum (49.8 ± 3.5% cover) and the introduced Amphibalanus reticulatus (33.9 ± 3.7% cover). Other introduced species were Garveia franciscana, on one stationary plate, and Megabalanus coccopoma also on one stationary plate and not very abundant on half of the floating plates (< 2%). Thus, stationary plates were more susceptible to introduced species that may become very abundant, suggesting that this type of substrate should be a priority in management for bioinvasion control. We also hypothesize that the native bivalve M. charruana is the dominant competitor for space on floating substrates, thereby reducing the invasiveness of that type of substrate.


Diversity ◽  
2020 ◽  
Vol 12 (2) ◽  
pp. 71 ◽  
Author(s):  
Katharine L. Stuble ◽  
Truman P. Young

Priority effects can be used to promote target species during restoration. Early planting can provide an advantage over later-arriving species, increasing abundance of these early-arrivers in restored communities. However, we have limited knowledge of the indirect impacts of priority effects in restoration. In particular, we do not understand how priority effects impact non-target species. Of particular conservation concern is how these priority effects influence establishment by non-native species. We use a field-based mesocosm experiment to explore the impacts of priority effects on both target and non-target species in California grasslands. Specifically, we seeded native grasses and forbs, manipulating order of arrival by planting them at the same time, planting forbs one year before grasses, planting grasses one year before forbs, or planting each functional group alone. While our study plots were tilled and weeded for the first year, the regional species pool was heavily invaded. We found that, while early-arrival of native grasses did not promote establishment of non-native species, giving priority to native forbs ultimately left our restoration mesocosms vulnerable to invasion by non-native species. This suggests that, in some cases, establishment of non-native species may be an unintended consequence of using priority treatments as a restoration tool.


2021 ◽  
Vol 210 (07) ◽  
pp. 2-15
Author(s):  
Liliya Beksheneva ◽  
Antonina Reut

Abstract. The article presents the results of an experimental assessment of the peculiarities of the water regime of 9 species of the genus Iris L. growing in the South-Ural Botanical Garden-Institute UFRC RAS (I. sibirica L., I. pseudacorus L. ‒ species of native flora, I. aphylla L., I. biglumis Vahl., I. lacteal Pall., I. orientalis Mill., I. ruthenica Ker-Gawl., I. setosa Pall., I. spuria L. ‒ introduced species). The purpose is a comparative evaluation of the main parameters of the water regime within the generic complex and depending on the detection of meteorological factors in different phenological periods. Methods. Studies were performed in growing periods 2019–2020’s physiological using conventional techniques (artificial saturation method and wilting). Made a detailed analysis of daily and seasonal dynamics of the water regime of the three parameters: the total water content, water-holding capacity, water scarcity. Typical forest species Convallaria majalis L. was investigated for a comparative analysis of water regime indicators. Results. The similarities and differences in the peculiarities of the water regime were established between the studied species, the dependence of the indicators on meteorological conditions was revealed. According to the type of water regime cultivars were divided into four groups: a flexible water-quiet mode ‒ I. pseudacorus, flexible water-tight mode ‒ I. sibirica, I. ruthenica, stably-calm water mode ‒ I. aphylla, I. biglumis, I. setosa, stably-tight water mode ‒ I. spuria, I. lactea, I. orientalis. Among the studied parameters of water scarcity was the most dependent on meteorological factors. Scientific novelty. The study helps to identify ecological and physiological adaptations of exotic species in comparison with the native species that could become the basis for assessing the prospects of growing in the culture and conservation of rare and endangered species.


Zootaxa ◽  
2012 ◽  
Vol 3508 (1) ◽  
pp. 1 ◽  
Author(s):  
ROBERT J. KALLAL ◽  
JOHN S. LaPOLLA

The taxonomy of the Nearctic Nylanderia fauna is revised. Three new species are established, bringing the total numberof native species from the region to 14. The new species are: N. magnella, N. querna, and N. trageri. Several speciespossess workers that are difficult to distinguish from each other and the presence of males is required for morphologicalidentification. This is particularly the case with N. vividula and N. terricola. Two subspecies are synonymized: N. vividulamjobergi is considered a junior synonym of N. vividula and N. vividula antillana is considered a junior synonym of N.guatemalensis. At least five Nylanderia species have been introduced to the Nearctic region, including: N. bourbonica,N. flavipes, N. fulva, N. pubens, and N. steinheili. Another species, N. guatemalensis, is also included because its widedistribution across the Caribbean and Central America suggest it could become introduced to the Nearctic region. Iden-tification keys are provided for the workers of native and introduced species and the males of native species. Distributionmaps are provided for native and introduced species. Photomontage images are provided for the worker of each introduced species and all castes of the native species.


1974 ◽  
Vol 8 (1) ◽  
pp. 23-28 ◽  
Author(s):  
D L Hawksworth

The activities of man have led to the extinction of relatively few species of plants and animals native to the British Isles over the last two centuries. Many have declined considerably as a result of increasingly intensive agriculture, industrialization and urbanization but others have expanded into man-made habitats. Introduced species continue to arrive in increasing numbers. For the rarer native species there is a need for careful recording and research into status and habitats.


Sign in / Sign up

Export Citation Format

Share Document