1
Wastewater Treatment PlantNablus West
Annual Report for Operations and Reuse
2017
February 2018
Prepared by
Eng. Suleiman Abu Ghosh
Eng. Yousef Abu Jaffal
Mr. Sameh Bitar
Eng. Mohammad Homeidan
Eng.Yazan Odeh
1
Wastewater Treatment PlantNablus West
Annual Report for Operations and Reuse
2017
February 2018
Prepared by
Eng. Suleiman Abu Ghosh
Eng. Yousef Abu Jaffal
Mr. Sameh Bitar
Eng. Mohammad Homeidan
Eng.Yazan Odeh
1
Wastewater Treatment PlantNablus West
Annual Report for Operations and Reuse
2017
February 2018
Prepared by
Eng. Suleiman Abu Ghosh
Eng. Yousef Abu Jaffal
Mr. Sameh Bitar
Eng. Mohammad Homeidan
Eng.Yazan Odeh
1
TABLE OF CONTENTS
1. ABBREVIATIONS............................................................................................... 3
2. INTRODUCTION .................................................................................................4
3. BACKGROUND ..................................................................................................5
3.1 Location of the WWTP Nablus West .................................................................................5
3.2 WWTP Nablus West ............................................................................................................6
4. GENERAL PERFORMANCE .............................................................................. 7
5. OPERATION OF WASTEWATER TREATMENT PLANT FACILITIES ............... 7
5.1 Screens and grit/grease removal .......................................................................................7
5.2 Two Primary sedimentation tanks with total volume (1,728 m3) ...................................7
5.3 Two Aeration tanks with total volume (18,000 m3) ..........................................................7
5.3.1 Nitrification and de- nitrification .....................................................................................8
5.4 Two Final sedimentation tanks with total volume (7,718 m3) ........................................8
6. OPERATION OF SLUDGE FACILITIES ............................................................. 9
6.1 Two Belt thickeners..............................................................................................................9
6.2 Primary thickener tank (548 m3).........................................................................................9
6.3 Anaerobic digester (3650 m3) .............................................................................................9
6.4 Gas balloon holder (660 m3) .............................................................................................10
6.5 Gas flare ..............................................................................................................................10
6.6 Sludge drying beds ............................................................................................................10
6.7 Two Belt Filter Presses......................................................................................................10
6.1 Other facilities .....................................................................................................................11
7. SCADA SYSTEM .............................................................................................. 11
8. PERFORMANCE OF WWTP ............................................................................ 12
8.1 Influent flow .........................................................................................................................12
8.2 Cleaning performance .......................................................................................................13
8.3 Power consumption............................................................................................................14
8.4 Gas production....................................................................................................................15
8.5 Desulfurization Unit ............................................................................................................15
8.6 CHP engine .........................................................................................................................16
8.7 Nablus CHP electrical figures...........................................................................................17
8.8 Online measurement For Nitrogen and suspended solids in the aeration tanks:.....17
9. PREVENTIVE MAINTENANCE......................................................................... 18
10. STAFF TRAINING AND ORGANIZATION STRUCTURE ................................. 18
2
11. REUSE PROJECTS.......................................................................................... 19
Table 1: Reuse projects by treated wastewater ........................................................................20
Table 2 : Results from reuse pilot project inside scheme ........................................................23
12. Future Improvements ...................................................................................... 24
13. Problems & Challenges in 2017...................................................................... 24
14. Staff .................................................................................................................. 25
15. Annexes ........................................................................................................... 28
Annex 01: Daily pattern readings of daily inlet flow ..................................................................29
Annex 02: Graphs ..........................................................................................................................30
Annex 03: Performance summary ...............................................................................................40
Annex 04: Power consumption ....................................................................................................40
Annex 05: Additional lab Tests in WWTP Lab ...........................................................................41
Annex 06: External laboratory analysis.......................................................................................42
Annex 07: Quality of tertiary treatment systems........................................................................43
16. Photos .............................................................................................................. 44
3
1. ABBREVIATIONS
µs/cm: Micro Siemens per centimeter NM Nablus Municipality
Al: Aluminum element NO3-N: Nitrate as nitrogenAT: Aeration tank Pb: Lead elementB: Boron element PE: Population equivalentBOD: Biological oxygen demand PLC: Programmable Logic Controller
Ca: Calcium element PO4-P: Phosphate as phosphorousCd: Cadmium element SAR: Sodium adsorption rationcfu: colony fecal unit SCADA: Supervisory Control and Data Acquisition
CH4: Methane Se: Selenium element
Cl: Chloride SO4: Sulphate compoundCn: Cyanide element TDS: Total dissolved solids
Co: Carbon monoxide TN: Total nitrogen
Co: Celsius degree TSS: Total suspended solids
CO2: Carbon Dioxide UV: Ultra violetCOD: Chemical oxygen demand WSSD: Water supply and sanitation departmentCr: Chrome element WWTP: Wastewater treatment plantCu: Cupper element WUA: Water user associationDO: Dissolved oxygen Zn: Zink elementFC: Fecal coliform Ni: Nickel elementFe: Ferric elementGIZ: Gesellschaft für International ZusammenarbeitHg: Mercury elementJV: Joint ventureKfW : Kreditanstalt für Wiederaufbaukg/d: Kilogram per dayKm: KilometerKPR: Kinetics- Passavant ReodigerkWh: Kilowatt hourLi/HEC: Consultant Lahmeyer and Hijjawi EngineeringCenterm³: Cubic meterMBAS: Methylene blue active substanceMCC: Motorized control centreMg: Magnesium elementMLSS: Mixed liquor concentrationMn: Manganese elementMoA: Ministry of Agriculture
Na: Sodium elementNH4-N: Ammonium as nitrogen
4
2. INTRODUCTION
Water supply and sanitation department (WSSD) is considered one of the important
departments of Nablus Municipality (NM) that provides safe drinking water and sanitation
services to Nablus citizens and several surrounding villages in addition to four refugee camps,
namely, Balata, Ein Beit Elma, New and Old Askar Camps. It is estimated that 230,000
inhabitants receive drinking water services. Water and sanitation department has a staff of
300 employees including engineers, technicians, skilled and unskilled laborers.
In 1998 the financial agreement for the implementation of Sewage Project Nablus West was
signed between the German Government through KfW and Nablus Municipality. So far the
allocated fund reached up to 39 million Euros. The Project consisted of construction trunk and
interceptor of 12 km and wastewater treatment plant (WWTP) of 150,000 PE. The WWTP was
designed to treat 14,000 m3/day and 8.0 tons of BOD5 per day. The plant is located near Beit
Leed village junction. The wastewater is collected from Zawata, Beit Eba, Beit Wazan, Deir
Sharaf and Qusin in the future by gravity after the implementation of relevant sewerage
networks.
Nablus West catchment area presently has a population of about 120,000. Presently about
95% of the population of Nablus west is connected to the sewerage network. The main
objective of the sewerage project Nablus West is:
Improve the environmental and health conditions in upper Wadi Zumer
Protect the surface and groundwater from pollution
Reuse of treated wastewater for irrigation purposes
The construction works of the project have been completed in July 2013; however it was put
into operation in November 2013. The consultant Lahmeyer and Hijjawi Engineering Center
(Li/HEC) who provided the consultancy services for Nablus west sewerage project had issued
the performance certificate to the contractor the JV of Kinetics- Passavant Reodiger (KPR) on
September 23th 2015.
Operation assistance (OA) for two years at the cost of 1.10 million Euros has been allocated
through KfW to provide operational assistance to operate, guide and train NM WWTP staff.
The OA was provided by the KPR which was concluded in November 2015.
A second phase of OA financed through KfW is provided now by Consul Aqua to guide the
WWTP staff on part time basis.
5
3. BACKGROUND
3.1 Location of the WWTP Nablus WestThe WWTP Nablus West is located approx. 12 km West of Nablus City and lies on a much
lower orthographical level than Nablus City. Ideally, wastewater is flowing into the treatment
plant through gravity sewer system.
Figure (1): Section of a topographic map in Figure (2): Direction of slopethe project area
Figure (3): Overview of WWTP Nablus West
WWTPNablus West
5
3. BACKGROUND
3.1 Location of the WWTP Nablus WestThe WWTP Nablus West is located approx. 12 km West of Nablus City and lies on a much
lower orthographical level than Nablus City. Ideally, wastewater is flowing into the treatment
plant through gravity sewer system.
Figure (1): Section of a topographic map in Figure (2): Direction of slopethe project area
Figure (3): Overview of WWTP Nablus West
WWTPNablus West
5
3. BACKGROUND
3.1 Location of the WWTP Nablus WestThe WWTP Nablus West is located approx. 12 km West of Nablus City and lies on a much
lower orthographical level than Nablus City. Ideally, wastewater is flowing into the treatment
plant through gravity sewer system.
Figure (1): Section of a topographic map in Figure (2): Direction of slopethe project area
Figure (3): Overview of WWTP Nablus West
WWTPNablus West
6
3.2 WWTP Nablus WestThe WWTP Nablus West is operated as an activated sludge process with a mechanical
treatment, a biological treatment and a sludge treatment steps with gas utilization. In Figure
(3) shows an overview of the WWTP Nablus West. Three construction stages have been
planned for the WWTP Nablus West: stage 1 with a design horizon in 2020, stage 2 with
design horizon in 2025 and a final stage 3 with design horizon in 2035. During the first
construction stage only the colored parts in green of the WWTP (Figure 4) were implemented.
Figure (4): WWTP Nablus West
7
4. GENERAL PERFORMANCE
Around three millions nine hundred and forty seven thousands (3,963,000 m3) cubic meters
of wastewater were treated in the year 2017, with an electrical consumption of two millions
nine hundred and thirty six thousands (2,998,000 kWh). During last year, in general the
average lab results were in line with the Palestinian standards. The average effluent
concentration of BOD5 was 7.7 mg/l and TSS was 13 mg/l. By these results, the treatment
efficiency in terms of BOD5 and TSS were 98 % and 98% respectively.
5. OPERATION OF WASTEWATER TREATMENT PLANTFACILITIES
5.1 Screens and grit/grease removalThe wastewater treatment in Nablus west began with a screening unit. The screening unit
consisted of two types of screens. The first is coarse screen (bar space of 5 cm), and the
second was fine screen (bar space of 5 mm). The main objective of this unit was to protect the
facilities from plastics, woods, rubbish and etc. The screened solid material removed by the
screen conveyors for disposal.
Grit/grease removal unit was designed to remove sand and grits/grease from wastewater. The
grease was sent to the anaerobic digester however, grits/sands were washed out by treated
wastewater in the grit classifier to sanitary disposal.
5.2 Two Primary sedimentation tanks with total volume(1,728 m3)
In this unit, around 60% of organic suspended solids were settled down in two rectangular
tanks forming primary sludge. The primary sludge was thickened in a gravity primary thickener
to increase its concentration from 1% to 4% to be digested in the anaerobic digester in a later
stage.
5.3 Two Aeration tanks with total volume (18,000 m3)The biological wastewater treatment in the aeration tanks was the core of the WWTP. High
concentration of special aerobic bacteria and other microorganisms were activated in the
aeration tanks at existence of high concentration of oxygen called activated sludge. The
soluble and other suspended organic material was digested by bacteria .This unit has to be
controlled in terms of the concentration of activated sludge and dissolved oxygen content.
Almost 90% of the power consumption of the WWTP is required to operate theses two tanks.
8
5.3.1 Nitrification and de- nitrification
The plant was designed for COD removal. Nitrification and de-nitrification also phosphate
elimination was not foreseen in the first stage. However, on the 17th of March, 2015 the plant
started to perform nitrification, and de- nitrification process in the aeration tanks in addition to
carbon removal process.
Inlet AT
Outlet AT
Figure (5): Aeration tank with implemented de-nitrification zone
In areas where oxygen was reduced, there were bacteria starting a de-nitrification process. In
de- nitrification, elemental gaseous nitrogen is produced from nitrate and nitrite and released
to the atmosphere.
5.4 Two Final sedimentation tanks with total volume (7,718m3)
The activated sludge was settled down in the two circular final sedimentation tanks. The
settled bacteria was withdrawn from the bottom of the tanks and returned back to the aeration
tanks as returned sludge. This recycling of activated sludge was necessary to maintain certain
concentration of activated sludge (around 2-3% SS) with optimal sludge age, however the
excess sludge was pumped to the mechanical thickeners for further treatment in the
anaerobic digester.
aerobic anoxicaerobic/anoxic
9
6. OPERATION OF SLUDGE FACILITIES
6.1 Two Belt thickenersThe excess sludge was withdrawn via pumps to the belt thickeners where polymer was
added. This machine thickened the excess sludge up to 1% to 6% SS concentration. After
thickening it was mixed with the primary thickened sludge to be pumped later on to the
digester.
6.2 Primary thickener tank (548 m3)The settled primary sludge in the primary sedimentation tanks was sent to the primary gravity
thickener circular tank. In this unit, the sludge was thickened to reach 6% which was treated in
the anaerobic digester.
6.3 Anaerobic digester (3650 m3)The thickened primary sludge and thickened excess sludge were treated in the anaerobic
digester; the retention time is 21 days. Temperature and pH were carefully monitored to
maintain optimum conditions for the anaerobic bacteria in the digester (pH= 6.8-7.5), the solid
content was around 3-4%. The biogas produced from the digester normally contained 33% of
CO2 and 66% of methane gas. The sludge was heated up via boiler to maintain mesophilic
conditions in the digester around 36 Co.
Figure (6): Digester tank in Nablus West WWTP with the gas flare
9
6. OPERATION OF SLUDGE FACILITIES
6.1 Two Belt thickenersThe excess sludge was withdrawn via pumps to the belt thickeners where polymer was
added. This machine thickened the excess sludge up to 1% to 6% SS concentration. After
thickening it was mixed with the primary thickened sludge to be pumped later on to the
digester.
6.2 Primary thickener tank (548 m3)The settled primary sludge in the primary sedimentation tanks was sent to the primary gravity
thickener circular tank. In this unit, the sludge was thickened to reach 6% which was treated in
the anaerobic digester.
6.3 Anaerobic digester (3650 m3)The thickened primary sludge and thickened excess sludge were treated in the anaerobic
digester; the retention time is 21 days. Temperature and pH were carefully monitored to
maintain optimum conditions for the anaerobic bacteria in the digester (pH= 6.8-7.5), the solid
content was around 3-4%. The biogas produced from the digester normally contained 33% of
CO2 and 66% of methane gas. The sludge was heated up via boiler to maintain mesophilic
conditions in the digester around 36 Co.
Figure (6): Digester tank in Nablus West WWTP with the gas flare
9
6. OPERATION OF SLUDGE FACILITIES
6.1 Two Belt thickenersThe excess sludge was withdrawn via pumps to the belt thickeners where polymer was
added. This machine thickened the excess sludge up to 1% to 6% SS concentration. After
thickening it was mixed with the primary thickened sludge to be pumped later on to the
digester.
6.2 Primary thickener tank (548 m3)The settled primary sludge in the primary sedimentation tanks was sent to the primary gravity
thickener circular tank. In this unit, the sludge was thickened to reach 6% which was treated in
the anaerobic digester.
6.3 Anaerobic digester (3650 m3)The thickened primary sludge and thickened excess sludge were treated in the anaerobic
digester; the retention time is 21 days. Temperature and pH were carefully monitored to
maintain optimum conditions for the anaerobic bacteria in the digester (pH= 6.8-7.5), the solid
content was around 3-4%. The biogas produced from the digester normally contained 33% of
CO2 and 66% of methane gas. The sludge was heated up via boiler to maintain mesophilic
conditions in the digester around 36 Co.
Figure (6): Digester tank in Nablus West WWTP with the gas flare
10
6.4 Gas balloon holder (660 m3)Produced CH4 gas from the digester was treated in stone filters to remove the humidity and
then store it in the gas holder.
6.5 Gas flareThe excess gas was burned by the gas flare. It started flaring when the storage in the balloon
reaches up to 90% and stop when it reached 80% of the volume of gas balloon.
6.6 Sludge drying bedsIn emergency cases, the digested sludge was pumped to the drying beds for drying via natural
evaporation. There were 11 beds with total area of 11.5 donum. After drying, the sludge was
transported to the sludge storage yard for disposal into Zahret Al-Fenjan sanitary landfill site
near Jenin.
6.7 Two Belt Filter PressesTwo belt filter presses were used to dewatering the digested sludge coming from the digester
to have solids more than 25%. Special polymers were used to improve the efficiency of these
machines as shown in Figure (7).
Figure (7): Dry solids content after mechanical dewatering.
20%
22%
24%
26%
28%
30%
32%
34%
36%
38%
40%
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Dry
solid
s con
tent
%
Month - 2017
Dry solids content %
Average = 25%
11
6.1 Other facilitiesOther equipment were available for the sustainability of the operation of the WWTP such as
well-equipped lab, stand by generator, spare parts, administration building and workshop.
7. SCADA SYSTEM
The sewage treatment plant was controlled by using Programmable Logic Controller (PLC)
and Supervisory Control and Data Acquisition (SCADA). The PLC’s are located in several
substations (electrical switch rooms) within the wastewater treatment plant.
The wastewater treatment plant was controlled by PLC’s. PLC’s and their support equipment
were computer controlled system that was capable of remote managing of the plant’s
operation. The control was executed from the analogous and digital in-puts / outputs received
from instruments, drives and MCC and from signals received from the SCADA system.
Figure (8): Nablus WWTP SCADA system
11
6.1 Other facilitiesOther equipment were available for the sustainability of the operation of the WWTP such as
well-equipped lab, stand by generator, spare parts, administration building and workshop.
7. SCADA SYSTEM
The sewage treatment plant was controlled by using Programmable Logic Controller (PLC)
and Supervisory Control and Data Acquisition (SCADA). The PLC’s are located in several
substations (electrical switch rooms) within the wastewater treatment plant.
The wastewater treatment plant was controlled by PLC’s. PLC’s and their support equipment
were computer controlled system that was capable of remote managing of the plant’s
operation. The control was executed from the analogous and digital in-puts / outputs received
from instruments, drives and MCC and from signals received from the SCADA system.
Figure (8): Nablus WWTP SCADA system
11
6.1 Other facilitiesOther equipment were available for the sustainability of the operation of the WWTP such as
well-equipped lab, stand by generator, spare parts, administration building and workshop.
7. SCADA SYSTEM
The sewage treatment plant was controlled by using Programmable Logic Controller (PLC)
and Supervisory Control and Data Acquisition (SCADA). The PLC’s are located in several
substations (electrical switch rooms) within the wastewater treatment plant.
The wastewater treatment plant was controlled by PLC’s. PLC’s and their support equipment
were computer controlled system that was capable of remote managing of the plant’s
operation. The control was executed from the analogous and digital in-puts / outputs received
from instruments, drives and MCC and from signals received from the SCADA system.
Figure (8): Nablus WWTP SCADA system
12
8. PERFORMANCE OF WWTP
8.1 Influent flowThe performance of WWTP Nablus West during 2017 was analyzed on the basis of the plant
loading which had been monitored regularly. Two aeration treatment tanks were mainly in
operation, the hydraulic treatment capacity of the plant was sufficient and the amount of inflow
in most cases under design capacity. Only extreme weather conditions (heavy rain) led to
capacity problems. The hydraulic and pollutants loading and the actual performance of WWTP
Nablus West from January 2017 to December 2017 were analyzed.
Figure (9) Shows the hydrographs of the daily wastewater flows which were treated in WWTP
Nablus West. It became clear that no strong fluctuation of the daily wastewater flows occurred
during summer time. However, in the winter time the fluctuation was sometimes very high due
to heavy rain events. In such cases, the bypass to Wadi prior to the WWTP had to be used for
plant protection design capacity.
The average daily wastewater flow in the year 2017 was approximately 10883 m³/day . The
amount of incoming wastewater will increase gradually over the next years.
Figure (9): Hydrograph of the daily treated wastewater inflow
7400
9400
11400
13400
15400
17400
19400
21400
23400
25400
27400
01-Ja
n15
-Jan
29-Ja
n12
-Feb
26-F
eb11
-Mar
25-M
ar08
-Apr
22-A
pr06
-May
20-M
ay03
-Jun
17-Ju
n01
-Jul
15-Ju
l29
-Jul
12-A
ug26
-Aug
09-S
ep23
-Sep
07-O
ct21
-Oct
04-N
ov18
-Nov
02-D
ec16
-Dec
30-D
ec
Wes
tew
ater
Inflo
w m
3/da
y
2017
Inflow pattern in 2017 m3/day
Inflow pattern in 2017 m3/day
Inflow pattern in(وفق معدل النقل 7 2017 m3/day)
13
8.2 Cleaning performanceThe current daily wastewater pollution load treated in WWTP Nablus West in terms of COD
and SS were calculated. The average daily COD load was approximately 11,449 kg/d and the
total COD load over the year of 2017 was 4,178,854 kg/year. The COD load at the effluent in
the same period was 154,760 kg/year. The cleaning performance is approximately 96%.
Figure (10): Influent and effluent concentration of COD
The hydraulic and pollutant load of WWTP Nablus West as well as site conditions had an
effect on the performance of the WWTP. The average daily suspended solids inflow was
approximately 4,843 kg/d. The reduction of suspended solids was in average approximately
97%.
0.84
0.86
0.88
0.90
0.92
0.94
0.96
0.98
1.00
0
200
400
600
800
1000
1200
1400
1600
180002
-Jan
02-F
eb
02-M
ar
02-A
pr
02-M
ay
02-Ju
n
02-Ju
l
02-A
ug
02-S
ep
02-O
ct
02-N
ov
02-D
ec
COD
mg/
l
2017
COD Inlet and outlet
COD In mg/l
COD out mg/l
PerformanceEfficency %
وفق معدل النقل 3)COD In mg/l)
وفق معدل النقل 3)COD out
mg/l)
14
Figure (11): Suspended solids of the inlet and outlet of the treatment plant
8.3 Power consumptionOptimization of operation was one of the most important challenges in municipal WWTPs. The
specific power consumption of similar WWTP is about below 0.85 kWh per m³ of treated
wastewater, and below 0.8 kWh of kg COD removed , however in Nablus WWTP is 0.77
kwh/m3 and is 0.73 kg/COD removed respectively. Deviations from this value can be
attributed to the circumstances of daily plant operation.
Figure (12): Monthly values of power consumption per treated m³ of wastewater
0.0050.00
100.00150.00200.00250.00300.00350.00400.00450.00500.00550.00600.00650.00700.00750.00800.00
02-Ja
n
02-F
eb
02-M
ar
02-A
pr
02-M
ay
02-Ju
n
02-Ju
l
02-A
ug
02-S
ep
02-O
ct
02-N
ov
02-D
ec
Susp
ende
d so
lids m
g/l
2017
Inlet and outlet SS in 2017
SS in mg/l
SS out mg/l
وفق معدل النقل 3)SS in mg/l)
وفق معدل النقل 3)SS out mg/l)
0.450.485
0.520.555
0.590.625
0.660.695
0.730.765
0.80.835
0.870.905
0.940.975
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Kwh/
Trea
ted
m3
Month - 2017
Kwh/Treated m3
Average =0.77Kwh/Treated m3
15
8.4 Gas productionPart of produced gas at this stage was used for heating the digester. However, the excess
used by CHP unit (Installed and operated in 2017). The average gas production in the year of
2017 was 2,473 nm3/d.
Figure (13): Gas production of the digester
In 2017 more regular operation of the digester was done and as a result a substantial increase
in biogas occurred. Biogas flowmeters were optimized for reading the flow in normal cubic
meters instead of kilogram. This optimization was done with reference of new installed sensor
of biogas flowmeter in the combined heat and power plant (CHP).
8.5 Desulfurization UnitThe desulphurization unit of biogas is considered as one of the main components of CHP unit,
which ensures sustainability for the operation of the CHP engine. It treats the produced biogas
from anaerobic digester from H2S gas and Siloxane. These gases are dangerous for the
engine and could cause engine failure.
0400800
12001600200024002800320036004000440048005200560060006400
1-Ja
n
22-Ja
n
12-F
eb
5-M
ar
26-M
ar
16-A
pr
7-M
ay
28-M
ay
18-Ju
n
9-Ju
l
30-Ju
l
20-A
ug
10-S
ep
1-O
ct
22-O
ct
12-N
ov
3-De
c
24-D
ec
Gas p
rod
kg/d
ay
2017
Gas production 2017 Average = 2473 kg/d
Gas ProductionNm3/day
16
Figure (14): Nablus West desulfurization unit
8.6 CHP engineOne of the best energy efficiency practices in WWTP’s is utilizing the biogas through CHP
engine. Nablus CHP engine has been put in operation in 18/6/2017. It is burning the treated
biogas which treated in desulfurization unit and produce electrical and thermal power. It was
covered around 60% of the total electrical consumption of Nablus plant. It is expected to cover
around 80% of total electrical demand as more organic load reaches to the Treatment plant
from the nearby villages of Nablus West.
Figure (15): Nablus West CHP engine.
16
Figure (14): Nablus West desulfurization unit
8.6 CHP engineOne of the best energy efficiency practices in WWTP’s is utilizing the biogas through CHP
engine. Nablus CHP engine has been put in operation in 18/6/2017. It is burning the treated
biogas which treated in desulfurization unit and produce electrical and thermal power. It was
covered around 60% of the total electrical consumption of Nablus plant. It is expected to cover
around 80% of total electrical demand as more organic load reaches to the Treatment plant
from the nearby villages of Nablus West.
Figure (15): Nablus West CHP engine.
16
Figure (14): Nablus West desulfurization unit
8.6 CHP engineOne of the best energy efficiency practices in WWTP’s is utilizing the biogas through CHP
engine. Nablus CHP engine has been put in operation in 18/6/2017. It is burning the treated
biogas which treated in desulfurization unit and produce electrical and thermal power. It was
covered around 60% of the total electrical consumption of Nablus plant. It is expected to cover
around 80% of total electrical demand as more organic load reaches to the Treatment plant
from the nearby villages of Nablus West.
Figure (15): Nablus West CHP engine.
17
8.7 Nablus CHP electrical figuresThe electrical consumption of the plant and CHP production are monitored on daily.
Figure (16): Electrical consumption of plant with comparison of CHP electrical production
8.8 Online measurement For Nitrogen and suspended solids inthe aeration tanks:
In 2017 an online system for measuring Nitrogen with suspended solids have been installed in
the aeration tanks, four sensors (NH4, NO3) and two (suspended solids) at specific locations in
the aeration tanks which help controlling the nitrification/denitrification process efficiently.
By direct on line measurement of such parameters, an optimization of energy could be
achieved in terms of oxygen supply via the surface aerators which are considered the
prominent energy consumers among other units, as a result a significant reduction of
wastewater energy demand.
A complete connection to SCADA will be optimized in terms of Oxygen supply from surface
aerators.
4775 3013 2998 5371 5160 5196 4613
4509
8328
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
Jun-
17
Jul-1
7
Aug-
17
Sep-
17
Oct
-17
Nov
-17
Dec-
17
kwh/
day
Month
Avg. daily electricalproduction of CHPunit
Avg. daily electricalproduction of CHPunit since start ofoperation untilnow = 4509 kwh/d
Avg. daily electricalconsumption ofNablus plant =8328 kwh/d
18
9. PREVENTIVE MAINTENANCE
From the beginning of the plant operation maintenance works and plans had been conducted
in accordance with the periodic and routine works of machines manuals. These works could
be classified as preventive maintenance. Preventive maintenance was done by Nablus
WWTP staff.
10. STAFF TRAINING AND ORGANIZATION STRUCTURE
Training was essential for the sustainability of the plant. The staff of Nablus plant had been
trained the through KfW in fields of plant operations such as:
Practical training on the CHP maintenance in Jordan. This training was done as (onthe job training) under the umbrella of Consulaqua consulting company. Fourmechanical and electrical technicians were trained in Irbid WWTP.
Theoretical training for the agricultural engineer on reuse issues of treated water andsludge funded by GIZ.
19
11. REUSE PROJECTS
In view of the limited water resources in the West Bank, reuse of treated wastewater
has a great potential to reduce part of these problems and improve crop yield. Designing
wastewater treatment plants for reuse in irrigation could potentially increase agricultural yields,
conserve surfaces water and balance chemical fertilizer demand. Nablus Municipality adopted
the policy to reuse treated wastewater in agriculture. With reference to Ministry of Agriculture
by-law 34-2012 the treated wastewater quality of Nablus WWTP has Grade (A). Four reuse
projects are foreseen in the time being as shown in the following table.
Figure (17): Area’s for reuse of treated WW within the boundary of Nablus WWTP
20
Table 1: Reuse projects by treated wastewater
No
Project Area(Donum) Crops Financing Objective
Quantityof
TWW (m3)\Year
Operatingparty
Cost(Euro)
StatusTaking
Over/foreseen steps
1Reuse InsideWWTPschemeFigures 14,15
40
Avocado-Olive-Apple-Almond-Pomegranate-Pirsamon-Pistachio-Apricot-Walnut-Pecan-Citruss-peach-Alfalfa-Barly-Vetch
EU+GermanGovernmentthroughKfW
EducationalPilot project
35,000 NablusMunicipality
462,000 Jan-2017
2
ReuseoutsideWWTPschemeFigure 16
120 Olive-Almond- Alfalfa
EU+GermanGovernmentthroughKfW
Pilot project 115,000 Deir SharafWUA
1,500,000 July-2018
3CompeteProjectFigure 17
140 Olive-Almond -Pomegranate-Apple-Fig USAID Pilot project 80,000 Deir Sharaf
WUA500,000 June-2017
4Reuseoutside 2800Figure 18
2800 Alfaalfa-Pecan-Walnut -almond-alfalfa-olive
GermanGovernmentthroughKfW
To reuse allTWW in
Agriculture
3,000,000 Deir SharafWUA
10 millions End 2019
21
Figure (18): Reuse inside scheme
.
Figure (19): Sand filtration and ultraviolet disinfection units
21
Figure (18): Reuse inside scheme
.
Figure (19): Sand filtration and ultraviolet disinfection units
21
Figure (18): Reuse inside scheme
.
Figure (19): Sand filtration and ultraviolet disinfection units
22
Figure (20): Reuse outside scheme
Figure (21): Reuse outside scheme (USAID)
22
Figure (20): Reuse outside scheme
Figure (21): Reuse outside scheme (USAID)
22
Figure (20): Reuse outside scheme
Figure (21): Reuse outside scheme (USAID)
23
Figure (22): Reuse outside scheme 2800 donum (KfW)
The growth status of the plants which have been planted inside the Nablus WWTP was
monitored. Table (2) shows the assessment of agricultural experts for the growth status of
the different plants types. Also figure (23) shows the growth of AlfaAlfa in two different
pictures which have been captured within duration of less than one month.
Table 2 : Results from reuse pilot project inside schemeCrop and planting date Growth status
Almond Tree Very GoodPistachio ExcellentPecan ExcellentWalnut (Camel eye) ExcellentPommel GoodLemon GoodOlive Tree ExcellentPomegranate ExcellentApple ExcellentPersimmon goodApricot ExcellentPeach ExcellentAvocado Very Good
23
Figure (22): Reuse outside scheme 2800 donum (KfW)
The growth status of the plants which have been planted inside the Nablus WWTP was
monitored. Table (2) shows the assessment of agricultural experts for the growth status of
the different plants types. Also figure (23) shows the growth of AlfaAlfa in two different
pictures which have been captured within duration of less than one month.
Table 2 : Results from reuse pilot project inside schemeCrop and planting date Growth status
Almond Tree Very GoodPistachio ExcellentPecan ExcellentWalnut (Camel eye) ExcellentPommel GoodLemon GoodOlive Tree ExcellentPomegranate ExcellentApple ExcellentPersimmon goodApricot ExcellentPeach ExcellentAvocado Very Good
23
Figure (22): Reuse outside scheme 2800 donum (KfW)
The growth status of the plants which have been planted inside the Nablus WWTP was
monitored. Table (2) shows the assessment of agricultural experts for the growth status of
the different plants types. Also figure (23) shows the growth of AlfaAlfa in two different
pictures which have been captured within duration of less than one month.
Table 2 : Results from reuse pilot project inside schemeCrop and planting date Growth status
Almond Tree Very GoodPistachio ExcellentPecan ExcellentWalnut (Camel eye) ExcellentPommel GoodLemon GoodOlive Tree ExcellentPomegranate ExcellentApple ExcellentPersimmon goodApricot ExcellentPeach ExcellentAvocado Very Good
24
Figure (23): A comparison between AlfaAlfa area (before and after)
12. Future Improvements
Implementation of a stone trap at the inlet of WWTP to protect screens
125 KW Pilot Project of PV Solar Panel financed through Nuremberg City-Germany. The Cooperation Agreement was signed in February 2017
Covering primary thickener tank and the sludge storage yard Replacement of thermal isolation sheets for the tank of the anaerobic digestion
13. Problems & Challenges in 2017
Unavailability of spare parts in local market.
Keep the staff of the WWTP.
Sludge Disposal:
1. High Cost of sludge disposal in Zeharet Al-Fenjan at 75 NIS/ton.
2. As per Palestinian standard, it is not allowed to reuse sludge in agriculturedue to high Water content in sludge of 75%
24
Figure (23): A comparison between AlfaAlfa area (before and after)
12. Future Improvements
Implementation of a stone trap at the inlet of WWTP to protect screens
125 KW Pilot Project of PV Solar Panel financed through Nuremberg City-Germany. The Cooperation Agreement was signed in February 2017
Covering primary thickener tank and the sludge storage yard Replacement of thermal isolation sheets for the tank of the anaerobic digestion
13. Problems & Challenges in 2017
Unavailability of spare parts in local market.
Keep the staff of the WWTP.
Sludge Disposal:
1. High Cost of sludge disposal in Zeharet Al-Fenjan at 75 NIS/ton.
2. As per Palestinian standard, it is not allowed to reuse sludge in agriculturedue to high Water content in sludge of 75%
24
Figure (23): A comparison between AlfaAlfa area (before and after)
12. Future Improvements
Implementation of a stone trap at the inlet of WWTP to protect screens
125 KW Pilot Project of PV Solar Panel financed through Nuremberg City-Germany. The Cooperation Agreement was signed in February 2017
Covering primary thickener tank and the sludge storage yard Replacement of thermal isolation sheets for the tank of the anaerobic digestion
13. Problems & Challenges in 2017
Unavailability of spare parts in local market.
Keep the staff of the WWTP.
Sludge Disposal:
1. High Cost of sludge disposal in Zeharet Al-Fenjan at 75 NIS/ton.
2. As per Palestinian standard, it is not allowed to reuse sludge in agriculturedue to high Water content in sludge of 75%
25
14. Staff
Waste Water Treatment Plant Nablus - WestOrganization Structure
Technical AdviserSuleiman Abu Ghosh
Chief OperatorYousef Abu Jaffal
Process EngineerMaintenance
EngineerAdministrativeAgricultural
engineerMohammadHumaidanAnas BarqAssistanceYazan Odeh
Sameh Bitar
Lab TechnicianWWTP SCADAGuardsAgriculture workersRola Abu SlamaAdminestratorRami HasanBara'a Fakr Aldeen
Amer ShanteerZeidan KayedWWTP OperatorZeiad Nasser
Abed al hadi NorieWWTP M.TechniciansRami HasebaMohammad TawashiOffice boy
Khaled MakhzomMohammad AzzamMohammad
HashashAmjad Shanteer
WWTP E.TechniciansAhmad Yaish
26
Suleiman Abu Ghosh
- Technical Adviser
Yousef Abu Jaffal
-Nablus WWTP Chief
Operator
Mohammad Homeidan
-Process Engineer &
Lab Officer in Nablus
WWTP
Anas Barq
- Electrical Engineer
Sameh Bitar
-Administrative Secretary
& Accountant
Rola Abu Slama
-Lab Technician
Amer Shanteer
- WWTP SCADA
Administrator
Yazan Oudeh
-Agricultural engineer
Operators
Khaled Makhzom Amjad Shanteer Rami Hasiba Abdel hadi Norie
26
Suleiman Abu Ghosh
- Technical Adviser
Yousef Abu Jaffal
-Nablus WWTP Chief
Operator
Mohammad Homeidan
-Process Engineer &
Lab Officer in Nablus
WWTP
Anas Barq
- Electrical Engineer
Sameh Bitar
-Administrative Secretary
& Accountant
Rola Abu Slama
-Lab Technician
Amer Shanteer
- WWTP SCADA
Administrator
Yazan Oudeh
-Agricultural engineer
Operators
Khaled Makhzom Amjad Shanteer Rami Hasiba Abdel hadi Norie
26
Suleiman Abu Ghosh
- Technical Adviser
Yousef Abu Jaffal
-Nablus WWTP Chief
Operator
Mohammad Homeidan
-Process Engineer &
Lab Officer in Nablus
WWTP
Anas Barq
- Electrical Engineer
Sameh Bitar
-Administrative Secretary
& Accountant
Rola Abu Slama
-Lab Technician
Amer Shanteer
- WWTP SCADA
Administrator
Yazan Oudeh
-Agricultural engineer
Operators
Khaled Makhzom Amjad Shanteer Rami Hasiba Abdel hadi Norie
27
Electro mechanic Technicians
Mohammad Tawashi Mohammad Azzam Ahmad Yaish
Labour office boy
Mohammad Antar Mohammad Hashash
Agriculture
Bara’a Fakrldeen
Guards
Rami Hasan Zeidan Kayed Zeiad Nasser
28
15. Annexes
29
150.0200.0250.0300.0350.0400.0450.0500.0550.0600.0
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ow m
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Flow pattern 14/9/2017
150.0200.0250.0300.0350.0400.0450.0500.0550.0600.0
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070140210280350420490560630700
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Flow
m3/
hr
Time
Flow pattern 28/5/2017
100170240310380450520590660730
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Flow pattern 16/10/2017
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Time
Flow pattern 15/11/2017
100.0150.0200.0250.0300.0350.0400.0450.0500.0550.0
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Flow pattern 13/12/2017
Annex 01: Daily pattern readings of daily inlet flow
30
Annex 02: Graphs
Graph 1: Average wastewater effluent
Graph 2: Average treated wastewater effluent
370.0390.0410.0430.0450.0470.0490.0510.0530.0550.0570.0590.0610.0
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Vens
uri r
eadi
ngs m
3/hr
Month - 2017
Venturi readingsm3/hr
Average = 453 m3/hr
9,0009,4009,800
10,20010,60011,00011,40011,80012,20012,60013,00013,40013,80014,20014,60015,000
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Out
flow
m3/
day
Month - 2017
Outflow m3/day
Average = 10883m3/day
31
Graph 3: Monthly dissolved oxygen concentration pattern in the aeration tank no. (1)
Graph 4: Monthly dissolved oxygen concentration pattern in tank no. (2)
1.35
1.425
1.5
1.575
1.65
1.725
1.8
1.875
1.95
2.025
2.1
2.175
2.25
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Aver
age
DO a
t AT
1m
g/l
Month - 2017
Average DO at AT 1mg/l
Average = 1.73 mg/l
1.35
1.4
1.45
1.5
1.55
1.6
1.65
1.7
1.75
1.8
1.85
1.9
1.95
2
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Aver
age
DO a
t AT
2m
g/l
Month - 2017
Average DO at AT 2mg/l
Average = 1.7 mg/l
32
Graph 5: The COD concentration in the influent of WWTP
Graph 6: The COD concentration in the effluent of the treated waste water
625675725775825875925975
102510751125117512251275
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
COD
inle
t mg/
l
Month - 2017
COD inlet mg/l
Average = 1052 mg/l
Design =1100 mg/l
30.0035.0040.0045.0050.0055.0060.0065.0070.0075.0080.0085.0090.0095.00
100.00105.00
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
COD
Out
mg/
l
Month - 2017
COD out mg/l
Average year = 39 mg/l
Design = 100 mg/l
33
Graph 7: The correlation between CODout and BOD5eff
Graph 8: The BOD5 concentration in the effluent of the treated wastewater
y = 4.9985xR² = 0.987
25
30
35
40
45
50
55
60
65
70
75
5 7 9 11 13 15 17 19
COD
out m
g/l
BOD 5 out mg/l
6.007.008.009.00
10.0011.0012.0013.0014.0015.0016.0017.0018.0019.0020.0021.00
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
BOD
outle
t mg/
l
Month - 2017
BOD outlet mg/l
Average = 7.7 mg/l
Design = 20 mg/l
34
Graph 9: TSS concentration of the treated wastewater (TSS)
Graph 10: Total Nitrogen for influent and effluent (TN)
5.007.009.00
11.0013.0015.0017.0019.0021.0023.0025.0027.0029.0031.00
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
TSS
outle
t mg/
l
Month - 2017
TSS out mg/l
Average = 13 mg/l
Design = 30 mg/l
0
10
20
30
40
50
60
70
80
90
100
110
120
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Tota
l Nitr
ogen
mg/
l
Month - 2017
Total Nitrogen outlet mg/lAverage Total Nitrogen 13.3 outlet mg/lTotal Nitrogen inlet mg/lAverage Total Nitrogen 95 inlet mg/l
35
Graph 11: The average produced quantities of biogas
Graph 12: Average pH of the inlet wastewater
1500
1700
1900
2100
2300
2500
2700
2900
3100
3300
3500
3700
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Biog
as q
uant
ity N
m3/
day
Month - 2017
Biogas quantity Nm3/day
Average Biogas quantity = 2473 Nm3/day
7.557.585
7.627.655
7.697.725
7.767.795
7.837.865
7.97.935
7.978.005
8.048.075
8.118.145
8.188.215
8.258.285
8.328.355
8.398.425
8.468.495
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
pH
Month - 2017
PH Average = 8
36
Graph 13: Mixed liquor suspended solids concentration (MLSS) in aeration tanks
Graph 14: Conductivity of the inlet flow
2.8
3
3.2
3.4
3.6
3.8
4
4.2
4.4
4.6
4.8
5
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
MLS
S
Month - 2017
MLSS
Average= 3.77 g/l
12001230126012901320135013801410144014701500153015601590162016501680
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
CON
D
Month - 2017
COND Average = 1513 µS/cm
37
Graph 15: Total dissolved solids in the effluent
Graph 16: Average monthly treated wastewater and power consumption
600620640660680700720740760780800820840860880900920940960
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
TDS
Month - 2017
190,000205,000220,000235,000250,000265,000280,000295,000310,000325,000340,000355,000370,000385,000400,000
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
ctrea
ted
wat
er a
nd E
lect
rical
con
sum
ptio
n
month - 2017
Treated Water quantity m3
Avg treated water =330294 m3
Electrical consumption kWh
Avg Electrical consumption =249839 kWh
38
Graph 17: Power requirement kWh/kg COD treated
Graph 18: Power requirement kWh/m3 treated
0.590.610.630.650.670.690.710.730.750.770.790.810.830.850.870.89
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Kwh/
Kg C
OD
rem
oved
Month - 2017
Kwh/Kg COD removed
Average =0.73 Kwh/KgCOD removed
0.450.485
0.520.555
0.590.625
0.660.695
0.730.765
0.80.835
0.870.905
0.940.975
Jan
Feb
Mar Ap
r
May Jun Jul
Aug
Sep
Oct
Nov De
c
Kwh/
Trea
ted
m3
Month - 2017
Kwh/Treated m3
Average =0.77Kwh/Treated m3
39
Graph 19: Expenditures versus collection
Graph 20: Expenditures breakdown 2017
0
500,000
1,000,000
1,500,000
2,000,000
2,500,000
3,000,000
3,500,000
4,000,000
2014
2015
2016
2017
NIS
Year
Total income
Totalexpenses
Indirectexpenses
Electricity43%
Salaries andwages19%
Otherdepartmentsparticipation
14%
Transportationand land filling
8%
Chemicalsconsumables
6%
Insurance5%
Fuels2% O&M
1% Vehicles1%
Administrativeexpenses
1%
Electricity
Salaries and wages
Other departmentsparticipationTransportation and landfillingChemicals consumables
Insurance
Fuels
O&M
Vehicles
Administrative expenses
40
Annex 03: Performance summary
ParametersDesign
value 2020
Treatmentefficiency
% Average
Month - 2017
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Average inlet flowm3/d 14000 ----- 10883 12657 14413 11112 10615 9965 9812 9223 9523 10500 10352 10660 11760
Inlet COD mg/L 1100 ----- 1052 864 732 957 1035 981 1269 1094 1169 1000 1232 1203 1088
Outlet COD mg/L 100 96% 39 45 46 37 36 38 41 36 39 36 38 39 33
Outlet BOD5 mg/L 20 99% 7.7 9 9 7 7 8 8 7 8 7 8 8 6.5
Inlet BOD5 mg/L 550 526 432 366 478 517 490 634 547 584 500 615 601 544
Sludge age (days) 13.7 ----- 18 19 17 16 14.5 15.4 20 17.5 18 21 20 20 20.2
MLSS g/L 3 ----- 3.77 3 3.66 3.53 3.5 3.3 4.95 4.3 3.6 3.5 3.6 3.7 4.55
TSS inlet mg/L 500 474 355 300 377 304 430 602 522 562 534 546 629 522
TSS outlet mg/L 30 97% 13 22 21 15 18 15 13 12 6 10 5 9 12TN out 30 13.3 45 18 6 7 8 9 6.6 6.3 13 12 12.5 16.5
Annex 04: Power consumption
2017DecNovOctSepAugJulJunMayAprMarFebJanAvgMonth
364,555319,719320,914315,040295,204285,900294,351308,906318,454344,468403,560392,381330,288Treated
wastewaterquantity m3
101,511109,994102,987102,002178,615180,512202,106252,791242,157233,542193,860214,198
249,839
Totalelectrical
consumptionkWhr
142,995161,101159,981166,50992,94193,41066,850-----
CHPelectrical
productionkWhr
0.670.850.820.850.920.960.910.820.760.680.480.550.76kWhr per m3
41
Annex 05: Additional lab Tests in WWTP Lab2017
AverageValuesTest / DecNovOctSepAugJulJunMayAprMarFebJan33.0039.0038.0036.0039.0036.0041.0038.0036.0037.0046.0045.0039Average
COD outmg/l 46.0060.0054.0047.0057.0039.0064.0060.0044.0059.0085.0069.0057.0Max
18.0031.0030.0032.0029.0033.0030.0029.0030.0027.0029.0024.0028.5Min
6.508.008.007.008.007.008.008.007.007.009.009.007.7AverageBOD out
mg/l 9.0012.0011.009.4011.007.8013.0012.009.0012.0017.0014.0011.4Max
3.606.006.006.406.006.606.006.006.005.006.005.005.7Min
0.30----0.80--0.900.450.500.000.150.000.250.4AverageNH4-N out
mg/l 0.40----0.80--0.900.900.500.000.300.000.400.5Max
0.20----0.80--0.900.000.500.000.000.000.100.3Min
6.557.508.9011.453.604.186.106.103.803.302.3032.908.1AverageNO3-N out
mg/l 9.308.7015.4013.404.505.306.906.103.803.302.3043.0010.2Max
3.806.405.006.602.203.405.306.103.803.302.3022.805.9Min
16.5012.5012.0013.006.306.609.008.007.006.0018.0045.0013.3Average
TN out mg/l 18.0018.0019.0017.009.008.0011.008.007.006.0018.0050.0015.8Max
15.007.006.008.003.005.007.008.007.006.0018.0040.0010.8Min
1.302.402.303.304.404.652.642.692.140.851.903.932.7AveragePO4-P out
mg/l 1.702.703.703.444.806.542.642.692.140.851.903.933.1Max
1.101.901.503.144.003.482.642.692.140.851.903.932.4Min
12.009.005.0010.006.0012.0013.0015.0018.0015.0021.0022.0013Average
TSS out mg/l 30.0020.0010.0032.0012.0030.0032.0032.0027.0025.0046.0040.0028.0Max
2.002.002.002.002.002.002.002.0010.006.004.002.003.2Min
4.554.463.603.503.604.304.953.823.453.563.663.003.77Average
MLSS mg/l 5.205.004.504.404.224.906.383.644.205.002.383.404.4Max
3.803.732.903.003.053.604.453.002.753.133.192.503.3Min
42
Annex 06: External laboratory analysisQuality of the sludge (NWWTP) with comparison of standard (59/2015)
Elements
Sampled on Obligatory Method of Testing
05/09/2016 15/1/2017 Tech.Ins59/2015
Cd (ppm) 0.27 0.48 20 Birzeit Lab, ICP instrument
Cu (ppm) 71.63 123.9 1000 Birzeit Lab, ICP instrument
Ni (ppm) 6.21 11.2 300 Birzeit Lab, ICP instrument
Pb (ppm) 7.5 13.1 750 Birzeit Lab, ICP instrument
Zn (ppm) 243.46 360.3 2500 Birzeit Lab, ICP instrument
Cr (ppm) 6.93 13.4 400 Birzeit Lab, ICP instrument
As (ppm) Not Detected 0.29 N.A Birzeit Lab, ICP instrument
Mo (ppm) 1.21 0.40 N.A Birzeit Lab, ICP instrument
Se (ppm) Not Detected Not Detected N.A Birzeit Lab, ICP instrument
Hg (ppm) 0.58 0.47 16 Birzeit Lab, DMA-80 instrumentPhosphorus(ppm) 3299 6771 N.A Birzeit Lab, ICP instrument
FC (cfu/g) 4300 - N.A Birzeit Lab, iso instrument
Salmonella (cu/g) Nil Nil N.A Birzeit Lab, iso instrumentConductivityµs/cm - 1180 Birzeit Lab, iso instrument
43
Annex 07: Quality of tertiary treatment systemsQuality of the treated water (NWWTP) with comparison of reuse standard (34/2014)
Maximum limits for chemicaland biological properties
KfW reuseprojectsampled14\8\2017
USAIDreuseprojectsampled18/5/2017
Quality of Tech. Spec 34-2014
HighQuality(A)
GoodQuality(B)
MediumQuality(C)
LowQuality(D)
(BOD5) mg/l 14.8 5 20 20 20 60suspended solids (TSS) mg/l <2 6 30 30 30 90FC (Colony/100ml) Nill 2 200 1000 1000 1000(COD) mg/l 45.3 25 50 50 100 150Dissolved Solids (TDS) mg/l 975 820 1200 1500 1500 1500pH 7.74 7.54 6--9 6—9 6--9 6--9Fat, Oil, & Grease mg/l 4 4 5 5 5 5Phenol mg/l - BDL 0.002 0.002 0.002 0.002MBAS - <10 15 15 15 25NO3-N ppm BDL 2.46 20 20 30 40NH4-N mg/l 1.3 1.4 5 5 10 15Total nitrogen 6.6 11.06 40 40 40 40CL ppm 260.82 239.38 400 400 400 400SO4 ppm 88.73 97.40 300 300 300 300Na ppm 177 197 200 200 200 200Mg ppm 26.2 21.9 60 60 60 60Ca ppm 74.7 82.28 300 300 300 300SAR 5.37 5.33 5.85 5.85 5.85 5.85PO4-P ppm 16.3 11.93 30 30 30 30Al ppm 0.10 0.05 5 5 5 5Cu ppm 0.035 0.013 0.2 0.2 0.2 0.2Fe ppm 0.113 0.07 5 5 5 5Mn ppm BDL 0.04 0.2 0.2 0.2 0.2Ni ppm 0.054 BDL 0.2 0.2 0.2 0.2Pb ppm 0.03 0.03 0.2 0.2 0.2 0.2Se ppm BDL BDL 0.02 0.02 0.02 0.02Cd ppm 0.01 BDL 0.01 0.01 0.01 0.01Zn ppm 0.08 0.16 2 2 2 2Cn ppm BDL BDL 0.05 0.05 0.05 0.05Cr ppm <0.04 BDL 0.1 0.1 0.1 0.1Hg ppm <0.05 ppb 0.44 ppb 0.001 0.001 0.001 0.001Co ppm BDL BDL 0.05 0.05 0.05 0.05B ppm 0.15 0.065 0.7 0.7 0.7 0.7Ag ppm BDL 1E. coli (Colony/100ml) Absent Absent 100 1000 1000 1000Nematodes (eggs/L) Absent Absent 1>= 1>= 1>= 1>=
BDL = below detection limit
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16. Photos
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