IMO - it should but I still think this method just crash all others - humble as I amWhat puzzled me though (slightly tangential) is that fishless cycle does not call for addition of phosphate sources. Any thoughts?
Sincerely Lasse
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IMO - it should but I still think this method just crash all others - humble as I amWhat puzzled me though (slightly tangential) is that fishless cycle does not call for addition of phosphate sources. Any thoughts?
I seem to recall that bottled bacteria medium contains enough PO4 that a recommended dose is likely enough to meet the needs of the bacteria. @taricha will have some thoughts on this from his research on bottled bacteria.I
I would suppose having po4 slightly in excess can exclude it as the limiting reagent. It will also unlikely to interfere with ammonium oxidation. Make sense.
What puzzled me though (slightly tangential) is that fishless cycle does not call for addition of phosphate sources. Any thoughts?
I love this article. Anyone follow these directions?IMO - it should but I still think this method just crash all others - humble as I am
Sincerely Lasse
Yes - I think one of the problems with experiments using test tubes - is its hard to mimic the actual 'stuff' going on in our tanks.I love this article. Anyone follow these directions?
What puzzled me though (slightly tangential) is that fishless cycle does not call for addition of phosphate sources. Any thoughts?
True, there was some in Waste Away - just enough for a full dose to be +0.03 PO4 in a system. But not really significant for heterotrophs. Compared to Dan's nitrifying experiments, when I grew heterotrophs, they'd slurp down the PO4. In some cases, it looked like the amount of available PO4 in the fish food or whatever I fed them was the limiter for the maximum culture population size. By comparison, Dan's nitrifiers just didn't consume much or need much.I seem to recall that bottled bacteria medium contains enough PO4 that a recommended dose is likely enough to meet the needs of the bacteria. @taricha will have some thoughts on this from his research on bottled bacteria.
So wouldn't this suggest there is no significant increase in bacteria population?Seems pretty hard to Phosphate - limit nitrification.
I think it's more that you can nitrify a ton of ammonia with a small number of true nitrifiers. So it takes absurdly small amounts of PO4 to keep them happy and growing. You might even be able to double or quadruple the nitrifiers in an initial dose of biospira with barely detectable PO4.So wouldn't this suggest there is no significant increase in bacteria population?
Good points. Nitrifyers use ammonia oxidation as an energy source and grow slowly. This means nitrogen uptake with a small biomass production. This leads me to the unanswerable question, when I see an increase in ammonia oxidation, is the nitrifyer population growing or just breathing a bit faster?I think it's more that you can nitrify a ton of ammonia with a small number of true nitrifiers. So it takes absurdly small amounts of PO4 to keep them happy and growing. You might even be able to double or quadruple the nitrifiers in an initial dose of biospira with barely detectable PO4.
You'll need way more cells (and probably more P) to handle ammonia if you were talking about heterotrophs.
and is it actual 'nitriiers' or 'heterotrophs'. Heterotrophs far more likely. IMHOGood points. Nitrifyers use ammonia oxidation as an energy source and grow slowly. This means nitrogen uptake with a small biomass production. This leads me to the unanswerable question, when I see an increase in ammonia oxidation, is the nitrifyer population growing or just breathing a bit faster?
The autotrophe -> heterotrophe development make sense. If autotroph population were to increase, they will still need to take up phosphate from the environment, yes?When experimenting this way is in an early stages - in spite of to much P or not - as long as you not dose organic carbon - the heterotrophs will not grow. However - After a while when biofilm is too dense to allowing oxygen to penetrate deeper (hence not surviving autotrophs) the dead autothrops create the organic carbon and heterotrophs can grow. But in the start - nope - in this type of experiment at least
Sincerely Lasse
You can do a reversed experiment. In water with PO4 and NH3/NH4 - have enough of alkalinity (above 2-3 dkH) and nitrospira - just measure the ammonia and total N in the water over time. analyse the N speciesSo if we remove all phosphate from the water sample, as well as the biospira itself, we can perhaps know if the mechanism is by autotrophic growth, or just whatever existing autotroph doing the heavy lifting.
This sounds right.what i think you will seer is that in the first experiment - NH3/NH4 will disappear (as specie) rather fast but total nitogen in the water column will be near the same. In experiment 2 - NH3/NH4 will be - as a species - much longer time in the water column but total dissolved inorganic N will be lesser
This leads me to the unanswerable question, when I see an increase in ammonia oxidation, is the nitrifyer population growing or just breathing a bit faster?
Interesting data, I would like to draw some ideas from it.Here's one that looks fairly persuasive to me...
This was sand that was cycled with biospira, ramped the capacity way up, then left it "curing" (circulating in the dark without input) for a couple of months, the capacity for nitrification dropped considerably but did not disappear.
Then I pulled some of the sand, added it to tank water spiked with ~1ppm total ammonia-N.
The green is the ammonia, but look at the blue - NO2-N. It's remarkable how cleanly you can fit it to an exponential for ~3 days.
The exponential function for that fit is y = 0.0486*e^(.824*t) - 0.048
That rate constant implies a nitrite doubling time of 0.841 days = 20.2hrs.
It stops fitting at 3+ days because then NO2->NO3 becomes significant, and by day 3.5 there's significantly lower ammonia concentration left to process.
Note that the ammonia decrease is much less clean - no evidence of exponential population growth, because there are a bunch of ways to consume ammonia. The ammonia oxidizers weren't the only path. But they were the only path to NO2 production and that capacity expanded in exactly the relationship you would expect for population growth.
If you just want to see pretty exponential curves, start with a tiny population and track nitrite until the NO3 producers catch up.
Some species can indeed utilize a lot of ammonia (ammonium) in heterotrophic nitrification, true. Iirc it's also linked to their capability to perform aerobic denitrification.@Lasse - perhaps I'm hallucinating - but it is (was) my impression that various pseudomonas sp. can merely use ammonia without much - if any carbon. I have tried looking it up - but can't find it completely - but was curious about your thoughts.
Nice demonstration of the staying power of AOB’s. Low death rate I guess.Here's one that looks fairly persuasive to me...
This was sand that was cycled with biospira, ramped the capacity way up, then left it "curing" (circulating in the dark without input) for a couple of months, the capacity for nitrification dropped considerably but did not disappear.
Then I pulled some of the sand, added it to tank water spiked with ~1ppm total ammonia-N.
The green is the ammonia, but look at the blue - NO2-N. It's remarkable how cleanly you can fit it to an exponential for ~3 days.
The exponential function for that fit is y = 0.0486*e^(.824*t) - 0.048
That rate constant implies a nitrite doubling time of 0.841 days = 20.2hrs.
It stops fitting at 3+ days because then NO2->NO3 becomes significant, and by day 3.5 there's significantly lower ammonia concentration left to process.
Note that the ammonia decrease is much less clean - no evidence of exponential population growth, because there are a bunch of ways to consume ammonia. The ammonia oxidizers weren't the only path. But they were the only path to NO2 production and that capacity expanded in exactly the relationship you would expect for population growth.
If you just want to see pretty exponential curves, start with a tiny population and track nitrite until the NO3 producers catch up.