In general, I would not add excess solids of anything since trace elements can bind to the solid surfaces. It happens, for example, to copper with excess calcium hydroxide:
This article expands on the basis of the claim that limewater may be able to deliver lower quantities of some metals compared to calcium reactors and it also provides some experimental data that demonstrates this claim.
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Precipitation of Copper from Limewater: Experimental Results
The fact that a number of aquarists have reported blue precipitates in their limewater residue suggested to me that there may be something more to this story. Sure, they could have been using especially impure lime, or had especially impure source water. Nevertheless, it was easy enough for me to run some experiments to see what was really happening. In all of the experiments to follow, I monitored copper concentrations using a modern analytical lab technique: Inductively Coupled Plasma (ICP) using atomic emission detection. I used two different emission peaks (324.754 and 327.395 nm).
To start,
I made a solution of 1.0 ppm copper as copper sulfate (ACS reagent grade) in deionized water (700 mL). It had no detectable color by eye. When this sample was analyzed by ICP, it had an easily quantified set of emission peaks for copper, and this emission intensity was used as a standard (1.0 ppm).
To this solution
I added 2.4 grams of calcium hydroxide (ACS Reagent Grade) and stirred it on a magnetic stirrer for 1 hour. This amount of lime is far more than necessary to saturate this solution (which would take just over 1 g of Ca(OH)2). The solution then settled for 24 hours, and a slightly cloudy sample was removed. This sample was analyzed and found to contain 340 ppb copper before filtration and 133 ppb copper after filtration through a 0.45mm polypropylene syringe filter. The value of 133 ppm copper represents a droop of 87% in the copper concentration.
The original solution was allowed to continue settling for 6 days total, and another sample was withdrawn. This sample was found to contain 160 ppm copper before filtration and 125 ppm copper after filtration through a 0.45mm polypropylene syringe filter.
Additional calcium hydroxide was added to the original solution (2 g/600 mL), the solution was stirred for an hour, and the solution was allowed to settle for 24 hours. This sample was found to contain 33 ppb copper before filtration and 25 ppb copper after filtration through a 0.45mm polypropylene syringe filter. The value of 25 ppb copper represents a drop of 80% from the 125 ppm copper solution just before this second lime addition, and a total drop of 97.5% from the initial copper sulfate solution.
As a control, I tested a solution of calcium hydroxide (2 g/50 mL of deionized water) without any copper sulfate added. In analyzing this sample, I could detect no real signal from copper, either before or after filtering. This result implies that the “natural” copper concentration in these samples is below about 10 ppb.
Precipitation of Copper from Limewater: Interpretation
Clearly, the first addition of excess calcium hydroxide dropped the copper concentration from 1 ppm to 133 ppb even though 133 ppb is below the solubility of copper at ANY pH according to literature values.17 Likewise, the addition of a second portion of solid calcium hydroxide to the solution, which should not have impacted the pH at all as there was already substantial excess solid calcium hydroxide before the second addition of solid lime, dropped the concentration from 125 ppb to 25 ppb.
The first result might be explained simply by errors in the literature values or on my part. The Dyer et al article shows that these calculations can be off and should be used as a guide rather than a strict value.17 But the second drop is really only consistent with an entirely different phenomenon: that of surface absorption or coprecipitation. The binding of metals to the surface of inorganic materials, such as calcium carbonate, iron oxide or hydroxide, alumina, and clay (e.g., kaolin) is well known.33-44 In this case, both calcium carbonate and calcium hydroxide are present in these solutions, and these minerals provide surfaces to which copper and other metals may absorb strongly. Additionally, as CaCO3 is precipitated in such mixtures, copper and other metals are likely to get incorporated into the growing crystals, further lowering the solution metal concentration.
Consequently, the purification of limewater may not be entirely driven by pH, but also by the presence of “clean” mineral surfaces to which impurities such as copper will adhere.