Laminar flow collar for use in a wastewater management system

Information

  • Patent Grant
  • 6261452
  • Patent Number
    6,261,452
  • Date Filed
    Thursday, December 23, 1999
    25 years ago
  • Date Issued
    Tuesday, July 17, 2001
    23 years ago
Abstract
A laminar flow collar for use with an effluent pump in a septic system. The laminar flow collar is a cylinder having a closed bottom and an open top portion. The laminar flow collar includes a plurality of holes drilled about the periphery of the cylinder at a certain distance from the bottom. The laminar flow collar sits on the bottom of the tank and the plurality of holes are positioned at a certain height from the bottom of the septic tank and below the surface of the effluent so as not to draw in “scum” floating on the top of the septic tank. The plurality of holes are engineered to match the pump flow so that flow into the collar is laminar, thereby avoiding turbulence in the tank which would otherwise stir up the sludge at the bottom of the tank. The effluent pump is inserted into a second cylinder which is placed within the laminar flow collar.
Description




BACKGROUND OF THE INVENTION




1. Field of the Invention




The present invention relates generally to a wastewater management system which maintains a laminar flow of wastewater (e.g., effluent) in a septic system and, more particularly, to a wastewater management system having a laminar flow collar which maintains a laminar flow of effluent within the septic system prior to discharging into an absorption field.




2. Background Description




In the absence of conventional public wastewater disposal and treatment systems, it is not uncommon for residential and small businesses to use on-site wastewater management systems. Typically, these wastewater management systems include a septic tank, and under certain conditions may additionally include a pump tank for discharging septic effluent into an absorption field.




In one such conventional system, wastewater flows into and out of the septic tank via baffled input and output pipes. These baffled input and output pipes slow the flow of water and prevent sewage from flowing directly through the septic tank. In the septic tank, solids are settled on the bottom of the tank while lighter particles including grease and foam float to the surface and form a layer of scum. The solid material in the septic tank is then broken down via a bacterial action.




The septic effluent may then be directed into the absorption field by gravity or, alternatively, may flow into a pump tank which doses the absorption field with the septic effluent. However, it is not uncommon for the solid waste to also flow into the pump tank. This usually occurs when the septic tank overflows due to high volume use and the like, and usually occurs despite the fact that baffles are positioned at the output of the septic tank. Similar to the septic tank, once the septic effluent including the solid waste flows into the pump tank, the solids settle on the bottom of the tank while lighter particles including grease and foam float to the surface and form a layer of scum.




A liquid pump within the pump tank (or septic tank) then provides a means for discharging the effluent into the absorption field. However, current systems have a tendency to create turbulent conditions within the tank (either a pump tank or a septic tank or the like) during the dosing process. These turbulent conditions, in turn, disturb the solid waste at the bottom of the pump tank as well as the scum on the surface of the effluent at the top of the tank such that the solid waste and the scum usually enter the intake ports of the pump. This leads to clogging of the pump which, in turn, may lead to a failure of the pump which would greatly increase the cost of maintenance of the wastewater management system. It is also noted that the efficiency of the system is also greatly reduced.




Solid pumps may also be used to discharge the septic effluent from the tank into the absorption field. However, solid pumps are not very efficient and cannot reach high heads. Thus, multiple stations or pump tanks are needed when using solid pumps, which greatly adds to the cost of the wastewater management system. Thus, the use of multiple stations or pump tanks is very expensive and still is not as efficient as the use of liquid pumps.




By way of example, U.S. Pat. No. Re. 32,312 to Crates et al. disclose an inlet and outlet baffle structure for sewage treatment tanks. The structure includes a septic tank ‘A’ which has opposing arcuate walls. An inlet


20


and an outlet


40


are disposed within the opposing arcuate side walls. The inlet includes first, second and third portions


60


,


70


and


80


. Incoming raw sewage is received in the first portion


60


and drops through the second portion


80


. The sewage is slowed by the third portion


90


which absorbs some of the kinetic energy of the sewage. The reduced velocity reduces the turbulence in the tank; however, it appears that there still may be some turbulence still present in the tank.




As another example, U.S. Pat. No. 2,605,220 to R. P. Logan discloses an anaerobic digester including a closed tank with inlet and outlets. A propeller


23


is located within an upward extending tube


24


. The propeller


23


violently agitates the fluid within the tank.




Moreover, U.S. Pat. No. 5,186,821 to Murphy discloses a tank having an influent delivery system


12


which delivers influent through a pipe tee


20


and pipe section


21


into substantially the bottom section of a collector


28


. A circular partition


26


, being larger in circumference than collector


28


, creates a pre-stratification zone


27


. Multiple air diffusers


30


are connected to a drop pipe


31


with the upper end of drop pipe


31


being connected to a conventional air compressor


58


which is mounted within the manway


56


. A floating decanter base section


35


and a submersible motor


36


and suction pump


38


are provided in the tank


11


.




What is needed is a wastewater management system that is capable of using a liquid pump having high head capabilities without being clogged by solid waste during the dosing process. This system would also control the effluent flow into the absorption field such that the absorption field is utilized in an efficient manner thereby providing enhanced effluent quality.




SUMMARY OF THE INVENTION




It is therefore an object of the present invention to provide a wastewater management system that prevents turbulence of effluent within either a septic tank or a pump tank or the like.




It is a further object of the present invention to provide a wastewater management system that prevents a dosing pump from being clogged with solid waste or scum during discharge of effluent into an absorption field throughout a range of effluent flows.




It is also a further object of the present invention to provide a wastewater management system that includes a laminar flow collar for housing a dosing pump having high head capabilities and which further maintains a laminar flow of the effluent throughout a range of effluent flows.




It is a also an object of the present invention to provide a wastewater management system that provides a cooling tower for cooling a dosing pump.




According to the invention, there is provided a laminar flow collar which prevents turbulence from being created in a septic system throughout a range of effluent flows. That is, the laminar flow collar of the present invention maintains a laminar flow of effluent within the septic system. The laminar flow of effluent in the septic system prevents a dosing pump (preferably a liquid pump) from becoming clogged which may lead to failure of the dosing pump.




The laminar flow collar includes a cylinder having a closed bottom and an open top portion. The cylinder further includes a plurality of holes positioned about the periphery of the cylinder at a certain distance from the bottom. The diameter and number of holes within the cylinder in combination with the flow rate of the dosing pump maintains the laminar flow of the effluent within the septic system and preferably within either a septic tank or a pump tank or the like. The dosing pump is inserted into a pump cylinder which is placed within the laminar flow collar cylinder. The flow collar acts as a receptacle and a guide tube for the placement of the dosing pump within the tank. This pump cylinder is open at the bottom for the pump intake and at the top terminates in a frustro-conical fitting that connects to an effluent pipe. The laminar flow collar assembly sits on the bottom of the tank and the plurality of holes are positioned between the solid waste (e.g., sludge) which has settled at the bottom of the tank and the scum floating near the top of the tank.




The plurality of holes are engineered to match the pump flow so that effluent flowing into the collar is laminar, thereby avoiding turbulence in the tank which would otherwise stir up the sludge at the bottom of the tank. This prevents the solids and scum from entering the input ports of the pump which may clog the pump and lead to a pump failure. Also, the pump cylinder also provides a reduced volume which increase the flow rate of the effluent at the bottom of the flow collar cylinder. This ensures that particulate matter will not accumulate at the bottom of the flow collar cylinder thus reducing the efficiency of the dosing pump.











BRIEF DESCRIPTION OF THE DRAWINGS




The foregoing and other objects, aspects and advantages will be better understood from the following detailed description of a preferred embodiment of the invention with reference to the drawings, in which:





FIG. 1

shows a flow collar cylinder of the laminar flow collar of the present invention;





FIG. 2

shows a disassembled pump cylinder for housing a pump;





FIG. 3



a


shows an assembled laminar flow collar of the present invention;





FIG. 3



b


shows a cross section of the laminar flow collar of the present invention along lines


3





3


of

FIG. 3



a;







FIG. 4

shows the laminar flow collar of the present invention inserted in a septic system; and





FIG. 5

shows a Moody Diagram charting laminar and turbulent flow conditions (Wastewater Engineering Treatment, Disposal & Reuse, Metcalfe & Eddy, Inc., 3


rd


ed., pg. 1282).











DETAILED DESCRIPTION OF A PREFERRED EMBODIMENT OF THE INVENTION




The present invention is directed to a wastewater management system having a laminar flow collar which maintains a laminar flow of effluent within the septic system prior to discharging into an absorption field. The present invention further has the advantage of preventing turbulence of effluent within either a septic tank or a pump tank in order to prevent solid waste or scum from clogging the dosing pump throughout a range of effluent flows. This allows for maximum settling of solid material at the bottom of the septic tank or pump tank.




In order to accomplish the above objectives, the present invention includes a laminar flow collar cylinder having a plurality of holes positioned about the periphery thereof at a certain distance from the bottom. The plurality of holes positioned about the periphery of the laminar flow collar cylinder are engineered to match the pump flow rate so that effluent flowing into the laminar flow collar cylinder is laminar throughout a range of effluent flows. This avoids turbulence in the tank which would otherwise stir up the sludge at the bottom of the tank. This further allows for maximum settling of the sludge at the bottom of the tank.




Positioned within the laminar flow collar cylinder is a pump cylinder which houses a dosing pump. In the preferred embodiments, the dosing pump is a liquid pump.




For illustrative purposes only a single embodiment of the laminar flow collar will be described herein with reference to FIGS.


14


. However, it will be understood from the disclosure that the laminar flow collar of the present invention can be made of many materials and engineered to accommodate various wastewater effluent flow rates and the like as provided in the examples below. Therefore the specific dimensions of the laminar flow collar, including length, width, shape and other variables and quantities specified herein may vary with the type and size of the laminar flow collar being used with the system contemplated herein. Therefore, numbers and dimensions specified herein are not to be construed as limitations on the scope of the present invention, but are meant to be merely illustrative of one particular application of the present invention. It is also well understood by one of ordinary skill in the art that an important feature of the laminar flow collar of the present invention is to maintain a laminar flow of effluent in a septic system at various designed flow rates thereby preventing solid waste and the like from clogging the inlet ports, impellers and the like of the dosing pump.




Referring now to the drawings, and more particularly to

FIG. 1

, there is shown a laminar flow collar cylinder of the laminar flow collar of the present invention Specifically,

FIG. 1

show a laminar flow collar cylinder


10


having an open top end


16


and a plurality of holes


14


about the periphery thereof. At bottom end of the laminar flow collar cylinder


10


is a cap


12


which sits on a floor of the septic system (see FIG.


4


). The holes


14


are preferably equally spaced apart from one another and are positioned so as to prevent suction from the dosing pump from suctioning the sludge at the bottom of the tank and scum at the surface of the effluent wastewater.




Still referring to

FIG. 1

, the laminar flow collar cylinder


10


and cap


12


are made of (polyvinlechloride) PVC; however, any other material suitable for a septic system may be used with the present invention. In this embodiment, there are three rows of holes


14


about the periphery of the laminar flow collar cylinder


10


which are arranged at a total distance of approximately four inches, with a bottommost row of holes


14




a


approximately 16 inches from the bottom of the laminar flow collar cylinder


10


. The height of the laminar flow collar cylinder


10


is approximately 27½ inches with a diameter of approximately six inches. In one preferred embodiment, there are 40 holes each having a diameter of less than or equal to one inch but greater than or equal to ⅞ inch. This configuration is designed so that when the laminar flow collar of the present invention is positioned within the tank of a septic system, the holes


14


are located within the clear effluent, i.e., below the scum floating on the surface of the tank and above the solid waste or sludge settled at the bottom of the tank, thereby resulting in a laminar flow of the wastewater effluent.




As previously discussed, the dimensions discussed herein are not in any way limiting, and other dimensions may equally be used depending on the capacity of the septic system and the flow rate of the pump and the like. For example, one further embodiment of the present invention is designed to include 30 holes each having a diameter greater than or equal to ⅞ inches and a flow rate of 15 gallons per minute. However, it is noted that other flow rates as well as number of holes and diameters of holes may equally be used with the present invention such as, for example, an eight inch diameter laminar flow collar cylinder having 30 holes about a periphery thereof and each having a diameter of approximately 1.15 inches.




It is important to note that the configuration (e.g., dimensions of the holes and the like) may vary depending on the different effluent flow rates and other variables used in different septic systems. However, it is important to stress that the present invention may accommodate any system according to the examples provided below. Thus, different diameter and number of holes and the like are contemplated so long as the laminar flow collar of the present invention maintains a laminar flow within the septic system (e.g., a Reynolds Number of less than 2000).





FIG. 2

shows a disassembled pump cylinder for housing a dosing pump. The pump cylinder


20


includes an open bottom end


21


and an assembly


22


coupled to the top portion of the pump cylinder


20


. The diameter of the pump cylinder


20


is large enough to house a dosing pump therein but small enough to fit within the laminar flow collar cylinder


10


. The assembly


22


includes a half coupling


23


and an adapter


24


coupled to the half coupling


23


. A pipe


26


is coupled to the adapter


24


. A pressure bushing


28


is fitted over the pipe


26


and a reducing coupling


30


is then fit over the entire assembly (e.g., half coupling


22


, adapter


24


, pipe


26


and pressure bushing


28


) such that the pressure bushing


28


and pipe


26


extend into the upper portion of the reducing coupling


30


. A coupling pipe


32


then extends from the reducing coupling


30


and leads to an effluent discharge. The pipe


26


may be coupled to an output of the dosing pump.




It is further noted that the assembly


22


as well as the cylinder


20


may also act as a cooling tower for the dosing pump. That is, the assembly


22


and the cylinder


20


provide for a uniform cooling of the dosing pump when inserted into the wastewater effluent. This prolongs the life of the dosing pump.




Still referring to

FIG. 2

, it is noted that the assembly


22


is not critical to the understanding of the present invention and is thus provided herein as one embodiment of the present invention. Thus, one of ordinary skill in the art would readily recognize that other assemblies


22


may be used with the present invention in order for the dosing pump to discharge the effluent from the septic system. By way of example, the present invention would work equally well with a flat cap for sealing the cylinder


20


instead of the half coupling


23


and the reducing coupling


30


.





FIG. 3



a


shows the assembled laminar flow collar of the present invention. As seen in

FIG. 3

, an upper portion of the pump cylinder


20


and the assembly


22


protrude from the open end


16


of the laminar flow collar cylinder


10


. Although not shown, the coupling pipe


32


extends from the reducing coupling


30


and leads to an effluent discharge. The flow collar cylinder


10


may as a receptacle and a guide tube for the placement of the dosing pump within the tank.





FIG. 3



b


shows a cross section of the laminar flow collar of the present invention along lines


3





3


of

FIG. 3



a


. A dosing pump


36


is housed within the pump cylinder


20


such that a bottom of the dosing pump


36


rests on the cap


12


of the laminar flow collar cylinder


10


. As wastewater effluent flows into the laminar flow collar cylinder


10


via the holes


14


, the water is forced down the sides of the laminar flow collar cylinder


10


between the inner surface of the laminar flow collar cylinder


10


and the outer surface of the pump cylinder


20


via the pumping action of the dosing pump


36


. The wastewater effluent then flows upward within the pump cylinder


20


between the inner surface of the pump cylinder


20


and the outer surface of the dosing pump


36


. The pump cylinder


20


provides a reduced volume which increases the flow rate of the effluent at the bottom of the laminar flow collar cylinder


10


which ensures that particulate matter will not accumulate or settle at the bottom of the laminar flow collar cylinder


10


thus reducing the efficiency of the dosing pump. The wastewater effluent then flows into the input ports and impellers


36




a


of the dosing pump


36


for discharging into the absorption field via the coupling pipe


32


.





FIG. 4

shows the laminar flow collar of the present invention in a septic system, e.g., a septic tank or pump tank or the like. As seen in

FIG. 4

, the holes


14


of the laminar flow collar cylinder


10


are located in the clear effluent. That is, the holes


14


are located between the sludge settled at the bottom of the tank and the scum that is floating at the surface of the wastewater effluent. The level within the tank is controlled by a float valve


35


.




In order to provide for a laminar flow using the laminar flow collar of the present invention, it is important to use the proper number of holes in combination with a proper diameter of each of the holes. By way of example, the following equations are used to show that particular embodiments of the laminar flow collar of the present invention may be used to provide a laminar flow within the pump tank or septic tank of the septic system. In these examples, it is assumed that the laminar flow collar of the present invention is used with wastewater temperature of approximately 15 degrees Celsius (or 59 degrees Fahrenheit). Of course, other temperature wastewater may equally be used the present invention, and that minor variations of the temperature of the wastewater will not affect the laminar flow of the wastewater as it flows through the laminar flow collar of the present invention.




It is further noted that the examples presented below are merely illustrative of several particular embodiments of the present invention and that other configurations (e.g., number and diameter of holes) of the laminar flow collar may equally be used, depending on such variables as the flow rate (gallons per minute) of the wastewater, the diameter of each hole and the like. Thus, the present invention is in no way limited to the illustrative examples presented below.




EXAMPLE I




FLOW RATE OF 25 GALLON PER MINUTE FLOW RATE




The following is an example of equations used to determine proper hole diameters for maintaining a laminar flow in laminar flow collar cylinders having 30 holes, 40 holes and 42 holes, and which is used in a septic system having a flow rate of 25 gallons per minute. In these equations, (i) “D” represents the diameter of each of the holes in the laminar flow collar, (ii) ‘Re’ represents a Reynolds Number (a Re of less than 2000 represents laminar flow conditions) (See FIG.


5


).




The following equations assume a wastewater temperature of approximately 15 degrees Celsius with a dynamic viscosity of 1.14×10


−3


N.S/m


2


and a density of 999 kg/m


3


(see Table I attached below) where








Reynold
'


s





Number

=

Re
=

NR
=


ρ







v





D

μ


=



ρ


(

Q
A

)



D

μ








Density
=

ρ
=

999






kg

m
3








(

see





Table





I





attached





below

)







V
=


Q
A

=



m3
S


m
2


=

m
s













Laminar Flow Collar Having 30 Holes




The following equations are solved to determine the flow rate per hole of a laminar flow collar using 30 holes.







flow





rate





per





hole

=



25





gpm


30





holes


=

0.83






gpm





hole









0.83






gal






min
.



×


1






ft
3



7.48





gal


×



(

12





in

)

3


1






ft
3



×



(

2.54





cm

)

3


1






in
3



×


1






m
3




(

100





cm

)

3


×


1






min
.



60






sec
.




=

5.24
×

10

-
5























h













In order to determine the effective diameter for each of the holes in the 30 hole laminar flow collar of the present invention, the Reynolds Number is set equal to 2000 and the below equation is solved for “D”, where “D” is the ideal diameter for each of the holes in the laminar flow collar using a 25 gallon per minute flow rate.






2000
=




(

999






kg

m
3



)



(
D
)




(

5.24
×

10
-


5



m
3

s


)



π
4




(
D
)

2










1.14
×

10
-


3







N
.
S


m
2








D
=


0.02923





m
×


100





cm


1





m


×


1






in
.



2.54





cm



=

1.15





inch












It is thus found that each of the 30 holes should have a diameter of approximately 1.15 inches in order to provide a laminar flow in a septic system having a flow rate of 25 gallons per minute.




Laminar Flow Collar Having 40 Holes




The following equations are solved to determined the flow rate per hole of a laminar flow collar using 40 holes.







flow





rate





per





hole

=



25





gpm


40





holes


=

0.625






gpm





hole








Q
=


0.625






gal






min
.



×


1






ft
3



7.48





gal


×



(

12





ϵ

)

3


1






ft
3



×



(

2.54





cm

)

3


1






in
3



×


1






m
3




(
100




)



cm
3



×


1






min
.



60






sec
.




=

3.94
×

10

-
5





m
s






hol














In order to determine the effective diameter for each of the holes in the 40 hole laminar flow collar of the present invention, the Reynolds Number is set equal to 2000 and the below equation is solved for “D”, where “D” is the ideal diameter for each of the holes in the laminar flow collar using a 25 gallon per minute flow rate.






2000
=




(

999






kg

m
3



)



(
D
)




(

3.94
×

10

-
5





m
3

s


)



π
4




(
D
)

2










1.14
×

10

-
3









N
.
S


m
2








D
=


0.02198





m
×


100





cm


1





m


×


1






in
.



2.54





cm



=

0.865





inch












It is thus found that each of the 40 holes should have a diameter of approximately 0.865 inches in order to provide a laminar flow in a septic system having a flow rate of 25 gallons per minute.




Laminar Flow Collar Having 42 Holes




By way of even further example, it is noted that 42 holes each having a diameter of ⅞ inches (0.02223 m) used with a 25 gallon per minute flow would also result in a laminar flow. The following equations confirm such a configuration of one embodiment of the present invention.







flow





rate





per





hole

=



25





gpm


42





holes


=


0.595






gpm





hole







=


0.595


gal






min
.



×


1






ft
3



7.48





gal


×



(

12





in

)

3


1






ft
3



×



(
2.54




)



cm
3



1






in
3



×


1






m
3




(

100





cm

)

3


×


1






min
.



60





sec



=

3754
×

10

-
5





m









ho










Re
=





(

999






kg

m
3



)



(

0.02223





m

)




(

3.75
×

10

-
5





m
3

s


)



π
4




(

0.02223





m

)

2










1.14
×

10

-
3









N
.
S


m
2




=
1882





D
=


0.02223





m
×


100





cm


1





m


×


1






in
.



2.54





cm



=

0.875





inch












Trial Tests for Laminar Flow Collar Using 40 Holes with ⅞ Inch and One Inch Diameter Holes




The following equation verifies that a drill bit having a diameter of approximately ⅞ inch (0.02223 m) for drilling 40 holes (each having a corresponding diameter of 0.02223 m) in the laminar flow collar of the present invention would result in a laminar flow (Re<2000).






Re
=





(

999






kg

m
3



)



(

0.02223





m

)




(

3.94
×

10

-
5





m
3

s


)



π
4




(

0.02223





m

)

2










1.14
×

10

-
3









N
.
S


m
2




=
1978











The following equation verifies that a drill bit having a diameter of approximately one inch (0.02540 m) for drilling 40 holes (each having a corresponding diameter of 0.02540 m) in the laminar flow collar of the present invention would result in a laminar flow (Re<2000).






Re
=





(

999






kg

m
3



)



(

0.02540





m

)




(

3.94
×

10

-
5





m
3

s


)



π
4




(

0.02540





m

)

2










1.14
×

10

-
3









N
.
S


m
2




=
1731











EXAMPLE II




FLOW RATE OF 15 GALLON PER MINUTE FLOW RATE




By way of an additional example, the laminar flow collar of the present invention may work equally well with a flow rate of 15 gallons per minute and a laminar flow collar having 30 holes. In this example, each hole has a diameter of approximately 0.6917 inches (0.01757 m). The following equations assume that the temperature of the wastewater is approximately 15 degrees Celsius with a dynamic viscosity of 1.14×10


−3


N.S/m


2


and a density of 999 kg/m


3


(see Table I attached below) where






Density
=

ρ
=

999






kg

m
3









Reynolds





Number

=

Re
=

NR
=



ρ





v





D

μ

=



ρ


(

Q
A

)



D

μ








V
=


Q
A

=


m3
S


m
2













The following equations are used to determine the flow rate of a laminar flow collar of the







flow





rate





per





hole

=



15





gpm


30





holes


=


0.5






gpm





hole







=


0.5






gal






min
.



×


1






ft
3



7.48





gal


×



(

12





in

)

3


1






ft
3



×



(

2.54





cm

)

3


1






in
3



×


1






m
3




(
100




)



cm
3



×


1






min
.



60





sec



=

3.15
×

10

-
5





m
s






ho
















In order to determine the effective diameter for each of the holes in the 30 hole laminar flow collar of the present invention, the Reynolds Number is set equal to 2000 and the below equation is solved for “D”, where “D” is the ideal diameter for each of the holes in the laminar flow collar using a 15 gallon per minute flow rate.






2000
=




(

999






kg

m
3



)



(
D
)




(

3.15
×

10
-


5



m
3

s


)



π
4




(
D
)

2










1.14
×

10
-


3







N
.
S


m
2








D
=


0.01757





m
×


100





cm


1





m


×


1






in
.



2.54





cm



=

0.6917





inch












It is thus found that each of the 30 holes should have a diameter of approximately 0.6917 inches in order to provide a laminar flow in a septic system having a flow rate of 15 gallons per minute.




Trial Tests for Laminar Flow Collar Using 30 Holes with {fraction (11/16)} Inch and ¾ Inch Diameter Holes




The following equation verifies that a drill bit having a diameter of {fraction (11/16)} inch (0.01746 m) for drilling 30 holes (each having a corresponding diameter of 0.01746 m) in the laminar flow collar of the present invention would not result in a laminar flow (Re<2000).






Re
=





(

999






kg

m
3



)



(

0.01746





m

)




(

3.15
×

10

-
5





m
3

s


)



π
4




(

0.01746





m

)

2










1.14
×

10

-
3









N
.
S


m
2




=
2013











However, a further trial test was performed to determine that a ¾ inch (0.01905 m) drill bit would result in a laminar flow in an embodiment of the laminar flow collar of the present invention using 40 holes (each having a corresponding diameter of 0.01905 m).






Re
=





(

999






kg

m
3



)



(

0.01905





m

)




(

3.15
×

10

-
5





m
3

s


)



π
4




(
0.01905
)

2










1.14
×

10

-
3









N
.
S


m
2




=
1845











In the preferred illustrative examples, a drill bit of less than one inch but greater than or equal to ¾ inches in the examples is preferred to be used in order to drill the holes in the laminar flow collar of the present invention. Thus, a laminar flow collar having either 40 holes or 42 holes (both used with a 25 gallon per minute flow rate) or a laminar flow collar having 30 holes (used with a 15 gallon per minute flow rate) is contemplated for use in the preferred embodiments of the present invention.




However, in further embodiments a laminar flow collar of the present invention may also use 30 holes each having a 1.15 inch diameter and the like (for a 25 gallon per minute flow rate). It is further noted that by using the above equations and knowing the temperature, density and viscosity of the wastewater as well as the Reynolds number and the like, one of skill in the art can easily determine other configurations of the laminar flow collar of the present invention which would provide a laminar flow. Moreover, the spacing between holes may vary, but in the preferred embodiments, the spacing between holes is approximately 0.92 inches for an eight inch diameter collar having 3 rows of 14 holes (total of 42 holes) (The spacing and amount of holes will vary depending on the diameter of the pipe.) The density and viscosity of the wastewater is determined from Table I below.












TABLE I











TABLE A.5






APPROXIMATE PHYSICAL PROPERTIES OF WATER° AT






ATMOSPHERIC PRESSURE


















Specific




Dynamic




Kinematic




Vapor






Temperature




Density




weight




viscosity




viscosity




pressure










kg/m


3






N/m


3






N · s/m


2






m


2


/s




N/m


2


abs.









 0° C.




1000 




9810




1.79 × 10


−3






1.79 × 10


−6






 611






 5° C.




1000 




9810




1.51 × 10


−3






1.51 × 10


−6






 872






10° C. = 50° F.




1000 




9810




1.31 × 10


−3






1.31 × 10


−6






1230






15° C. = 59° F.




999




9800




1.14 × 10


−3






1.14 × 10


−6






1700






20° C.




998




9790




1.00 × 10


−3






1.00 × 10


−6






2340






25° C.




997




9781




8.91 × 10


−4






8.94 × 10


−7






3170






30° C.




996




9771




7.97 × 10


−4






8.00 × 10


−7






4250






35° C.




994




9751




7.20 × 10


−4






7.24 × 10


−7






5630






40° C.




992




9732




6.53 × 10


−4






6.58 × 10


−7






7380






50° C.




988




9693




5.47 × 10


−4






5.53 × 10


−7






12,300  






60° C.




983




9643




4.66 × 10


−4






4.74 × 10


−7






20,000  






70° C.




978




9594




4.04 × 10


−4






4.13 × 10


−7






31,200  






80° C.




972




9535




3.54 × 10


−4






3.64 × 10


−7






47,400  






90° C.




965




9467




3.15 × 10


−4






3.26 × 10


−7






70,100  






100° C. 




958




9398




2.82 × 10


−4






2.94 × 10


−7






101,300  










slugs/ft


3






lbf/ft


3






lbf-s/ft


3






ft


2


/s




psis









40° F.




1.94




62.43




3.23 × 10


−5






1.66 × 10


−5






0.122






50° F.




1.94




62.40




2.73 × 10


−5






1.41 × 10


−5






0.178






60° F.




1.94




62.37




2.36 × 10


−5






1.22 × 10


−5






0.256






70° F.




1.94




62.30




2.05 × 10


−5






1.06 × 10


−5






0.363






80° F.




1.93




62.22




1.80 × 10


−5






0.930 × 10


−5







0.506






100° F. 




1.93




62.00




1.42 × 10


−5






0.739 × 10


−5







0.949






120° F. 




1.92




61.72




1.17 × 10


−5






0.609 × 10


−5







1.69 






140° F. 




1.91




61.38




0.981 × 10


−5







0.514 × 10


−5







2.89 






160° F. 




1.90




61.00




0.838 × 10


−5







0.442 × 10


−5







4.74 






180° F. 




1.88




60.58




0.726 × 10


−5







0.385 × 10


−5







7.51 






200° F. 




1.87




60.12




0.637 × 10


−5







0.341 × 10


−5







11.53 






212° F. 




1.86




59.83




0.593 × 10


−5







0.319 × 10


−5







14.70 














(Engineering Fluid Dynamics, Roberson/Crowe, 4


th


ed., App. A-24)




While the invention has been described in terms of a single preferred embodiment, those skilled in the art will recognize that the invention can be practiced with modification within the spirit and scope of the appended claims.



Claims
  • 1. A laminar flow collar adapted for use in a septic system having a dosing pump, the laminar flow collar comprising:a laminar flow collar cylinder having spaced apart holes, the spaced apart holes having a predetermined diameter which match a pump flow rate of the dosing pump thereby maintaining a laminar flow of effluent flowing within the laminar flow collar cylinder; and a pump cylinder for housing the dosing pump, wherein the laminar flow collar cylinder acts as a receptacle for the dosing pump in the pump cylinder and a guide for proper placement of the dosing pump within a tank.
  • 2. The laminar flow collar of claim 1, wherein the pump cylinder and the laminar flow collar cylinder form a reduced volume area within the laminar flow collar cylinder, the reduced volume area increases a flow rate of the effluent flowing within the laminar flow collar cylinder in order to prevent particulate matter from settling or accumulating at a bottom of the laminar flow collar cylinder.
  • 3. The laminar flow collar of claim 1, wherein:the effluent has a flow rate of 25 gallons per minute; the spaced apart holes have a diameter greater than approximately ⅞ inches but less than approximately 1.15 inches; and the spaced apart holes include one of 30, 40 and 42 holes.
  • 4. The laminar flow collar of claim 3, wherein the spaced apart holes have a diameter of between the range of approximately ⅞ inch to one inch and the spaced apart holes include 40 or 42 holes.
  • 5. The laminar flow collar of claim 3, wherein the spaced apart holes have a diameter of approximately 1.15 inches and the spaced apart holes include 30 holes.
  • 6. The laminar flow collar of claim 1, wherein:the effluent has a flow rate of 15 gallons per minute; the spaced apart holes have a diameter of approximately ¾ inches; and the spaced apart holes include 30 holes.
  • 7. The laminar flow collar of claim 1, wherein the spaced apart holes are located at a certain height such that when the laminar flow collar cylinder is placed in a dosing tank the spaced apart holes are located within clear effluent which is between solid waste settled at a bottom of the dosing tank and scum floating on a surface of the clear effluent.
  • 8. The laminar flow collar of claim 1, wherein the spaced apart holes maintain a laminar flow of the effluent flowing within the laminar flow collar cylinder at a range of flow rates.
  • 9. The laminar flow collar of claim 1, wherein the spaced apart holes are evenly spaced apart from one another.
  • 10. The laminar flow collar of claim 1, wherein the spaced apart holes include multiple rows about a periphery of the laminar flow collar cylinder.
  • 11. A laminar flow collar adapted for use in a septic system having a dosing pump, the laminar flow collar comprising:a laminar flow collar cylinder having spaced apart holes, the spaced apart holes having a predetermined diameter which match a pump flow rate of the dosing pump thereby maintaining a laminar flow of effluent flowing within the laminar flow collar cylinder; and means for uniformly cooling the dosing pump, the cooling means being a pump cylinder which houses the dosing pump within the laminar flow collar cylinder.
  • 12. A laminar flow collar adapted for use in a septic system having a dosing pump, the laminar flow collar comprising:a laminar flow collar cylinder having spaced apart holes, the spaced apart holes having a predetermined diameter which match a pump flow rate of the dosing pump; and a pump cylinder for housing the dosing pump, the pump cylinder fitting partially within the laminar flow collar cylinder, wherein effluent in the septic system flows in a laminar manner through the spaced apart holes in response to suction created from the dosing pump, the spaced apart holes are at a height on the laminar flow collar cylinder such that the spaced apart holes are located within clear effluent when the laminar flow collar cylinder is in a dosing tank.
  • 13. The flow collar of claim 12, wherein:the dosing pump rests at a bottom of the laminar flow collar cylinder, the pump cylinder and the laminar flow collar cylinder form a reduced volume area within the laminar flow collar cylinder, the reduced volume area increases a flow rate of the effluent flowing within the laminar flow collar cylinder such that particulate matter is prevented from settling or accumulating at the bottom of the laminar flow collar cylinder and clogging the dosing pump.
  • 14. The laminar flow collar of claim 12, wherein the location of the spaced apart holes allows for settling of solid waste and sludge at a bottom of the laminar flow collar cylinder.
  • 15. The laminar flow collar of claim 12, wherein the pump cylinder is a cooling tower for cooling the dosing pump within the laminar flow collar cylinder.
  • 16. The laminar flow collar of claim 12, wherein:the effluent has a flow rate of 25 gallons per minute; the spaced apart holes have a diameter between the range of approximately ⅞ inch to one inch; and the spaced apart holes include 40 or 42 holes.
  • 17. The laminar flow collar of claim 12, wherein:the effluent has a flow rate of 25 gallons per minute; and the spaced apart holes have a diameter of approximately 1.15 inches; and the spaced apart holes include 30 holes.
  • 18. The laminar flow collar of claim 12, wherein:the effluent has a flow rate of 15 gallons per minute; the spaced apart holes have a diameter of approximately ¾ inches; and the spaced apart holes include 30 holes.
US Referenced Citations (15)
Number Name Date Kind
RE. 32312 Crates et al. Dec 1986
2173932 Buckley Sep 1939
2605220 Logan Jul 1952
4439323 Ball Mar 1984
5186821 Murphy Feb 1993
5242584 Hoarau Sep 1993
5262065 Hansen Nov 1993
5417553 Gibson et al. May 1995
5492635 Ball Feb 1996
5569387 Bowne et al. Oct 1996
5635064 Bovington Jun 1997
5639366 Bazell et al. Jun 1997
5690824 Stuth Nov 1997
5779896 Nurse, Jr. Jul 1998
5985139 Zoeller Nov 1999
Foreign Referenced Citations (1)
Number Date Country
29668 Nov 1903 CH
Non-Patent Literature Citations (3)
Entry
Steele & McGhee “Water Supply and Sewerage” 5th ed p. 210, 1979.*
Streeter & Wylie “Fluid Mechanics” 8th ed p. 187, 1985.*
Linsley & Frazzini “Water Resources Engineering” 3rd ed p. 434 and 436, 1979.