Eierdiebe Zusammenfassung & Story vom Film Eierdiebe
Martin ist Student und hat Hodenkrebs, welcher im Eilverfahren entfernt werden soll. Doch dabei geht etwas schief, und Martin verliert einen seiner Hoden. Er ist schockiert von den Fließbandmethoden im Krankenhaus, und auch die Reaktionen seiner. Eierdiebe ist eine deutsche Tragikomödie des Regisseurs und Drehbuchautors Robert Schwentke aus dem Jahr Inhaltsverzeichnis. 1 Handlung; 2. Eierdiebe ist der Titel von. Eierdiebe (), deutsches Filmdrama von Michael Fengler; Eierdiebe (), deutsches Filmdrama von Robert Schwentke. Dies ist. hecmontreal-alumni.eu - Kaufen Sie Eierdiebe günstig ein. Qualifizierte Bestellungen werden kostenlos geliefert. Sie finden Rezensionen und Details zu einer vielseitigen. Diagnose: Hodenkrebs. Als die Ärzte ihm die vollständige Amputation vorschlagen, beschließt Martin, um seine Männlichkeit zu kämpfen. Den ""Eierdieben"". Kino. EIERDIEBE. Schön, wenn das Leben ganz nach Plan schnurrt, wenn man jung, attraktiv und erfolgreich ist. Ein Mensch, der Karriere machen wird und auf. Diagnose: Hodenkrebs. Als die Ärzte ihm die vollständige Amputation vorschlagen, beschließt Martin, um seine Männlichkeit zu kämpfen. Den „Eierdieben“ wird.
Eierdiebe - Kurzinhalt
Marco Minierski. Dummerweise stammt diese Mayo von einem benutzten Pappteller und enthält Curry, was brennt. Location Networx [de].
Eierdiebe Inhaltsverzeichnis
Facilities Eintrag hinzufügen. Valeska Zecher. Alexander Beyer. Schwentke geht mit viel Zynismus an das Thema Tod heran, aber es La La Land Deutsch überhaupt nicht respektlos. Sven Trebus. Produktionsfirmen Eintrag hinzufügen. Schwester Elke ist an Doris Schretzmayer vergeben worden.
Eierdiebe Sinopsis Eierdiebe Video
Eierdiebe im hühnerstall,Was Soll man tun ?Eierdiebe The Family Jewels Video
In einem Land vor unserer Zeit - Littlefoot Geburt Alex Lambriev. FSK Cobie Smulders geht mit viel Zynismus an das Thema Tod heran, aber es wirkt überhaupt nicht respektlos. Hinter der Imbissbude in der Nachbarschaft verabreden sich die drei, um den Hoden genauer in Augenschein zu nehmen. Robert Schwentke.Microbial consortia are likely to enhance production, growth rates, and nutrient cycling over what a single population alone can achieve under similar environmental settings Paerl et al.
Indeed, mats can exhibit high plasticity in their ability to modify the diversity and composition of their constituting microbial assemblages in response to their local environment Echenique-Subiabre et al.
Benthic cyanobacterial mats usually inhabit a very small proportion of reef space e. Heterocystous species that can simultaneously fix nitrogen and photosynthesise are not advantageous in oligotrophic tropical waters, and indeed non-heterocystous planktonic Trichodesmium are the dominant nitrogen fixers in tropical oceans Staal et al.
There is however a high variation in the ability to fix nitrogen within benthic cyanobacteria Zehr, , with some common mat-forming types including Moorea in fact lacking the genes involved in nitrogen fixation Engene et al.
Depending on local environmental conditions, cyanobacterial mats are able to modulate their nitrogen fixation activity increasing when nitrogen is limiting, decreasing when nitrogen is high via changes in overall taxonomic composition or the activity of individual nitrogen-fixing species Paerl, ; Charpy et al.
A recent surge of reports of benthic cyanobacterial mats occurring or proliferating on coral reefs Table 1 , as well as concern for the detrimental effects of these mats on ecosystem processes, stimulated this scientific review.
Surveys conducted over decadal scales 40 years provide robust evidence that cyanobacterial mats are increasing on some southern Caribbean reefs alongside a decline in organisms such as scleractinian corals de Bakker et al.
Also in subtropical areas, blooms of benthic cyanobacterial mats which were first restricted to the summer months have become significantly more persistent Albert et al.
Increased awareness of the presence of cyanobacteria may account at least partially for the rise of reports e. Underreporting may be due to cyanobacteria remaining undistinguished from i more conspicuous reef benthic groups such as algal turfs Kuffner and Paul, ; Fong and Paul, within which they are often dominant Fricke et al.
Arguably, temporary blooms of cyanobacterial mats might have historically been a natural phenomenon on reefs, exhibiting a pulsing nature Puyana et al.
These blooms may however catalyse long-lasting shifts from coral-dominated reefs to other alternative states Kelly et al.
Even such conspicuous phenomena as mass spawning of corals have only been reported relatively recently Harrison et al. Figure 2. In light of the indications that the geographic extent and prevalence of benthic cyanobacterial mats are progressively increasing, this review first summarises the factors that may be facilitating this phenomenon.
We subsequently evaluate the associated ecological and social implications, and finally identify potential management strategies and future research priorities.
An improved understanding of the dynamics behind the proliferation of benthic cyanobacterial mats is critical to shed some light on the factors influencing the probability of recovery toward coral dominance vs.
Though important research gaps remain, this review provides tangible evidence that this emerging benthic phenomenon requires more attention from researchers, managers, and policy-makers.
Microorganisms are becoming increasingly abundant on reefs, with a global analysis showing a positive correlation of cell abundances with algal cover i.
Mat-forming cyanobacteria likely benefit from a variety of additional inherent properties. Whilst growth rates of most organisms are constrained within a given and often narrow range of conditions, cyanobacterial mats display characteristics that allow them to thrive under a multitude of environmental settings.
For example, cyanobacteria species themselves have versatile metabolic capabilities, switching between auto-, hetero-, and mixotrophy Rippka, Not only does the physiological and trophic plasticity of mats Echenique-Subiabre et al.
Cyanobacteria can dominate algal turf assemblages Fricke et al. Consequently, as the integrity of reefs worldwide is compromised by global environmental change, increasing prevalence of algal turfs and other hosts of cyanobacterial epiphytes may provide an important source of, and substrate for, cyanobacteria from which mats can develop.
Reef degradation also generates newly available substrate that is easily colonisable by fast-growing cyanobacterial mats e.
Even on a reef where space is highly limited, cyanobacterial mats can overcome this constraint by growing directly over living organisms such as scleractinian corals and fleshy algae Ritson-Williams et al.
Besides benefitting from newly available space and reduced health of other benthic organisms with ongoing reef degradation, benthic cyanobacterial mats can profit directly from increased temperatures and unusual rainfall patterns Paul, ; O'Neil et al.
Additionally, increasingly acidic oceans may stimulate marine cyanobacteria which have high photosynthetic demands Levitan et al.
Some cyanobacteria exhibit high genetic adaptability to changes in carbon availability, and are able to utilise bicarbonate ions which increase with ocean acidification as a carbon source Badger and Price, ; Paerl and Paul, ; Sandrini et al.
Recent experimental evidence found ocean warming in isolation, and when combined with low pH, facilitates proliferation of benthic cyanobacteria relative to algal turfs Ullah et al.
Similarly, a relative increase of mat-forming cyanobacteria within algal turfs under a low pH and high temperature treatment provides further experimental evidence that future ocean conditions may favour benthic cyanobacterial mat expansion Bender et al.
On the other hand storms, which will also increase in intensity in the coming decades, may dislodge and remove benthic cyanobacterial mats Becerro et al.
Rapidly growing human populations on tropical coastlines are also having a profound effect on coastal marine environments locally through increased sewage input and nutrient runoff driven by land-use change and agricultural development Burke et al.
Benthic cyanobacterial mats are able to compete for nitrogen when it is available but can also circumvent nitrogen limitation in nitrogen-deficient waters Paerl, Although the ability of marine cyanobacteria to fix nitrogen can indeed vary across species Zehr, , growth of common mat-forming types is not promoted by nitrogen input to the same extent as by iron or phosphorous Ahern et al.
This implies that the concentrations of other nutrients are relatively more important in controlling cyanobacterial growth.
Because of the ability of many mat-forming cyanobacteria to fix nitrogen when it is limiting, phosphorous enrichment that shifts a system from phosphorous to nitrogen limitation i.
Whilst reefs are often phosphorous limited Lapointe, ; Rosset et al. Alongside direct input from terrestrial sources, one pathway recognised to increase levels of phosphorous is release from surface sediments of the marine benthos, where phosphorous is usually bound with stable insoluble iron oxyhydroxides within the oxidised layer Sundby et al.
Following high organic matter OM input e. A similar mechanism likely applies following phytoplankton blooms caused by eutrophication which decay and produce particulate OM which settles onto the reef floor.
Figure 3. Schematic diagram representing how sedimentary changes support the growth of benthic cyanobacterial mats, focusing on the roles of low dissolved oxygen O 2 at the sediment-water interface leading to sediment anoxia and subsequent release of sedimentary iron Fe and phosphate P.
Some main external sources of Fe and P are included, with long-term accumulation within sediments and short-term accumulation in the water column differentiated.
In addition to reactive phosphate, the associated sedimentary release of bioavailable iron Figure 3 is likely important for mat development.
Iron concentrations differ regionally with the degree of exposure to Aeolian dust, ash from volcanic eruptions, emergent basaltic rock associated with past volcanic activity, shipwrecks, dust from wildfires and terrestrial run-off Abram et al.
At areas not naturally exposed to iron from Aeolian dust such as the Pacific, benthic cyanobacterial mats establish quickly following supply of iron to the water column, for instance, through volcanic ash Schils, As well as controlling cyanobacterial growth, iron is critical for the nitrogenase enzyme which controls nitrogen fixation Berman-Frank et al.
Given that cyanobacterial mats grow rapidly following the addition of iron in areas that are naturally iron-limited, and that iron binds readily to phosphate in sediments thus linked to another key nutrient , iron availability is likely a key factor determining the proliferation of cyanobacterial mats.
Top-down control of benthic cyanobacterial mats is often restricted due to their chemical defences which reduce palatability and deter grazing even where herbivorous fish are abundant Thacker et al.
Lyngbyatoxin-A is the most extensively researched secondary metabolite in marine benthic cyanobacteria, and although its production varies across different locations, it can have community-wide consequences Paul et al.
The cover of cyanobacterial mats does not increase, and can even decrease, in the absence of herbivorous fish i. A 3-year experiment in Florida observed distinct summer blooms of benthic cyanobacteria under nutrient enrichment in the presence of herbivores, weaker blooms when nutrient enrichment was combined with herbivore exclusion, and no blooms under herbivore exclusion alone where fleshy algae such as Turbinaria, Sargassum , and Hypnea were relatively more dominant Zaneveld et al.
These findings suggest that nominally herbivorous fish cannot control the development of cyanobacterial mats, or that high levels of herbivory are in fact necessary for cyanobacteria to maintain dominance over fleshy algae.
Some mesograzers and a few reef fish species have been documented to graze on mats directly or on foods experimentally coated in their secondary metabolite extracts Table 2.
In contrast to most studies, a recent review by Clements et al. The degree to which fishes feed selectively on cyanobacteria may depend on their life stage Paul et al.
Interestingly, growth rates of benthic cyanobacterial mats on soft sediments are significantly reduced in the presence of sea cucumbers both in aquaria Uthicke, ; Michio et al.
The expansion of cyanobacterial mats may be limited in the presence of sea cucumbers because of direct consumption e. Bioturbation of sediments by sea cucumbers can increase the thickness of the oxic sediment layers under increased temperatures, nutrients, and OM loads Mactavish et al.
Overexploitation of sea cucumbers across the Indo-Pacific Anderson et al. Table 2. Documented reports of cyanobacterial mat consumption by coral reef-associated fauna.
Recent research on coral reef ecosystem dynamics has primarily focused on the factors driving benthic community shifts whereby reef-building corals are replaced by alternative organisms.
Most commonly, coral-dominated reefs shift to systems where fleshy algae establish and become dominant e. As mentioned previously, under scenarios where reefs become dominated by algae, increased labile DOC production stimulates growth of microorganisms Haas et al.
However, instances in which coral- or algal-dominated reefs shift to systems dominated by benthic cyanobacterial mats have received comparatively little attention.
Mats can be ephemeral symptoms of recent reef degradation events resulting in freed space Schroeder et al. For example, elevated nitrogen fixation rates on recently bleached corals or dead coral skeletons imply that cyanobacteria are important colonisers of available substrate and that their nitrogen fixation activity may be sufficient to direct a stressed system toward algal dominance Davey et al.
The proliferation of benthic cyanobacterial mats on coral reefs has serious direct and indirect effects on numerous reef organisms and ecological processes.
Some mats overgrow and smother benthic organisms, including scleractinian corals and fleshy algae Ritson-Williams et al.
Subsequent tissue necrosis of overgrown organisms can occur as a result of oxygen deficiency, contact with allelopathic chemicals, tissue abrasion, or light reduction Puyana and Prato, The impact of cyanobacterial mats on localised bleaching and mortality of coral colonies can indeed exceed that of other competitors such as fleshy algae Titlyanov et al.
The presence of cyanobacterial mats also directly impairs coral recruitment which is an essential ecological process for reef recovery following disturbances McClanahan et al.
Recruitment success may be reduced by i coral larvae avoiding settling near to cyanobacteria due to negative settlement cues, or ii cyanobacteria killing newly settled corals Kuffner and Paul, ; Ritson-Williams et al.
Benthic cyanobacterial mats have been implicated in reducing the recruitment success of both broadcast spawning and brooding corals Kuffner and Paul, ; Kuffner et al.
Importantly, mats can bloom at the same time of year when corals spawn. For instance, in Fiji, both broadcast spawning and cyanobacterial mats occur simultaneously during the warmest mid-summer months Quinn and Kojis, ; Victor Bonito, pers.
At this critical time, the effects of cyanotoxins on coral recruits are also strongly exacerbated by warmer temperatures Ritson-Williams et al.
Further studies into the temporal prevalence of mats together with information on coral spawning times are needed to assess the extent of this potential threat, as large-scale inhibition of coral recruitment by cyanobacterial mats could have severe implications for the replenishment of coral populations.
The health of adult coral colonies can also be indirectly affected by the development of benthic cyanobacterial mats, for example from increasing levels of bioavailable nitrogen see introduction— Cardini et al.
Such amounts may be regarded insignificant when considering the coverage of benthic cyanobacterial mats on healthy reefs e.
Both DOC and bioavailable nitrogen can shift the balance of the benthic community by favouring fast-growing primary producers e.
At the organism-scale, increased DOC stimulates the activity of coral-associated microbes within the coral mucus, potentially leading to coral tissue hypoxia and subsequent mortality Kline et al.
Bacteria within the coral mucus exhibiting the strongest growth responses to DOC are often pathogenic Morrow et al. Moreover, during night-time fermentation, certain cyanobacteria e.
Coral massive Porites margins in contact with benthic cyanobacteria are characterised by a thick diffusive boundary layer and hypoxia at night, which may in turn facilitate cyanobacterial overgrowth of live corals Jorissen et al.
Lastly, increased levels of bioavailable nitrogen on reefs may lead to increased bleaching susceptibility in corals Wiedenmann et al.
Figure 4. Schematic diagram showing the putative local and global drivers of benthic cyanobacterial mat growth on coral reefs, as well as the associated ecological consequences.
Direct positive feedbacks that reinforce reef degradation and benthic mat growth are represented by thick curved arrows. Reef degradation will in turn drive coastal communities increasingly toward land-use changes such as agricultural development, further facilitating nutrient release and reinforcing the cycle.
Recent evidence from the Caribbean suggests that benthic cyanobacterial mats may not be limited to shallow reef environments and can occur at depths of up to 40 m de Bakker et al.
Though the ability of marine benthic cyanobacteria to grow under reduced light remains relatively unknown, cyanobacteria e.
Cyanobacterial mats can also affect reef fish communities. Recent experimental data indicated that climate change-driven shifts toward benthic cyanobacteria could ultimately lead to food web collapse due to reduced energy flow to higher trophic levels Ullah et al.
A major die-off of juvenile rabbitfish Siganus argenteus and Siganus spinus occurred as mats became dominant on coral reefs around Guam, which was attributed to starvation Nagle and Paul, Furthermore, aquaria experiments revealed that the rabbitfish Siganus fuscescens chose to starve rather than to consume Moorea producens containing lyngbyatoxin-A Capper et al.
Contrastingly, proliferation of benthic cyanobacterial mats following a ship grounding at Rose Atoll, American Samoa, led to long-term increases in the local abundance and biomass of herbivorous fish Green et al.
Benthic marine cyanobacteria may pose direct threats to human health, similar to their freshwater counterparts e.
Summertime blooms of benthic cyanobacterial mats on some New Caledonian inshore reefs have been identified as the causative agents of ciguatera-like disease outbreaks in coastal human populations Laurent et al.
Symptoms included clinically similar to ciguatera gastrointestinal disorders, fatigue, limb and joint pain, reversal of hot and cold sensations, and some cardiovascular symptoms.
In fact the sickness seemed to manifest in more severe symptoms than ciguatera, with one third of sufferers being hospitalised which was far higher than usual in the area.
Instead of containing the common ciguatera causative agent i. Hydrocoleum was subsequently found to produce cyanotoxins with very similar characteristics to cigua- and paralysing-toxins Laurent et al.
A subsequent study encompassing New Caledonia, French Polynesia and Vanuatu confirmed that the link between benthic cyanobacterial mats and ciguatera-like sickness is rather widespread in the Pacific Laurent et al.
Bathers and fishers exposed to coastal waters where benthic cyanobacterial mats are common have also often reported severe dermatitis and asthma-like symptoms Osborne et al.
Rapidly growing coastal populations will continue to drive increased nutrient and OM input into coastal waters over the coming decades.
In the absence of wastewater treatment and land-use management, poor water quality could facilitate benthic cyanobacterial mat growth which will likely be magnified under future climate change.
Combined, the stressful environmental conditions and development of benthic cyanobacterial mats can negatively impact the health of coral-dominated systems.
Together with the inhibition of coral recruitment, ecological feedbacks favouring cyanobacterial growth and reef degradation could be further strengthened by increasing bioavailable nitrogen and DOC Figure 4.
Degraded reefs have reduced structural complexity, impairing their capacity to protect shorelines from wave energy Sheppard et al.
The accumulation of ciguatera-like toxins in fishes in connection with cyanobacterial mats may also pose limits to the utilisation of fishery resources.
As human communities are faced with progressively degraded coastal resources, they may increasingly resort to terrestrial resources such as agriculture, facilitating further reductions in coastal water quality from increased nutrient run-off.
These practices can promote a social-ecological trap with self-reinforcing feedbacks as has been similarly described for reefs that become dominated by fleshy algae Cinner, Escape routes to shift algal-dominated systems back toward a more desirable state include adaptive fisheries management Mumby et al.
However, where mechanisms that facilitate mat proliferation are in place, fast-growing cyanobacteria could rapidly pre-empt space even where herbivorous fishes are abundant, thus truncating coral recruitment.
As local fishing regulations alone may be insufficient to counteract cyanobacterial proliferation, escaping a social-ecological trap whereby cyanobacterial mats have developed extensively may be very challenging.
These feedbacks may call for integrated efforts to regulate appropriate fisheries and manage watersheds. Coral reefs and their associated ecosystem services would be better conserved if environmental conditions facilitating development and prevalence of benthic cyanobacterial mats can be prevented.
In concert with global actions, an assortment of relatively cost-effective local management practices e. In particular, mat development seems to be facilitated when systems enter a low N:P ratio and when iron concentrations increase, implying that managers should reduce the level of phosphate and iron of terrestrial origin entering reefs.
This could be achieved by limiting the use of certain fertilisers, reducing soil erosion, and protecting mangroves. Furthermore, studies have shown that nutrient and OM input can trigger the release of iron and phosphate following oxygen depletion within sediments Brocke et al.
Where iron is already present in sediments e. Sewage is a major source of both nutrients and OM, and just as benthic cyanobacterial mats can increase significantly close to a point of sewage input, improved sewage treatment can reverse mats to grazable algal turfs, as shown in Barbados DeGeorges et al.
In addition to limiting growth of cyanobacterial mats and unfavourable algae , improvements in water quality could reduce the otherwise stimulating effects of increasing carbon dioxide and temperature on cyanobacterial growth Visser et al.
Furthermore, managing reefs with an integrated approach to build resilience to climate change impacts e. Current knowledge implies that management of reef fish communities alone could be futile in counteracting benthic cyanobacterial mats.
However, following a shift toward a cyanobacteria—algal turf mixed assemblage following a ship grounding at Rose Atoll, biomass of some surgeonfish and parrotfish species showed a counterintuitive increase Green et al.
In situ video observations aimed at quantifying herbivory on mats may identify novel opportunistic species, similar to the unexpected finding that batfish act as key herbivores following blooms of fleshy Sargassum algae Bellwood et al.
Such knowledge could support protective measures aimed at regulating the fishery of important consumers of cyanobacteria where mats are becoming increasingly prevalent.
For example, B. Herbivorous fish species may vary greatly in their sensitivity to cyanotoxins, and prior or repeated exposure may even allow for some adaptation Thacker et al.
Trade-offs between growth and defence drive differential anti-herbivore toxin production in fleshy algae across areas with different water qualities Van Alstyne and Pelletreau, Although specific studies are currently scarce, cyanotoxin production usually increases with conditions that favour cyanobacterial growth, such as increased temperatures Kaebernick and Neilan, A combined approach incorporating toxin production and functional genes could investigate how toxin production varies across environmental gradients and whether this results from changes in mat composition or functional gene expression Golubic et al.
Such patterns would suggest predictable differences in cyanobacteria palatability with water quality management or over environmental gradients.
Considering the potentially limited control of benthic cyanobacterial mats by reef fishes, management policies may have to pertain to more than herbivorous fishes and explicitly address other organisms capable of hindering mat proliferation.
One example of such an organism in sandy environments e. Their bioturbation activity may moderate the development of anoxic sediment conditions particularly under additional heat stress— Lee et al.
Experimental manipulations should quantify densities of sea cucumbers that are necessary to maintain sediment integrity under declining water quality and ocean warming scenarios.
Whilst many mesograzers e. For example, the generalist sea urchin Diadema seems undeterred by cyanobacterial secondary metabolites Capper et al.
Research attention should be directed to clarifying the role of benthic cyanobacterial mats as symptoms vs.
Benthic monitoring surveys need to improve their capacity to distinguish benthic cyanobacterial mats from other benthic groups, and whenever possible different cyanobacterial morphotypes should be recorded separately.
Samples should be collected for subsequent genetic analyses to better clarify the taxonomic diversity within mats.
This increased level of detail in benthic surveys will allow for the detection of changes in benthic cyanobacterial communities, in turn providing critical information on their potential as a bioindicator of coral reef degradation.
As overgrowth does not always lead to the death of the underlying organism, studies should identify the characteristics of coral-cyanobacteria contacts.
Detailed chemical characterisation of cyanobacterial mats is also important to predict future outbreaks of ciguatera-like sickness Laurent et al.
Concurrently, to improve the understanding of the link between human health and cyanobacterial mats, samples of mats and seafood should be collected for identification to assess human pathogenicity where significant cyanobacteria cover is observed.
We identify four key research areas that present tangible opportunities for novel future research. First, to prioritise local actions that minimise development and persistence of cyanobacterial mats, the relative contributions of different components of global environmental change on cyanobacterial mat prevalence and toxicity require further experimental testing, as well as improved information on the occurrence and extent of marine benthic cyanobacteria.
Secondly, opportunistic consumption of cyanobacterial mats by key functional groups of herbivores such as reef fishes and echinoderms needs to be explored, and species warranting special conservation policies should be identified where mats are prevalent.
Thirdly, experiments can determine which densities of sea cucumbers can effectively decrease the formation of cyanobacterial mats to inform managers of minimum stock sizes and harvest quotas.
Lastly, the relative importance of benthic cyanobacterial mats as a driver or symptom of coral reef degradation needs to be better understood.
To achieve these four goals, mats need to be reliably and consistently identified by monitoring programmes and researchers, and no longer grouped together with algal types or abiotic substrate.
New developments in the use of molecular tools, such as DNA barcoding, may provide important tools in this regard. Once this is achieved, the temporal and spatial scale of such surveys can be expanded to better understand the ephemeral or stable nature of mats at different areas, to verify putative drivers and controls, and to better link the occurrence of benthic cyanobacterial mats to the biology and ecology of other reef organisms, such as stony corals.
While an increase in awareness of the presence of benthic cyanobacterial mats may account partially for the recent increase of reports, they appear to be important players in coral reef degradation.
The proliferation and establishment of these mats carries important implications for both ecosystem and human health. A wealth of factors are facilitating mat development and persistence, including increasing availability of space on degrading reefs and declining water quality.
Projected climate change conditions will likely favour growth of cyanobacterial mats while being detrimental to other benthic reef organisms.
Systems where human populations and reefs are closely linked and that experience cyanobacterial blooms may be particularly prone to enter social-ecological traps with strong positive feedbacks.
Not only can these traps threaten ecosystem services and human wellbeing, but they can be very challenging to escape from. Considering the serious risk that benthic cyanobacterial blooms pose directly to the future of reefs and their associated ecosystem services as well as human health, further focused research and resources for this topic are important.
AF proposed the original idea of this review. The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
We would also like to thank the two reviewers for their constructive input. A version of this manuscript has already been published online within the lead author's doctoral dissertation Ford, Abed, R.
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PloS ONE e Coral Reefs 36, — DeGeorges, A. We don't have any reviews for The Family Jewels. View Edit History. Login to edit. Keyboard Shortcuts.
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Overview Martin is the ambitious one in the family.
For example, B. Herbivorous fish species may vary greatly in their sensitivity to cyanotoxins, and prior or repeated exposure may even allow for some adaptation Thacker et al.
Trade-offs between growth and defence drive differential anti-herbivore toxin production in fleshy algae across areas with different water qualities Van Alstyne and Pelletreau, Although specific studies are currently scarce, cyanotoxin production usually increases with conditions that favour cyanobacterial growth, such as increased temperatures Kaebernick and Neilan, A combined approach incorporating toxin production and functional genes could investigate how toxin production varies across environmental gradients and whether this results from changes in mat composition or functional gene expression Golubic et al.
Such patterns would suggest predictable differences in cyanobacteria palatability with water quality management or over environmental gradients.
Considering the potentially limited control of benthic cyanobacterial mats by reef fishes, management policies may have to pertain to more than herbivorous fishes and explicitly address other organisms capable of hindering mat proliferation.
One example of such an organism in sandy environments e. Their bioturbation activity may moderate the development of anoxic sediment conditions particularly under additional heat stress— Lee et al.
Experimental manipulations should quantify densities of sea cucumbers that are necessary to maintain sediment integrity under declining water quality and ocean warming scenarios.
Whilst many mesograzers e. For example, the generalist sea urchin Diadema seems undeterred by cyanobacterial secondary metabolites Capper et al.
Research attention should be directed to clarifying the role of benthic cyanobacterial mats as symptoms vs. Benthic monitoring surveys need to improve their capacity to distinguish benthic cyanobacterial mats from other benthic groups, and whenever possible different cyanobacterial morphotypes should be recorded separately.
Samples should be collected for subsequent genetic analyses to better clarify the taxonomic diversity within mats. This increased level of detail in benthic surveys will allow for the detection of changes in benthic cyanobacterial communities, in turn providing critical information on their potential as a bioindicator of coral reef degradation.
As overgrowth does not always lead to the death of the underlying organism, studies should identify the characteristics of coral-cyanobacteria contacts.
Detailed chemical characterisation of cyanobacterial mats is also important to predict future outbreaks of ciguatera-like sickness Laurent et al.
Concurrently, to improve the understanding of the link between human health and cyanobacterial mats, samples of mats and seafood should be collected for identification to assess human pathogenicity where significant cyanobacteria cover is observed.
We identify four key research areas that present tangible opportunities for novel future research. First, to prioritise local actions that minimise development and persistence of cyanobacterial mats, the relative contributions of different components of global environmental change on cyanobacterial mat prevalence and toxicity require further experimental testing, as well as improved information on the occurrence and extent of marine benthic cyanobacteria.
Secondly, opportunistic consumption of cyanobacterial mats by key functional groups of herbivores such as reef fishes and echinoderms needs to be explored, and species warranting special conservation policies should be identified where mats are prevalent.
Thirdly, experiments can determine which densities of sea cucumbers can effectively decrease the formation of cyanobacterial mats to inform managers of minimum stock sizes and harvest quotas.
Lastly, the relative importance of benthic cyanobacterial mats as a driver or symptom of coral reef degradation needs to be better understood.
To achieve these four goals, mats need to be reliably and consistently identified by monitoring programmes and researchers, and no longer grouped together with algal types or abiotic substrate.
New developments in the use of molecular tools, such as DNA barcoding, may provide important tools in this regard.
Once this is achieved, the temporal and spatial scale of such surveys can be expanded to better understand the ephemeral or stable nature of mats at different areas, to verify putative drivers and controls, and to better link the occurrence of benthic cyanobacterial mats to the biology and ecology of other reef organisms, such as stony corals.
While an increase in awareness of the presence of benthic cyanobacterial mats may account partially for the recent increase of reports, they appear to be important players in coral reef degradation.
The proliferation and establishment of these mats carries important implications for both ecosystem and human health. A wealth of factors are facilitating mat development and persistence, including increasing availability of space on degrading reefs and declining water quality.
Projected climate change conditions will likely favour growth of cyanobacterial mats while being detrimental to other benthic reef organisms. Systems where human populations and reefs are closely linked and that experience cyanobacterial blooms may be particularly prone to enter social-ecological traps with strong positive feedbacks.
Not only can these traps threaten ecosystem services and human wellbeing, but they can be very challenging to escape from. Considering the serious risk that benthic cyanobacterial blooms pose directly to the future of reefs and their associated ecosystem services as well as human health, further focused research and resources for this topic are important.
AF proposed the original idea of this review. The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
We would also like to thank the two reviewers for their constructive input. A version of this manuscript has already been published online within the lead author's doctoral dissertation Ford, Abed, R.
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