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January 2006 Edition Introduction
By: Scott Zachow & Gene Schwartz

Welcome to the January 2006 Edition of Reef Hobbyist Online - Wishing You A Happy New Year!


Wow, already another year passes us as we enter 2006. The Staff of Reefland.com hopes that you had a wonderful holiday and wish you the very best in 2006!


This month in Reef Currents, Dr. Ron continues describing the variation in marine environments and describes how these variations are used, and perhaps necessary in captive marine aquariums. "The Paradox Of A Consistent Need For Variation" details changes that occur in natural waters and how an aquarist might use these changes in their own systems. The benefits and natural reactions animals have when these changes occur just might influence you to rethink some things in your aquarium.

For our Feature article in January, Steven Pro provides some intriguing possibilities for some uncommon displays. As described, a lot of marine aquariums have the same look, a pile of rock with a mix of corals from different natural conditions and fish from different locations. There are some amazingly simple, yet creative ideas in this article that might help steer you in the direction of creating a unique display in "Where I Think The Hobby Should Be Going".

This edition also brings you the final article in the "Nuisance Algae In The Reef Aquarium" series. This series is a documentation of experiencing nuisance algae and how to overcome the problem. In the first part we talked about some specific algae encountered in the author's personal aquarium and some potential causes. In Part II of this series, analysis of the problem and steps that were taken to reduce the nuisance was documented and explained. In the final part of the series, some insight on removal and perhaps a bit of hope is offered to our readers.


The final article in this edition, we bring you a glimpse into the beautiful aquarium of Iwan Lasser in Reeflections. Following our theme of providing our readers insight to different techniques and displays, the reef tank of Iwan shows how amazingly healthy and beautiful a reef aquarium can be even using simple methodologies. If you like varied colors in a reef aquarium, you will love this Swedish reef!

For anyone who doesn't have the time to sit in front of his or her computer to read each edition of RHO, we are pleased to provide a Printable Version. Look for the Printable Version link at the bottom of each page of RHO.

We hope that you'll enjoy the eighth edition of Reef Hobbyist Online and hope to see you around as we release new editions of RHO bi-monthly!
The Staff of Reefland.com

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Nuisance Algae in the Reef Aquarium - Part III
By: Scott Zachow

Nuisance Algae in the Reef Aquarium - Part III
By: Scott Zachow


Well here we are, 5 months after the first article was published in this series on removing nuisance algae from my own reef aquarium. The task has not been easy, and I wasn’t expecting it to be. What I wanted to accomplish in this series was to provide hope. Many newcomers to the marine aquarium hobby have, and will continue to face challenges with undesirable algae such as those I encountered. Many of these same newcomers won’t stick around long, fearing that the money and efforts they spent were wasted only to have a tank full of unsightly algae they cannot control or get rid of. Who can blame them? Besides, having a tank full of green algae that smothers everything in its growth path isn’t what inspired them to get salt on their hands. The inspiration was more likely a beautiful display of marine fish at their areas finest restaurant. Or perhaps they visited a local fish store whose caretaker had a display of colorful Acropora spp. with long branches and small Chromis viridis swimming through them. Maybe it was the common inspiration that comes when the symbiotic relationship between an Anemone fish and its host was observed. Whatever it was, I will say with certainty that it wasn’t a reef exhibit that was plagued with Derbesia sp. algae and bright white coral skeletons that once lived on the reef structure before the polyps were smothered and eventually killed. As they say, beauty is in the eye of the beholder. I have to believe however, that a tank full of green filamentous alga isn’t what the caregiver is after when setting up an expensive marine system.

The marine aquarium hobby is much different today than it was 10 years ago. With advancements in technology and better understandings of captive requirements, a saltwater aquarium isn’t out of the reach of anyone with a little bit of a disposable income and some dedication. That doesn’t mean that problems won’t pop-up, or are non-existent. Unexplained deaths in fish and corals, disease, and of course, the dreaded nuisance algae outbreaks are all things that hobbyist still experience today. The difference is that today we have a better understanding of how to prevent these problems, or at least reduce the probability of their occurrence. Even still these problems can rear their ugly heads and we must be ready to fight them. Rest assured there are plenty of ways to fight off the troubles of marine aquariums, including nuisance algae. There are also plenty of ways to add to the problem like using “miracle cures” and “magic elixirs” marketed to cure your tank of problems and end poverty in the modern world all with one dose. I assure you that the only way to fix a marine aquarium problem is through diagnosis and hard work. And poverty, well we'll leave that to the politicians.


This picture recently taken of the right side of the aquarium shows the elimination of all of the nuisance algae except a little bit of Valonia sp..

The Good, The Bad, And The Ugly

There are over 7,000 species of green algae; most of them are aquatic. Yet only a few of them are commonly recommended in the marine aquarium. How often have you heard someone recommend buying a couple of rocks covered in hair algae to place in their refugium? Both Caulerpa spp. and Derbesia spp. are green algae from the phylum Chlorophyta, which use chlorophyll A to capture light energy to produce carbohydrates. They both also utilize phosphates and nitrates in their growth. But why don’t people recommend hair algae? The answer might be in the appearance. Although not recommended, aquarists could easily place rocks with hair algae into their refugiums, prune it often and have the same type of nutrient control as they would with Caulerpa spp. The same could be said for Bryopsis and Chaetomorpha. Yet Bryopsis and Derbesia are not used for these purposes, at least not on purpose. All of these algae exist in nature and for the same reasons, nutrient consumption. And when they appear in a captive marine aquarium it is because the conditions are right for their growth. When someone says they are having a problem with nuisance algae, they are effectively having a problem with nutrient control. Adding Caulerpa spp. to a separate vessel is often recommended as a cure since they too utilize the same components for their survival. But you have to hope that the algae purposely added will out-compete the less desirable algae.


A picture of our green Montipora sp. that has been in teh aquarium since the red algae outbreak described below.

In the reef aquarium, there are many different ways to remove nutrients from the system, including adding other algae that will uptake the same nutrients at a faster rate (because they grow faster). This always isn’t practical and alone, not even guaranteed. If nuisance algae are present in the aquarium, they may still consume the available nutrients quicker than the more desirable algae that were added to a refugium. This will lead to the desired algae dieing off due to a lack of available nutrients and the nuisance continuing to flourish. As a different approach, you might try to take some of the nuisance from the display and add it to the separate vessel. The hope here is that the amount in the separate vessel will grow faster and out compete what remains in the display. My point here is if the appearance of the algae consuming the nutrients isn’t an issue, use the same algae that is already flourishing, except in a different, out of sight, vessel. Caulerpa spp., Chaetomorpha or Derbesia spp.; it doesn’t matter as all would consume the same nutrients in the same manner.

Having a separate vessel to grow algae for nutrient consumption isn’t always feasible; it wasn’t in my case. When it’s not, the aquarist must look at other ways to remove the nutrients from the system. Protein Skimming and water changes are effective methods and should be used even in nutrient poor systems or those containing refugiums for algae growth. Without this separate vessel, more aggressive skimming and water changes might be necessary. Even with the more aggressive water corrections, manual removal should be done. For our algae infestations, we were able to get rid of the turf algae and hair algae through water exchanges, but not the Bryopsis. This alga required a lot of tedious manual removal in addition to the heavy skimmer production and water changes. The difficult part with removing algae like Bryopsis is that the thallus easily breaks and floats away. It is difficult to get a good grasp of a bunch and remove it without it breaking away. This loose thallus will float and get hung up elsewhere in the aquarium and quickly grow into a new bush. The edges of porous liverock are a great place for it to get hung up on. Once the thallus is caught, if not removed before it begins to grow and gains a foothold, you have a new bushel in no time that will need to be removed. Because of this, when you are manually removing algae you should quickly remove any broken pieces that are floating in the aquarium. To do this, we used a fish net and scooped it from the water column. Siphoning it out is another method that could be used however you would have to be quick to catch it all.


A nice frag of Montipora sp. that is growing in a plating form with white polyps.

Writing about this, I am taken back to 2003 when I had the worse algae outbreak ever documented! Ok, maybe not that bad but it was totally uncontrollable and forced us to completely tear down our system and start from scratch. During the battle with this unknown alga, we lost many beautiful corals and suffered the loss of a couple of fish as well. It was red algae, very pretty actually and I never considered it a nuisance until it grew out of control. Remember, algae is in the eye of the beholder. It came in on a piece of Florida Gulf aquacultered liverock and lived in the aquarium in a small ball for many, many months with no signs of plaguing growth. Our aquarium was very young in age but developing very nicely. Suddenly, the algae grew out of control. Of course, like with other outbreaks we search for the nutrient load. Skimming, water changes, etc., nothing slowed the growth. It was time for manual extraction, but you couldn’t pull it out due to it breaking so easily and in such small pieces. Just like I described with the Bryopsis, the small pieces would settle in the aquarium and quickly grow into new bushes.



Pictures of the unidentified red algae that I could not remove from the system. The algae broke very easily and made it impossible to remove.

After fighting the manual algae for a few months, it was time for drastic measures. I removed everything from the system and discarded all of the liverock that had any signs on the algae growing on it. I scrubbed the remaining rock with a toothbrush for safe measures and start the tank over again. After only a few months, all of the rock that was in the system with the outbreak was soon covered and we were fighting the same loosing battle. At this point, it was time to remove everything again, but this time discard of everything and start from scratch. Although this time we did have some green algae problems, we have overcome it and are now enjoying a beautiful aquarium stocked with lush Montipora spp. and clams. The purpose of me adding this to the text is to show that even algae that don’t appear problematic can quickly become uncontrollable in the aquarium. For this, I recommend to never allow any alga to grow in the display.


This coral was added to the tank several years ago but was thought to be totally lost to this algae outbreak. While manually removing some Bryopsis, it was located and has begun to recover.

Conclusion

The hobby of captive marine life is not perfect, nor is it easy. But it is not impossible and not out of reach of anyone. Patience is important but sometimes, quick and decisive action is necessary. If you experience a nuisance algae problem in your system, don’t give up. Find the source of your problem and eliminate it. Make sure your equipment is properly tuned. Ensure you don’t have any build-ups of waste accumulating anywhere. Perform more aggressive water changes. Manually extract as much of the algae as possible. Act quickly and aggressively and you will soon be enjoying a beautiful, healthy marine aquarium.

Reef On!
Scott Zachow


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The Paradox Of A Consistent Need For Variation
By: Ronald L. Shimek Ph.D.



Changes

According to legends and nursery rhymes, King Canute is reputed to have had his throne placed on the beach so he could sit and command the tide not to come in. His command went unheeded, of course, and he and his throne began to get wet. Legend has morphed the tale through the years, though. Old Canute was not trying to stop the tide from coming in; rather he wanted to demonstrate to his over-demanding subjects that even the king was not omnipotent. As time the centuries passed, people forgot what the big picture was and they missed his point. Reef aquarists are seemingly more powerful than Canute; at least in their little puddles they can stop the tides by keeping the water level constant. Perhaps the degree of one’s omnipotence is dependent upon how big a fish one is relative to the size of one’s body of water. On the other hand, however, it may not be in our best interest to mess too much with Mother Nature’s various rhythms.

As I wrote in my previous article, no reef environment is consistent or constant in any factor, except perhaps in that of change. Such variability is not unique to reefs; the shallow water marine environment is, in fact, characterized by change no matter where or when you examine it. The three major reasons for the changes that are a part of the life of all reef organisms are the irradiation and gravitational pull of the sun, leveled with the gravitational pull of the moon and nicely spiced by the inclination of the Earth’s axis. Combined together these three factors generate the tidal, seasonal and climatic variability that characterizes all shallow water marine environments, including those on reefs.

Given that we encounter the effects of climatic variability literally from moment to moment, it seems absurd in the extreme to continually encounter the patently false idea that reef animals must be kept in an environment characterized by constancy in physical factors. Not only do things vary on a reef, the range of variation varies from place to place on a given reef and also between reefs. Consequently, reef animals must be adapted for change if they are to persist and spread to occupy suitable environments. It is one thing to note that reef animals are adapted to withstand change; this should be obvious to all but the dimmest light bulb in the package. It is quite another thing, however, to also note, as I will do in this article, that not only are they adapted for change, they actually NEED change.

Daily EnLIGHTenment

It is worthwhile to examine the types of change that are most commonly encountered on coral reefs. To aquarists living in the temperate regions, the most obvious of these changes is probably the regular diurnal cycle of light and dark. It is a trite statement to say that numerous activities and behaviors are regulated by changes in light intensity; yet, it IS worth reiterating that statement. Numerous activities are regulated by changes in light intensity; including feeding, photosynthesis, and virtually all activities of animals such as crabs, shrimp, fishes and aquarists whose sensory input is dominated by vision. The diurnal rhythm of illumination is probably THE single aspect of environmental change that aquarists deal with in a reasonable manner. As such, I really don’t need to deal with it further in this essay.

There are some hidden aspects of these diurnal change on reefs that most hobbyists can’t, don’t, or don’t want to accept and deal with. These aspects are the fact that day length varies continuously throughout the year. The effect of this is more pronounced the closer one gets to the polar areas, but it also occurs in the tropics. In the tropics, another factor that may be as important as the actual magnitude of the change is the position of the sun relative to the zenith. To an equatorial observer, the apparent position of the sun in the sky will vary from 23.5ºN to 23.5ºS of the celestial equator. Changing this factor changes the direction of light impingement and all things that are dependent upon that property of illumination such as shadows, shadow intensity, and amount of total direct illumination. In a very real sense, then, the illumination of aquaria from a light source that does not move with the seasons may be yet another unresolved factor in the husbandry of reef animals.

Time and Tide
“Time and tide wait for no man.”
                                 Geoffrey Chaucer

They don’t wait for reef animals either. The upper edge of a coral reef is absolutely limited by the height of the water over it, so that the reef ends somewhere below the highest water line. In general, only those organisms in the shallowest areas are ever exposed. These shallow areas, those between the highest and lowest tides, are in a zone called, with some uncharacteristic clarity for a biologically used term, “the intertidal zone.” The intertidal zones are bounded by the highest and lowest water levels found in a given region. How wide, or how deep, the intertidal zone is varies with the region. Although the gravitational forces of the moon and sun acting on both the Earth and the water on it generate the tides, the actual magnitude of the tides tends to depend a lot on the local geography. Where the tides push water into and out of triangular- or funnel-shaped embayments the tidal range may be quite large. The highest tides are found in the Bay of Fundy on Canada’s east coast, but other extremely high tidal fluxes are found in the upper reaches of Cook Inlet, near Anchorage, Alaska, and near the head of the Gulf of California. In these regions, the highest and the lowest tides may be separated by more than 10 m (33 ft). In others where the basin doesn’t confine the water mass, such as most coral reef areas, however, the tidal height may fluctuates less than a meter (3.3 ft) over the course of a year. Weather conditions may also influence the tides, winds may blow waters toward or away from the shores either increasing extreme tides, or dampening them out altogether if they blow water in directions contrary to tidal flow. Likewise, high barometric pressure can push water out of an ocean basin lowering the height of tide, while low barometric pressure can allow water to flow into a basin increasing tidal height. The extremely low barometric pressure seen in cyclonic storms, such as hurricanes, contributes to the “storm surge” that is often more devastating that the storms’ winds. However, for reef organisms, possibly more important than the actual exposure of shallow water corals during the tidal cycle, is the movement of water that the tides generate.


Figure 1. An example of the variation through the month of tidal height in feet related to a datum (= zero level) of Mean Lower Low Water. A semi-diurnal tidal cycle has two unequal high tides and two equal low tides during an average day. Many coral reef areas have a diurnal tidal cycle where both highs and both lows are roughly equivalent to each other. Other areas may have a tidal cycle with one high and one low tide per day. In all cases, however, organisms can adapt to, and use, the tidal cycle as a trigger for essential behaviors.

Water flow in and around coral reefs is due generally to two types of currents that differ in their mode of generation. As it would be trite to say, “water movement is water movement;” to an organism, it might seem trivial to differentiate between the types of water movement; after all, in either case, the medium moves and as long as that movement is within certain specific extremes, the organism can withstand it and survive. However, from the aspect of a biologist or a reef aquarist, it is definitely necessary to discriminate between the types of water flow. Currents of the first type are wind driven oceanic currents. Although there may be some significant variations with the season, these currents tend to be more-or-less steady, in both direction and magnitude. Oceanic currents are vital to coral reefs as they bring to the reef the planktonic food that feeds many of the animals on it. A more variable subset of the wind driven currents would be those generated by storms, in particular the large cyclonic storms, such as hurricanes and typhoons, common in the tropics. Most of these currents are inconsequential, except inasmuch as the worst of them may significantly reorganize the geography of the reef and in the process, they may contribute to the spread of those animals such as shallow-water acroporids that depend upon fragmentation for asexual reproduction. Nonetheless, as far as animals are concerned, a major distinction between these two types of currents is that the former are absolutely periodic and predictable from day to day, and the latter, while “expected” over the lifetime of the organism are not predictable.

The second current category includes those generated by tidal influences. Tides are essentially long oceanic waves of low amplitude and long period generated by the interactions of the gravitational pulls of the moon, sun, and Earth. Waves, as long as they don’t impinge on a surface, generate no net water flow; what sloshes forward also sloshes back. However in shallow basins, where the water moved by these waves encounters the frictional drag of the ocean bottom, all waves including tides, may result in a lot of localized water movement. To the point of this essay, however, such tidally-generated currents have a specific tidal periodicity, changing both magnitude and direction up to four times per day. Interestingly, due to astronomical factors, the tidal pattern is not on a strictly daily scale. Although the earth rotates on its axis once every twenty-four hours, the time for the combined motion of the Earth’s axial rotation and the lunar orbital velocity to put the moon at approximately the same place in the sky on subsequent days is about 24 hours and 50 minutes. Consequently, the corresponding tides are about 50 minutes later each day. The tidal pattern is a consistent and highly predictable one that repeats every 18.6 years. Although the magnitude and directional flows are variable from place to place and, particularly, from ocean basin to ocean basin, they are very predictable in local habitats. This local predictability has significant consequences as natural selection can, and has, attuned the organisms in most places to take advantage of it.

The Periodicity and Constancy Of Change

One of the things, then, that characterizes reef environments is change, and change with a predictable periodicity. If an organism can sense this change, it has the major important consequence of making the world predictable. The question then becomes, “Do organisms seem to be able to predict changes in their environment?” The answer is, undoubtedly and unequivocally, “Yes!” Probably the most common examples of this predictive ability, however, come from temperate marine environments rather than reefs. The reason for the predominance of temperate examples (See, for example, MacGinitie and MacGinitie, 1968; Morris, et al., 1980; Kozloff, 1983; Shimek, 1987; Ruppert and Fox, 1988) is two fold. First, most marine research has been done in temperate areas, and the work that has been there is better known than is the work done in reef environments. Secondly and perhaps more importantly, because of the wider range of swings in both daylight and temperature in temperate areas changes in animal behaviors are easier to document and correlate with the environmental changes. In all temperate marine areas that have been investigated, the working rule is that both generalized and specific behavior patterns are correlated with environmental changes, such as those due to tidal, temperature, and illumination variables.

The filter feeding sea cucumbers of the cool waters of the northern Puget Sound region provide a good example of a series of generalized behaviors that are apparently triggered by environmental cues. There are several different and very common sea cucumbers found in this region including five or more species each of Cucumaria and Pentamera, as well as other species in several other genera such as Eupentacta. These animals are commonly found extended and feeding from late February to late September. During this period, the region’s waters are rich with plankton. Snowmelt and rain generate nutrient-laden runoff, and the annual plankton bloom follows this and is continually fueled by it. The water can be as murky as thick soup during the rich spring and summer plankton blooms, and the cukes take full advantage of this abundant supply of food. There is a risk to feeding, however, as feeding activities increase the cucumber’s exposure to predators. By late summer, however, the bloom tapers off. Shortly thereafter all of these animals cease feeding and disappear into hiding in burrows and under rocks; presumably the benefits gathered by feeding during this period do not outweigh the risks generated by feeding behavior. The reduction in food in the water, resulting in a drop in the amount of food eaten per feeding period may be the proximate cue for this behavioral change, but the cue may also be the slight drop in water temperature that occurs in the fall. The water temperature in the Puget Sound region is far LESS variable than in most coral reef areas, but during the fall it slowly drops a couple of degrees Celsius. Whatever the cues, the sea cucumbers appear to “vanish” from the areas. They withdraw into burrows or into the sediments or under the rocks and become non-feeding and quiescent. They remain out of sight and out of mind until late January or early February. By this time, the amount of daylight has increased significantly from the low of the winter solstice. The water temperature is starting to rise. The water is still clear, however, as the spring plankton bloom has not yet commenced. The benthic environment becomes covered with diatoms where it was clean of them in the dead of winter, and all of a sudden, within a week or two, sea cucumbers appear and inflate into their feeding postures. They are not responding to the presence of food, there really isn’t any more during this period than there was a few weeks before. Temperature and light, however, have changed. A few weeks after this the spring plankton bloom commences and the animals can really start feeding. During this period, they rapidly gain weight and produce gametes. Then on the first sunny day following the spring equinox, on an outgoing or ebbing tide, in the afternoon they spawn. Most of the populations will spawn during this first blast of reproduction, but some animals will also spawn over the next week or so.



Figure 2. The top picture was taken in September, the lower one in November at the same locality in northern Puget Sound illustrating seasonal differences in feeding behavior of sea cucumbers discussed in the text. Note the orange (Cucumaria miniata) and red (Psolus chitonoides) feeding tentacles are visible in the top image and not the lower one. In the lower image, the cucumbers are not feeding. The Cucumaria are withdrawn into burrows and are not visible. The Psolus are visible when not feeding; one is present in the lower image (the orange structure above the snail to the lower right).



Figure 3. Seasonal feeding differences in sea cucumbers are found in soft sediment areas as well in hard substrates. The top picture was taken in July, the lower one in December at the same locality in northern Puget Sound. Note the abundance of white cucumbers (Pentamera populifera) visible in the top image and not the lower one. The cukes are buried under the sediment in the lower image. The scallops are Patinopecten caurinus and are about 8 inches in diameter.

In such habitats, the animals appear to respond to the cues of increasing day length and/or temperature as the signal to begin to feed. Subsequent to that, they appear to use several cues: 1) the equinox, manifested as equally long periods of light and dark in a day, 2) the currents generated by an outgoing tide, and 3) the bright light of a sunny day (which may boost the temperature a bit, as well, as the signals to spawn. And spawn they do… These animals may be very abundant; Cucumaria miniata, a large animal up to 30 cm (1 foot) long and 2 cm (0.8 inch) in diameter, commonly reaches densities of 150 animals per square meter. In some areas, the densities of some species of Pentamera are in excess of 10,000 animals per square meter. When these animals spawn, enough of the large greenish eggs of Cucumaria are released to change the color of moderate sized bays (those about a mile long and wide) from blue to green. All of these events appear to be triggered by environmental changes.


Figure 4. Mass spawning of Cucumaria miniata occurs shortly after the spring equinox while the tide is ebbing on a sunny afternoon. Here a female is releasing some of her eggs.

Reef Coral “Jollies”

Similar things happen on reefs. Until as recently as about twenty-five years ago, no one had ever seen or documented spawning in nature for a reef coral. Rather by happenstance, the first examples of coral spawning were noted by some divers to be nocturnal and synchronous within many species. This type of pattern had been previously seen in other types of animals in temperate regions, and it was realized that what was occurring with the corals was a synchronous spawning event triggered by some environmental cue. In the corals, as with many temperate animals, the spawning is synchronized with the lunar cycle. However, that synchronization doesn’t imply that the cycle is triggered directly by changes in the phase of the moon. In fact, such direct synchronization is rather unlikely. In this type of situation, the signals that trigger spawning are likely to be derived from the lunar cycle, but are unlikely to have any direct relationship to moonlight. The reason for this may be obvious, if the spawning were to be triggered by moonlight alone, a series of stormy nights could seriously disrupt spawning and may even delay the spawning time well past what would be necessary for the survival of the larvae that would result from the spawning event. Moonlight may be one of the cues, but other cues would certainly also be important. The other primary variables linked to lunar periodicity are, of course, the tides and day length.

As corals have no eyes the question might arise as how they are able to measure and assess changes in day or night length. It turns out that in many animals, the synthesis of numerous chemicals is dependent upon light. In humans, for example, vitamin D synthesis is dependent upon the action of ultraviolet light in outer layers of the skin. Similar types of chemical formation can trigger the production of specific hormones in many invertebrates. Often these same chemicals are broken down in darkness. Even the slight, but regular, changes in day length or illumination, such as those that occur in the tropics, can trigger regular patterns in the concentration of a chemical that might be used as triggers for gonad maturation or spawning. For example, after the summer solstice, a slight but progressive lowering of the rate of production of a given photochemical might result in the decrease of an inhibitory material. When the level of the inhibitory material falls below a given threshold, the inhibition ceases; with the cessation of the inhibition might come the initiation of gamete production. Changes in the levels of another chemical, perhaps one made in response to the buffeting of the animals’ bodies in strong tidal currents, could subsequently result in spawning but only if the gonads were “ripe.” Such cybernetic chemical arrays utilizing the interactions of both inhibiting and stimulating chemicals are quite common in many animals. These interactions are often quite complex because they may result from the interactions of several different types of chemicals, all of which may be termed as “hormones.” Under the action of natural selection, the synergy of these chemicals could be fine tuned to give an extremely precise response: the synchronous spawning of a large number of corals of different species. Of course, all the chemicals have to do is to get the animal “primed” for spawning. The final trigger could be the reception of chemical released into the water by any other spawning individual. In other words, once the population is ready to spawn, it would only take the spawning of one animal to trigger all downstream animals to spawn right along with it.

Aquarium Concerns

The deteriorating state of coral reefs (see here, and here) means sooner or later, and mostly likely sooner than later, aquarists will either need to be propagating the animals they are maintaining or they won’t have animals to maintain. Although the techniques of asexual propagation are well known for some animals, these techniques produce only few clones of the original animal. They introduce no new varieties, and because of the traumatic nature of the fragmentation, they are limited in the number of animals that can be produced at any one time. Additionally, cloning by fragmentation in many marine animals is impossible.

If aquarists were familiar with the events necessary for the triggering of sexual reproduction, large numbers of offspring, all new individuals, could be produced at any one time. This would lead both to large numbers of the animals and new color and morphological varieties. By selective manipulation of the appropriate parameters, the spawning event would not be haphazard or unexpected. The few spawning events that have occurred in aquaria have been, without exception, unplanned and unexpected, and most have resulted in problems. That need not be the case, as there is no reason why reef tanks cannot be set up with current and lighting regimes that mimic natural conditions so effectively that spawning times will be known to the nearest half hour. Animals in nature are tuned into the variability of their environment. As hobbyists, we should not only be providing variation to our animals in a natural pattern, we should be planning for the natural outcome of that variation and using it to further our hobby.

References Cited:

Kozloff, E. N. 1983. Seashore Life of the Northern Pacific Coast. An illustrated guide to Northern California, Oregon, Washington, and British Columbia. University of Washington Press. Seattle. 370 pp.

Morris, R. H., D. P. Abbott and E. C. Haderlie. 1980. Intertidal invertebrates of California. Stanford University Press. Stanford. 690 pp.

MacGinitie, G. E. and N. MacGinitie. 1968. Natural history of marine animals. McGraw-Hill Book Co. New York. 523 pp.

Ruppert, E. E. and R. S. Fox. 1988. Seashore Animals of the Southeast. University of Southern Carolina Press. Columbia, S. C. 429 pp.

Shimek, R.L. 1987. Sex among the sessile: With the onset of spring in cool northern Pacific waters, even sea cucumbers bestir themselves. Natural History 96: 60-63.

Coral Spawning References (This Is A Short List, There Are A Lot More). These references are generally available in libraries and provide many of the appropriate data necessary to understand spawning in the animals discussed:

Achituv, Y. and Y. Benayahu. 1990. Polyp dimorphism and functional, sequential hermaphroditism in the soft coral Heteroxenia fuscescens (Octocorallia). Marine Ecology Progress Series. 64:263-269.

Arai, T., M. Kato, A. Heyward, Y. Ikeda, T. Iizuka and T. Maruyama. 1993. Lipid composition of positively buoyant eggs of reef-building corals. Coral Reefs. 12:71-75.

Babcock, R. C. 1984. Reproduction and distribution of two species of Goniastrea (Scleractinia) from the Great Barrier Reef province. Coral Reefs. 2:187-195.

Babcock, R. C. and A. J. Heyward. 1986. Larval development of certain gamete-spawning scleractinian corals. Coral Reefs. 5:111-116.

Babcock, R. C., G. D. Bull, P. L. Harrison, A. J. Heyward, J. K. Oliver, C. C. Wallace and B. L. Willis. 1986. Synchronous spawnings of 105 scleractinian coral species on the Great Barrier Reef. Marine Biology (Berlin). 90:379-394.

Beauchamp, K. A. 1993. Gametogenesis, brooding and planulation in laboratory populations of a temperate scleractinian coral Balanophyllia elegans maintained under contrasting photoperiod regimes. Invertebrate Reproduction and Development. 23:171-182.

Benayahu, Y. and Y. Loya. 1984. Life history studies on the Red Sea soft coral Xenia macrospiculata Gohar,. 1940. I. Annual dynamics of gonadal development. Biological Bulletin (Woods Hole). 166:32-43.

Benayahu, Y. and Y. Loya. 1984. Life history studies on the Red Sea soft coral Xenia macrospiculata Gohar,. 1940. II. Planulae shedding and post larval development. Biological Bulletin (Woods Hole). 166:44-53.

Benayahu, Y. and Y. Loya. 1986. Sexual reproduction of a soft coral: Synchronous and brief annual spawning of Sarcophyton glaucum. Biological Bulletin (Woods Hole). 170:32-42.

Chadwick-Furman, N. E. and M. Spiegel. 2000. Abundance and clonal replication in the tropical corallimorpharian Rhodactis rhodostoma. Invertebrate Biology. 119:351-360.

Chadwick-Furman, N. E., M. Spiegel and I. Nir. 2000. Sexual reproduction in the tropical corallimorpharian Rhodactis rhodostoma. Invertebrate Biology. 119:361-369.

Chiappone, M. and K. M. Sullivan. 1996. Distribution, abundance and species composition of juvenile scleractinian corals in the Florida reef tract. Bulletin of Marine Science. 58:555-569.

Delvoye, L. 1988. Gametogenesis and gametogenic cycles in Agaricia agaricites (L.) and Agaricia humilis Verrill and notes on gametogenesis in Madracis mirabilis (Duchassaing & Michelotti) (Scleractinia). Uitgaven Natuurwetenschappelijke Studiekring Voor Suriname En De Nederlandse. Antillen:101-134.

Fabricius, K. E. and J. Metzner. 2004. Scleractinian walls of mouths: Predation on coral larvae. Coral Reefs. 23:245-248.

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Fadlallah, Y. H. 1996. Synchronous spawning of Acropora clathrata coral colonies from the western Arabian Gulf (Saudi Arabia). Bulletin of Marine Science. 59:209-216.

Fan, T. Y. and C. F. Dai. 1995. Reproductive ecology of the scleractinian coral Echinopora lamellosa in northern and southern Taiwan. Marine Biology (Berlin). 123:565-572.

Fan, T. Y. and C. F. Dai. 1999. Reproductive plasticity in the reef coral Echinopora lamellosa. Marine Ecology Progress Series. 190:297-301.

Fautin, D. G. 2002. Reproduction of Cnidaria. Canadian Journal of Zoology. 80:1735-1754.

Fisk, D. A. and V. J. Harriott. 1990. Spatial and temporal variation in coral recruitment on the Great Barrier Reef: implications for dispersal hypotheses. Marine Biology (Berlin). 107:485-490.

Gittings, S. R., G. S. Boland, K. J. P. Deslarzes, C. L. Combs, B. S. Holland and T. J. Bright. 1992. Mass spawning and reproductive viability of reef corals at the East Flower Garden Bank, northwest Gulf of Mexico. Bulletin of Marine Science. 51:420-428.

Glynn, P. W., N. J. Gassman, C. M. Eakin, J. Cortes, D. B. Smith and H. M. Guzman. 1991. Reef coral reproduction in the eastern Pacfic: Costa Rica, Panama, and Galapagos Islands (Ecuador). I. Pocilloporidae. Marine Biology (Berlin). 109:355-368.

Glynn, P. W., S. B. Colley, C. M. Eakin, D. B. Smith, J. Cortes, N. J. Gassman, H. M. Guzman, J. B. Del-Rosario and J. S. Feingold. 1994. Reef coral reproduction in the eastern Pacific: Costa Rica, Panama, and Galapagos Islands (Ecuador). 2. Poritidae. Marine Biology (Berlin). 118:191-208.

Glynn, P. W., S. B. Colley, N. J. Gassman, K. Black, J. Cortes and J. L. Mate. 1996. Reef coral reproduction in the eastern Pacific: Costa Rica, Panama, and Galapagos Islands (Ecuador). 3. Agariciidae (Pavona gigantea and Gardineroseris planulata). Marine Biology (Berlin). 125:579-601.

Hall, V. R. and T. P. Hughes. 1996. Reproductive strategies of modular organisms: comparative studies of reef-building corals. Ecology (Washington D C). 77:950-963.

Harriott, V. J. 1983. Reproductive ecology of four scleractinian species at Lizard Island, Great Barrier Reef. Coral Reefs. 2:9-18.

Harriott, V. J. 1983. Reproductive seasonality, settlement, and post-settlement mortality of Pocillopora damicornis (Linnaeus), at Lizard Island, Great Barrier Reef. Coral Reefs. 2:151-157.

Harriott, V. J. 1992. Recruitment patterns of scleractinian corals in an isolated sub-tropical reef system. Coral Reefs. 11:215-219.

Harrison, P. L. 1985. Sexual characteristics of scleractinian corals: systematic and evolutionary implications. Proceedings of the Fifth International Coral Reef Symposium. 4:337-342.

Harrison, P. L. and C. C. Wallace. 1990. Reproduction, dispersal and recruitment of scleractinian corals. In: Dubinsky, Z. Ed. Coral Reefs. Elsevier. Amsterdam. pp. 133-207.

Harrison, P. L., R. C. Babcock, G. D. Bull, J. K. Oliver, C. C. Wallace and B. L. Willis. 1984. Mass spawning in tropical reef corals. Science (Washington D C). 223:1186-1189.

Hayashibara, T., K. Shimoike, T. Kimura, S. Hosaka, A. Heyward, P. Harrison, K. Kudo and M. Omori. 1993. Patterns of coral spawning at Akajima Island, Okinawa, Japan. Marine Ecology Progress Series. 101:253-262.

Heyward, A. J. 1986. Sexual reproduction in five species of the coral Montipora. Hawaii Institute of Marine Biology Technical. Report:170-178.

Heyward, A. J. 1988. Reproductive status of some Guam corals. Micronesica. 21:271-274.

Heyward, A. J. and J. D. Collins. 1985. Growth and Sexual Reproduction in the Scleractinian Coral Montipora digitata (Dana). Australian Journal of Marine and Freshwater Research. 36:441-446.

Heyward, A. J. and R. C. Babcock. 1986. Self- and cross-fertilization in scleractinian corals. Marine Biology (Berlin). 90:191-195.

Heyward, A., K. Yamazato, T. Yeemin and M. Minei. 1987. Sexual reproduction in the corals in Okinawa. Galaxea. 6:331-343.

Holloran, M. K. 1986. The relationship between colony size and larva production in the reef coral Pocillopora damicornis. Hawaii Institute of Marine Biology Technical. Report:167-169.

Hughes, T. P. and J. E. Tanner. 2000. Recruitment failure, life histories, and long-term decline of Caribbean corals. Ecology. 81:2250-2263.

Jokiel, P. L., R. Y. Ito and P. M. Liu. 1985. Night irradiance and synchronization of lunar release of planula larvae in the reef coral Pocillopora damicornis. Marine Biology (Berlin). 88:167-174.

Kapela, W. and H. R. Lasker. 1999. Size-dependent reproduction in the Caribbean gorgonian Pseudoplexaura porosa. Marine Biology (Berlin). 135:107-114.

Karlson, R. H. 1981. Reproductive patterns in Zoanthus spp. from Discovery Bay, Jamaica. Proceedings of the Fourth International Coral Reef Symposium. 2:699-704.

Kenyon, J. C. 1992. Sexual reproduction in Hawaiian Acropora. Coral Reefs. 11:37-43.

Kinzie, R. A., III. 1993. Spawning in the reef corals Pocillopora verrucosa and P. eydouxi at Sesoko Island, Okinawa. Galaxea. 11:93-105.

Kojis, B. L. and N. J. Quinn. 1981a. Aspects of sexual reproduction and larval development in the shallow water hermatypic coral, Goniastrea australensis. Bulletin of Marine Science. 31:558-573.

Kojis, B. L. and N. J. Quinn. 1981b. Reproductive strategies in four species of Porites (Scleractinia). Proceedings of the Fourth International Coral Reef Symposium. 2:145-152.

Kojis, B. L. and N. J. Quinn. 1982. Reproductive ecology of two faviid corals (Coelenterata: Scleractinia). Marine Ecology Progress Series. 8:251-255.

Kojis, B. L. and N. J. Quinn. 1984. Seasonal and depth variation in fecundity of Acropora palifera at two reefs in Papua New Guinea. Coral Reefs. 3:165-172.

Kojis, B. L. and N. J. Quinn. 1985. Puberty in Goniastrea favulus age or size limited. Proceedings of the Fifth International Coral Reef Symposium. 4:289-293.

Krupp, D. A. 1983. Sexual reproduction and early development of the solitary coral Fungia scutaria (Anthozoa: Scleractinia). Coral Reefs. 2:159-164.

Lirman, D. 2000. Fragmentation in the branching coral Acropora palmata (Lamarck): Growth, survivorship, and reproduction of colonies and fragments. Journal of Experimental Marine Biology and Ecology. 251:41-57.

Liu, P. J. and T. Y. Fan. 2005. Timing of larval release by the blue coral, Heliopora coerulea, in southern Taiwan. Coral Reefs. 24:30.

Martinelli, F. J. 1986. Time-series analysis of biological data: a case study involving periodicity of coral spawning. Hawaii Institute of Marine Biology Technical. Report:488-501.

Miller, K. J. and C. N. Mundy. 2005. In-situ fertilisation success in the scleractinian coral Goniastrea favulus. Coral Reefs. 24:313-317.

Muller, W. A. and T. Leitz. 2002. Metamorphosis in the Cnidaria. Canadian Journal of Zoology. 80:1755-1771.

Neigel, J. E. and J. C. Avise. 1983. Clonal diversity and population structure in a reef-building coral, Acropora cervicornis: self-recognition analysis and demographic interpretation. Evolution. 37:437-453.

Omori, M., H. Fukami, H. Kobinata and M. Hatta. 2001. Significant drop of fertilization of Acropora corals in 1999: An after-effect of heavy coral bleaching? Limnology and Oceanography. 46:704-706.

Permata, W. D., R. A. Kinzie III and M. Hidaka. 2000. Histological studies on the origin of planulae of the coral Pocillopora damicornis. Marine Ecology Progress Series. 200:191-200.

Reichelt-Brushett, A. J. and P. L. Harrison. 1999. The effect of copper, zinc, and cadmium on fertilization success of gametes from scleractinian reef corals. Marine Pollution Bulletin. 38:182-187.

Richmond, R. H. 1987. Energetic relationships and the biogeographical differences among fecundity, growth and reproduction in the reef coral Pocillopora damicornis. Bulletin of Marine Science. 41:594-604.

Richmond, R. H. 1987. Reproduction and recruitment of corals: comparisons among the Caribbean, the eastern Pacific, the Indo-west Pacific, and the Red Sea. Unesco Reports in Marine Science. 46:239-253.

Richmond, R. H. 1990. Relationships among reproductive mode, biogeographic distribution patterns and evolution in scleractinian corals. Advances in Invertebrate Reproduction. 5:317-322.

Richmond, R. H. and C. L. Hunter. 1990. Reproduction and recruitment among corals: comparisons among the Caribbean, the tropical Pacific, and the Red Sea. Marine Ecology Progress Series. 60:185-203.

Richmond, R. H. and P. L. Jokiel. 1984. Lunar periodicity in larva release in the reef coral Pocillopora damicornis at Enewetak and Hawaii. Bulletin of Marine Science. 34:280-287.

Rinkevich, B. and Y. Loya. 1979. The reproduction of the Red Sea coral Stylophora pistillata. 1. Gonads and planulae. Marine Ecology Progress Series. 1:133-144.

Rinkevich, B. and Y. Loya. 1979. The reproduction of the Red Sea coral Stylophora pistillata. II. Synchronization in breeding and seasonality of planula shedding. Marine Ecology Progress Series. 1:145-152.

Sakai, K. 1998. Effect of colony size, polyp size, and budding mode on egg production in a colonial coral. Biological Bulletin (Woods Hole). 195:319-325.

Sakai, K. and K. Yamazato. 1984. Coral recruitment to artificially denuded natural substrates on an Okinawan reef flat. Galaxea. 3:57-69.

Shlesinger, Y. and Y. Loya. 1985. Coral community reproductive patterns: Red Sea versus the Great Barrier Reef. Science (Washington D C). 228:1333-1335.

Sier, C. J. S. and P. J. W. Olive. 1994. Reproduction and reproductive variability in the coral Pocillopora verrucosa from the Republic of Maldives. Marine Biology (Berlin). 118:713-722.

Simpson, C. J. 1991. Mass spawning of corals on Western Australian reefs and comparisons with the Great Barrier Reef. Journal of the Royal Society of Western Australia. 74:85-91.

Soong, K. 1991. Sexual reproductive patterns of shallow-water reef corals in Panama. Bulletin of Marine Science. 49:832-846.

Steiner, S. C. C. 1995. Spawning in scleractinian corals from SW Puerto Rico (West Indies). Bulletin of Marine Science. 56:899-902.

Stimson, J. S. 1978. Mode and timing of reproduction in some common hermatypic corals of Hawaii and Enewetak. Marine Biology (Berlin). 48:173-184.

Stoddart, J. A. and R. Black. 1985. Cycles of gametogenesis and planulation in the coral Pocillopora damicornis. Marine Ecology Progress Series. 23:153-164.

Stoddart, J. A., R. C. Babcock and A. J. Fleyward. 1988. Self-fertilization and maternal enzymes in the planulae of the coral Goniastrea favulus. Marine Biology (Berlin). 99:489-494.

Szmant, A. M. 1986. Reproductive ecology of Caribbean reef corals. Coral Reefs. 5:43-53.

Szmant, A. M. and N. J. Gassman. 1991. Caribbean Reef Corals. The evolution of reproductive strategies. Oceanus. 34:11-18.

Szmant-Froelich, A., M. Reutter and and L. Riggs. 1985. Sexual reproduction of Favia fragum (Esper): Lunar patterns of gametogenesis, embryogenesis, and planulation in Puerto Rico. Bulletin of Marine Science. 37:880-892.

Szmant-Froelich, A., P. Yevich and and M. E. Q. Pilson. 1980. Gametogenesis and early development of the temperate coral Astrangia danae (Anthozoa: Scleractinia). Biological Bulletin (Woods Hole). 158:257-269.

Tanner, J. E. 1996. Seasonality and lunar periodicity in the reproduction of pocilloporid corals. Coral Reefs. 15:59-66.

Tomascik, T. and F. Sander. 1987. Effects of eutrophication on reef-building corals. 3. Reproduction of the reef-building coral Porites porites. Marine Biology (Berlin). 94:77-94.

Van Moorsel, G. W. N. M. 1983. Reproductive strategies in two closely related stoney corals. Marine Ecology Progress Series. 13:273-283.

Van Veghel, M. L. J. 1994. Reproductive characteristics of the polymorphic Caribbean reef building coral Montastrea annularis. I. Gametogenesis and spawning behavior. Marine Ecology Progress Series. 109:209-219.

Van Veghel, M. L. J. and M. E. H. Kahmann. 1994. Reproductive characteristics of the polymorphic Caribbean reef building coral Montastrea annularis. II. Fecundity and colony structure. Marine Ecology Progress Series. 109:221-227.

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Ward, S. 1992. Evidence for broadcast spawning as well as brooding in the scleractinian coral Pocillopora damicornis. Marine Biology (Berlin). 112:641-646.

Westneat, M. W. and J. M. Resing. 1988. Predation on coral spawn by planktivorous fish. Coral Reefs. 7:89-92.

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Where I Think The Hobby Should Be Going
By Steven Pro

Where I Think The Hobby Should Be Going
By: Steven Pro


I have had the pleasure recently to get out to a good number of local aquarium clubs. As part of these trips, inevitably, I get to visit the homes of some of the aquarists and view their displays. And, while I am truly grateful to talk to my fellow aquarists, travel the country, and see these tanks, more and more lately I find myself feeling that if I have seen one tank, I have seen them all. That is not to take away from these aquariums. I have seen some very pretty exhibits. It is just that I find myself wanting to see something different, something new, something that takes me back for a moment and makes me think, “Wow! I never thought about doing something like that before!”

It is with this frame of reference that I offer up some intriguing possibilities. Not so much to be copied, but to inspire my fellow hobbyists to think outside the box and come up with new and interesting ways to appreciate our aquatic pets.

Well-rounded fish geeks like me should be familiar with the name Takashi Amano. For the uninitiated, Amano style freshwater-planted aquariums are becoming quite popular, and in my opinion, they can rival many so-called reef displays in their attention to detail and overall beauty. Many times, they tend to focus on a monospecific display of fish and plants instead of the all too common hodge podge of fish and corals that we emulate, the so-called coral reef garden, if I could borrow a phrase from my friend Anthony Calfo. Amano also tends to tell a story with his aquariums. Or, give the viewer an overall impression of something else, for instance a mountain range, or of something already existing in nature but on a smaller scale. In short, these displays are much more than a typical freshwater community tank. I have tried to emulate some of Amano’s style in the following ideas while replacing the plants with corals.

Red Sea Representation:
Who amongst us does not recognize the beauty in a typical Red Sea image of a ‘forest’ of non-photosynthetic Dendronepthea with a large school of Anthias intermingled? Pictures such as these were what initially inspired many of us into marine ornamentals. Soon afterward though, we learned of how keeping Dendronepthea long-term is nearly impossible. And then, it seems the image then faded away from our collective memory.

While I am not going to recommend that anyone go out and fill their tanks with corals that are doomed to perish, why not try to devise a realistic representation of this habitat with animals that can be kept successfully? What I envision is an aquarium stocked with various colors of what we generally refer to as Finger Leathers. Sinularia in particular come naturally in pinks, yellows, and fluorescent greens. While not the same thing, a display dominated by these Finger Leathers and a school of Red Sea Pseudoanthias squamipinnis would be impressive and yet easy enough to maintain using current husbandry techniques and equipment.


Sinularia are typically hearty species suited for many types of aqaurium since they adapt to many types of conditions. This would be an excellent coral for the display described above. Photo by Steven Pro.



Anthias are beautiful fish and although they do have some captive challenges, they are not out of the reach of any aquarist. Photos by Steven Pro.



A Little Atoll:
The theme of this display would be to recreate a small outer patch reef. A small mound of rock would be situated such that it was centered in the aquarium with a fair amount of sand all around it. Onto the rockwork, small frags of the common Green Slimer Acropora would be attached and encourage to grow into one large, massive colony to the point that nearly none of the underlying rock would be visible any longer. The fish stocking would be made up entirely of a small group of Four Stripe Damsels, Dascyllus melanurus. Preferably the water flow would be constructed in such a way that it would create ripples in the sand bed. This would further give the illusion that this patch reef is isolated and set apart from the greater reef structure. The final touch would be the stark blue background, signifying that this little piece of rock is the last refuge before the wide-open blue sea.


Dascyllus melanurus are not just for cycling new aquariums as they are often recommended. These small fish are excellent candidates for smaller aquariums and can be used to create appealing displays. Photo by Steven Pro.

Plating Stand of Coral:
With this idea, I set out to mimic a portion of an overall reef. I have always been impressed with the pictures of the reefs showing large stands of plating Acropora. But, getting and then maintaining plating Acropora is a challenge. Specimen selection is very important, as is strong lighting and massive amounts of strong, turbulent water flow to keep the branches growing thick and robust. An alternative can be found, though, in rather easy to keep corals. Imagine an aquarium made up entirely of various colors of plating Montipora instead. They are not nearly as demanding as their plating cousin Acroporas in terms of lighting or water flow. They also tend to grow like weeds. A few small frags of orange, red, green, and purple plating Montiporas strategically placed and permitted to flourish would quickly fill a display with their intricate whirling forms and colors. One could even add a yellow Turbinaria reneformis for additional color, although careful pruning of the Montiporids will be needed to ensure that the Turbinaria is not overgrown, shaded, or otherwise killed. To this boldly colored montage, I would incorporate a slightly modest fish for balance. Something like a school of Threadfin Cardinalfish, Apogon leptacanthus, with their understated beauty would be a perfect compliment to the bold, contrasting colors of the plating corals in the background.


A beautiful purple encrusting coral. Photo by Steven Pro.

Seagrass Environment:
A lot of people have urged fellow aquarists to experiment with seagrass habitats, but so far most of us have refused for some unknown reason. But, I am going to plug along and try to inspire you as well to attempt these necessary components of the greater reef ecosystem.

Regardless of where ones falls in the deep sand bed (DSB) versus bare bottom (BB) debate, we should all be able to agree that in this instance a DSB is appropriate and frankly necessary. A lush growth of Turtle Grass in a DSB is a challenging, yet attainable goal. Insert some cnidarians for a change of pace and a very nice biotope can be created. Fungiids such as an orange Cycloseris and a purple Fungia would add some needed splashes of color against the green backdrop of seagrass as would Squamosa or Derasa clams of the genus Tridacna. Even a red Trachyphyllia geoffroyi would be a reasonable addition to the coral life. And, a Diadema urchin or two would be fitting here, as would a mated pair or small grouping of their commensal Banghai Cardinalfish, Pterapogon kauderni. One could continue this theme and really focus on interspecies relationships here by the addition of a Pistol/Snapping Shrimp with its symbiotic Goby. Or, perhaps a shrimp of the genus Perclimmes to host in one of the large polyp stony corals. These would all go together to recreate an interesting biotopic presentation.


Banghai Cardinalfish are popular amongst aquarists whom are interested in fish breeding. The Cardinalfish are common spawners in captive care and watching them in the protection of an urchins spines provides a look into their natural existance. Photo by Steven Pro.

Low Profile Mangrove Habitat:
A relatively shallow vessel, perhaps no more than 12” but definitely not more than 24” would be my choice for this exhibit. And, I would place the tank on or very near the ground. This would permit the mangroves to grow to truly become small trees in the house. An aquarium sitting on the ground with five-foot trees coming out of it would rightly be a sight to behold. This display too would be suited by a DSB and if sticking with the biotope theme, Pearly Jawfish would be a logical choice. Or, one could mix both the Mangroves with the above Seagrass theme with an Indo-Pacific flare. Being able to stand above the tank and look down would be a particularly attractive option when housing Tridacna clams. One word of caution, as a relatively new father I am sensitive that this sort of display would be a potential drowning hazard for young children, so please keep this in mind when deciding if this setup is right for you.


The Opistognathus aurifrons have excellent personalities. Photo by Steven Pro.

Deep Water Indonesia Display:
Picture black sand and starkly colored large polyp stony corals underneath VHO lighting so that every bit of those corals fluorescence an almost unnatural color. The contrast one would obtain by using black sand with the large polyp stonies would create something reminiscence of a hippie, day glow poster, but would be both natural and realistic. Again, because of the almost gaudy colors of the corals, I would tone things down a bit with my choice of fish. Orange Lined Cardinalfish would be nice. But, for a change of pace, try a breeding colony of Fuzzy Dwarf Lionfish; perhaps some with hints of yellow, others with a little red, and of course one or two common tan-brown ones to illustrate the differences.

Tank of the Month Honoree’s:
It is also worth noting some of the previous Tank of the Month honorees. There have been a handful of displays that I can recall months, even years later that I found interesting for one reason or another. Flame Angel’s 120 gallon display was intriguing because of its unusual rockwork design and nice ensemble of inhabitants. Also, Mucho Reef’s tank was great because it demonstrated the beauty of a tank that did not house the prototypical ‘reef’ tank residents. It is also a good example to show beginning aquarists because of its likely lower initial and ongoing costs due to the modest amount of light required and lack of a calcium reactor or any other high-tech gizmo’s common to ‘SPS’ style aquariums.

Conclusions:
As I started off with in the beginning, it is not my purpose to convince everyone to setup one of the above displays. I merely want to encourage others to think outside of the box when it comes to how we aquascape and stock what is inside our little glass boxes. My fear is that too often the Tank of the Month on the various message boards or books such as Michael Paletta’s “Ultimate Marine Aquariums” are not merely demonstrating what can be done, but are encouraging replication, stagnation, and even stifling creativity. We can all build a pile of rocks with little corals stuck all over with little to no regard for what naturally occurs together. I would hope one day that there would be enough different displays out there that Tank of the Month would evolve to become a celebration of the diversity of reef keeping, inspiring us all to come up with new and interesting exhibitions. Now come on people, show me what you can do.

Suggested Reading:
Borneman, Eric. 2002. “Do You Know Where Your Corals Are Coming From?” Advanced Aquarist’s Online Magazine, March 2002. http://www.advancedaquarist.com/issues/mar2002/feature.htm

Calfo, Anthony. 2004. “Mangroves for the Marine Aquarium.” Reefkeeping Online Magazine, December 2004. http://reefkeeping.com/issues/2004-12/ac/feature/index.htm

Knop, Daniel. 2002. “Mangroves in Reef Aquaria.” Advanced Aquarist’s Online Magazine, April 2002. http://www.advancedaquarist.com/issues/apr2002/feature.htm

Sprung, Julian. 1999. A Guide to the Ecology and Care of Mangroves. Two Little Fishies, Inc. Coconut Grove, Florida. http://www.twolittlefishies.com/images/mangrove_manual.pdf

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Reeflections:
Incredibly Simple By: Iwan Lässer



Tank Introduction:
First, I would like to thank the Reefland community and Reef Hobbyist Online for honoring my system. Since I was a little boy I was fascinated by the life found on coral reefs. I have always observed aquatic life whenever I had the opportunity. To increase my ability to view aquatic life, I began to care for fresh water aquaria. Later in life I learned to dive and was able to experience the beauty of the oceans very closely. Because Switzerland isn't really located by the sea, I have tried to fetch the sea and bring it to Switzerland with my reef aquarium. From that grew my first step towards a saltwater aquarium.


Tank Details:
- Tank Size:
220 Gallon Aquarium


- Lighting:
Pure T5!!
2x54 Watt ATI Aquablue Special
2x54 Watt ATI Blue Plus
4x80 Watt ATI Aquablue Special
4x80 Watt ATI Blue Plus
For a total of 856 Watts. The lamps are changed every 6-8 months.



- Water Changes:
10% weekly changes with Reverse Osmosis water.

- Technical Equipment:
Skimmer: 1 Aquamedic Turbofloater, 1 no-name product (self-made) (Yes, I use 2 skimmers)
Flow pumps: Tunze Streams
Ozone: None
UV: None


- Calcium Management:
Calcium reactor (Korallin)
Balling method
The consumption of calcium is about 40 mg/liters daily

- Filtration:
I prefer to limit the amount of technical solutions and focus on biological filtration methods:
Live rock
DSB (100% Livesand)

- Current Water Parameters:
Temperature: 78 degrees F +/- 1.0
Salinity: 35ppt
pH: low 7.90 high 8.3
No3: undetectable
No2: undetectable
NH4: undetectable
Po4: undetectable
Si3 : undetectable
Ca: 420ppm
Alk: 7-9 DKH
Mg: 1300ppm
Redox: 400-450


- Additions:
Daily:
Phytoplankton (DT's)
ZEOstart2 (Korallenzucht)
Amino acids (Korallenzucht)
Coral Vitalizer (Korallenzucht)
Potassium (Korallenzucht)
Trace elements (element mix/strontium mix/iodine mix of QFI)

Weekly:
Amino acids/vitamins (Prodibio)

Bi-Weekly:
Bacteria (Prodibio)
Bacteria food (Prodibio)


Tank Inhabitants:
- Corals:
99% of the corals in this tank are SPS and LPS corals, 54 in all. Most of the corals in the tank started as frags, many from local reefers. When I first started in the hobby I have cared for soft corals. As time passed, however, I have replaced these with stoney corals. When I first started with stoney corals I was a little sceptical; I doubted whether I was able to keep stoney corals successfully. My passion was soon clear: Stoney corals in all colors and forms. I love their growth forms and the variety of their colors.



- Fish:
I try to reconstruct a natural coral-reef in my small tank. So of course fish and invertebrates are also included. My fish population: 2 Zebrasoma flavescens
1 Zebrasoma veliferum
20 Pseudanthias squamipinnis
11 Chromis virdis
3 Amphiprion ocellaris
2 Oxycirrhites typus
2 Synchiropus splendidus
2 Labroides dimidiatus
1 Salarias fasciatus
1 Gobiodon okinawae
2 Gobiodon histrio

- Inverts:
30 Hermit crabs
5 Tridacna squamosa
4 Mesipilia globulus
8 Lysmata amboinensis
2 Stenopus hispidus



Advice For Others:
In my opinion the most important ingredients for successfully keeping sensitive sea animals are:
Committ the time, much time and watch the animals closely.
Changes to the system must always be done slowly. Fast changes usually have negative impacts.
Carry out five measures after each change as two changes are parallel!

Don't overlook the fact that most of the available animals and decorations (LR) are taken from the oceans.

As a diver in tropical waters I enjoy swimming in untouched coral-reefs, full of great and small life. The ability to do this in an incomparable system is very important to me.

As a diver there is an unwritten law: "Grasp nothing, do not carry anything forward... Except photos and memories." The thought to put animals from this singular habitat into an artificial biotope seems grotesque.

The uniqueness of the habitat "coral reef" is dependent on every resident. Every organism is a small, important part in the success of this wonderful world.

It is necessary to understand and be conscience of these.


I try to offer my animals an adequate and natural habitat.
If possible, I always give after-cultivations and coral fragments the advantage.
My topmost aim is keeping corals and fishes and not have to replace them. Unfortunately, there are reef keepers who replace the fishes and corals once in a while. Simply, unsuitable conditions and a lack of experience/interests are the reasons for it. I personally disassociate myself with those that do not care. The preservation of the natural coral-reefs isn't only a thing for the governments, everybody can and should make their own contributions.

You can learn more about my reef on my home page: www.hausriff.ch

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