MBBR OM Manual-250

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1 OPERATION AND MAINTANANCE MANUAL FOR EEC HIGH SPEED BIO TEC SYSTEMS MODEL 33CON 3 2*250 m3/day SEWAGE TREATMENT PLANT FACILITY SABAA AKBAR IRAQ SUBMITTED BY E.T.A. Zenath ENVIRONMENTAL ENGINEERING SERVICE LLC. POST BOX NUMBER 7113 DEIRA, DUBAI. United Arab Emirates Tel: +9714-2713006 Fax: +9714-2713487 Email: [email protected] www.etazenath.com www.eecme.com

Transcript of MBBR OM Manual-250

1

OPERATION AND MAINTANANCE

MANUAL FOR EEC HIGH � SPEED BIO TEC SYSTEMS MODEL 33CON 3

2*250 m3/day SEWAGE TREATMENT PLANT

FACILITY

SABAA AKBAR

IRAQ

SUBMITTED BY E.T.A. Zenath ENVIRONMENTAL ENGINEERING SERVICE LLC.

POST BOX NUMBER � 7113

DEIRA, DUBAI. United Arab Emirates

Tel: +9714-2713006 Fax: +9714-2713487 Email: [email protected]

www.etazenath.com www.eecme.com

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CONTENTS SECTION 11.. CCOOMMPPAANNYY PPRROOFFIILLEE

22.. IINNTTRROODDUUCCTTIIOONN

33.. DDEESSIIGGNN BBAASSIISS

44.. WWAATTEERR AANNAALLYYSSIISS

55.. PPRROOCCEESSSS DDEESSCCRRIIPPTTIIOONN

66.. SSYYSSTTEEMM OOPPEERRAATTIIOONN

77.. CCOOMMPPAARRIISSOONN DDAATTAASSHHEEEETT

88.. BBIILLLL OOFF MMAATTEERRIIAALLSS

99.. TTEECCHHNNIICCAALL DDAATTAASSHHEEEETTSS && CCAATTAALLOOGGUUEESS

1100.. DDRRAAWWIINNGGSS 1111.. TTRROOUUBBLLEE SSHHOOOOTTIINNGG GGUUIIDDEE

1122.. MMAAIINNTTAANNCCEE SSCCHHEEDDUULLEE

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1. Company Profile

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PROFILE

EEC - ME, a part of the large and diversified ETA-Ascon, a 30 years old group, again

part of Al Ghurair Group. Also, we present you with our professional team of people,

which has provided you with the best technical and professional assistance for a total

waste management / water treatment program, especially in the field of desalination

(RO), sewerage and industrial water along with the most reputed and specialized

American and European companies in this field. EEC - ME fields of concentration

are:

1 Industrial Water: We provide you with the design study and installation for most if not all-industrial water treatment. This water for the most part can be recycled back into the plant and can make tremendous saving to the companies.

2 General and Sewerage Water: This water can be treated for irrigation use, or some of it can be circulated back into the bathrooms for flushing purposes- saving hotels and labor camps a lot of money.

3 Desalination and Brackish Water Treatment: If you are looking for fresh,

potable water, EEC - ME can provide you a Membrane desalination plant designed to your particular needs and requirements. This can be either Seawater or Well Brackish Water.

4 Total Waste Management: EEC - ME with corporation with other ETA

divisions and other international companies can provide you with design implementation and operation of a total waste management for your community or city.

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EEC - ME are joining hand with a list of specialist and reputed companies in the field of

water treatment from USA and Finland such as, Environmental Equipment Consulting,

EEC, USA; Enviro-Chemie, Germany; IPM, Germany. With our extensive experience in

the Environmental / Water Treatment field in the USA, coupled with long and acclaimed

work history of ETA-Ascon Group and the help of the group of specialist with which we

have joined, we believe we provide Companies / Industries in the Middle East with the

best, most economical way for a total water and waste water management.

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2. Introduction

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INTRODUCTION

The ever stricter requirements that industry around the globe has to meet in regard to

the use of the natural resource water are boosting the demand for profitable, low-cost

and highly efficient sewerage / waste water treatment systems. Copying nature�s

fascinating capabilities as perfectly as possible and harnessing them for our technical

applications is the source of innovative renewal processes. Nature shows us in an

exemplary manner that organic matter contained in water can be converted biologically

into energy-rich and utilizable.

EEC ME shall provide you an efficient, cost effective, time saving solution for any water

needs, especially the waste and sewage treatment systems. AMB BIOMEDIA ensures

that the system footprint is five times smaller and ten times faster than regular treatment

plants.

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3. Design Basis

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DESIGN BASIS

The basic design and the processes use stichomythic factors to alter the concentrations

of the materials involved. As a result of the high level of process linkage, a material can

be of decisive importance to several processes in the model. Should an alteration in the

concentration of this material occur due to one process, and then the processing speed

of another will be influenced, which in turn, has consequences for the entire system.

We have assumed wastewater fully domestic in character from residential application

and that metal contents documented in the consent for discharge would not be present

in any higher amount in the influent and therefore will not present in the effluent. Based

on this assumption we have not allowed for any removal of inorganic material and metals

from the wastewater. We have also assumed the 2*250 m3/day in the residential area

and have allowed a flow of 200 liter per person per day and BOD of � 300 mg/liter in the

influent.

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4. Water Analysis

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WATER ANALYSIS

Flow Profile 1. Capacity 2*250 m3/day 2. Max. Hourly flow 2*11.36 m3/hr 3. Peak flow factor 2.5 4. Plant offered 2*33 con 3 (Max Capacity � 600m3/day) Influent Parameters of Waste water 1. Nature of influent Raw Domestic Waste Water

2. BOD5s 350 � mg/l

3. COD 500 � mg/l

4. Total Suspended Solids 300-400 � mg/l

Quality of Treated Water 1. BOD Less than or equal to 20 mg/l

2. TSS Less than or equal to 30 mg/l

3. pH 6 � 9

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5. Process Description

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PROCESS DESCRIPTION

The treatment of the sewage water designed for this system can be broken down into

following phases.

Treatment scheme They are;

A. Inlet screening includes manual Bar screen

B. Pre clarification (Buffer or feed / sludge)

C. Mechanical � Biological Sewage Treatment plant � MBBR

a. Bio � reactor - 2 nos

b. Settling / Clarifier - 1 nos

D. Post Treatment includes Chlorination System

E. Irrigation Pumps.

A. BUFFER SYSTEM This will be a construction of three chambers forming the Buffer & Pump well system.

The wastewater will first pass though the Barscreen chamber before it enters into

equalization tank; this separates all solids above 10 MM like, plastics, sanitary pads,

bags etc.

Buffer tank have been aerated continuously with the help of coarse bubble diffusers in

order to keep the particles in suspension. It also helps to avoid wastewater turning

septic. Buffer chamber will avoid any excess oil entering into the pump well chamber

which in turns affects the treatment process.

Note: Buffer tank is continuously aerated, so if you can add the septic sewerage into it, it

will take care of initial polishing and avoid any bad smell so that it won�t have any

negative affect when it enters the Bioreactor. This is achieved by the aeration, the

dilution with sludge that has not turned septic and the time taken by this sewage to enter

into the MBBR plant.

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B. BIOLOGICAL TREATMENT SYSTEM The treatment plant will take suction from the pump well by its own feed pump. The

pump is level controlled and has a capacity, which is 2 times the average daily flow. The

plant has therefore intermittent working mode in terms of hydraulic flow, while the air

blower supplying air to the bioreactor is continuously running.

The biodegradation reactor comes in three stages. The bioreactors degrade the

dissolved organic matter by oxidation into carbon di oxide, which escapes to the air, and

also a biomass, which acts as an activated sludge. A suspended, free-floating bio film

carrier provides a large protected surface as host for the bacteria and simultaneously

active bio sludge accumulates inside the reactors.

The biodegraded water flows into a clarification chamber where the suspended solids

settle by gravity. The water is directed through a skim well to a Tube settler system,

which provides the final clarification of the effluent. An addition of polymer to the

sedimentation may enhance the cleaning/ settling efficiency if it is required.

C. SLUDGE SEPERATION SYSTEM

The sludge pump will be activated for approximately 5 minutes for every 1 hrs of

operation with suction from the clarification stage. The pump causes the discharge of the

sludge through a hydrocyclone, which separates volatile and non volatile solids with an

overflow back to the bioreactor, while the underflow is discharged to the Equalization

tank. Feed pump will stop whenever sludge pump is working. When necessary, the

sludge is emptied by a vacuum truck and hauled away for disposal.

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6. System Operation

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SYSTEM OPERATION

Moving Bed Process Technology Using AMB Bio Media. Description of the moving bed process

The basic principal of the moving bed process is the growth of the biomass on plastic

supports that move in the biological reactor via agitation generated by aeration systems

(aerobic reactors) or by mechanical systems (in anoxic or anaerobic reactors). The

supports are made from plastic with a density close to 1 g/cm3 letting them move easily

in the reactor even when the capacity reaches 70%.

The moving bed processes come from the current trend in wastewater treatment, from

the use of systems that offer an increased specific surface in the reactor for the growth

of the biomass, achieving significant reductions in the biological reactor volume.

Initially fixed bed systems were used, however it was discovered that this type

of process show a series of operational inconveniences such as the blocking of the bed

because of the excessive growth of the biomass, this makes periodical cleaning

obligatory. These drawbacks have caused the need for the creation of simple biofilm

processes that eliminate them and that ease their operation; these are the moving bed

processes.

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This type of process can be applied both to treatment plants for the biodegradation of

organic material as well as for installations with nutrient elimination, in urban and

industrial wastewaters. Another application is the use of this technology in the redesign

of current activated sludge processes, which only treat organic material, to expand them

and include simple nitrogen elimination without the need to construct new biological

reactors.

With respect to the aeration system is via a grid of perforated stainless steel tubes that

avoid problems of efficiency loss, diffuser replacement, etc.

All the wastewater is collected in a 3 chamber Equalization tank. This tank acts as a

balancing reservoir, keep the wastewater in suspension and bar screen used to

separate solids, paper and other waste to be received with the wastewater. The last

chamber of this tank is fitted with a level control system, which starts or stops the

system feed pump. The feed pump takes suction from the last and discharges in to the

first chamber of the High-Speed Bio Tec.

The first and the second chamber of the High-Speed BioTech are filled with AMB Bio

media and water. The last chamber, which is a Tube settler, is filled with water only.

Before starting pumping of wastewater, the system blower starts. The blower forces air

through the manifolds into the first 2 chambers of the bio system and the equalization

chamber.

The influent wastewater enters the first chamber and comes in constant with the AMB

Bio Media and air Large Surface area provided by the AMB Bio Media helps the

bacteria to form large colonies on the AMB Bio Media. Slow circular motion of the

media is caused by the airflow. Each element of the media slowly moves in a circular

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motion from the surface to the bottom and then upward again. During this movement, it

is in constant with the injected air, slowly a bio film develops over each element, which

disintegrates the biomass present in the effluent.

From the first chamber the effluent flow to the second chamber through the perforated

partition at the top. The same treatment is repeated in this chamber and the remaining

biomass from the first chamber gets fully digested here, effluent at this stage will go to

the 3rd Biodegradation chamber. The treated water then enters the third chamber at the

top.

A baffle plate guides the water entering the third chamber downwards. Then enters the

tube settler from the bottom. The settler provides a large surface area for the

suspended particles to settle down on its surface and the same area guided towards

the bottom. Clean water is let out of the system from the outlet provided at the top of

the third chamber.

When the level of the influent drops in the collection tank the feed pump gets tipped.

Simultaneously the sludge pump is started. The sludge pump draws sludge from the

bottom of the 3 chambers and discharges it into a Hydro-cyclone separates our heavier

sediments from the sludge, which settles in the collection tube mounted at the bottom of

the hydro-cyclone. Clarified water is discharged back into the first chamber of the

bioreactor. The sludge pump operates for pre-set time and is stopped automatically.

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The solid sludge accumulated in the sludge collection tube is discharge out periodically.

This sludge can be used as manure or for land farming.

High-Speed Bio System should not compare with regular job systems (activated sludge)

as we implemented a leading technology known as �Assisting Moving Bed� or AMB Bio

Media. These systems are designed to handle sewer (black and Grey water) and most

biological wastewater from industrial application.

The AMB Bio Media represents 850 sqm / cum active area once submerged inside the

bio chambers. Activated sludge process and other bio film systems have often proven to

the unstable and difficult to control. By implementing the AMB Bio Media, your benefits

are numerous including reliable and compact bioreactors. The systems are self-

cleaning, non-clogging, can handle server BOD loading, pH variations, and colder

temperatures than regular systems, all this without loss of bioactivity. No sludge return

as in activated sludge system and our systems require minimum service and almost no

attention.

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7. Manual Description

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MANUAL DESCRIPTION

This manual describes the function, operation procedures, maintenance, and installation

requirement for the HIGH-SPEED BIOTECH reactor.

NOTES, CAUTIONS and WARNINGS are included in the Operating Procedures. They

should be interpreted as follows:

"NOTE� indicates an operating procedure or condition that is essential to highlight or

which provides a given procedure.

"CAUTION" indicates an operating procedure or practice that, if not strictly observed,

may result in damage to or destruction of equipment, or degradation of the water quality.

"WARNING" indicates an operating procedure or practice that can result in bodily injury

or loss of life if not correctly followed.

NOTES, CAUTIONS and WARNINGS always precede paragraphs to which they apply.

Under normal operating conditions, adherence to the procedures described in this

manual will assure trouble -free operation.

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8. Installation & Start up

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INSTALLATION OF HIGH SPEED BIO-TECH REACTOR The High Speed BIOTECH Bio reactor containers require properly leveled ground,

preferably concrete slab with drain facility or properly graveled. The High Speed

BIOTECH reactor must be carefully water leveled before commissioning and checked for

deviation afterwards. Otherwise national safety regulation must be adhered to. A

wastewater pond or buffer tank should be provided upstream of the plant. The pond

should be sized as to level out daily variation in hydraulic load and is to be arranged for

returns of reject water from the plant.

Downstream sludge receiving tank or pond must be provided, the daily produced sludge

and the haul away regularity determine the size of which. Local regulations with respect

to handling and disposal of sludge will determine any further treatment of the sludge.

WARNING

A qualified electrician in accordance with pertinent codes and regulations must perform

electrical installation and connection to the main power source. Turn off facility power

before making any electrical connections. System must be grounded in accordance with

applicable electrical codes.

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THE AMB-BIOMEDIUM

The AMB bio film mediums are a proprietary bio medium. The Bio medium is produced

of plastic material, which has long lifetime in water. Renewal of the Bio medium during a

treatment plant's regular lifetime should normally not be required.

The bio film carrier elements are extruded tube cuttings with an internal cross and have

25 external low fins. Nominal measurements are Diameter 1/2�, Length 3/8�. The surface

to volume ratio is approx. 850 m² per m3 of Bio medium in bulk.

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BIOMEDIUM FILLING PROCEDURES (Only applicable for media delivered in bags and separate from system.)

Preparations

Before filling-up and start-up the following preparations to be done:

1. Check that the air holes in the Spurger pipes are facing downwards. If not, drill ½

inch drain holes in each end of the spurges.

2. Check that the bulkhead strainers are positioned correctly and sufficiently secured

3. Check that there are no openings outside the strainers that the biomedia can

penetrate and also no passage for biomedia above the bulkheads where biomedia

can be carried over by eventual foaming. Any gaps to be less than ½�.

4. Start the air blower(s) against open-air valves, and throttle gradually. Listen for

unexpected noises from motor and housing. Run finally the blower(s) against closed

valves for a short time and note the discharge pressure. The discharge pressure

should be not less than 1.5 times the operating water head.

5. Fill the bio reactors with ½ of water, run the air blower from zero to low capacity and

check that the air diffusers are delivering equal and uniformly distributed amount of

air from each Spurger.

6. Start and run the sludge pump in recirculation mode, with successive suction from all

drain valves. Check that the flow is equal from each drain. Checks that the drain

suctions in the bioreactor tanks are enclosed in strainers to prevent biomedia from

entering the pump suction.

7. Start the feed pump with closed discharge valve and note the pump pressure. Open

the discharge valves fully and note full flow and discharge pressure.

8. Start the chemical pumps on water and check capacity.

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Charging of biomedia

New Bio medium will repels water and must go through a wetting procedure before it will

properly mix in water:

1. Add wastewater to until overflow to the settling tank. Start up the blower(s) and

aerate moderately with ¼ to ½ of normal capacity.

2. Fill biomedia until the bulkhead screens are covered. Aerate continuously during the

filling.

3. Top up with remaining biomedia as space allows. If actual filling degree in the

reactors is 50% or less, then the whole amount of biomedia can be filled in one

charge.

4. Continue aeration until good mixing is obtained, meaning visible movement of

biomedia in the surface.

5. Charge more wastewater while recirculating from the settling tank. When the settling

tank is filled, increase aeration as the water level is increasing in all tanks. Aerate

moderately, just enough to have the media circulating in the reactors.

NOTE

Good mixing is normally obtained after 2 - 3 days on usual municipal wastewater. In the

beginning there will be an almost immobile blanket of biomedia on the surface, while

there will be a good mixing below this blanket and down to the bottom.

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START UP PROCEDURES

When the media wetting procedure is completed, the reactors are ready for start

up

Municipal wastewater will contain sufficient degrading type bacteria to develop a healthy

bioculture in the reactors without being specifically seeded. Hence, during wetting, the

bioculture will already have started to grow. This can be observed visually by a slight

change in turbidity and pH, usually 1-2 days after completion of wetting.

1. Run the plant on recirculation for 1 or 2 days after wetting. Use the feed pump

instead of the sludge pump. Note the pH and observe any changes. The pH will

first go down during the acidic stage, and then up again as the degradation is

being completed.

2. When the pH is on way back to its initial value, add more wastewater. Change to

recirculation with the sludge pump and shift feed pump suction to the feed tank.

Add a volume corresponding to approx. 1/3 of the total volume.

3. Changes back to recirculation with the feed pump and observe pH again. Repeat

above procedures, and observe the time between each charging.

4. When the time between charging is decreasing, the plant is ready for continuous

operation.

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BIOFILM GENERATION Time for generation of a bio film on the carrier elements will vary depending on type of

wastewater and the temperature:

Municipal wastewater 3 - 4 week

Food industry 1 - 2 weeks

Paper/pulp industry 3 - 4 days

As time goes by, the bio film will develop and become more efficient and robust. It will

reach its maximum capacity after one year of normal operation.

FOAM CONTROL

During start-up of bioreactors, when establishing bio film on the plastic elements,

foaming may occur. Also greater load variations in fully developed reactors may result in

foaming.

Foaming is caused by surface tensions in the wastewater. Reducing aeration and waste

charging reduces foaming during start up. Foaming in a started reactor is reduced by

combined recirculation and feeding. Foaming in a correctly dimensioned bioreactor,

running on municipal wastewater should normally not occur. However, the wastewater

may contain substances, which make foaming unavoidable.

Sustained foaming during operation may be controlled either by spraying or by chemical

injection. Any available antifoam agent will normally do.

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SHUT-DOWN AND RESTART

If it becomes necessary to stop the load on the bioreactors for a shorter period, for

instance one-week, all reactors should be moderately aerated to keep aerobic biomedia

condition.

If it becomes necessary to stop the load on the bioreactors for a longer period, it is

recommended to aerate the reactors the first week after the stop, and to restart aeration

2 days before the reactors are re-loaded with organic matter.

Before wastewater again can be pumped to the biological stage, it is important that all

the biomedia is in good suspension in all bioreactors first.

NOTE

Always remember first to stop and start the aeration before stop and start the water

flow.

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COMPARISON OF ACTIVATED SLUDGE / SBR PROCESSES TO HIGH SPEED BIO TECH PROCESS.

FEATURES ACTIVATED SLUDGE

PROCESSES / SBR PROCESSES

HS HIGH SPEED BIO TEC.

AMB BIO ELEMENTS NON CLOGGING MEDIA

Footprint Large Small or 1/5

Sludge return required Yes-sludge Bulking No-no sludge Bulking

High BOD Loading Sensitive Not sensitive to high BOD

Size Not Modular Modular

Containerized No Yes

Sensitive to pH Yes No

Sensitive to Cold

Temp. Yes Less Sensitive

Stabile/Robust

Operation

No Yes

Pre assembled ready

to go Large Number Max 10,000

Service Demanding No Yes

Clogging Yes No* Guaranteed Clog free

Central Operation

including

All Valves and Pumps

Depend on design

Standard

Labor Intensive

Installation Yes No

Shipping Coat High Low

Quick Start up 3 months 1-4 Weeks

Sludge Production Yes Empty once a year

Require backwash Yes No

Retention Time 20 Hours 5 Hrs

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• Service: Require one man once a day to inspect system.

The High Speed Bio Tec are proven to be very stable and self-adjusting even under

harsh conditions, where most biological plants will shut down, and start to polluting the

environment (due to non-bio-activity). The High Speed Bio Tec with AMB Media secures

stabile and non-clogging reactors. Learn more about the system at www.eecme.com

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9. Trouble Shooting

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Trouble shooting:

S.no Process Cause Solution

1. Floating Sludge 1. Inefficient timing of sludge remove 2. Inefficient aeration

1.Check the sludge in buffer and holding tank 2. Check the aeration and airflow/blower.

2. High Suspended solids Inefficient Sludge removal Check the sludge removal timing.

3. Low Feed in the out put May cause floating Sludge Control the flow

4. High Feed in the out put High Suspended solids high TSS and high BOD

Control the flow

5. Foaming 1. Due to detergent in the laundry water 2. Due to high BOD in feed.

1. Check the incoming water 2. Do recirculation and spray clear water.

6. Chlorination BOD could be high at Sampling point.

Check the chemical dosage and the chemical tank

7. Blockage at the inlet Overflow at the manual screen and no flow into the equalization tank.

Remove the blockage at the barscreen

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TO DO ! To follow the guidelines provided in the Operation Manual for proper starting and

shut down of the plant. ! The plant to be operated by the trained and experienced personnel. ! To check the line of the feed flow bar screen if any particles obstructing the flow. ! To check for any abnormality of Air blower, pumps ! To monitor the system pressure at different stages of the process as per the

recommendation provided in the Operation Manual. ! To keep proper record keeping such as daily operational log sheets, review the plant

status, recording of daily events, activities carried out and to maintain the equipment history record to carry out necessary service in time.

! Always maintain minimum inventory of original spares and regular consumables to

reduce down time of the plant equipment�s.

DO NOT:

# Not to stop the plant more than 90 mins.

# Never stop the Air blower of the plant for more than 2 hr. Bacterial colonies will be

affected.

# Not to open and dismantle the plant during the Warranty Period without prior information to the manufacturer.

# Not to use duplicate spare parts/regular consumables, which may impair the long life

of system and its equipment. Maintenace of Manual Barscreen: Bar screen will stop solids, plastics and other non volatile solids which are more than 12 mm entering into the Buffer tank.

The screen rack is removable type. Every week the operator has to remove the rake and wash with fresh water. In case of Grinder submersible pumps used at Lift station. Use of Bar screen is minimized or almost nil.

Note: The list provided above is provided as a quick guideline. It should not be considered as �complete� and exhaustive� information on system operation.

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10. Bill of Materials

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BILL OF MATERIALS

SNO Description Quantity 1. Feed Pump 2 Nos. 2. Sludge Pump/ Recirculation Pump 2 Nos. 3. Hydro cyclone 2 Nos. 4. Air Blower: Regenerative type 2 Nos. 5. Bio �Reactor Tank with 3 chamber in MSEP 2 Nos. 6. Float level Switch 2 Nos. 7. Control Panel for the plant 1 No. 8. Bio Media 1 lot 9. Tube setter Media 1 lot

10. SS piping and fittings 1 lot 11. PVC fittings and piping 1 lot 12. Electrical cable and accessories 1 lot 13. Junction Box 2 Nos. 14. Diffuser 27 Nos. 15. Flow Meter 1 Nos. 16. Dosing Pump 4 Nos.

BILL OF MATERIALS (SPARES) SNO Description Quantity

1. Feed Pump 1 No. 2. Sludge Pump/ Recirculation Pump 2 No. 3. Air Blower: Regenerative type 1 No. 4. PVC ball valves 4 Nos. 5. Pressure gauge 2 Nos. 6. Float Level Switch 1 No 7. Dosing Pump 1 No.

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11. Data sheets & Catalogues

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TECHNICAL DATASHEETS

EQUIPMENT SUBMERSIBLE FEED PUMP DESCRIPTION VALUE Technical: Maximum flow: 40m3/h Head max: 20.8m Type of impeller: VORTEX Type of primary shaft seal: SIC/SIC Type of secondary shaft seal: CARBON/CERAMICS Approvals on nameplate: PA-I Model No: SEV.65.65.30.2.50D Made: GRUNDFOS, DENMARK Materials: Pump housing: Cast iron GS20 Impeller: ` Cast iron GG20 Installation: Maximum ambient temperature: 40°C Maximum operating pressure: 10bar Maximum installation depth: 20m Liquid: Temperature range: 0-40°C Electrical data: Number of poles: 2 P1: 3.8kW P2: 3kW Frequency: 50Hz Rated voltage: 3*380-415V Stating method: direct-on-line Rate of speed: 2910 rpm Motor protect: THERMAL SWITCH Pump weight 95Kg Catalogues Attached Curves Attached

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TECHNICAL DATASHEETS

EQUIPEMENT SLUDGE / RECYCLE PUMP

DESCRIPTION VALUE Technical: Maximum flow: 15.2m3/h Head max: 22.3m Actual impeller diameter: 130 mm Type of shaft seal: BAQE Pump version: A Model No: NBG 50-32-125/130 Made: GRUNDFOS, HUNGARY. Materials: Pump housing: Cast iron EN-JL1040 DIN W.-Nr. A48-40B ASTM Impeller: ` Cast iron EN-JL1030 DIN W.-Nr. A48-40B ASTM Installation: Maximum ambient temperature: 40°C Maximum operating pressure: 16bar Liquid: Temperature range: 0-120°C Electrical data: Motor type 90LA Number of poles: 2 P2: 2.2kW Frequency: 50Hz Rated voltage: 3*380-415V Rate of speed: 2860-2890 rpm Pump weight 54 Kg Catalogues Attached Curves Attached

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TECHNICAL DATASHEETS

EQUIPMENT REGENERATIVE AIR BLOWER

DESCRIPTION VALUES

Tag RB - 1

Manufacturer RKR - Germany

Quantity 3 No.

Mode of working 2 Working (1 Spare Loose)

Type Roots Type (Three Lobed)

Model No BLP 15-15

Nominal Capacity 590 m3/hr

Back Pressure 450 m bar

Motor Rating ISO, F Class

Material of Construction SS / CI

Sound pressure Level 91 dB

Discharge connection DN 100

RPM 2440 RPM

Phase 3

Power Rating 18.5 KW

Voltage (Delta/Star) 400 /690 V AC

Current Supply 12 / 7 A

Weight 165 Kgs. Approx.

Catalogues Attached

Curves Attached

Spare List Attached

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DATASHEET FOR HYDROCYCLONE

DATA DESCRIPTION

ITEM HYDROCYCLONE

Manufacturer LAKOS, USA

Quantity 2 no

Model ILB 0100

Working Mode 1 No Working

Mode of service Manual

Service Sewerage water

Application Removal of solids from liquids or vice versa

Body Carbon steel / stainless steel

Coatings Epoxy

Connections Flanged / Threaded

Working Pressure 2 Bar

Max. Working Pressure 10.2 Bar

Pressure loss range 0.31 � 0.82 Bar

Process flow rate 8 m3/hr.

Working Temperature Ambient

Catalogues Attached

GA drawings Attached

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DATA SHEET FOR CABLES

DATA DESCRIPTION

ITEM ARMOURED CABLES

Manufacturer DUCAB, DUBAI

Service Feed Pump Armored

Recirculation Pump Armored

Regenerative blower Armored

Control Panel Un Armored

Level Switches Un Armored

Type of the cables Multi core / single core

Size As per the power rating

Accessories Cable Glands

Cable Ferrules

Cable Markers

Junction Boxes (If Required)

Catalogues Attached