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Scale
Inhibiting Features of Solid Treatment Feed Products C20M-C and
C20-C
A Report to
Solid Concentrate Distributors
September
5, 2000
Jeff Derks
Buckman
Laboratories Incorporated
Introduction
United Supply Service, Incorporated employs
a unique process-water chemical delivery system. Chemical treatments
are deployed and installed as a solid. Dissolution into a system
takes place as water passes over the condensed product. A satisfactory
feed rate was initially established, but it is not known if a single
feedrate is economical for all water conditions.
This study was designed to optimize treatment dosages
inhibiting calcium carbonate scale. Two products C20M-C and C20-C,
supplied by the customer in final solid form, were evaluated in
three different stressed water chemistries.
Experimental
Procedures
Calcium carbonate inhibitor treatments were evaluated
in twelve separate Dynamic Hot Rod Scaling Reactors (Figure 1) using
synthetic make-up water. Each rod, or heat transfer site, is a 250W
120V stainless steel immersion heater placed at a specific depth
in a 1L reaction flask. The rods draw full current from a common
110V outlet. Water in each flask quickly boils at the center and
cools near the flask wall providing convection circulation.
Figure 1. Diagram of the Dynamic Hot Rod Scaling System
Calcium carbonate crystals form and adhere to the
rod and flask walls. Other CaCO3 crystals can free float
and settle at the bottom of the flask. Depending on a treatments
crystal modifying ability, more or less scale accumulates to the
bottom as conditioned sludge. Calcium can also remain
soluble in the system water.
Scale Distribution was determined by quantifying
the Ca2+ residing on the rod itself and on the flask
walls. Rod and bottle-bound CaCO3 were dissolved off
in 5% (v/v) nitric acid, collected, and analyzed for Ca2+
using Inductively Coupled Plasma (ICP) mineral detection.
Figures 1 and 2 show the actual 12-chamber rig and
the rod heat-transfer site as it accumulates scale.
Figure
1 12 Hot Rod Reaction Flasks
Figure
2 A Rod Scaling
Data
Twenty liters of synthetic water was made up to specified
hardness and alkalinity (Table 1) in DI water using ACS grade calcium
chloride dihydrate and sodium bicarbonate.
Table 1
Synthetic Water Targets
Condition
|
Units
|
Water A
|
Water B
|
Water C
|
|
Calcium Hardness
|
ppm as CaCO3
|
500
|
1200
|
1000
|
|
Total Alkalinity
|
ppm as CaCO3
|
200
|
400
|
1000
|
C20M-C and C20-C were dosed as product into each reaction
chamber at 10, 25, and 50ppm. Each dose was run in triplicate and
averaged to insure statistical validity. Results for relative scale
are recorded as milligrams of Ca2+ in tables 2-4.
Table 2 - Water A
Treatment
|
Dose (ppm)
|
Rod Scale (mg
Ca2+)
|
Bottle Scale (mg Ca2+)
|
Total Ca2+
(mg)
|
|
Control
|
--
|
15.64
|
1.78
|
17.42
|
| |
|
|
|
|
|
C20M-C
|
10
|
5.79
|
1.12
|
6.91
|
| |
25
|
4.45
|
0.25
|
4.70
|
| |
50
|
2.32
|
0.93
|
3.25
|
| |
|
|
|
|
|
C20-C
|
10
|
6.00
|
2.26
|
8.26
|
| |
25
|
3.00
|
0.22
|
3.22
|
| |
50
|
2.09
|
0.20
|
2.29
|
Table 3 - Water
B
Treatment
|
Dose (ppm)
|
Rod Scale (mg
Ca2+)
|
Bottle Scale (mg Ca2+)
|
Total Ca2+
(mg)
|
|
Control
|
--
|
31.67
|
16.98
|
48.65
|
| |
|
|
|
|
|
C20M-C
|
10
|
36.33
|
3.19
|
39.52
|
| |
25
|
26.33
|
7.00
|
33.33
|
| |
50
|
21.04
|
5.40
|
26.44
|
| |
|
|
|
|
|
C20-C
|
10
|
39.73
|
3.00
|
42.73
|
| |
25
|
26.53
|
9.32
|
35.85
|
| |
50
|
19.71
|
6.3
|
26.01
|
Table 4 - Water
C
Treatment
|
Dose (ppm)
|
Rod Scale (mg
Ca2+)
|
Bottle Scale (mg Ca2+)
|
Total Ca2+
(mg)
|
|
Control
|
--
|
186.5
|
9.23
|
195.73
|
| |
|
|
|
|
|
C20M-C
|
10
|
96.4
|
5.13
|
101.53
|
| |
25
|
78.87
|
10.02
|
88.89
|
| |
50
|
67.6
|
11.04
|
78.64
|
| |
|
|
|
|
|
C20-C
|
10
|
84.33
|
3.13
|
87.46
|
| |
25
|
71.87
|
10.72
|
82.59
|
| |
50
|
60.07
|
16.00
|
76.07
|
Summary
In all tests, regardless of water conditions, increasing
the chemical dose from 10ppm to 50ppm decreases the amount of calcium
on the rod and flask. Meaning that calcium carbonate scale is decreased.
Also, the data here does not support one product consistently working
better than the other under these specific conditions.
It is important to note that in each water condition
experiment, the amount of calcium scaled is relative to the initial
calcium in the synthetic water.
Water A
There is an 87% decrease in calcium scale from the
control to the 50ppm dose of C20-C. Compared to the 10ppm dose,
25ppm and 50ppm have approximately a 61% and 72% improvement respectively
(Graph 1).
Graph 1
Treatments at 10ppm have the highest calcium scale,
but are a 50% improvement over the non-treated control. 25 and 50ppm
treatments have similar performance effects on scale inhibition.
Water B
Higher hardness/mid-range alkalinity water conditions
alter the effectiveness of the treatments. Changes in product dosage
from 10 to 50ppm are less dramatic than in graph 1 (Graph 2).
Graph 2
There is only minimal scale control over the control
at 10ppm. Stepping up in dose to 25ppm improves scale inhibition;
however, the improvement does not compare to the lower hardness
waters found in Water A @ 25ppm. Treatment @ 50ppm provides the
most desirable scale control under these water conditions.
Water C
These water conditions are of the highest stress at
1000ppm calcium and 1000ppm alkalinity. Graph 3 indicates similar
performance between the three treatment levels. Each with approximately
50% or greater reduction in calcium carbonate scale.
The product formulations for C20M-C and C20-C were
not provided, but based on the amount of sludge accumulated at the
bottom of the Water C reaction flasks, one could predict that crystal
modifying agents are present.
Sludge accumulation without scaling is a typical response
in high-stress water when sludge-conditioning agents are being fed.
With combinations of the correct polymers, it does not require high
doses to modify crystal structure. Similar results have been demonstrated
using various Buckman polymers.
In high hardness and alkalinity situations such as
this, total calcium-based precipitation inhibition is not realistic
or economical. The goal is to condition and disperse scale so it
will not stick to heat transfer surfaces and be removed during blow-down.
Graph 3
Conclusions
Water A
500ppm calcium, 200ppm alkalinity
·
25ppm of either C20M-C
or C20-C product is sufficient to maintain scale control.
·
10ppm of C20M-C or
C20-C provides less desirable control, but still effective.
Water B 1200ppm calcium, 400ppm alkalinity
· 50ppm treatment level should
be the minimum dose for scale control under these conditions.
Water C 1000ppm calcium, 1000ppm alkalinity
· 10 and 25ppm doses are sufficient
to control scale under these conditions.
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