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Transactions of the American Society of Civil Engineers, vol. LXXII, June, 1911
Water Purification Plant, Washington, D. C. Results of Operation.
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Transactions of the American Society of Civil Engineers, vol. LXXII, June, 1911 Water Purification Plant, Washington, D. C. Results of Operation.

by American Society of Civil Engineers

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Plate 1: Washington Aqueduct, D. C. Filtration Plant Injector Sand-Handling System

AMERICAN SOCIETY OF CIVIL ENGINEERS

INSTITUTED 1852


TRANSACTIONS


Paper No. 1191


WATER PURIFICATION PLANT, WASHINGTON, D. C.
RESULTS OF OPERATION.1

By E. D. Hardy, M. Am. Soc. C. E.


With Discussion by Messrs. Allen Hazen, George A. Johnson,
Morris Knowles, George C. Whipple, F. F. Longley, and E. D. Hardy.


The Washington filtration plant has already been fully described.2 At the time that paper was written (November, 1906), the filtration plant had been in operation for only about 1 year. It has now been in continuous operation for 5 years, and many data on the cost, efficiency, and methods of operation, have accumulated in the various records and books which have been kept. It is thought that a brief review of the results, and a summary of the records in tabular form, will be of interest to the members of the Society, and it is also hoped that the discussion of this paper will bring out the comparative results of operation of other filter plants. As a matter of convenience, the following general description of the plant is given.

Description of the Filtration Plant.—The Washington filtration plant was completed and put in operation in October, 1905. It consists of a pumping station for raising the water from the McMillan Park Reservoir to the filter beds; 29 filters of the slow sand type, having an effective area of 1 acre each; the filtered-water reservoir, having a capacity of about 15,000,000 gal.; and the necessary piping and valves for carrying water, controlling rates of filtration, etc.

1 Presented at the meeting of February 15th, 1911.
2 "Works for the Purification of the Water Supply of Washington, D. C.," by Allen Hazen and E. D. Hardy, Members, Am. Soc. C. E., Transactions, Am. Soc. C. E., Vol. LVII, p. 307.

In the pumping station, there are three centrifugal pumps, which are directly connected to tandem compound engines; two sand‑washer pumps; three small electric generating sets for furnishing electric light; and four 200‑h.p., water-tube boilers.

Each of the centrifugal pumps has a nominal capacity of 40,000,000 gal. per day when pumping against a head of 21 ft., and each sand‑washer pump has a capacity of 2,500,000 gal. when pumping against a head of 250 ft. The electric light engines and generators supply the current for lighting the pumping station, the office and laboratory and other buildings, and also the courts and interior of the filter beds, and for operating a machine‑shop.

The filters and filtered‑water reservoir are built entirely of concrete masonry. The floors are of inverted groined arches on which rest the piers for supporting the groined arch vaulting. All this concrete work is similar to that in the Albany, Philadelphia, and Pittsburg filters.

The filters contain, on an average, 40 in. of filter sand and 12 in. of filter gravel. The gravel is graded from coarse to fine; the lower and coarser part acts as part of the under‑drain system, and the upper and finest layer supports the filter sand. The raw water from the pumps is carried to the filters through riveted steel rising mains which have 20‑in. cast‑iron branches for supplying the individual filters. The filtered water is collected in the under‑drainage system of the several filter beds, and is carried through 20‑in., cast‑iron pipes to the regulator‑houses. These regulator‑houses contain the necessary valves, registering apparatus, etc., for regulating the rate of filtration, showing the loss of head, shutting down a filter, filling a filter with filtered water from the under‑drains, and for turning the water back into the raw‑water reservoir, or wasting it into the sewer. From the regulator‑houses, the filtered water flows directly to thefiltered‑water reservoir. Generally, five filters are controlled from one house, but there are two cases where the regulator‑houses are smaller, and only two filters are controlled from each.

The dirty sand removed from the filters is carried by a portable ejector through one or more lengths of 3‑in. hose and a fixed line of 4‑in. pipe, to the sand washers. From the sand washers, the washed sand is carried to the reinforced concrete storage bins, each of which has a capacity of 250 cu. yd., and is at such an elevation that carts may be driven under it and loaded through a gate.

Until April, 1909, the sand was replaced in the filters by carts which were filled through the gates in the sand bins. It was then hauled to the top of the filter beds and dumped through the manholes on the chutes, which could be revolved in any direction. These chutes were used to prevent the sand from being unduly compacted in the vicinity of the manholes, and to facilitate spreading it in the filters. Since April, 1909, all the sand has been replaced by the hydraulic method. An ejector is placed under the gate in the sand bin, and the sand is carried in a reverse direction from the bin through the 4‑in. piping and one or more lengths of hose to the filter bed. This process has lowered the cost of re‑sanding considerably, and present indications are that it will prove entirely satisfactory in every way.

The average effective size and uniformity coefficient of the filters are shown in Table 1.

 Table 1—Filter Sand as Originally Placed. Filter No. Average effective size, in millimeters. Average uniformity coefficient. Depth of sand, in inches. Average turbidity. 1 0.32 1.88 35.3 2,600 2 0.30 1.78 37.7 2,200 3 0.32 1.77 40.2 3,000 4 0.29 1.80 42.5 1,800 5 0.34 1.74 44.9 2,700 6 0.31 1.78 37.7 2,300 7 0.29 1.72 40.1 2,300 8 0.32 1.75 40.2 2,800
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9 0.32 1.78 42.5 2,900 10 0.30 1.69 39.5 2,500 11 0.34 1.93 37.1 2,600 12 0.29 1.66 34.7 2,100 13 0.32 1.83 33.6 3,500 14 0.29 1.66 33.6 2,600 15 0.33 1.75 39.0 2,400 16 0.33 1.78 42.3 3,000 17 0.33 1.86 45.5 3,300 18 0.34 1.80 48.7 3,100 19 0.34 1.80 52.0 ... 20 0.34 1.87 39.0 2,700 21 0.32 1.82 42.3 2,400 22 0.33 1.74 45.5 2,200 23 0.33 1.81 48.7 2,300 24 0.35 1.80 52.0 2,600 25 0.29 1.64 39.5 2,400 26 0.31 1.71 37.1 2,100 27 0.31 1.71 34.7 1,900 28 0.33 1.93 33.6 2,300 29 0.34 1.93 33.6 3,000 Maximum 0.36 1.93 52.0 3,300 Minimum 0.29 1.64 33.6 1,800 Average 0.32 1.77 40.4 2,600

Description of Washington Aqueduct.—The water supply of Washington is taken from the Potomac River, at Great Falls, about 16 miles above the city. At that place, a dam has been built across the river, which holds the water at an elevation of 150.5 ft. above mean tide at Washington. From Great Falls the water flows by gravity for a distance of 16 miles through a 9‑ft. conduit, three reservoirs, and a tunnel. From McMillan Park Reservoir, the last of the three, the water is lifted by centrifugal pumps about 21 ft. to the filters. After passing through the filters, it flows to the filtered‑water reservoir, and later to the city mains. In its passage from Great Falls to the filters, the water flows through three settling reservoirs, which have already been referred to. These reservoirs are known as the Dalecarlia, the Georgetown, and the McMillan Park Reservoirs, and have available capacities of 141,000,000, 140,000,000, and 180,000,000 gal., respectively.

Turbidity.—The Potomac River water is rather turbid, the turbidity being caused by very fine particles of clay. The river is subject to sudden fluctuations, it being no uncommon thing to have a turbidity of 100 one day, and 1,000 the next. The high turbidity usually disappears about as rapidly as it comes, and is seldom higher than 500 for more than 5 days at a time. It is frequently the case, however, that a succession of waves of high turbidity will appear so close together that the effect of one has not disappeared before that of another is felt.

The clarification of the water supply begins at the dam at Great Falls. Here it is a clarification by exclusion, for when an excessive quantity of mud appears in the river water, the gates are closed, and the muddy water is allowed to flow over the dam and form mud‑bars in the Lower Potomac, while the city is supplied from the water stored in the three settling reservoirs. Until a comparatively recent date, the excessively muddy water was never excluded, having been taken, like other decrees of Providence, as it came.

During the summer of 1907, the practice of shutting out water with a turbidity of 500 or more was established for the warm months. This practice was discontinued during the cold months, as it was feared that a very high consumption of water might occur at the time of low water in the reservoirs, and so cause a partial famine. During the winter of 1909‑10, however, the gates were closed, as was the practice throughout the summer months.

When the reservoirs are well filled, and the consumption of water is less than 70,000,000 gal. per day, it is safe to close the gates at Great Falls for a period of about 4 days.


Figure 1—Plan and Profile of Washington Aqueduct.

While a considerable reduction in turbidity is effected in each of the reservoirs, the bulk of the mud is deposited at the upper end of Dalecarlia Reservoir. This reservoir had become so completely filled, that, in 1905, it was necessary to dredge a channel through the deposit, in order to allow the water to pass it. During the summers of 1907 and 1908, a 10‑in. hydraulic dredge removed more than 100,000 cu. yd. of mud which had been deposited in this reservoir. The mud deposited in Georgetown and McMillan Park Reservoirs is so fine that the accumulation of many years is not very noticeable in its effect on the depth of water.

The particles of clay which remain in the water after its passage through the three reservoirs, are so exceedingly small that they do not settle out in any reasonable length of time. Even the filtration of the water through one or more slow sand filters occasionally fails to remove the last trace of turbidity. This is especially true in the colder months, and not a winter has passed when the water supply has not been noticeably turbid at some time.

A general idea of the quantity of mud contained in the river water, the quantity excluded by closing the gates at Great Falls, and that removed by sedimentation and filtration, may be gained from

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class="pginternal" tag="{http://www.w3.org/1999/xhtml}a">Table 2, which is, of course, only a rough approximation.

Table 2 also shows that the gates were closed 10.50% of the time, thereby excluding 40.06% of the total suspended matter which otherwise would have entered the system.

The turbidities, bacterial counts, and chemical analyses of numerous samples of water are shown in Tables 3, 4, 5, and 6. The amount of work done in the pumping station, average consumption of water, death rate from typhoid fever, and filter runs are shown in Tables 7, 8, 9, and 10.

Raking.—At the time the filters were first put in service, the sand bins had not been completed, and, consequently, the work of cleaning the filters was carried on in the old‑fashioned way of scraping by hand and wheeling out the sand in barrows. This method of cleaning was used from October, 1905, to April, 1906; then the regular sand‑handling system was commenced.

At times, during the first two summers the filters were in operation, considerable difficulty was experienced in keeping them cleaned as fast as was necessary to provide an ample supply of filtered water. For a short period in each summer it was found necessary to organize night shifts, and keep the work of cleaning in progress for from 16 to 24 hours per day.


Figure 2—General Plan of Washington Filtration Plant Showing Finished Surfaces.
Table 2—Tons of Suspended Matter Entering System, Etc. Month. Amount that would have entered the system if the gates had been left continuously open. Number of hours gates were closed. Amount shut out. Amount deposited in Dalecarlia Reservoir. Amount deposited in Georgetown Reservoir. Amount deposited in McMillan Park Reservoir. Amount entering filtration plant. Total. 1909. July 318 32.0 3 0 125 74 116 318 August 146 47.0 1 0 78 38 29 146 September 97 57.0 7 21 13 38 18 97 October 61 90.5 8 7 9 25 12 61 November 50 60.0 4 13 5 17 11 50 December 370 99.0 126 108 33 59 44 370 1910. January 2,410 136.0 1,109 1,020 67 117 97 2,410 February 839 117.5 481 126 56 75 101 839 March 208 7.5 13 43 15 13 124 208 April 321 65.0 17 195 43 43 23 321 May 197 84.5 58 54 22 24 39 197 June 1,505 124.0 786 535 49 88 47 1,505 Total 6,522 920.0 2,613 2,212 515 611 661 6,522

In order to relieve the situation at such times, the expedient of raking was tried. This was first attempted with the filters filled with water; the effluent was first shut off in order to prevent a downward flow of water, and the filter was then raked or harrowed from boats. This method was not satisfactory, however, as the work was neither as uniform nor as thorough as necessary. Later, the filters were drained to the necessary depth, and the surface of the sand was thoroughly stirred with iron garden rakes. The filters were then filled with filtered water through the under‑drains and put in service.

This latter method proved so satisfactory that it has been resorted to at all times when the work was at all pressing. When the runs were of short duration, and the depth to which the mud had penetrated the filter sand was slight, a raking seemed to be nearly as effective in restoring the filter capacity as a scraping; it could be done in 8 hours by 3 laborers, and there seemed to be no ill effects from lowered efficiency.

Table
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3—Turbidities.
Average by Months.
(United States Geological Survey Standard.) Month. Great Falls. Reservoirs: Dalecarlia Outlet. Gerogetown Outlet. McMillan Park Outlet. Filtered water. Max. Ave. Max. Ave. Max. Ave. Max. Ave. Max. Ave. 1905. October 100 36 40 21 32 18 20 11 4 1 November 35 19 34 19 22 14 14 11 3 1 December 1,500 199 250 84 150 74 95 39 14 6 1906. January 700 94 180 60 120 60 85 52 20 12 February 120 45 85 41 55 29 35 22 5 3 March 1,750 272 350 181 120 56 90 46 8 6 April 1,270 167 180 72 95 58 75 46 12 7 May 600 56 50 20 45 16 34 10 3 2 June 1,700 303 500 125 450 94 180 41 13 2 July 1,000 130 180 54 150 47 250 43 13 3 August 1,530 375 250 112 95 66 65 45 5 2 September 120 33 180 34 95 28 75 25 7 2 October 1,025 127 110 37 60 24 55 21 1 1 November 160 27 75 20 45 16 24 13 1 1 December 600 69 110 31 80 28 80 26 8 2 1907. January 400 135 150 70 110 75 70 53 11 7 February 55 26 26 15 36 16 40 17 5 2 March 950 248 180 77 130 70 90 57 7 4 April 200 47 80 33 60 30 45 24 4 2 May 130 29 40 18 26 15 14 9 1 1 June 400 104 160 48 75 32 40 18 1 1 July 600 114 130 61 78 47 45 31 1 1 August 800 73 130 35 85 26 30 14 1 0 September 600 129 1 1 150 51 70 28 1 0 October 75 32
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tag="{http://www.w3.org/1999/xhtml}a">1 1 65 28 75 26 4 0 November 300 97 1 1 100 45 45 23 2 1 December 680 135 1 1 180 61 100 46 10 4 1908. January 2,100 202 340 73 250 82 160 65 20 7 February 3,000 302 300 52 150 52 75 32 7 4 March 300 91 150 78 100 68 65 42 5 4 April 75 23 65 41 37 27 26 20 3 2 May 2,000 172 130 48 85 37 50 20 1 1 June 400 40 70 29 40 24 30 18 1 1 July 1,500 149 ... 74 170 44 75 15 0 0 August 900 129 200 1 150 56 85 39 2 1 September 75 24 1 1 50 19 35 18 0 0 October 95 20 1 1 55 18 28 15 0 0 November 24 11 1 1 20 11 19 10 0 0 December 20 9 17 11 14 9 10 7 0 0 1909. January 400 72 95 32 60 23 25 16 4 1 February 650 194 120 64 90 51 55 35 4 3 March 250 51 1 1 90 44 60 37 8 4 April 750 98 1 1 130 42 76 31 2 1 May 480
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align="right">57 1 1 30 19 30 12 2 1 June 650 141 1 1 120 51 80 30 1 0 July 400 48 1 1 215 46 120 35 2 1 August 180 23 1 1 50 17 18 9 0 0 September 26 16 24 14 1 1 25 6 0 0 October 14 10 15 10 11 9 8 4 0 0 November 11 9 11 8 10 8 6 4 0 0 December 600 63 110 31 80 28 50 15 3 0 1910. January 3,000 357 200 58 150 53 115 30 5 2 February 3,000 143 150 55 120 50 100 36 7 4 March 210 36 100 35 95 38 100 43 9 5 April 350 55 100 25 55 18 25 8 1 02 May 300 33 55 19 50 17 28 13 1 02 June 1,500 246 180 42 110 37 50 16 1 02 Fiscal years. 1905-062 1,750 133 500 70 450 47 180 31 20 5 1906-07 1,530 114 250 46 150 37 250 29 13 2 1907-08 3,000 117 340 53 250 45 160 31 20 2 1908-09 1,500 79 200 50 170 32 85 22 8 1 1909-10 2,100 86 200 30 215 29 120 18 9 1