the digestion of sewage sludge containing various concentrations of solids
TRANSCRIPT
The Digestion of Sewage Sludge Containing Various Concentrations of SolidsAuthor(s): C. E. KeeferSource: Sewage Works Journal, Vol. 19, No. 1 (Jan., 1947), pp. 39-42Published by: Water Environment FederationStable URL: http://www.jstor.org/stable/25030401 .
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THE DIGESTION OF SEWAGE SLUDGE CONTAINING VARIOUS CONCENTRATIONS OF SOLIDS
By C. E. Keefeb
Bureau of Sewers, Baltimore, Md.
In the operation of sludge digestion tanks attempts are often made to con
centrate the inflowing raw solids. This
practice conserves sludge gas where
tanks are heated and makes available more space for the digestion of sewage solids. It is doubtful, however, if the
average solid content in digestion tanks
exceeds 10 per cent. In view of these facts it was considered desirable to in
vestigate the extent to which partially dewatered sludge digested. If the
moisture content of raw sludge were
reduced from 95 to 70 per cent, the
dewatered material would occupy one
sixth its original volume. Should this dewatered material digest rapidly, a
considerable saving in digester volume would result.
Experimental Procedure
Raw sludge was obtained from the
mechanically cleaned primary sedimen tation tanks at the Back River sewage
works, and digested material was
drawn from a small-scale laboratory di
gester. As indicated in Table I, the raw sludge contained 85.54 per cent
volatile matter and had a pH of 5.4, and the digested material contained 57.08 per cent volatile matter and had a pH of 7.5.
The two materials were mixed in the ratio of two parts by weight of raw
volatile solids to one part by weight of
digested volatile material. The mix ture was divided into five equal por
tions, each weighing 20.42 lb. To each of four of the portions, 225 ml. of a 10 per cent ferric chloride solution was added to coagulate the solids. Three of the portions were then dewatered on a
B?chner funnel.
These sludges, Nos. 1, 2, and 3
(Table II) contained the following moistures: 67.53, 74.99, and 85.08 per
cent, respectively. The above-men
tioned volume of ferric chloride was also added to sludge No. 4, one of the con
trols, which was not dewatered. Sludge No. 5, to which ferric chloride was not added and which was not dewatered, also served as a control. Lime was added to each of the mixtures to raise the pH to 6.7. Each mixture was then
placed in a 5-gal. carboy and incubated at 37? C. The volumes and the analy ses of the gas produced were deter
mined at regular intervals. The gas was passed through calcium chloride so that any moisture entrained therein could be caught and subsequently
weighed. At the end of the experiment the volatile and the solid contents of the sludges were determined.
Discussion of Results
Sludge No. 1, the moisture content of which was 67.53 per cent at the
beginning of the experiment, digested less than any of the other materials.
During the 73-day digestion period the volatile solids on the dry basis were reduced from 72.10 to 65.82 per cent. The loss in weight of volatile solids amounted to 64.9 grams, or 29.9 per
TABLE I.?Analyses of Raw and Digested Sludges Used in Experiment
Material Quan
tity Used
(lb.)
Dry Solids
(%)
Volatile Matter,
Dry Basis
(%)
pH
Raw sludge.
Digested sludge...
12.42
8.00
4.93
5.73
85.54
57.08
5.4
7.5
39
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40 SEWAGE WORKS JOURNAL January, 1947
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cent of the original raw volatile solids. The gas produced amounted to 223.9 ml. per gram of fresh volatile solids and weighed 61.1 grams.
Sludge No. 2, which had a moisture content of 74.99 per cent, digested quite
well. The volatile solids were reduced from 71.57 to 58.16 per cent, with a loss in weight of 132.2 grams. This
sludge produced 616.6 ml. of gas per gram of fresh volatile solids, which amount was greater than that from any of the other materials except sludge
No. 5.
Sludge No. 3, the moisture content of which was 85.08 per cent, lost 165.3
grams of volatile solids with a reduc tion of 72.7 per cent of the raw volatile solids. This reduction was accom
panied by an unusually low gas pro duction of 10.12 ml. per gram of fresh volatile solids. On the other hand, there was a gain of 156 grams in the moisture
content, indicating a considerable
liquefaction of solids.
Sludge No. 4 contained 94.73 per cent moisture at the beginning of the
experiment. The loss in volatile solids amounted to 162.5 grams. This loss
was accompanied by a production of 564.8 ml. of gas per gram of fresh volatile solids; this gas weighed 140.9
grams. There was also an increase of
35 grams in the moisture content, which indicated some liquefaction of solids.
Sludge No. 5, the only one to which ferric chloride was not added con tained 94.82 per cent moisture. This
sludge produced 756.9 ml. of gas per gram of fresh volatile solids. The gas
weighed 183.6 grams; the correspond ing loss in volatile matter was 176.3
grams.
The experiments indicate the possi bility of digesting raw sludge that has been dewatered and properly seeded. This method of treatment as compared with the more usual one of digesting sludge prior to dewatering presents certain disadvantages. A larger vacu
um filter installation would be required, as more material would be handled
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Vol. 19, No. 1 DIGESTION OF SEWAGE SLUDGE 41
FIGURE 1.?Total gas production from sludge containing various quantities of water.
and the cake output per unit area of
filter would be less. Moreover, more
coagulant would be needed. On the
other hand, there would be a great re
duction in digestion space. Eeducing the moisture content of sludge from
95 to 75 per cent, for example, de creases it to one-fifth its original volume.
A material reduction in the amount
of gas to heat the sludge would also
result. Getting the thickened sludge into and out of digestion tanks would
present new problems. At the present time most sludge pumps handle ma
terials containing 90 per cent or more
of moisture. There are pumps, how
ever, such as those used to pump con
crete, that can handle much more concentrated materials. New ways of re
moving the thickened sludge from di
gestion tanks would have to be devised.
Digesting sludge after it had been fil
tered would in all probability solve
both the scum problem in digesters and the problem of disposal of supernatant
liquor.
It is a long step from experimenting with small quantities of sludge in
bottles and investigating the problem in a full-size plant. The results are of
sufficient interest, however, to warrant a continued study of the problem on a
larger scale.
Conclusions
The following conclusions may be drawn from the results obtained :
1. Gas production was less from
sludges to which ferric chloride was
added. 2. Reducing the moisture content of
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42 SEWAGE WORKS JOURNAL January, 1947
sludge to 67.5 per cent materially re
tarded digestion. 3. There was a gradual increase in
the digestibility of the sludge as its moisture was increased from 67.5 to
85.1 per cent.
4. The sludge containing 85.1 per cent moisture produced practically no
gas. There was, however, considerable
liquefaction of the solids. There was a
loss of volatile solids of 165.3 grams and a corresponding increase in mois ture content of 156 grams.
5. The sludge containing 74.99 per cent moisture produced 8.4 per cent
more gas per gram of fresh volatile solids than the sludge containing 94.73
per cent moisture. The loss of volatile solids in the latter sludge was greater,
however, as about 10 per cent of the material liquefied.
6. The most complete digestion oc
curred in sludge No. 5.
These experiments indicate that sew
age sludge digests over a considerable
range of moistures. Although ferric chloride inhibited digestion slightly, the effect was not great. There was considerable digestion when the mois ture content was 75.0 per cent. Re
ducing the moisture to 67.5 per cent
materially retarded digestion. The Back River sewage works is
under the general supervision of Na than L. Smith, Chief Engineer of the
Department of Public Works, and
George E. Finck, Sewerage Engineer.
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