present status of sludge gas utilization
TRANSCRIPT
Present Status of Sludge Gas UtilizationAuthor(s): Richard H. GouldSource: Sewage Works Journal, Vol. 19, No. 2 (Mar., 1947), pp. 170-174Published by: Water Environment FederationStable URL: http://www.jstor.org/stable/25030437 .
Accessed: 14/06/2014 01:04
Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at .http://www.jstor.org/page/info/about/policies/terms.jsp
.JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range ofcontent in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new formsof scholarship. For more information about JSTOR, please contact [email protected].
.
Water Environment Federation is collaborating with JSTOR to digitize, preserve and extend access to SewageWorks Journal.
http://www.jstor.org
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions
PRESENT STATUS OF SLUDGE GAS UTILIZATION *
By Richard H. Gould
Director, Division of Engineering and Architecture, Dept. of Public Works, New York City
For a comprehensive discussion of
the status of sludge gas utilization it
would be necessary to canvass the ex
periences of literally hundreds of im
portant installations in this country and abroad where sewage sludge is di
gested and the resulting gas is collected
and utilized. Rather than attempting such an arduous and time consuming task, the present contribution will be confined to the experiences in the sew
age works of New York City during the past ten years.
It is important to bear in mind that
sludge digestion and gas utilization is but one of several alternate methods that may be available in the disposal of sewage solids. Its adaptability and
economic feasibility will vary consid
erably in different localities and with
special conditions that always are pres ent in each particular project.
Much depends on the possibilities of
disposal of the ultimate residues. If
disposal at sea is available there is one set of circumstances. If large tracts of cheap land may be had the possibili ties are different. Fertilizer manufac ture may be attractive to some, while incineration may be the best compro
mise to others. A determinant in
many cases will be the economic avail
ability of possible treatment plant sites, their size and degree of isola tion.
In New York City in recent years the trend has been definitely toward the digestion of sludge and the utiliza tion to the extent considered practical of the resulting gases. New York
City's largest plant, on Wards Island, *
Presented at Nineteenth Annual Meeting, Federation of Sewage Works Association, To
ronto, Canada, October 7-9, 1946.
and the first of its modern plants to be
placed under construction, is the only exception. Here the solids removed from the sewage are shipped to sea in a fluid state with no treatment other than the d?cantation of excess liquids.
Of the newer plants in operation all
provide for sludge digestion. At
Coney Island, Tallmans Island, Bow
ery Bay and Jamaica the digester gas is utilized to generate power and heat, and at one small plant (City Island) the gases are used for heat only. The same condition will obtain in the 26th
Ward plant now under construction and those for which plans have been
made or are under way. Included in the latter category is the extension of the present Wards Island plant to over twice its present capacity.
Conditions Favoring Digestion in New York Plants
It may be of general interest to out line some of the conditions that make
sludge digestion adaptable to the New York problem.
Of the seventeen locations in use or
adopted for future plants there are
only four that are distant as much as
1,000 ft. from residential areas; many are much closer, hence odor control
and aesthetics are of paramount im
portance. Control of large scale fer tilizer production has not yet been de
veloped to a stage where it could be
safely practiced in most of these loca tions.
One distinct asset is the city's loca tion on the ocean and the economy, simplicity and lack of offense with
which sewage solids can be disposed of at sea. The disposal of the voluminous raw solids from the activated sludge
170
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions
Vol. 19, No. 2 PRESENT STATUS OF SLUDGE GAS UTILIZATION 171
plant at Wards Island is accomplished at an operating cost with city-owned vessels of about 12 cents per ton of
liquid sludge, or about $2.64 per ton of dry solids. This is, of course, much
cheaper than local costs would be for
filtration and incineration.
There is a problem, however, in the
control of odors at the plant site in the
storage and loading of the raw sludge on the vessels. Provision has been
made for the use of ozone in the sludge storage building and for the use of activated carbon at the vents of the
sludge tanks on the vessels, but the
latter was found difficult to maintain in effective condition and has been dis
continued. In general, however, no
serious trouble from odors has de
veloped.
It has been found that when the
combined primary and activated
sludges are digested the destruction of
organic matter and the greater concen
tration of the solids result in a volume
of residue of about one-half the bulk
of the raw sludges. The resulting
saving in the shipping cost of the resi dues is enough to pay for the capital and differential operating costs of di
gestion tanks. Digestion tanks can be
operated without offense. The hazards of handling raw sludges are thus
avoided and at no additional cost. There is substantial value in the large volumes of methane gas that are col lected as a by-product of digestion. It is the utilization of this by-product, secured at substantially no additional
cost, that is the subject of the present discussion.
Gas Utilization in New York Plants
Coney Island
New York City first embarked on the
digestion of sludge and the utilization of digester gases at the Coney Island
plant in 1936. The first installation here was designed for a flow of 35
m.g.d. This plant was laid out to pro vide chemical precipitation and chlo
rination during the summer and plain sedimentation only during the winter.
Eight digestion tanks with gas holder
type covers of our own design were
provided. What was then considered a bold
step was taken in that entire reliance for the power requirements for pump
ing and all other uses was placed on
three 300-h.p. gas engine generator
sets. No provision was made for the
purchase of electricity from an outside
source, however, provision was made
for the purchase of utility gas in case
of a possible deficiency of digester gas. In 1941 the capacity of the plant
was doubled. Six new digesters were
added. These were fitted with covers
floating on the sludge, as the gas stor
age in the older plant was considered
adequate. Three gas engine generator units, each of 920 h.p., were added. The digestion tank capacity now totals
1,200,000 cu. ft., which is 2 cu. ft. per
capita on the design population of
600,000. Gas storage amounts to
400,000 cubic feet. Gas utilization at the Coney Island
plant has been eminently satisfactory. Sewage has been lifted 40 ft. and aux
iliaries and services maintained with but a trivial amount of utility gas being purchased. There is no means to record surplus gas wasted, but gas utilized and metered represents less than half of that which should be re covered from the volatile matter added to the digesters, based on experience in other city plants. In ten years of
operation there has been no flooding of the sewers due to power failure.
Heat recovered from engine cooling water and exhaust gases has been ade
quate for heating the digestion tanks and plant buildings except on a few
extremely cold days when digester gas was used under the heating boilers.
Tallmans Island
The second digester installation to go into service was at Tallmans Island in 1939. This plant of 40 m.g.d. ca
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions
172 SEWAGE WOEKS JOUENAL March, 1947
38?5
-^%??*1?L
- *'-. v> . .>3$v4'
Sfe^SSB'
m -
FIGURE 1.?Gas engines driving pumps and compressors at Tallmans Island sewage treatment plant, New York City.
pacity is of the activated sludge type. It was felt that the power requirements of this process would exceed the poten tial power that might be secured from
gas utilization. The four digestion tanks, providing 705,000 cu. ft. ca
pacity, were therefore fitted with float
ing covers and no gas storage was pro
vided as little excess gas over the de
mand was expected.
Four gas engines were directly con
nected to positive displacement blowers for the air supply and four others by
means of angle gears to the main verti
cal centrifugal pumps working against a 39-ft. head. Facilities were provided to make up any deficiency in gas pro duction by utility gas. Electric power for lighting and auxiliary equipment
was purchased from the power com
pany. The eight engines have total
rating of 3,620 horse-power.
Gas production at Tallmans Island
has more nearly met power require
ments than was expected. There are
many days when full engine require ments are met and no gas is purchased.
The annual average for 1945, for ex
ample, shows that of the gas produced 3 per cent was wasted and the re
mainder met 91 per cent of the engine demand. About 1.4 per cent of all gas was used for heat during cold weather.
Taking into account the electric power
purchased for auxiliaries as well as the
requirements of the main pumps and
blowers, the gas produced accounted
for a little over 75 per cent of the total
power requirement for the plant and all but a very small part of the heating of digesters and buildings.
Bowery Bay
The 40 m.g.d. activated sludge plant at Bowery Bay was placed in full op eration in 1942. Four digestion tanks
provided 728,000 cu. ft. capacity for a
population of 308,000. They were
fitted with gas holder type covers giv
ing 206,000 cu. ft. of storage.
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions
Vol. 19, No. 2 PRESENT STATUS OF SLUDGE GAS UTILIZATION 173
Negotiations with the utility com
pany for outside services were not en
tirely satisfactory. It was not practi cable to bring in a supplementary source of gas and the company opposed cross connections on the electrical
boards that would allow alternate op eration of the main pumping and
blower units either by generated or
purchased power. This has resulted in a lack of flexibility and some unbalance in the proportioning of the capacity of
units on the gas engine half of the
plant.
Two 800-h.p. gas engine generating units were installed. While in some
months they may produce nearly 70
per cent of the total power required at
the plant, the annual averages show
only about 45 per cent of this require ment. About 7 per cent of the gas
produced was used under the heating boilers.
Jamaica
The 65 m.g.d. activated sludge plant at Jamaica started operation in 1943. This plant designed for 500,000 people, has twelve digestion tanks of 1,618,000 cu. ft. capacity with gas holder covers
of 400,000 cu. ft. capacity. There are
three gas engine generator units each of 1,450 b.h.p.
The arrangements with the utility company at this plant are much more
satisfactory than at Bowery Bay. Here there is a utility gas connection to supplement the digester gas if neces
sary. The main pumping and blower units may be supplied with either pur chased electricity or that generated from gas.
Gas production here was sufficient in 1944 and 1945 to supply 85 per cent
of all the power used and on some days there has been a surplus. It should be
noted, however, that for the period in
question the plant was operating with low solids in the aeration tanks under the system developed and described under the term "modified sewage aera
tion." Air consumption has been
about 0.4 cu. ft. per gal. of sewage. Heat requirements for the digesters and buildings were met for the most
part by heat recovered from engine operation. Only about 1 per cent of the total gas produced and purchased
was burned under the heating boilers.
Design Practice
There is nothing particularly unique in the New York City sludge digestion
practice. In the four plants described above the tanks are circular, varying in diameter from 54 ft. in the early Coney Island plant to around 80 ft. for the others. They have conical bot toms with side water depths from 24 to 30 feet. Temperatures are main tained at from 85? to 90? F. by means
of pipe coils in the tanks. The hot water circulating therein comes from the water jackets of the engines, the heat exchangers from the engine gases and may be supplemented by gas or oil fired boilers. Part of the tanks are
used as primary and others as secon
dary digesters with surplus liquid de canted from the secondaries.
The new designs provide for larger tanks. In some cases diameters will be as much as 120 ft. and side water
depths up to 40 feet. In these larger tanks multiple inlets will be provided to assure distribution and mixing of solids in the tanks. Provisions for
positive circulation are also to be made. At the proposed Hunts Point plant preheating of sludge before discharge to the digesters is called for.
The quality of the digester gas is
quite uniform, averaging about 64.4
per cent methane with plus or minus variations of from 2 to 3 per cent. Its heat content is about 654 B.t.u. as com
pared to the local utility gas of about 540 B.t.u. The sulfur content aver
ages about 2.4 gr. per 100 cu. ft. and has not required any special treatment.
Dual Fuel Engine at Tallmans Island
The engines are of the heavy duty slow speed type. Many of them are
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions
174 SEWAGE WORKS JOURNAL March, 1947
designed so that they can be rather
easily converted to the diesel cycle. In
deed an interesting recent development is based on the conversion of one of the
blower engines at the Tallmans Island
plant to the full diesel cycle and its
operation with oil and digester gas as
fuel.
The engine at Tallmans Island has
been under test operation for over a
year. It is known, of course, that the
diesel cycle permits approximately 25
per cent greater power recovery from a gaseous fuel as compared to the Otto
cycle of the ordinary gas engine. It
has been found elsewhere that in order
to ignite a gas uniformly at diesel
pressures it was necessary to inject a
small amount of oil with the gas. It was found that successful operation with digester gas was possible with the
injection of diesel oil in the amount of
from 5 to 7 per cent of the heat value
of the total fuel used. The engine per formed well with the use of 100 per cent oil or any combination of oil and
gas between these limits. Economies
in fuel consumption were demonstrated to be quite as anticipated.
This new combination seems to offer
great advantages in the utilization of
digester gases. The greater economy of the diesel cycle will make the gas
go further and in most cases would
seem to stretch the supply so that all
normal power requirements can be met.
Should there be a deficiency of gas dur
ing the first months of operation, or
later for any reason, the cost of power
using oil alone as a fuel would be less
than power from purchased gas or
from electricity that is subject to the
usual demand charges. The possibilities of this new combina
tion are so promising that one existing contract for gas engines for the 26th
Ward plant has been modified to con
vert these engines to the dual fuel Diesel type. Provision is being made in new plants under design for installa
tion of this new type. In these new
units the supercharging of gas fed to
the engines will probably be provided for, thus further increasing the fuel
economy and increasing the capacity of units of equivalent size.
Conclusion
The utilization of sludge gas does
undoubtedly call for considerable extra effort in plant design and operation. To be successful it presupposes intelli
gent layout and proper operation and
maintenance. With a power installa
tion that is reasonably well loaded so
that the capital charges are not out of
line there is a very substantial margin of cost in favor of the utilization of this
by-product of sludge digestion.
SLUDGE GAS UTILIZATION?A DISCUSSION
By A. M. Boehm
Engine Division, Worthington Pump and Machinery Corp., New York, N. Y.
Since Mr. Gould's very informative
paper covers utilization of sewage
sludge gas in many ways, some of
which are foreign to the writer's field, these remarks will be confined to that
portion which deals with gas utilization
for power purposes and, more spe
cifically, to the dual fuel engine. Perhaps it would not be amiss at this
time to define a dual fuel engine as it
is now understood. Briefly, it is an
internal combustion engine which con
sumes gaseous fuels, using compression
pressures approximating those of a full
Diesel oil engine and employing a small
amount of fuel oil called "pilot oil"
to ignite the compressed gas and air
charge.
This content downloaded from 185.44.77.28 on Sat, 14 Jun 2014 01:04:32 AMAll use subject to JSTOR Terms and Conditions