I am sorry, but you guys are not understanding the process. So let's try this.
If you read what Dr. Hovanec writes you will see that he considers having substrate in a new tank being cycled matters as the bacteria colonize it to the extent there is sufficient oxygen. Dr. H. instructs folks doing a cycle to be sure you have some form of substrate on the the bottom of a tank. Here is exactly what he says here
https://www.drtimsaquatics.com/resources/library/quick-guide-to-fishless-cycling-with-one-and-only/
Now, you may want to argue with me, but arguing with the scientist who identified a lot of the bacteria in tanks and has his information published in peer reviewed journals, you will lose the argument every time.
I have done a lot ofcycling and I have used Dr, Tim's One and Only a number of times over the years. (I have never used Safe Start). If you have used One and Only you should have learned a few things. The first is we are instructed to shake the bottle before adding the contents to a tank. The rreason is simple. The bacteria are microscopic and need to be attached to solid particles. These particles are very tiny. And they will sink to the bottom of the bottle and dhaking gets them back into solution. You can clearly see that they are there because you see a white cloud in the water which dissipates as it spreads out to all the places in a tank it will end up. This is the particulate matter to which he bacteria is attached.
But before going one it is important to understand something that becomes easily confusing and that is the term substrate. For the purpose of thos thread substrate refers to the gravel or sand etc. on the bottom of out tanks. But there are two more use of the term as well which are relelvant. The particle to which the bacteria attach are als called substrate and in this case has a different meaning. A piece of gravel or a grain of sand are things we see with out baked eye. But what comes out of bottled bacteria or the sludge we rinse from out filter media or suck out of whatever we have on the bottom of a tank is also called substrate. There is clearly a differenece netween some we can see v.s. something we ned a microscope to view.
The above two uses of the term substrate are not difficult to undestand. The problem is in the third use of the term substrtae in connection with the bacteria or Archaea that actually convert ammonia and nitrite. The ammonia and nitrite are also called substrate. But in this case it refers to what the bacteria use. And the use of the term substrate here refers to what concentration of ammonia or nitrite a specific strain of bacteria need to thrive. And this is what actually determine which starin we have in our tanks.
The term most often seen is substrate affinity. This refers not to particles but to the concentration of ammonia/nitrite on which any given strain can thrive. The term used is substrate affinity. Basically, what is being measured is how much ammonia or nitrite a given strain of bacteria or Archaea needs to thrive. The higher the affinitity, the lower the concentration needed is. So a good example here is the difference between Nitrobacter and Nitrospira. The first thrives in waste water treatment while the second thrives in our aquarums. The nitrospira have a higher affinity which means they thrive at lower concentrations.
So what we have to grasp is that the term substrate has 3 different meanings depending upon the context in which the term is being used. And this will circle us back to the brown sludge we see coming out when we rinse out our filter media or we vacuum the substrate on the bottom of our tank (unless we go bare bottom). This is the bacteria attached to particles. This brown sludge may also be called slime. So let us consider what Dr. Stephan Tanner tells up on this subject.
I would urge everyone to read this article on the Swiss Tropical site:
Aquarium Biofiltration . I understand that Dr. Tanner sells Poret foam (among other things, and this is a business which make money for him. But it is also important to know that he is a cancer researcher by profession. He makes money selling Poret. So please put the economic side of things aside for a moment and coinsider the science he explains in terms of using the Poret foam as one's biomedia.
Also,
I know the above is the case as I use Mattenfilters. The water in these tanks is the clearest I have. I do not even consider nitrate in those tanks as I have had the mattenfilters going for years. I know I have denitrification established.
Btw, I have the research papers bookmarked that explain how chloramine doesn't kill the bacteria but puts them to "sleep." The presence of ammonia then wakes them back up. Chlorine can kill the bacteria ina biofilm. But the bio-film protects the bacteria etc. to some extent. research shows that it takes chlorine about 24 hours to penetrate a biofilm completely. The amount of chlorine in our tap water is not great. Smaller concentration of chlorine do not last long enough to do serious damage. It takes a higher concentration of it to wipe out the bacteria.
Lee WH, Wahman DG, Bishop PL, Pressman JG. Free chlorine and monochloramine application to nitrifying biofilm: comparison of biofilm penetration, activity, and viability. Environ Sci Technol. 2011 Feb 15;45(4):1412-9. doi: 10.1021/es1035305. Epub 2011 Jan 12. PMID: 21226531.
Abstract
Biofilm in drinking water systems is undesirable. Free chlorine and monochloramine are commonly used as secondary drinking water disinfectants, but monochloramine is perceived to penetrate biofilm better than free chlorine. However, this hypothesis remains unconfirmed by direct biofilm monochloramine measurement. This study compared free chlorine and monochloramine biofilm penetration into an undefined mixed-culture nitrifying biofilm by use of microelectrodes and assessed the subsequent effect on biofilm activity and viability by use of dissolved oxygen (DO) microelectrodes and confocal laser scanning microscopy (CLSM) with LIVE/DEAD BacLight. For equivalent chlorine concentrations, monochloramine initially penetrated biofilm 170 times faster than free chlorine, and even after subsequent application to a monochloramine penetrated biofilm, free chlorine penetration was limited. DO profiles paralleled monochloramine profiles, providing evidence that either the biofilm was inactivated with monochloramine's penetration or its persistence reduced available substrate (free ammonia). While this research clearly demonstrated monochloramine's greater penetration, this penetration did not necessarily translate to immediate viability loss. Even though free chlorine's penetration was limited compared to that of monochloramine, it more effectively (on a cell membrane integrity basis) inactivated microorganisms near the biofilm surface. Limited free chlorine penetration has implications when converting to free chlorine in full-scale chloraminated systems in response to nitrification episodes.
Similar articles
Effect of free ammonia concentration on monochloramine penetration within a nitrifying biofilm and its effect on activity, viability, and recovery.
Pressman JG, Lee WH, Bishop PL, Wahman DG. Water Res. 2012 Mar 1;46(3):882-94. doi: 10.1016/j.watres.2011.11.071. Epub 2011 Dec 7. PMID: 22192761
Three-Dimensional Free Chlorine and Monochloramine Biofilm Penetration: Correlating Penetration with Biofilm Activity and Viability. Lee WH, Pressman JG, Wahman DG. Environ Sci Technol. 2018 Feb 20;52(4):1889-1898. doi: 10.1021/acs.est.7b05215. Epub 2018 Feb 8. PMID: 29376332 Free PMC article.
So, when we clean our media too often or clean too much of the substrate on the bottom of a tank too thoroughly, we may be doing more harm than good. Any of the gunk down in the substrate began as stuff on the surface of that substrte. If we remove some of the gunk on the surface of the substrate, it means there will be less of it breaking down and going deeper.
But, we also know that that when we clean reasonably, that we will not degrade our bio-filtration to the extanet it will create ammonia or nitrite issues. So the trick here is not to over due the cleaning of out substrate and media.
I never vacuum the substrate in my planted tanks unless I am removing a pile of uneaten food. ANd I have some planted tanks for many years that have never been vacuumed. I will conclude this here with one last bit of information. There are some plants in our tanks that actually encourage nitrifying babteria to be ablle to colomize what is usually an aqnaerobic part of a somewhat deep substrtae. The plans will transport oxygen down to their roots where they release it. This creates and aerobic zone in the middle of an anaerobic substarte. The result is nitrification.
Petersen, N.R. and Jensen, K., 1997. Nitrification and denitrification in the rhizosphere of the aquatic macrophyte Lobelia dortmanna L.
Limnology and Oceanography,
42(3), pp.529-537.
Abstract
Nitrogen and O2 transformations were studied in sediments covered by
Lobelia dortmanna L.; a combination of 15N isotope pairing and microsensor (O2, NO3−, and NH4+) techniques were used. Transformation rates and microprofiles were compared with data obtained in bare sediments. The two types of sediment were incubated in doublecompartment chambers connected to a continuous flow-through system.
The presence of
L. dortmanna profoundly influenced both the nitrification-denitrification activity and porewater profiles of O2, NO3−, and NH4+ within the sediment. The rate of coupled nitrification-denitrification was greater than sixfold higher in
L. dortmnanna-vegetated sediment than in bare sediment throughout the light–dark cycle. Illumination of the
Lobelia sediment reduced denitrification activity by ∼30%. In contrast, this process was unaffected by light–dark shifts in the bare sediment. Oxygen microprofiles showed that O2 was released from the
L. dortmanna roots to the surrounding sediment both during illumination and in darkness. This release of O2 expanded the oxic sediment volume and stimulated nitrification, shown by the high concentrations of NO3− (∼30 µM) that accumulated within the rhizosphere. Both 15N2 isotope and microsensor data showed that the root-associated nitrification site was surrounded by two sites of denitrification above and below, and this led to a more efficient coupling between nitrification and denitrification in the
Lobelia sediment than in the bare sediment.
from
https://aslopubs.onlinelibrary.wiley.com/doi/epdf/10.4319/lo.1997.42.3.0529