Plenums and the wasting "option"

Iââ"šÂ¬Ã¢"žÂ¢ve been following this thread closely because I am a fan of sand in display tanks. I simply like the way sand looks, and the animals contained within fascinate me.

Thus far, the topic has focused on:


1) The drawing of water from the plenum through the use of suction by means of a siphon, where the replacement water is pulled through the sand bed.

2) To what detriment, if any, the flow of oxygenated water through the bed has on the obligate and/or facultative anaerobic bacteria within the bed.

3) Determining the correct flow through the bed, so as to disturb the aerobic -> anoxic -> anaerobic layers as minimally as possible.

There are a couple of issues regarding the mechanics of this method that I would like to discuss. I am wondering...

1) What about the potential for detrital accumulation within the plenum? Using low to moderate flow (suction, as described) to flush the plenum would still leave a significant amount detritus behind unless it was suspended before flushing. If Bomber's theory about "bacterial turgor" is correct (I think it is), the sandbed should shed a fantastic amount of detritus if given a way to do so.

2) Does anyone think that the small holes in the manifold may tend to clog up over time, rendering the apparatus useless?

3) Why it is necessary or desirable to draw water through the sandbed when all we are attempting to do is flush the water from the plenum? Two riser tubes could be used- one for discharge and one for pushing the water through the plenum with a small pump- this action would suspend the detritus and allow it to be discharged with the wastewater as it flows up the exhaust riser (which would be still be aided by gravity siphon). Since the flow would take the path of least resistance, its intrusion upwards and into the sandbed would be minimal. A larger volume of water could be forced through the plenum, ensuring a more efficent flush.
 
Well, I can answer for #2. I think the idea is to cover the grid with layers of screening to keep the grid holes themselves clear.

#3 is really interesting, but I don't know how it wouldn't take the sandbed with it. That sounds like the perfect setup for erosion, but I guess the screen would keep the sand in place. I would think friction and erosion would move the sand bed around, though.

Regarding #1. Hmm, interesting but I would think that anything small enough to get through the screen is small enough to get pulled through the siphon.

Interesting thoughts. I would love to see #3 in action and/or hear how it's working for you.

Andy
 
originally posted by "Umm, fish?"

I think the idea is to cover the grid with layers of screening to keep the grid holes themselves clear.


I was thinking more along the lines of the grid holes becoming coated in bacterial film, very fine particulate matter, and bacterial flock that the sand bed is likely to shed over time rather than the larger particles of substrate which would be held back by a properly designed screen. I am not convinced this would actually happen, but the possibility is worth consideration- any repair/removal of the manifold would require a complete break down of the tank.

originally posted by "Umm, fish?"

#3 is really interesting, but I don't know how it wouldn't take the sandbed with it.


I think that choosing the right substrate particle size and screening material would prevent erosion of the sand bed. I'm not talking about using a large pump- just something to create enough turbulence to get the detritus into suspension. I'm having a hard time visualizing all those small holes drawing enough suction to pull all the mulm off the bottom without some turbulence to aid the process.

I've never run BB, so I can't speak from experience here, but it's my understanding that it takes both high flow rate and turbulence to keep detritus suspended long enough to get it through the overflow and to the skimmer. Without proper water movement, detritus tends to collect in the areas with less flow. I keep visualizing it doing the same in the calm, still area of the plenum. All those 90ââ"šÂ¬Ã¢"žÂ¢ bends and tiny holes are going to drastically reduce the flow rate of any siphon, thus reducing its ability to pull detritus off the bottom. Drawing water through the sand bed may reduce the flow rate even further. Getting the detritus suspended within the plenum would greatly facilitate its removal- even when using a very low flow rate.

I think plenum wasting is a based on sound theory and could be proven to be an effective way to maintain a DSB indefinitely. The caveat is that, once in place, the manifold canââ"šÂ¬Ã¢"žÂ¢t be maintained or tweaked or repaired. Let me state for the record- I am no expert when it comes to fluid dynamics, and I donââ"šÂ¬Ã¢"žÂ¢t know how the fluid in the plenum or the crud that accumulates there will actually behave in practice. Iââ"šÂ¬Ã¢"žÂ¢m just thinking out load to help design an effective mechanism.
 
No, no. Please don't misunderstand. We all appreciate any input. Heck, this is all new territory, so the more brains the better.

I think Barry's idea is have the manifold holes small enough and the siphon pipe large enough so that the siphon is just a little starved. That way the suction at each hole is pretty strong. Maybe strong enough to unplug itself? I don't know.

The fiberglass screening I have has holes smaller that the holes in my manifold. I'm hoping that anything that can get through the screening can be sucked right out of the system.

What's the worst-case scenario, though? The manifold plugs up so that it isn't useful? At that point I cap the sucker so it's just a deep sandbed. And if my sandbed craps out 4-5 years down the line I remove the manifold along with the sandbed and try to figure out something new. So all I've lost is my time making the sucker and the money spent on PVC.

Thanks again for your input Steve!

Andy
 
Steve,

Very Interesting Post.
If I understand you correctly, you propose a small pump on the inflow riser tube. When the pump is not running, which is almost always, that would not be much different than an open tube from the plenum into the aquarium. On the other hand, if you plan on this pump to be running 24 -- 7, every time it stops for whatever reasons nasty plenum water would be introduced into the aquarium. Or am I missing something?

By the way, I don't know anything about bombers theory of bacterial turgor. Is there any chance you could break it down to its most basic form and put it in a nutshell for me?


Joe
 
sradmin said:
Iââ"šÂ¬Ã¢"žÂ¢ve been following this thread closely because I am a fan of sand in display tanks. I simply like the way sand looks, and the animals contained within fascinate me.

Thanks for getting on board with us Steve: As UmmFish states, this is new territory, and all are welcome. We are heartened by the look of sand and gravel, and the creatures that dwell therein, especially me.

I will restate my own personal viewpoint, that the reason for the "substrate" is for the creatures that require it primarily, and that nutrient and chemical processing is an important, BUT SECONDARY, function of the substrate.

I find your proposal interesting and potentially valuable, and I will get into that a little later, but let's address some of your questions and concerns first, so we have a better foundation on which to proceed.

Nice summary by the way, on our efforts thus far.

My ramblings here, will also be a summary, and not always specifically in response to your post, so take some "extra ramblings", with "a grain of salt".

There are a couple of issues regarding the mechanics of this method that I would like to discuss. I am wondering...

1) What about the potential for detrital accumulation within the plenum? Using low to moderate flow (suction, as described) to flush the plenum would still leave a significant amount detritus behind unless it was suspended before flushing. If Bomber's theory about "bacterial turgor" is correct (I think it is), the sandbed should shed a fantastic amount of detritus if given a way to do so.

I am not convinced about all of this detritus entering the "plenum". We need to define "detritus". If any "solids" are entering the plenum area, this "entrance" needs also to be described.

Sand beds have been run by countless individuals, and probably countless specifications of "sandbed". Anthony Calfo likes 6" or better of "oolitic" ( sugar fine ) sand only, and keeps a "light" bioload. He also has broken down many tanks of his, and has never seen any "black yuck", and further states that all sand below about 1" is as pristine as the "day it was put in". He also utilizes protien skimming, refugiums, etc. and we all know that there is no "magic bullet" for reef systems.

Others use a "mix" of anywhere from oolitic to 4mm particle sizes, in "god knows" what combinations, and every depth from 1" to 12" ( although 4 to 6" is common ).

Bio-loads and feeding regimens can wreac havoc on anything, including my belly, but there is a tendency to blame all failures that occur in "sandbeds", on the sandbed. BIG MISTAKE!!!!!!!!

( A ) Sandbeds do not need to suffer from "sandstorm" problems that are "supposedly" associated with "high flow". A little 1 to 2mm substrate at 1/2" deep, and and judicious use of flow nozzles accomplishes this ( no dummies allowed in "advanced concepts" ).

( B ) Sandbeds have been "touted" as "set it and forget it" and many people have taken this to heart, to the detriment of the hobby. ( The BB boyz just "love it" )

( C ) Sand critters are terribly important to a "sandbed", and anyone who has algae or "cyano" on the surface of their substrate does not have enough "critters" IMHO.

( D ) Rock work should be supported in a number of small contact points, to keep the majority of the rock work above the substrate, in order to help promote "detritus free" conditions at the surface of the substrate.

SO, with good ( high ) flow, "appropriate sand critters", and "rock support", detritus should not occur on or in the sandbed. I do not have algae or detritus anywhere in my tank, and I am going to keep it that way.

I layed out, earlier in this thread a substrate layering "model", that is intended to address all of the concerns that you are having, and I have this layering model existing in my current tank. This layering model includes 2 to 3" of "oolitic" part way down in the substrate, and is intended to accomplish most of the denitrification in the substrate.

It also serves to keep anything of significant size from "fouling" the lower layers of larger gravel, which act as a "gravel membrane" ( or screen ) for inhibiting "particle migration" of the smaller "upper layers" of substrate.

I don't believe that any "detritus" ( which still needs defining ) can penetrate "oolitic sand". Anything that can will be quite small and will easily exit through the plenums "feeder holes".


I must point out here again, that I am in the "frequent wasting camp", and that this approach helps to eliminate some of these concerns. while I will gladly help anyone with any version that they wish to use, my explanations in this post are primarily geared toward "frequent wasting", and its advantages.


2) Does anyone think that the small holes in the manifold may tend to clog up over time, rendering the apparatus useless?

No. If you are not convinced yet, look back in the thread for the "substrate layering model", and in my gallery, for the "Particle Migration" graphic. If this does not seem self explanatory, let me know, and I will explain.

3) Why it is necessary or desirable to draw water through the sandbed when all we are attempting to do is flush the water from the plenum?

Why would you say that "we" are only trying to "flush water from the plenum"? A "wasting plenum" has little in common with a "standard plenum", and I do not support the use of standard plenums, because they can only accomodate "light bio-loads" per Bob Goemans, and this is not where I am headed.

Two riser tubes could be used- one for discharge and one for pushing the water through the plenum with a small pump- this action would suspend the detritus and allow it to be discharged with the wastewater as it flows up the exhaust riser (which would be still be aided by gravity siphon). Since the flow would take the path of least resistance, its intrusion upwards and into the sandbed would be minimal. A larger volume of water could be forced through the plenum, ensuring a more efficent flush.

Ahh, and now we get to the "good part". Firstly, I don't believe that this is necessary, because as stated above, I don't understand how this detritus gets into the plenum to begin with.

We may need to investigate some of this "bacterial tugor" that has been mentioned. I don't think much of most of Bomber's information, because he throws "it" around like "chucking spears". Not that much of it isn't valid, but his "context" sucks IMHO. Bomber does not discuss anything, he "debates", which is worthless in my opinion.

Still, if it was to remain percieved, that "gook" might accumulate in the "plenum", it would be valuable to eliminate it. I believe that by "wasting" frequently, no such build up will occur, however, for the sake of "discussion", let's solve this "requirement".

Whether "we" are in the "frequent", or "occasional" wasting "camps", the problem, if it were to exist, would not be inside the plumbing ( feeder tubes ), but in the plenum space itself. This being the case, flushing water through the plumbing is not going to solve the problem.

If there is anything in the "plenum space" that you wish to "flush", then you need to flush the plenum space, not the "plumbing". One easy way to accomplish this would be to incorporate a canister filter, with input at at one end of the "plenum space", and output at the other. The media in the filter should not need to be anything other than floss or your favorite foam or "pad". This would move any "mulm", or whatever into the canister for "capture", without affecting the "vertical travel" of water in the substrate.

I am sure much more can be done with this, and everyones input is appreciated by all of us.

Thanks for the input Steve, It's all good!

Happy Thanksgiving everyone, I am going to try to fire up the "outside plumbing" that SaltyJoe initiated, along with the "below tank level "high flow option", that was described recently. It's only Saturday, I might still have a chance yet this weekend.

Let's make this thing work, I know it will! > barryhc :beachbum:
 
Hi All,

Ok, let me try to sum up the goals of the people who posted this thread to make sure I have understood everything going on until now.

1) people want sand in their main display tank for asthetic reasons

2) those that are proposing a deep sand bed want to maintain critters that may require several inches of sand that can turn into a "sink" for nutrients

3) in order to prevent the DSB "sink" from filling with wastes and leaching back into the system, people are trying to incorporate a wasting plenum to constantly or periodically draw the sludge water from the bottom of the sandbed. For the "lazy" people this will act as daily small water changes *wink*.


I'm hoping you guys get some good results but I like to play devil's advocate and try and poke holes in theories to see if people have answers or theories to cover my concerns.

Question 1)
Is there any chance of solids precipitating out of solution in your matrix of PVC under the sand bed? Possibly blocking the holes or eventually constricting the pipes themselves?

There are threads on RC where people end up having to do vinegar baths etc to clean up calcium deposits on pumps etc.

I think this would be more a concern with people doing less frequent and larger pulls as they would pull water into the pipes that has much different chemistry than the water would end up with after sitting in the pipes for days or weeks. Could drops in pH as the water is processed anaerobically in the tubes cause anything in solution to precipitate out?

2) particle migration of very small particles into the plenum space or even into the PVC pipe matrix

I understand the geometry involved in the layering scheme, but this assumes uniform diameter on the particles, and even packing.
It also assumes that the particles are not moving and no channeling occurs.

Even with the assumptions above, any particle smaller than the interstitial (sp) space is still going to move through the sand bed and accumulate in the plenum area.

When I lived in Tucson, I tore up some carpeting when replacing it with tile, and I was amazed at the amount of chalk fine dirt/dust that had made it under the carpet. What shocked me even more was the amount that had somehow even found its way under the foam padding under the carpet which was glued to the slab foundation. The foam was glued around the edges, and all throughout the floor space, the joint between pieces of foam had been taped, yet there was still almost a quarter inch of dust UNDER the foam.

What I am saying is you are probably going to end up with small particles accumulating in the plenum area. Maybe they will work their way around the edges, maybe they will be able to just work their way completely through the sandbed with the water you are pulling through during wasting, but smaller particles are going to come down into the plenum area. Once down there unless they are kept in suspension and pulled out during the wasting, they will end up settling. Once they settle, they are going to provide a nice surface area for biofilms or whatever so that they will not dislodge easily during the next draw. If this stuff accumulates to a depth to block the holes in your PVC matrix, you won't get even drawing, or may just end up with some PVC in the bottom of your sandbed.

Didn't ldrhawke originally have a way to backflush the wasting mechanism? Was there a conclusion in this thread on how that was going to be accomplished, or are you of the opinion that it won't be necessary so have simplified the system by going without a backflush mechanism?

3) compaction of your sandbed
By having smaller particle media above larger media, and drawing from the bottom of the tank, you are going to end up sucking small particles into the spaces between bigger particles, and basically compact your sandbed.

Since I don't expect this to happen evenly, this is going to be a source of uneven flow through the sand bed and channelling.

I also see this as being a possible problem with your stretching of the zones in the sandbed. If you compact the sandbed, and have layers where sand critters are not moving the sand and disturbing any compacted areas, this will end up stretching the anaerobic area and shrinking the area breaking down ammonia and nitrite/nitrate.

Basically if you compact the sandbed this will prevent the natural downward migration of water from the water column into the sandbed and will end up with the oxygen being consumed in the sandbed quickly and not replaced leading to the anaerobic area being predominant. (I believe this is why Dr. Ron states it is necessary to have such a diverse group of animals to basically stir the sand and help the migration of oxygen and other chemicals into and out of the sandbed)

Now if you are doing constant pulling of water into the sandbed, this may not be as much of an issue (maybe another reason to do more frequent smaller wastings than longer duration less frequent ones).

One thing that you may want to test to see if your bed is compacting is this:

If you are always pulling a consistent amount with the U tube idea (which I like) and it is gravity fed, keeping track of how long it takes for the U tube to fill with your wasting water and seeing if this increases over time will tell you if your flow is being constricted. Just something maybe to keep an eye out for as something easily measured outside that can indicate a problem developing inside.

If your times for wasting the same amount is consistent, that would be good, if they are increasing you are probably getting constricted flow in the sandbed because of compaction or filling of spaces by detritus (i.e. your sandbed is not able to process as much waste as you are pulling into the sandbed), if the times fluctuate where some days they are slower and then faster and this never stabilizes, that would indicate to me channeling is happening, and that as a channel develops the flush time decreases.

4) Even with wasting from the bottom of the sandbed, I still think you are only buying time before you have to rip out the sandbed because of detritus and phosphate accumulation.

The only way to prevent accumulation in a closed system is to balance intake and output, which I think is almost impossible for reefkeepers because there are too many variables.

How do you calculate the input of phosphates by feeding, dosing of chemicals, make up water, etc?

Assuming you can accurately account for the amount of phosphates (or any other thing you are trying to keep in check for that matter) that is being fed into the system, can you really accurately reflect the amount of phosphate being extracted from the system? Are the tests only for phosphate in solution? What about phosphate bound in the bacteria that you are going to be sucking out by the millions? Also, how do you account for any phosphate bound in the growth of inhabitants of the reef system?

If you know a way to accurately track inputs and outputs that would be a first step in developing a steady state system where you can have it go on forever. I don't see that being feasible for a reef system though.

5) What are the feelings of people on here about the need to periodically "cook" live rocks because they act as a sink for P and other nasties that eventually lead to algae outbreaks etc?

Is live rock refurbishing accepted as necessary reef maintenance?

If so, I think you would have to accept that sandbed maintenance is necessary to refurbish the substrate.

6) I didn't see anybody suggesting to incorporate vascular marine plants that would feed from the stuff accumulating in the sandbed as a means for extending the life of the sandbed.

Using macroalgae to strip P from the water column for export is good means of slowing any buildup in the substrate, and if you are going for a DSB in display tank, why not incorporate some manatee grass or whatever in the sandy area to try and suck it out of the sandbed the old fashioned way by growing plants you can harvest that absorb through roots for export.

***
Personally I like the idea of wasting from the bottom of the tank, if this is the dirtiest location where wastes accumulate then it only makes sense to pull water out from this location for Water Changes etc.

It is similar in how people use skimmers to concentrate waste for removal from the water column, or concentrating waste by growing macro algae for manual export.

Is there any cheap reliable way to test for heavy metals in the plenum wasting you are going to do? I'd be interested in seeing if there is an accumulation of any heavy metals deep in the sandbed. If you don't introduce heavy metals into the system, I don't see how they could be accumulating though. The only inputs with any heavy metals would be your water supply, your salt mix, medications or dosing, and food.

If you limit the input of heavy metals, you won't have them accumulating. If you grow your own food for your reef from the wastes most people just throw away, you would slow down or prevent accumulation of heavy metals. Instead of draining the plenum waste to a drain after testing, why not drain it to a separate tank specifically for growing macro algae/pods that does not cycle water back to your main tank? That way you can harvest food algae like gracilaria or ulva for fishes that you may have in your reef etc.

It would also give you a test system to see if the waste from the plenum is really something that needs to be removed from the reef system. As you continue to feed the waste from the plenum to this separate test tank, which you shouldn't feed at all, you can monitor for the health of the tank inhabitants. Do you see this waste from the plenum eventually killing off the tank due to accumulating heavy metals? If the waste from the plenum actually results in a healthy system where there is plenty of macro processing the phosphate etc, and then everything feeding off the algae like pods etc and making a little food chain, you could then simply drain your plenum wasting to the sump or refugium and really set up a constant flow scheme, more like a large trickle filter where the goal then isn't to export from the bottom of the sand bed in the display tank, but to just keep anything from accumulating there.

Just my 2 cents, or $1.50 considering how long the above is.

The long term results will be very interesting, so take good notes along the way :)
 
Good discussion- thanks for the replies. After browsing the thread again, I found the answers to some of my questions. Itââ"šÂ¬Ã¢"žÂ¢s easy to miss things when you are eager to get to the end of a long thread. Hahaha, maybe like not listening when youââ"šÂ¬Ã¢"žÂ¢re eager to speakââ"šÂ¬Ã‚¦ :)


originally posted by salty joe

By the way, I don't know anything about bombers theory of bacterial turgor. Is there any chance you could break it down to its most basic form and put it in a nutshell for me?


As I understand it, heââ"šÂ¬Ã¢"žÂ¢s using it to describe the pressure gradient created when bacteria multiply in certain marine environments:

originally posted by Bomber (various threads)

A few years ago we needed a word to describe bacterial pressure/migration/bacterial transportation of nutrients in marine sediments. Turgor was the word that was adapted as a catch all word to describe that.

In rock, bacterial turgor - two bacteria take up more room than one - and that growth and pressure migrate it out of rock.

Rocks try to reach a equilibrium with nutrients in the surrounding water - they can't pull a higher gradient of nutrients out of the water or fabricate a higher concentration. When you cook rocks, keeping them in cleaner water forces that bacteria to release chemically bound nutrients. Bacterial turgor (pressure) forces those nutrients out of the rocks.

Sandbeds store those same nutrients reaching a much higher concentration. There is no where for bacterial turgor to push but up. Marine sediments do not shed particulate bacterial detritus until they are full.

Bacterial turgor is referring to the pressure created by bacteria as they feed and multiply. To understand that you have to understand how bacteria feed. They don't have mouths, so through a process of different enzymes and acids they make their food liquid. The front line bacteria liquefying, creating a soup, and to a certain extent passing it on to the bacteria behind them that are also feeding on this soup.
In rock they have something solid to push against and the only way out is - out of the rock. If you've ever cycled rock in a barebottom tank, that's the huge quantity of bacterial detritus you see produced by the rock as it cleans up. As the bacteria run out of food, detritus production will slow.
In sand beds, bacteria have the bottom of the tank, the side walls to push against, and the only way this detritus can go is up. This detritus is heavier than water and is also composed of very fine particulates and a disportionate amount of phosphorous compounds, not only making the sand bed finer - restricting water movement - but the phosphorous compounds skew the fauna associated with the sand bed. Making the bed skewed to bacterial driven.
This particulate material - most importantly - drives the bed to being anaerobic dominated.

It's the movement of the bottom anaerobic area toward the surface that's referred to as the bed filling up.



Barryhc,


I am in total agreement with you about the reason for having sand in the display. I like the critters that live in it and I like the way it looks. Although nutrient cycling abilities are secondary, I think it would be remiss to not take advantage of, and even help facilitate them.

"Detritus": In the context of marine aquariums, I define it as any excess, unwanted organic material anywhere in the tank. Uneaten food, bacterial flock, poop (whether it be from fish, coral, pod, or worm), dead bacteria, scales from a fish, you name it.

I would define ââ"šÂ¬Ã…"œentranceââ"šÂ¬Ã‚, as it applies to our plenum, as any opening through which water can pass to enter the space of the plenum.

Re-reading the thread, I see now why you suggest drawing water through the bedââ"šÂ¬Ã‚¦ It is to purge the lower layer of sand. A question that comes to mind is what is actually being purged in the wasting method? One page one you said:

The area ( or depth zone ) that we waste needs to contain the nutrients and compounds that we are interested in wasting, agreed?

Are we talking about wasting the nutrients and compounds bound in the biomass of bacteria?

Wasting a plenum can "export" some of this Phosphate, sulfur, and metals "sink" can't it? Maybe even avoid a "crash"?

Export it in what form? Once again, is it bound up in bacteria?

As I have mentioned, re-reading the thread helped me to sort through many of my own questions. I had originally perceived plenum wasting to be a method of flushing the sand bed of everything it tends to collect over time, including that elusive term, ââ"šÂ¬Ã…"œdetritusââ"šÂ¬Ã‚, which is why I was concerned about getting it into suspension before flushing. However, you have chosen to layer your substrate in such a way as to (hopefully) prevent detritus from entering the plenum at all- although this makes sense to me theoretically, I am still having a hard time visualizing it happening in practice. Short of using some sort of semi-permeable membrane and sealing it to the sides of the aquarium, I think millions upon millions of substrate particles are going to naturally, eventually overcome any attempt to stop ââ"šÂ¬Ã…"œparticle migrationââ"šÂ¬Ã‚. I also wonder what affect ââ"šÂ¬Ã…"œbacterial turgorââ"šÂ¬Ã‚ will have on forcing detritus (as bacterial flock) into the lower bed and plenum.

It is because of your layering of the substrate that I worry about something else: Compaction. Complete and total detritus removal is difficult in a BB tank. It will be even more so in a tank with sand. You can be obssessive about removing it and still not get it all. That material has to go somewhere- eventually it will work its way down into even the finest substrate. Finer substrates are more apt to cause channeling, especially if they become clogged with organic material. Would it perhaps, be more efficient to use a courser grade of substrate without layering to actually encourage organic particles to migrate into the lower area of the bed? Even into the plenum to be removed when wasting? I was under the impression that in order for a sand bed to denitrify, it had to partially fill because P is limiting in sediments. I didnââ"šÂ¬Ã¢"žÂ¢t think denitrifciation could happen without it.

Please understand that I am not being critical- I am only trying to understand the mechanics of this method because I think it's a great idead and wI would like to use it when I set up a future tank.
 
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Wow... what a read that was.

I am so interested in this design. I am thinking of doing this with an old 10 gal under my soon to be new 90 gal. I am contemplating BB in the display, with the overflows running to the 10 gal filled 2/3 with sand then into a sepearte fuge. I would drill the bottom of the 10 for the plenum drain.

I have a few questions about the membrane though. My thought was to build the manifold, then set eggcrate on top, then place the membrane on the eggcrate. What product are you guys using for the membrane? How do you attach the membrane to the sides of the aquarium so that you ensure sand can't escape around the edges into the plenum?

second question... since my setup is a remote DSB, do I need to light it sepeartely, or will the biodiversity of pods, worm, stars and such thrive without light?

Thanks,
-J
 
ddoering, welcome to our "adventure". Aren't we such brave "souls" here after all, "flying in the face" of conventional systems like DSB, and BB. About he only thing that I have found so far in reefkeeping, that isn't controversial, is adding salt to the water!

You have offered us here, a beautifully concise post, and I appreciate it highly. I am going to respond to Steve here, which covers about 90% of your questions, and if you would do me the favor, please review the response and "nitpick" it for questions that you have asked that do not get covered.

This is an ongoing concern, and any questions left unanswered or not understood deserve further discussion.

sradmin said:
Barryhc,
I am in total agreement with you about the reason for having sand in the display. I like the critters that live in it and I like the way it looks. Although nutrient cycling abilities are secondary, I think it would be remiss to not take advantage of, and even help facilitate them.

ABSOLUTELY!!!!

"Detritus": In the context of marine aquariums, I define it as any excess, unwanted organic material anywhere in the tank. Uneaten food, bacterial flock, poop (whether it be from fish, coral, pod, or worm), dead bacteria, scales from a fish, you name it.

I love this definition! "Detritus" is organic, and not chemical, or mineral.

I would define ââ"šÂ¬Ã…"œentranceââ"šÂ¬Ã‚, as it applies to our plenum, as any opening through which water can pass to enter the space of the plenum.

This is also quite good, but there may be many. The first, is the entrance to the surface of the substrate. "Entry" here is the most important point of control. I believe that 1-2mm gravel here, will reject the vast majority of detritus from entry into the substrate, and still eliminate the vast majority of "sand storm" problems. This will allow "high flow" in general, which I am very much in favor of.

However, as I state continuously, The substrate function is firstly for the animals that require it, including those that maintain it. So "we" need subastate at the surface, and for some distance "down" that is conducive to "pearly jaw fish", "sand goby and shrimp" symbiosis", and of course, also to the "critters" that do most of the "clean-up work", as well as some "food critters".

Now that is one hell of a specification for the upper substrate, and everything is "a question of balance", so we have to come with a best case scenario.

So for the first 1/2" say, we need to reject detritus, and for some additional depth ( say 2-3" ) allow gobies and shrimp something to dig, play and feed in. I think that food production is probably best accomplished in a refugium or similar, and we may only need a couple of "cryptic" areas with rubble or "the like", for "pods" and food to hide in until the mandirins etc. "find it", and not dwell on trying to supply a "food factory" in the display tank substrate.

I can't prove it yet, but I think that "oolitic" sand at the surface, is a detriment to the system for several reasons, and that this fine sand at the surface, contributes a lot to the "clumping" that is often times reported in DSB's. I have seen pictures of it, and it has often been within the first 1" of substrate.

I don't know much yet about the best, or acceptable particle size for gobies and shrimp. I've been looking and asking, but . . . .

I think that "sand burrowing critters" in general should be a big positive here, including "cukes" and "sifting stars" etc., to help reduce any "clumping" and channeling problems.

I think were getting to about 3-5" depth here. I am calling it about 3" of the top, for the time being. Let's beat up on this some, I don't really know. What we do here will certianly have a major impact on the bacterial colonies for both the frequent and infrequent types of wasting. The layering for the two types may very well not be the same, although if we keep the overall bed depth deep enough, the bacteria may figure it all out for themselves to some degree.

The specific intervals for Wasting Frequency, are yet to be tested or proven, and that will take a while. Testing of parameters, at various depths will be highly conducive to a better understanding of the chemical and bacterial processes that occur, and how to modify the wasting schedule and volume.

A second "entry" will be at the boundary of the the first and second layers of substrate, especially if the second layer is finer than the first surface layer, which is what I am currently proposing. This is where "fines" will tend to accumulate, and is the reason for having the "burrowing critters", to keep this boundary "broken up".

Below this level, fines will not be able to accumulate at layer boundaries, so long as the remaining layers, are progressively coarser, as I propose. The largest particles that the plenum plumbing will have to deal with, will be those that can "pass thru" the "finest second layer". Actually this will be true at the beginning, and years later, as substrate melting occurs ( if it does )will become the size of particles that can pass thru the later just below the finest layer.

So, this layer, below the finest layer, will determine the largest particles that can make it to the "plenum space", and the "plumbing". I have specified 2-4mm particles here, and when properly "graded" before use, this will restrict particles to smaller than .5mm ( .020" ). I realize this has been quite difficult for many people to "swallow", but I assure you, it is the case. Membranes or small screens are the worst thing you can put in here. They will clog-up for sure!!!!! Particles smaller than .5 mm will not have problems exiting thru 1.5 mm holes in the plumbing.







Re-reading the thread, I see now why you suggest drawing water through the bedââ"šÂ¬Ã‚¦ It is to purge the lower layer of sand.

This is quite true, but should also improve both nitrification and denitrification, if done properly done. Denitrification will occur at a greater depth than with DSB.

Are we talking about wasting the nutrients and compounds bound in the biomass of bacteria?.

Yes, to some degree, the compounds would be those that are precipitating in the lowest layers of coarse gravel, and are so fine as to cause no difficulty in exiting thru the holes in the plumbing.

I also wonder what affect ââ"šÂ¬Ã…"œbacterial turgorââ"šÂ¬Ã‚ will have on forcing detritus (as bacterial flock) into the lower bed and plenum.

"Turgor" will cause "diffusion" in both directions", hopefully to "our" advantage.




Would it perhaps, be more efficient to use a courser grade of substrate without layering to actually encourage organic particles to migrate into the lower area of the bed? Even into the plenum to be removed when wasting?.

I don't think so, I prefer to keep the detritus out of the substrate to begin with, using particle size, high flow, elevated rockwork, and "critters". Larger particle size throughout the substrate will cause a severe restriction to the total surface area for bacterial colonization. A whole "crew" of people at ReefFrontiers.com tried promoting this concept for 18 mos. and never really got anywhere with it.

I was under the impression that in order for a sand bed to denitrify, it had to partially fill because P is limiting in sediments. I didnââ"šÂ¬Ã¢"žÂ¢t think denitrifciation could happen without it..

I don't believe that extra high levels of P are necessary for denitrification. I believe that they only happen to coexist in standard DSB's.

Let's beat around on this a lot, it is actually where I was at when I started the thread, and it deserves a lot of research and discussion.

Thanks all! > Your turn, ddoering. > barryhc :beachbum:
 
For people that are planning a void space like a plenum to draw from, an easy way to stir up any small particles into solution before doing your draw would be to include a magnet scraper under the plenum membrane if your tank stand supports the tank from the edges.

That way you could just use the magnet algae scraper on the bottom of the tank to stir things into solution to get sucked out during the draw.

This won't work for people with the big pipe matrix on the bottom, or for those people with substrate all the way to the bottom, but may be something to think about for those wanting the empty plenum to draw from.

If your tank stand doesn't give you access to the bottom glass, you could still rig something up with a magnet at the bottom of the front and back glass and sweeping back and forth with two magnet scrapers with a stick or something connecting them to stir the bottom up.

Just a possible idea to try and make it so you can get those little particles into solution in a void plenum without having to put a power head down there, or having to try and flush with a backflush pump.

Cheers,
Doug
 
Hi, Barry

O.k.-

You have completely lost me with regard to your layering. Could you describe it using a similar representaion of what I have typed below? Starting with the uppermost layer and in descending order, each typed line representing approximately one inch of substrate:

2-4mm
2-4mm
******
1-2mm
******
3-5mm
3-5mm
3-5mm

You are not using any sort sort of screen between the layers- the only screen you are using is directly above the plenum and has

as originally posted by barryhc

about 1.5mm ( or 1/16" ) holes in it

I think I am missing something... Please be patient, this is a long thread!
 
Steve,
Thanks for the reply concerning bacterial turgor, although I think displacement would be a much better choice of words. When I think of turgor, I think of wilted plants. Thanks again for gathering all that information. I really do appreciate it.
Joe
 
Joe,

No problem. Displacement does sound like a better word since that's what's actually happening. I don't know why he chose to redefine the word "turgor". The standard definition (dictionary.com):

turÃ"šÃ‚·gor (tûrgr, -gôr)
n.

1) The state of being turgid.

2) The normal fullness or tension produced by the fluid content of blood vessels, capillaries, and cells.
 
Hi Barry,

Ok, just to keep me on the same page.

Aerobic: requires oxygen
NH3 to NO2-
Ammonia to Nitrite

NO2- to NO3-
Nitrite to Nitrate

Anaerobic: requires no oxygen
NO3- to N2
Nitrate to Nitrogen gas

Every step consumes P as it is a building block in most proteins/cells.

Most P in aquariums is bound in organic molecules and is not measured with common P tests.

P that is measurable is inorganic orthophosphate.

Organic phosphate is usually removed/exported from aquarium by skimming before it can break down into orthophosphate.

Phosphates are also exported as solids in macroalgae.

Since most phosphate in a reef system is in the form of organic phosphate that is not detected by test kits, how useful will it be to measure the phosphate content of plenum waste water?

http://www.advancedaquarist.com/issues/sept2002/chem.htm

This article states that phosphate is bound in the reef system by adhering to live rock and sand by bonding to calcium carbonate:
***
phosphate can precipitate onto the surface of calcium carbonate, such as onto live rock and sand. The absorption of phosphate from seawater onto aragonite is pH dependent, with the maximum binding taking place around pH 8.4 and with less binding at lower and higher pH values. If the calcium carbonate crystal is static (not growing), then this process is reversible, and the aragonite can act as a reservoir for phosphate. This reservoir can make it difficult to completely remove excess phosphate from a tank that has experienced very high phosphate levels, and may permit algae to continue to thrive despite cutting off all external phosphate sources. In such cases, removal of the substrate may even be required.
***
What I see as the importance of the above is that in practical terms most sand beds and live rock will store P at normal reef pH, that will be released as P is consumed/exported or if pH fluctuates. Now if the pH remains constant, the P that is released from the stockpile of P in rocks and substrate will not increase the measurable levels of P in the water column, but it will be buffered so that even if you cut your P inputs, or increase your P outputs the concentration of orthophosphate will not drop as quickly as expected until you leach all the stored P out that has accumulated in the rocks and substrate.
.
As long as you recognize the need to start drawing out more P than you are putting in, then you shouldn't see any further accumulation and as long as P is not in dangerous amounts to prevent calcification of corals or be toxic, then I'd be comfortable just letting things work themselves out slowly over time.
.
The above may explain why some people experience a DSB "leaching" P back into the system though. Since phosphate does not bond to the rock/ substrate as well at lower pH, and since pH drops as you go down into the sandbed to the anaerobic areas, this is going to result in more P in solution than in the water column above, but this may just be a result of making the measurements at different pH for the water column
vs. the bottom of the bed and not be a sign of P accumulating in the bottom of the sandbed.
.
So another thing to make sure that is being tested in the plenum wasting system is to measure pH of the draw off water along with the P, and then see if this correlates to the same level of P in the water column once adjusted for pH difference.
.
This also makes me wonder if you are just shooting yourself in the foot by drawing oxygenated water down into a deep sandbed in order to extend the aerobic area.
.
Doing this is going to make the gradient of pH change different in the sandbed along with the oxygen gradient, extending the aerobic surface area deeper into the bed and creating a greater surface area for P to bind to in the higher pH range. Wouldn't this simply make the "sink" for P larger creating a larger resevoir for P.
(Now this may be a reason FOR using a silica based substrate instead of aragonite/southdown type sand since the P wouldn't bind to it since it isn't calcium carbonate).
.
The P would leach back into the water column if the anaerobic layer approached the surface of the substrate, which would be seen with compacted sandbeds, or sandbeds that do not have enough infauna shifting the sediments and clumping occurs. The P would then diffuse up into the water column (moving from an area of greater concentration to lower concentration) where it would quickly be utilized by algae. This would probably be seen as surface algaes on the sandbed.


In conclusion from the above, there are several things I would want to see tested by people setting up these systems. (If I can use you as guinea pigs since you are testing this setup anyway :)
.
From my first post, I would test the time it takes to make your standard sized draw and see if it is increasing the longer the system is running, as this would be a way to judge compaction or restriction of flow in the sandbed.
.
From my second post, if people who have set up a system with the plenum space can visually inspect the bottom of their tank glass to see if small particles are accumulating in the bottom of the tank that would help to understand how effective layering is at restricting particle migration, or if bacterial processes are resulting in accumulation of solids in the plenum.
.
From this post, if you are testing the plenum or wasted water to measure levels of phosphate being removed, make sure to measure temp and pH of the wasted water to compare to the P level in the water column above the substrate to see if there is a true accumulation in the bed, or simply a higher level of measurable P due to lower pH and the phosphate not binding to the substrate as well at that pH.


Cheers,
Doug
 
Doug,
If the pH drops in the sand bed, and this forces phosphate into solution which can be drained and measured, wouldn't this be mission accomplished as far as phosphate is concerned?

Joe
 
sradmin said:
O.k.-

You have completely lost me with regard to your layering.

I think I am missing something... Please be patient, this is a long thread!

I have explained this many times before, but this is a long thread, so I will try once again. Please keep in mind that plenum wasting is quite experimental at this point, and we are collectively developing an "EDUCATED ESTIMATE" as to the best initial approach for this.

This could be done a thousand different ways, 5 or 10 of them might work very well. One will for sure.

Substrates that are left relatively stagnant, as in occasional wasting, will function differently than those which are wasted frequently. For occasional wasting, the substrate will likely be the same or similar to DSB, whatever someone believes that to be. I find that it varies a great deal.

For Frequent Wasting, I will Identify 5 areas or levels that differ in their functionality. Much of this occurs to some degree, in a "standard" DSB. These grain sizes should be carefully graded by the aquarist to avoid excessive fines at start-up, as these fines could unduly compromise the initial setup. We will start at the "top":

Layer #1 > The surface ( entry #1 )
. . . The first layer at the surface needs to accomplish three things.

> ( A ) Reject the entry of detritus into the substrate > smaller is better

> ( B ) Avoid "sand storms" from "high flow" > larger is better

> ( C ) Allow the entry of sand sifting and burrowing animals ( gobies etc. ) and maintainence critters ( stars, cukes, worms etc. ) > H-m-m-m what size, I'm not sure.

My current estimate for this first layer is 1-2mm particles at about 1/2" depth. This layer along with crabs, snails, and brittle stars, will effectively keep the vast majority of detritus out of the substrate, and will also avoid any "sand storms". I have this layer in my current tank, and it performs as stated. No vacuuming, no stirring, no siphoning, and at 9 mos., no algae and no visible detritus.

Layer #2 > This layer is for the animals who want to live in it, especially those who like to live in "burrows" ( gobies etc. ) and also for the "sifting creatures" like cukes, worms, and stars. My guess is that this layer may be about the same as the first at 1-2mm, or maybe a bit smaller and probably 2-3" deep ( call it 2 1/2" ), I'm trying to find information on this, and have not gotten much help with this question. Maybe someone will dig into this question and find us some good information. Please?

Layer #3 > This layer is for DENITRIFICATION and is considered to be very functional with "oolitic" sand, about 3" deep ( .7-1.7mm might be an option ). I will have a "CRITTER SCREEN" about 1/2 way down in this layer. 6mm openings in this screen would be good. The idea is to stop large critters from messing with the substrate below, and otherwise have NO EFFECT on the substrate.

LEVEL #4 > This could be one or more layers, and it's function is to be a "GRAVEL MEMBRANE" that protects the plenum from clogging. These must be PROGRESSIVELY LARGER, to avoid any clogging.

This is where most people seem to lose it. Anything that "screens", will hold larger particles above it, and allow smaller particles to pass through. Simple geometry shows us that any size of gravel or particle will restrict the passage of smaller particles down to 1/6 ( or 16% ) of the size of the "screening gravel". Smaller particles will pass through. We want the smallest particles to pass through. This allows them to exit the system thru the plenum plumbing and therefore avoid any clogging of the plenum.
Actually, Layer #3 above is the beginning of this "gravel membrane", and is where any clogging or channeling of the substrate will occur. This is why we allow the critters access to the first half of it's depth, to keep things "stirred-up". The second half of layer #3 remains undistuurbed for reliable denitrification purposes. Denitrification has been shown to occur at depths as little as 12mm deep ( 1/2" ) in oolitic sand, and has often been shown to exist for only a thickness of as little as .5 mm ( .020" ) IF LEFT UNDISTURBED BY CREATURES.

Now we have to go progressively larger to promote free flow in the plenum space, while inhibiting migration of the fine substrate into the plenum area. If we have used "oolitic sand" in Layer #3 above ( I remember .2-.4mm here I believe ), then a 1/2" thick layer of .7 to 1.7mm gravel will restrict it's migration downward.
A 1/2" thick layer of 2-4mm gravel below this will effectively restrict the above layers downward migration. A 1/2" layer of 5mm below this will allow screen at the bottom with 3mm openings.

So, this fourth LEVEL, which is comprised of 1 1/2" of Layer #3, 1/2" - Layer #4, 1/2" - Layer #5, 1/2" - Layer #6, totals a depth of 3". This is a 3" thick gravel membrane, mostly about 2" of the "oolitic" layer is really doing the membrane work, but this 2" thick "gravel membrane" is going to hold up about 30 times as long as some .015" ( 1/64" ) thick plastic screen or the like.

The fifth LEVEL or area, is of course, the plenum itself. It is comprised of PVC tubing to accomodate the feeder holes, etc., and then the eggcrate above it, and the screen on top of the eggcrate to keep the coarse gravel out of the plenum space.

If a person was not trying to have an option for "flushing" in the plenum space, much like doug suggested, then you could probably just start with some 8-12mm gravel directly on the plenum plumbing, and then "grade down" with 5mm, then 2-4mm, as you go up as previously described, and eliminate the eggcrate and screen altogether. ( THIS WOULD NOT ELIMINATE the CRITTER SCREEN described above however. )


While this may turn out not to be the "very best" substrate "model" in the end, it is the best that I have been able to conjure up so far, and is of course, open for discussion.

OK, from the top down"

> 1/2" of 1-2mm
> 2 1/2" of .7-1.7mm ( maybe just more 1-2mm )
> 1 1/2" of "oolitic" sand ( .2-.4mm I think )
CRITTER SCREEN
> 1 1/2" of "oolitic sand"
> 1/2" of .7-1.7mm
> 1/2" of 2-4mm
> 1/2' of 5mm

This totals up to 7 1/2" of substrate, and the plenum uses up 1 1/2" itself. That is a grand total of 9" of the bottom of your tank being used here. This could probably be pinched down by an inch or two if need be.

I happen to be going for a 29" tall tank, instead of the 24" that has become more popular recently for lighting and "area to volume" considerations, so for me, with an extra 5" of tank, and an extra 5" of height used for "the plenum" ( VS the 4" of depth "common" for DSB's ), it's no problem for me. Other's may cry bloody murder about the "depth", but those "old, tall, out of date" tanks are going pretty cheap these days! :idea:

I hope that clears up the "layering scheme" somewhat. It will not be anything very similar to a DSB, nor should it be, if it is being wasted frequently, and that is still where I am at.

>Thanks to all who are posting, It is exceedingly helpful!
> barryhc :beachbum:
 
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