Wednesday, May 25, 2011

Very amazing software used for drawing longtidunal sections (profiles)


Pipe2CAD is an AutoCAD add-on which can be used efficiently to complete the design work of pipe networks, such as water supply, sanitary sewer, and storm drainage networks.
After finishing the hydraulic design of your pipe networks with any of the available hydraulic design packages, networks are easily imported into Pipe2CAD environment to proceed with all subsequent design steps. From checking interference points and conflicts between different networks, verification of low and high points in pressure networks, and editing networks by adding, deleting, or adjusting pipes; to finally producing fully formatted plan views and longitudinal profiles, ready for submission.
  

For any questions don’t hesitate to ask me  

Design of Sewers part 2


Sewer Appurtenances

Sewer appurtenances are the various accessories on the sewerage system and are necessary for the efficient operation of the system. They include man holes, lamp holes, street inlets, catch basins, inverted siphons, and so on.

Man-holes: Man holes are the openings of either circular or rectangular in shape constructed on the alignment of a sewer line to enable a person to enter the sewer for inspection, cleaning and flushing. They serve as ventilators for sewers, by the provisions of perforated man-hole covers. Also they facilitate the laying of sewer lines in convenient length.

Man-holes are provided at all junctions of two or more sewers, whenever diameter of sewer changes, whenever direction of sewer line changes and when sewers of different elevations join together.

Special Man-holes:

Junction chambers: Man-hole constructed at the intersection of two large sewers.

Drop man-hole: When the difference in elevation of the invert levels of the incoming and outgoing sewers of the man-hole is more than 60 cm, the interception is made by dropping the incoming sewer vertically outside and then it is jointed to the man-hole chamber.

Flushing man-holes: They are located at the head of a sewer to flush out the deposits in the sewer with water.

Lamp-holes: Lamp holes are the openings constructed on the straight sewer lines between two man-holes which are far apart and permit the insertion of a lamp into the sewer to find out obstructions if any inside the sewers from the next man-hole.

Street inlets: Street inlets are the openings through which storm water is admitted and conveyed to the storm sewer or combined sewer. The inlets are located by the sides of pavement with maximum spacing of 30 m.

Catch Basins: Catch basins are small settling chambers of diameter 60 - 90 cm and 60 - 75 cm deep, which are constructed below the street inlets. They interrupt the velocity of storm water entering through the inlets and allow grit, sand, debris and so on to settle in the basin, instead of allowing them to enter into the sewers.

Inverted siphons: These are depressed portions of sewers, which flow full under pressure more than the atmospheric pressure due to flow line being below the hydraulic grade line. They are constructed when a sewer crosses a stream or deep cut or road or railway line. To clean the siphon pipe sluice valve is opened, thus increasing the head causing flow. Due to increased velocity deposits of siphon pipe are washed into the sump, from where they are removed.

Pumping of Sewage

Pumping of sewage is required when it is not possible to have a gravitational flow for the entire sewerage project.

Sufficient pumping capacity has to be provided to meet the peak flow, atleast 50% as stand by.

Types of pumps :
Centrifugal pumps either axial, mixed and radial flow.
Pneumatic ejector pumps.




Design of Sewers part 1


Design of Sewers

The hydraulic design of sewers and drains, which means finding out their sections and gradients, is generally carried out on the same lines as that of the water supply pipes. However, there are two major differences between characteristics of flows in sewers and water supply pipes. They are:
The sewage contain particles in suspension, the heavier of which may settle down at the bottom of the sewers, as and when the flow velocity reduces, resulting in the clogging of sewers. To avoid silting of sewers, it is necessary that the sewer pipes be laid at such a gradient, as to generate self cleansing velocities at different possible discharges.
The sewer pipes carry sewage as gravity conduits, and are therefore laid at a continuous gradient in the downward direction upto the outfall point, from where it will be lifted up, treated and disposed of.

Hazen-William's formula

             U=0.85 C rH0.63S0.54

Manning's formula

             U=1/n rH2/3S1/2

where, U= velocity, m/s; rH= hydraulic radius,m; S= slope, C= Hazen-William's coefficient, and n = Manning's coefficient.

Darcy-Weisbach formula

             hL=(fLU2)/(2gd)

Minimum Velocity

The flow velocity in the sewers should be such that the suspended materials in sewage do not get silted up; i.e. the velocity should be such as to cause automatic self-cleansing effect. The generation of such a minimum self cleansing velocity in the sewer, atleast once a day, is important, because if certain deposition takes place and is not removed, it will obstruct free flow, causing further deposition and finally leading to the complete blocking of the sewer.

Maximum Velocity

The smooth interior surface of a sewer pipe gets scoured due to continuous abrasion caused by the suspended solids present in sewage. It is, therefore, necessary to limit the maximum velocity in the sewer pipe. This limiting or non-scouring velocity will mainly depend upon the material of the sewer.

Effects of Flow Variation on Velocity in a Sewer

Due to variation in discharge, the depth of flow varies, and hence the hydraulic mean depth (r) varies. Due to the change in the hydraulic mean depth, the flow velocity (which depends directly on r2/3) gets affected from time to time. It is necessary to check the sewer for maintaining a minimum velocity of about 0.45 m/s at the time of minimum flow (assumed to be 1/3rd of average flow). The designer should also ensure that a velocity of 0.9 m/s is developed atleast at the time of maximum flow and preferably during the average flow periods also. Moreover, care should be taken to see that at the time of maximum flow, the velocity generated does not exceed the scouring value.



WORLD’S LARGEST WATER TREATMENT PLANT OPTIMIZES PROCEDURES BASED ON ALGOR FLUID FLOW RESULTS

Nearly one billion gallons of water are processed on an average day at James W. Jardine Water Purification Plant, which is located next to Navy Pier in Chicago, Illinois. This plant and the South Water Purification Plant serve nearly 5 million consumers in the City of Chicago and 118 outlying suburbs. Engineers at the plant are using ALGOR’s complete suite of simulation tools to formulate modifications that improve the water purification process.
Nearly one billion gallons of water are processed on an average day at the James W. Jardine Water Purification Plant in Chicago, Illinois, the largest water treatment plant in the world. This plant and the South Water Purification Plant serve nearly 5 million consumers in the City of Chicago and 118 outlying suburbs. With that volume of water to purify, the chemical treatment process must be as efficient and effective as possible. Recently, the Jardine plant needed to change the location at which activated carbon is added in order to increase its contact time with water. Engineers at the plant studied the water flow patterns in the intake area with ALGOR’s Fluid Flow Analysis software to find the optimal feed point at which to add the carbon so that dispersion time would be minimized. 
Approaching this challenge with computer simulation tools diverges from the water industry’s standard practice of building scale models and performing tests in a laboratory. The use of ALGOR’s Fluid Flow Analysis software enabled water plant engineers to determine the best location for the activated carbon feed point in less time and with less expense than would have been possible with a traditional, laboratory testing approach. 

The First Step in a Seven-Hour Water Purification Process

There are a number of steps in the 7-hour water purification process, which consists of chemical treatment with activated carbon, polyphosphate, chlorine, fluoride, alum (aluminum sulfate) and polyelectrolyte, followed by sedimentation and filtration. Each chemical additive serves a different purpose, such as killing bacteria, aiding in the removal of micro-organisms or preventing tooth decay. Activated carbon is the first chemical treatment, added to remove objectionable tastes and odors. The tiny carbon particles are tremendously absorbent, like a sponge. In order for it to do its job, the activated carbon must mix thoroughly within the water for as long as possible. 
Adding activated carbon to lake water is the first step of many in the 7-hour water purification process. The diagram above shows a generalized, schematic view of the process used by the City of Chicago Department of Water to purify Lake Michigan water. Activated carbon is used to remove objectionable tastes and odors and must mix thoroughly within the water for as long as possible in order to be effective.

 In the late 1990s, engineers for the City of Chicago Department of Water determined that the activated carbon feed should be moved to the intake basins through which lake water enters the plant. Each spring, plant workers drain and clean each of the two intake basins. Water plant workers have only a short window of time each year to clean the basins and make any needed modifications. The activated carbon feed line was extended and mounted on the inside wall of each intake basin, over a small ledge – a location that was selected for installation convenience. 
This modification achieved the goal of increasing contact time that the carbon has with the water. Next, Department of Water Filtration Engineer Anthony Wietrzak, Ph.D., P.E. turned his attention to the challenge of optimizing the dispersion and mixing of carbon within the water. This challenge required Wietrzak to study the hydraulics of the water flow within the intake basin. 
“The water industry’s standard practice for approaching such a problem is to build a scale model and perform tests in a laboratory,” said Wietrzak. “Unfortunately, this process is time-consuming and expensive. Chicago’s Bureau of Water Treatment engineering section at the Jardine Water Purification Plant acquired ALGOR’s Professional Multiphysics software package several years ago to provide computer simulation tools for just such a challenge.” In addition to the unsteady laminar fluid flow analysis capabilities Wietrzak would use for this project, the Professional Multiphysics package also offers static stress with linear and nonlinear material models, Mechanical Event Simulation with linear and nonlinear material models, steady and unsteady laminar fluid flow analysis with turbulence, steady-state and transient heat transfer analysis, electrostatic analysis, vibration analysis and the capability to consider the effects of multiple physical phenomena.

Pump Cells Analyzed to Determine Inputs for the Intake Basin Model

To analyze the flow pattern within the intake basin, Wietrzak had to start with the physical characteristic of the system that he knew quantitatively: the capacity of each of the pumps that pulls water from the intake basin into the water treatment plant and the physical dimensions of the intake area. Wietrzak did not want to assume that the flow was uniform coming out of the intake basin. That assumption could result in an unrealistic flow pattern within the intake basin. Thus, he would have to model the pump cells in addition to the intake basin. However, modeling both the pump cells and the intake basin would result in a very large model. Wietrzak was concerned that his computer hardware would not process such a large model and achieve solution convergence in a reasonable amount of time. Therefore, Wietrzak decided to model and analyze one pump cell and the intake basin separately. The pump cell model results at the boundary between the intake basin and the pump cell would determine the input for the intake basin model. 
Wietrzak began by modeling the volume within a pump cell in Superdraw III, ALGOR’s precision finite element model building tool. The pump cell model resulted in 6,492 solid “brick” elements. Wietrzak applied zero velocity constraints to the surfaces on the walls of the pump cell. To the free surface at the top of the pump cell, he applied a zero shear constraint. Next, Wietrzak converted the pump capacity of 300 million gallons per day to a volumetric flow rate in feet per second. The flow rate was then applied to the pump cell outlet as a velocity boundary constraint. No constraints were placed on the inlet to the pump cell. 


An unsteady fluid flow analysis was performed on the pump cell model with the applied velocities ramping up over 50 time steps. Performing an unsteady fluid flow analysis and ramping up the velocities over time facilitated convergence.

Wietrzak first analyzed one of the pump cells that pulls water out of the intake basin and into the water treatment plant. The known pump capacity was used as the input to the analysis in order to find the velocity profile at the inlet to the pump cell. The sketch shows where the water enters and exits the pump cell (upper left) while the velocity contour resulting from the ALGOR fluid flow analysis shows the fluid dynamics within the volume of the pump cell. 

“The largest assumption I made for the pump cell model is that the flow is uniform coming out of the pump,” said Wietrzak. “I ran several variations of the pump cell model in which I varied the outlet velocity constraints at the pump discharge and none made a significant difference in the velocity profile at the inlet to the pump cell. All models yielded higher velocities at the top of the entrance and lower velocities near the bottom. Since I was concerned only with the velocity profile boundary condition at the outlet of the basin (which is also the inlet to the pump cell), I am satisfied that this is a sensible assumption.”
Running several variations on the pump cell model gave Wietrzak the opportunity to experiment with different model constraint techniques and gauge the effectiveness of those techniques in terms of model convergence. “I know the theory and how to handle problems with a textbook approach. However, there were several constraint techniques that I needed to learn in order to run this model and get realistic results,” said Wietrzak, who holds a Ph.D. in fluid dynamics from Northwestern University. “For example, the free surface boundary condition had to be properly applied in order to get the solution to converge. ALGOR’s technical support team was very helpful in answering any questions that arose during the solution process.” 

Intake Basin Model Reveals the Need to Change Activated Carbon Feed Point




Armed with the results of the pump cell fluid flow analysis, Wietrzak was ready to tackle the intake basin model. He began by modeling the volume within the basin in Superdraw III, a model which resulted in 8,138 solid “brick” elements. As with the pump cell model, Wietrzak applied zero velocity constraints to the surfaces on the walls of the basin and zero shear constraints to the free surface. The velocity results of the pump cell analysis were then applied to the area where the basin connects to the pump cells. An unsteady fluid flow analysis was performed on the intake basin model with the applied velocities ramping up over 50 time steps. 
The simulated velocity profile at the inlet to the pump cell was applied to the intake basin model. The sketch shows where the water enters and exits the intake basin (upper left); the location of the original activated carbon feed point (Add Point 1); and the location of the new feed point based on analysis results (Add Point 2). The velocity contour resulting from the ALGOR fluid flow analysis shows the fluid dynamics within the volume of the intake basin. 

Wietrzak then studied the simulated flow patterns by slicing through the model layer by layer and viewing the flow patterns throughout the model. He also used animated analysis replays to see how the solution progressed over time. He discovered a recirculation pattern next to the wall, very near to the current feed point. “The feed point is located above a narrow ledge,” describes Wietrzak. “The flow pattern predicted that the carbon would tend to be dragged along the ledge rather than mixing quickly and thoroughly with water throughout the volume of the basin. Our observations of the carbon deposits qualitatively confirmed the fluid flow analysis results.”
Wietrzak therefore determined that the activated carbon feed pipe should be moved out between 5 and 10 feet from the wall in order to maximize mixing. This modification was implemented in one of the two intake basins in the Spring of 2000. 
Wietrzak has also used the ALGOR Multiphysics package to model other areas of the plant that may benefit from modifications. For example, since completing the activated carbon feed point project, Wietrzak has studied the effectiveness of the air scrubber system on exchanging the air in the chlorine battery room, from where chlorine is supplied for the treatment process. The scrubber releases caustic gas to neutralize airborne chlorine. Wietrzak used fluid flow analysis to find the “dead spots” in the air flow. 
“We do not redesign everything, but ALGOR’s complete suite of simulation tools is enabling us to formulate modifications that improve the water purification process,” said Wietrzak. “The variety of simulation tools offered by the Professional Multiphysics package will enable us to study many phenomena on the computer and make many enhancements without the need for laboratory testing.”

Sewage Water Treatment


There are many Chemical Physical and Biological methods for treatment of aqueous waste waters. Most combination of these chemical, Physical and biological treatments is necessary to remove contaminants effectively.
The method has to be determined based on the requirement of the waste water and its contaminants.
Simple Household Sewer Treatment
Septic system:  Though simple but very important system covering rural and urban areas in most of the developed and under developing countries.
Septic systems are constituted of number pipe lines by which the house hold aqueous waste water is drained to a series of tanks which are connected by pipe lines. The first tank is connected to inlet line and the last to outlet.
The septic tank has two chambers usually each with manhole and separated by a wall that has opening on the roof and floor of the tank.
The household waste water enters the first chamber of the first tank; at this point, the solids settle to the bottom and the scum floats to the top. The solids are settled and digested, which lessens the content of the tank. The remaining liquid flows through the dividing wall and into the second chamber. Here, further settlement takes place so that the excess liquid becomes nearly clear and empties into the drainage field, also known as the leech field. The remaining impurities of the water are then broken down into the soil and taken to irrigate plants around.

Conventional Municipal Waste Water Treatment


Conventional municipal waste-water treatment, preliminary steps include, screening to remove large solids. Grit removal to protect mechanical equipment against abrasive wear

Flow measuring and pumping to lift the waste water.
Primary treatment is to remove settle able organic matter accounting to percent of suspended solids and scum.
Secondary treatment is by aeration in open basins with return biological solids or fixed media followed by final setting excess microbial growth settled out in the final clarifier is wasted while the supernatant is disinfected with chlorine prior to discharge to a receiving water course.
Waste sludge’s from primary settling and secondary biological flocculation are thickened and dewatered for preparation to disposal.
Anaerobic bacterial digestion may be used to stabilize the sludge prior to dewatering.
The overall process of conventional waste water treatment` can be viewed as, thickening: to percent depending upon the plant Solvents moved from solution are concentrated in a small volume convenient for final disposal.
The contribution of raw sanitary waste water is about gallons per person with a total solid content of 0.1 percent.
240mgs/l suspended solids.
200 mgs of B.O.D
Liquid waste sludge is withdrawn from primary and secondary processing amounts to approximately 2l/persons with a solids content of 5 percent by weight.
This is further concentrated to handle able material by mechanical dewatering, the extracted water is returned for reprocessing. Cake , amounts to about 1/3l/l  with a 30 percent solid concentration from vacuum filter which is used in large plants to extract water directly  from raw sludge.
This type of physical -biological scheme is effective in reducing the organic content of waste water and the main objective is maximum reduction of suspended solids and BOD

Sewage Definition


Sewage water is generated from domestic, factories and agricultural activities. Domestic waste water is called as sewage

Sources of sewage
Sources of sewage
  • waste water from kitchen and bathroom is called gray-water or sullage
  • waste water from toilet is called excreta or black- water
Sewage water consists of 99.3 to 99.7 % of liquid state and 0.3 to 0.7% of solids state.
The solids present in the sewage water are of two types
  1. Organic solids
  2. Inorganic solids.
Organic solids are the substances derived from living things like produces from plant and animal. The organic solids undergo decomposition by the microorganisms.
Examples : carbohydrate, protein & fat.
Inorganic solids are inert materials that they do not undergo decomposition by the microorganisms and are inert fixed solids.
Examples: Grit, Salt, Chemicals, Metals etc.
These two states are mainly degradation of the environment if they are discharged into the environment as such.
If these solids are removed  from the sewage water by Treatment process the water can be reclaimed and reused.
Composition of Sewage
Composition of Sewage