New York State Energy Research and Development Authority FLEXTECH STUDY Town of Ulster Wastewater Treatment Plant October 2019
New York State Energy Research and Development
Authority
FLEXTECH STUDY Town of Ulster Wastewater Treatment Plant
October 2019
FLEXTECH STUDY: TOWN OF ULSTER WASTEWATER TREATMENT PLANT
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FLEXTECH STUDY
TOWN OF ULSTER
WASTEWATER
TREATMENT PLANT
Prepared for:
James Quigley
Town Supervisor
Town of Ulster WWTP
1101 Dogwood Street
Kingston, NY 12401
Prepared by:
Arcadis of New York, Inc.
855 Route 146
Suite 210
Clifton Park
New York 12065
Tel 518 250 7300
Fax 518 371 2757
Our Ref.:
02255220.0000
Date:
October 7, 2019
This document is intended only for the use of
the individual or entity for which it was
prepared and may contain information that is
privileged, confidential and exempt from
disclosure under applicable law. Any
dissemination, distribution or copying of this
document is strictly prohibited.
Daniel J. Loewenstein, PE
Senior Vice President
FLEXTECH STUDY: TOWN OF ULSTER WASTEWATER TREATMENT PLANT
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FLEXTECH STUDY: TOWN OF ULSTER WASTEWATER TREATMENT PLANT
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CONTENTS
Acronyms and Abbreviations ........................................................................................................................ iii
Executive Summary ................................................................................................................................. ES-1
1 Introduction ............................................................................................................................................. 1
2 Facility Description .................................................................................................................................. 1
2.1 Equipment Description .................................................................................................................... 1
2.2 Utilities ............................................................................................................................................ 2
2.2.1 Electricity Use ...................................................................................................................... 2
2.2.2 Propane Use ........................................................................................................................ 2
2.3 Energy Use Breakdown .................................................................................................................. 3
3 Energy Conservation Measures .............................................................................................................. 3
3.1 ECM 1: Replace Influent Pumps ..................................................................................................... 3
3.2 ECM 2: Compare Grit Removal Systems ....................................................................................... 4
3.3 ECM 3: Compare UV Disinfection Systems ................................................................................... 5
3.4 ECM 4: Replace Anaerobic Digester Mixing System ..................................................................... 6
3.5 ECM 5: Digester Heating System ................................................................................................... 7
4 Screening Evaluation – Non-Energy Task .............................................................................................. 9
5 Anaerobic Digesters Evaluation – Non-Energy Tasks .......................................................................... 10
5.1 Sludge Thickening ........................................................................................................................ 11
5.2 CHP System ................................................................................................................................. 11
5.3 Digester Cover Replacement ........................................................................................................ 12
5.4 Haul Un-Stabilized Sludge ............................................................................................................ 12
6 Recommendations ................................................................................................................................ 14
TABLES
Table ES1 - Summary of ECM Recommendations, Costs and Savings…………………………………..ES-2
Table ES1 - Summary of ECM Recommendations, Costs and Savings ....................................................... 2
Table 1 - WWTP Power Usage and Cost Summary ..................................................................................... 2
Table 2 - Pumping Energy Savings Estimates .............................................................................................. 4
Table 3 - Grit Removal Energy Savings Estimates ....................................................................................... 4
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Table 4 - UV Disinfection Energy Savings Estimates ................................................................................... 5
Table 5 - Anaerobic Digester Mixing Energy Savings Estimates .................................................................. 7
Table 6 – Anaerobic Digester Heating System Energy Savings Estimates .................................................. 8
Table 7 - Influent Screening Operations and Budget Estimates ................................................................. 10
Table 8 – Anaerobic Digester Heating System Energy Savings Estimates ................................................ 11
Table 9 - Anaerobic Digester Tank Cover Replacement Budget Estimates ............................................... 12
Table 10 - Sludge Handling Costs Analysis ................................................................................................ 14
FIGURES
Figure 1 - Ulster WWTP Overview
Figure 2 - Electricity Usage by Process Type
Figure 3 - Propane Usage by Process Type
Figure 4 - All Energy Source Usage by Process Type
Figure 5 - Influent Pumps Design Curve and Field-Tested Curves
APPENDICES
Appendix A – Engineer’s Opinion of Probable Costs
Appendix B – Manufacturers Cut-Sheets
Appendix C – Historical Energy Costs
Appendix D - Calculations
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ACRONYMS AND ABBREVIATIONS
ECM Energy Conservation Measure
MGD Million Gallons per Day
RBC Rotating Biological Contactors
WWTP Wastewater Treatment Plant
NYS DEC New York State Department of Environmental Conservation
SPDES State Pollution Discharge Elimination System
CHP Combined Heat and Power
UV Ultraviolet
UVT Ultraviolet Transmittance
UCRRA Ulster County Resource Recovery Agency
CHG&E Central Hudson Gas & Electric
SBC System Benefit Charge
GPM Gallons per Minute
SCF Standard Cubic Feet
FlexTech Flexible Technical Energy Assessment
kWh Kilowatt Hours
HP Horsepower
ft3/lb-VSR cubic feet of gas per pound of Volatile Solids Reduced
SRT Solids Retention Time
VFD Variable Frequency Drive
NG Natural Gas
WSEL Water Surface Elevation
thm Terms
MMBTU Million British Thermal Units
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EXECUTIVE SUMMARY
The Town of Ulster owns and operates a wastewater treatment plant (WWTP) that discharges to the
Esopus Creek. The WWTP last underwent upgrades in the late 1990s where many of the liquid stream
processes were replaced, with the exception of influent screening. Much of the equipment at the WWTP
is between 20 and 50 years old.
Arcadis of New York, Inc. (Arcadis), in conjunction with Brinnier & Larios, P.C. (B&L) assessed the energy
consumption, operability, and the present over-all WWTP process at the Ulster facility. A Flexible
Technical (FlexTech) energy assessment was completed on existing and proposed high energy demand
equipment, including the influent pumps, the addition of wet-stream grit removal, UV disinfection, and
anaerobic digester mixing and heating systems. The goal of the study was to identify energy savings
opportunities associated with replacing aging units at the facility.
Under Energy Conservation Measure (ECM) 1, the influent pumps were field tested and determined to be
under-performing their design curves. Pumps can be replaced with new proposed pumps, which would
result in a simple payback equal to the expected life. The proposed pumps would have the capacity to
pump the peak plant flow, in addition to providing energy savings. Grit removal systems were compared
under ECM 2 for energy efficiency and feasibility of incorporation into the treatment process. Compared
to each other, since there isn’t a current grit removal system, the vortex type has a payback of 4.5 years
and is recommended over the aerated type. Under ECM 3, the existing UV disinfection system energy
use was calculated and compared with estimated energy use to operate open-channel and enclosed
systems. The existing UV disinfection system’s energy use efficiency under performs all the UV
disinfection systems analyzed for feasibility. It is estimated that a replacement of the UV system with an
enclosed system will result in the smallest total project cost but has an estimated pay-back of 118 years.
In addition to a decrease in energy consumption, the proposed system will improve hydraulics, reduce the
number of UV lamps used per year and reduce operational labor with automatic wiping system to keep
the lamps clean. ECM 4 includes a review of the digester mixing system, which is currently a pumped
mixing setup. The recommended replacement with lower horsepower motors and VFD equipment will
provide the highest energy savings and a 12-year payback. ECM 5 reviewed expected energy savings of
upgrading the existing propane boiler with a new dual-fuel or mixed fuel boiler which can fire natural gas
or digester gas. The recommended equipment will provide a payback of 34 years. Improvements will
provide a more stable operation of the digestion process.
Additional technical reviews were performed on the feasibility of incorporating influent screening
equipment, and improvements to the anaerobic digester processes. The digester heating system,
digester tank covers, and sludge thickening systems were reviewed for design adjustments and
upgrades. The digesters are currently operating outside of design conditions. The digester tank
temperature is regularly dipping below appropriate operating temperatures for mesophilic anaerobic
digestion. The digesters are operating at volumetric capacity, evident in the calculated solids retention
time (SRT) in the primary digester. Unit processes and associated equipment was reviewed to improve
these operational deficiencies. Installation of a combined heat and power (CHP) unit was reviewed for
feasibility to aid in the digester heating process and electricity production. Upgrades to the digester
heating system and incorporation of sludge thickening prior to digestion will improve the operational
parameters of the digesters.
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Table ES1 - Summary of ECM Recommendations, Costs and Savings
Measure
Description Status
Fuel
Type
Saved
Electric
Demand
Savings
(kW)
Electric
Supply
Saved
(kWh)
Fuel
Saved
(mmBTU)
Percent of
Savings to
Total Fuel
Consumed
Annual
Dollars
Saved*
($)
Estimated
Budget
($)
Simple
Payback
(Years)
Emissions
Reduction
(lbs CO2e)
EMC 1: 20-HP
Flygt pumps R Elec 3 84,600 N/A 53% $8,500 $191,400 23 25
ECM 2: Vortex
Grit Removal R Elec 1.5 13,100 N/A 62% $1,300 $379,000 4.5 3.9
ECM 2: Aerated
Grit Removal NR Elec N/A N/A N/A N/A N/A $373,000 N/A N/A
ECM 3: Wedeco
Enclosed UV
Disinfection
R Elec 6.5 30,900 N/A 64% $3,100 $364,000 118 9.1
ECM 3: Suez
Open-Channel
UV Disinfection
NR Elec 5 19,300 N/A 40% $1,900 $365,600 189 5.7
ECM 3: Trojan
Open-Channel
UV Disinfection
NR Elec 1 13,500 N/A 28% $1,350 $803,600 595 4.0
ECM 3: Wedeco
Open-Channel
UV Disinfection
NR Elec 8 34,400 N/A 71% $3,400 $247,100 72 10
ECM 4: Pumped
Digester Mixing R Elec 6 40,500 N/A 62% $4,100 $49,050 12 12
ECM 4: Draft
Tube Digester
Mixing
NR Elec 5 32,700 N/A 50% $3,200 $135,000 41 9.6
ECM 4: Linear
Motion Digester
Mixing
NR Elec 2.5 16,300 N/A 25% $1,600 $282,000 172 4.8
ECM 5: Digester
Heating System
(Dual-Fuel)
NR NGas N/A N/A 264 5.3% $2,200 $145,000 79 0.4
ECM 5: Digester
Heating System
(Mixed)
R NGas N/A N/A 763 16% $6,600 $222,000 34 1.2
Total
(Recommended
Only)
17 169,100 280 $23,600 $1,210,000 51 51
Notes: (1) R = Recommended, NR = Not Recommended * Energy cost estimates are based on total per kWh cost of $0.10
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1 INTRODUCTION
The Town of Ulster owns and operates a wastewater treatment plant (WWTP) that discharges to the
Esopus Creek under State Pollution Discharge Elimination System (SPDES) NY0021563 as administered
by the New York State Department of Environmental Conservation (NYS DEC). The WWTP was last
upgraded in the late 1990s where most of the liquid stream processes were replaced, except for influent
screens. Much of the equipment at the WWTP is more than 20 years old.
The objective of this FlexTech study is to complete energy evaluations at the WWTP to determine the
technical and economic feasibility of reducing the energy usage through energy efficiency and
conservation measures. In addition, Arcadis evaluated the feasibility of improving the digestion process,
employing combined heat and power (CHP), and replacing the influent solids grinder with screens which
are not included as part of the FlexTech funding but are included in the report (refer to Sections 4 and 5).
2 FACILITY DESCRIPTION
The Ulster WWTP was constructed in 1970 as a secondary treatment plant consisting of primary settling,
a single stage trickling filter, final clarification and chlorine disinfection. The 1998 upgrade replaced the
trickling filter process with rotating biological contactors (RBCs) and the chlorination process with
ultraviolet (UV) disinfection. Other improvements consisted of converting the primary clarifier to a final
clarifier, construction of an additional final clarifier, and converting the existing final clarifiers to primary
clarifiers. Figure 1 depicts an aerial representation of the WWTP.
The upgrade included an increase of the SPDES permitted flow to 1.6 million gallons per day (MGD).
During the period from January 2018 to December 2018, the average influent flow rate treated by the
WWTP was approximately 1.0 MGD. Consistent with 10-State Standards, a peaking factor of 3.0 was
applied to the design average daily flow to estimate the design peak hourly flow of 4.8 MGD.
The facility consists of open and covered tanks, covered RBCs, and five buildings: 1) Administration and
Control Building, 2) Blower and Emergency Generator Building, 3) UV Disinfection Building, 4) Sludge
Treatment and Garage, and 5) Digester Control Building.
2.1 Equipment Description
Raw wastewater enters the WWTP at the southwestern corner of the Administration Building into an
influent channel which is equipped with a Muffin Monster grinder; a secondary channel has a manual bar
rack. Wastewater then accumulates in a wet-well and is pumped to a splitter box by one or more (total of
three) 20-HP submersible dry-pit pumps. The pumps were replaced during the 1998 upgrade and recently
had new single vane impellers installed. There is a fourth, original vertical turbine pump, which is currently
not used. Typical daily operations require two pumps operating during day-time hours, and one pump
operating during night-time hours.
From the splitter box, wastewater flows by gravity to the primary clarifiers, primary effluent flows by gravity
to the aerated RBCs, secondary clarifiers, and into the UV Disinfection Building. The UV disinfection is
comprised of five pressurized UV reactors, three of which contain 48 lamps (large reactors), the
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remaining two contain 37 lamps (small reactors). The UV disinfection system is required by the SPDES
permit to be operational during the recreational season, May 1st until October 31st. Typically two large
reactors and one small reactor are in operation, with a third large reactor coming online when Ultraviolet
Transmittance (UVT) readings indicate it is needed. Effluent is discharged to the Esopus Creek.
Primary sludge is pumped through a sludge degritter and is thickened in a gravity thickener, then pumped
into the primary anaerobic digester. Secondary sludge is pumped directly into the primary digester. The
two-phase mesophilic anaerobic digestion system consists of a primary tank, which is mixed and heated,
and a secondary tank, which is equipped with a floating cover to collect digester gas. Currently, the
digester gas is flared. The digested sludge is dewatered in a belt filter press before being hauled to the
Ulster County Resource Recovery Agency (UCRRA) facility in New Paltz.
2.2 Utilities
The electric utility is supplied by Direct Energy, with delivery service from Central Hudson Gas & Electric
(CHG&E). Propane gas is supplied by both Heritage and Bottini over the time period reported herein.
Annual utility costs for March 2018 through February 2019 were $114,300 for electricity and $25,700 for
propane gas. The Town of Ulster WWTP pays into the Systems Benefit Charge (SBC) through its
electricity bills.
Electrical and propane gas utility data from January 2017 through February 2019 were provided by the
WWTP and reviewed. The blended utility data for usage from the most recent available 12-month period,
March 2018 to February 2019, is presented in Table 1.
Table 1 - WWTP Power Usage and Cost Summary
Energy Type Usage Average
Blended Rate Total Costs
Electricity 1,125,300 kWh $0.10 $114,300
Propane Gas 19,600 gal $1.31 $25,700
2.2.1 Electricity Use
The Ulster WWTP’s total annual electrical consumption for March 2018 to February 2019 was 1,125,300
kWh, with a high of 111,680 kWh in May and a low of 70,720 kWh in January. A review of the electricity
bills for the same time period was performed to determine the average blended rate of electricity. The
delivery charges average $0.03/kWh, and the electricity supply averages $0.07/kWh with all fees and
taxes included. The blended rate is $0.10/kWh. A breakdown of the electrical energy use distribution of
processes at the Ulster WWTP is shown in Figure 2.
2.2.2 Propane Use
Propane gas usage from the period from March 2018 to February 2019 ranged from a high of 3,230
gallons in March 2018, to a low of 670 gallons in September 2018. The average monthly delivery was
1,640 gallons. An approximate distribution of propane gas use at the WWTP is shown in Figure 3.
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2.3 Energy Use Breakdown
Using the electrical and propane gas usage described above, results of energy use breakdown
calculations are presented in Figure 4. The RBC blowers and digester heating systems use the most
energy of any individual end use item at the WWTP.
3 ENERGY CONSERVATION MEASURES
3.1 ECM 1: Replace Influent Pumps
The existing influent pumping operations are accomplished by three submersible dry-pit pumps. The
three duty pumps are Davis EMU (now Wilo), 20-HP pumps and were installed in the 1998 WWTP
upgrade. These pumps were recently retrofitted with single vane impellers. A fourth pump, a vertical
turbine, is not used as a duty pump; it is turned on periodically to confirm functionality. On April 2, 2019 a
pump test was performed on the three pumps used for operations (pump #1, pump #2, and pump #3).
Flow through the pumps was controlled with the outlet pump control valve; the variable frequency drive
(VFD) flow controls were deactivated during the test. Flow, outlet pressure, wet-well water surface
elevation (WSEL), and amperage were recorded during the test for a range of discharge pressures.
Figure 5 shows the measured pump curve against the design curve provided by Wilo for the new
impellers.
Through analysis of the typical pump operations, flow data provided by the facility operators, and the field
verified pump curves, the actual duty point was determined to be approximately 700 gallons per minute
(gpm) at 27 ft of head. The design point of pumps #1 and #2 appears to be 1,070 gpm, at 42.3 ft of head
based on the manufacturers pump curves. The pump test indicated that all three active pumps operate on
a similar curve. It was determined that the existing pump, motor, and impeller combination are running
significantly below the manufacturers pump curves.
The typical annual electric consumption of the influent pumping operations was determined using the field
observed pump curves. A typical diurnal hourly flow curve was used to represent the WWTP’s annual
average influent flow of 1.0 MGD. The pump test curves were then applied to the diurnal flow entering the
WWTP to determine the pumps operation (i.e. number of pumps running, VFD settings). The average
electrical consumption of the existing pumps is estimated to be 161,000 kWh annually.
New pumps were proposed based on the permitted design average daily flow for the WWTP, which is 1.6
MGD. The actual average daily flow into the plant from the data collected during 2017-2018 is 1.0 MGD.
Consistent with 10-State Standards for designing pump stations, a peak factor of 3.0 was applied to the
design average daily flow to estimate the design peak hourly flow of 4.8 MGD. The proposed pumps are
capable of pumping the design peak hourly flow with 3 pumps running and one pump in standby.
Proposed equipment presented later in this report affecting the system head curve were considered when
sizing the proposed pumps. The new pump design curves, provided by Flygt for the NT 3153 MT ~3 433
model, were applied to the influent flow data, estimating the average annual electricity usage of the
pumps to be 76,400 kWh.
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Table 2 - Pumping Energy Savings Estimates
* Energy cost estimates are based on total per kWh cost of $0.10 ŧ Budget estimates are a simple estimate of equipment purchase and installation. Appurtenant work and equipment not included.
Engineer’s Opinion of Probable Cost can be found in Appendix A.
Replacement of the existing pumps with the proposed pumps will result in an energy savings of
approximately 85,000 kWh, or $8,500 per year, based on a cost of $0.10 per kWh. Applying these
savings to the cost of purchasing and installing the new pumps and VFD controls results in a simple pay-
back of 23 years. Typically, pumps can be expected to operate up to 25 years. The existing pumps have
been in operation for 21 years. Though the replacement pumps payback is near that of their supposed
useful life, the update is recommended due to the existing pumps operating off their design curves
making them unable to pump the design flow of 4.8 MGD.
3.2 ECM 2: Compare Grit Removal Systems
The Ulster WWTP is currently not equipped with a grit removal system in the headworks. Grit removal
improves the wastewater treatment process by removing larger inorganic materials, improving longevity of
equipment and reducing loadings on the anaerobic digester. A grit removal system would be ideally
located upstream of the influent pumps and downstream of the grinder or a bar screen, however, due to
site constraints a system can be placed immediately upstream of the existing Splitter Box #1, resulting in
grit removal occurring prior to the flow reaching the primary clarifier.
Two grit removal system types were evaluated: 1) vortex grit removal system, and 2) aerated grit removal
system. Since this is a new installation, the incremental costs and savings of the proposed options were
compared.
Table 3 below outlines the equipment costs, energy consumption estimates, and simple pay-back
estimates for each design option.
Table 3 - Grit Removal Energy Savings Estimates
Grit Removal
System
Equipment
Power Rating
(hp)
Annual Energy
Consumption
(kWh)
Annual
Energy
Costs*
($)
Estimated
Budget ŧ
($)
Simple
Payback+
(years)
Vortex Type 1 6,540 $650 $379,000 4.5
Aerated Type 3 19,600 $1,960 $373,000 N/A
* Energy cost estimates are based on total per kWh cost of $0.10
Pumps
Annual Energy
Consumption
(kWh)
Annual
Energy
Costs*
Estimated
Budget ŧ
Annual Energy
Savings
Simple
Payback
(years)
Existing 161,000 $16,100 N/A N/A N/A
Proposed 76,400 $7,640 $191,400 $8,500 23
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ŧ Budget estimates are a simple estimate of equipment purchase, installation, and concrete tank construction. Appurtenant work and
equipment not included. Engineer’s Opinion of Probable Cost can be found in Appendix A. +As compared to the cost of operating the Aerated Type grit system
A vortex grit system would result in the lowest annual energy costs. The estimated budget is higher than
that of the aerated grit system. The estimated 10-year cost (capital and operational) of the grit systems
are $385,500 for the vortex type, and $392,600 for the aerated type.
3.3 ECM 3: Compare UV Disinfection Systems
The WWTP currently uses an enclosed UV disinfection system designed by UV Water Purification, Inc.
which replaced a chlorine disinfection system in 1998.
The system is comprised of five UV reactors, which are a combination of large units with 48 lamps, and
small units with 37 lamps. The lamps are low-pressure lamps emitting UV light in the 254-nanometer
wavelength. Each lamp uses 65 watts of electricity and the system does not have any turn-down
capabilities. The operators have indicated that there is a distinct difference in the headloss of the large
and small units where more flow goes to the smaller units and less flow goes to the larger units.
The electrical usage of the existing UV disinfection system was estimated based on interviews with plant
operators and the SPDES permit requirements. The permit requires disinfection between May 1st and
October 31st. The operators turn on two large and one small unit from May 1st until the middle of June, at
which time an additional large unit is added to the treatment process until the end of October when all
units are powered off. Considering the operating procedures, number of lamps in operation, and lamp
wattage the total annual electrical usage of the existing UV system was estimated to be 48,500 kWh.
Four alternative UV Disinfection systems were reviewed, one enclosed reactor and three open channel
systems: 1) Wedeco’s LBX enclosed system, 2) Suez’s Aquaray 40 HO Vertical Lamp open-channel
system, 3) Trojan’s UV 3000 Plus open channel system, and 4) Wedeco’s TAK open channel system.
The evaluated enclosed reactor would be placed in the same building as the existing UV disinfection
system with a different configuration of one duty and one standby unit. UV system manufacturers have
made significant progress on technology in open channel systems, which are more commonly installed at
WWTPs. The open channel system would be placed downstream of the existing UV Building in a new
channel cut into the effluent pipe to the northwest of the UV Building. The open channel system would
need to be protected from sunlight by a canopy cover. Due to the large amount of site-work and new
infrastructure needed to establish an open-channel UV disinfection system the total installed cost tends to
be higher than an enclosed solution (see Appendix A for engineer’s opinion of probable cost). Table 4
below outlines the equipment costs, energy consumption estimates, and simple payback estimates for
each design option.
Table 4 - UV Disinfection Energy Savings Estimates
UV Disinfection System
Minimum
UV dose
(mJ/cm2)
Annual
Energy
Consumpti
on
(kWh)
Annual
Energy
Savings* ($)
Estimated
Budget ŧ
($)
Simple
Payback
(years)
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Existing – Enclosed System 30 48,500 N/A N/A N/A
Wedeco – Enclosed System 60 17,600 $3,090 $364,000 118
Suez – Open Channel 30 29,200 $1,930 $365,600 189
Trojan – Open Channel 80 35,000 $1,350 $803,600 595
Wedeco – Open Channel 60 14,100 $3,440 $247,100 72
* Energy cost estimates are based on total per kWh cost of $0.10 ŧ Budget estimates are a simple estimate of equipment purchase, installation, and concrete tank construction. Appurtenant work and
equipment not included. Engineer’s Opinion of Probable Cost can be found in Appendix A.
Wedeco’s open channel unit would result in the highest annual energy savings, 34,400 kWh or $3,440
each year at the current electricity rates. Wedeco’s enclosed system provides comparable energy savings
to the open channel solution and will result in smaller construction costs due to the existing UV
disinfection building. The proposed enclosed system is equipped with automatic wipers to reduce labor
associated with maintaining the system. Estimated budget costs shown in Table 4 do not include
construction of a canopy over the new open UV channel, yard piping, electrical work, and instrumentation
and controls. When these costs are considered, the enclosed system becomes the most economical
option (Appendix A).
The open channel designs vary between the different manufacturers based on number of modules,
number of and power rating of UV lamps, and turn-down capabilities. Trojan’s proposal prescribes a UV
design dose of 80 mJ/cm2. Trojan cites the UV Disinfection system being downstream of RBCs which
may have periodic slough off of biological material as to their reasoning for the high dosage and
references Ultraviolet Disinfection Guidelines for Drinking Water and Water Reuse, published by the
National Water Research Institute. A pilot study of the Ulster effluent performed by Trojan in 2017 shows
a dose of 60 mJ/ cm2 provides adequate disinfection. The Wedeco enclosed system provides a minimum
dose of 60 mJ/cm2, which exceeds the minimum recommendations of 30 mJ/cm2 by 10-State Standards.
The enclosed system proposed by Wedeco is recommended for upgrade to the UV Disinfection system.
This upgrade will improve hydraulics, decrease energy consumption, and decrease the number of UV
lamps used per year by the disinfection process.
Installation of the UV system in an open channel downstream of the existing UV building could provide
the additional advantage of allowing the use of the building for future process equipment. The UV
disinfection building was reviewed to be used to house sand filters for phosphorus removal in preparation
for possible future effluent limits of phosphorus. Preliminary calculations indicate the footprint of the
building would need to be expanded up to 2,000 sq. ft. to accommodate a rapid sand filter capable of
treating the peak hourly flow rate of 4.8 MGD. A UV channel could be built accounting for headloss from
the sand filter in the hydraulic profile. The added benefit of the UV building as a slow sand filter does not
appear to offset the cost increase of placing UV disinfection in a new open-channel configuration.
3.4 ECM 4: Replace Anaerobic Digester Mixing System
The anaerobic digestion process is driven by mixing and temperature control. The primary digester is
mixed by two 10 HP mixing pumps (one duty and one standby) that pump sludge out of the primary
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digester and back into the primary digester through a nozzle. To maintain proper anaerobic digestion the
digester must be mixed continuously, resulting in a large and continuous power draw for the process.
Three alternative digester mixing systems were reviewed: 1) pumped mixing system, 2) linear motion
mixing system, and 3) vertical draft tube mixing system. Any of the proposed systems would require the
primary digester to be taken offline and completely emptied during retrofit. The secondary digester would
be utilized as the primary digester during this time. Due to the potential need for future tank emptying
procedures, the existing pumped mixing system can be maintained operational in the secondary digester
tank for purposes of back-up operations.
Table 5 - Anaerobic Digester Mixing Energy Savings Estimates
Digester Mixing
System
Equipment
Power Rating
(hp)
Annual
Energy
Consumption
(kWh)
Annual
Energy
Savings *($)
Estimated
Budget ŧ
($)
Simple
Payback
(years)
Existing - Pumped
Mixing System 10 65,350 N/A N/A N/A
Pumped Mixing
System 3.8 24,800 $4,050 $49,050 12
Linear Motion Mixing
System 7.5 49,000 $1,600 $282,000 172
Vertical Draft Tube
Mixing System 5 32,700 $3,300 $135,000 41
* Energy cost estimates are based on total per kWh cost of $0.10 ŧ Budget estimates are a simple estimate of equipment purchase and installation. Appurtenant work and equipment not included.
Engineer’s Opinion of Probable Cost can be found in Appendix A.
Replacement of the existing system with an upgraded pumping system of higher efficiency pumps with
VFD capabilities would result in the highest annual energy savings, 40,500 kWh or $4,050 each year at
the current electricity rates. With a budget estimate well below that of the other alternatives, the simple
payback period is the shortest of all the alternatives at 12 years.
3.5 ECM 5: Digester Heating System
The temperature inside the Primary Digester is maintained by a Weil-McLain propane boiler and Dorr-
Oliver spiral heat exchanger installed during the original 1970 design of the WWTP. The target sludge
temperature is 98oF, however the average temperature during 2017 and 2018 was 96.8 oF, with
temperatures dipping as low as 94.2 oF during winter months. A stable operating temperature is important
to maintain bacterial functions. Generally, temperature changes greater than 2 oF per day can affect
process performance.
Sludge is withdrawn from the primary digester with a 5 HP pump at 75 gpm and pumps through the heat
exchanger, where hot water from the propane boiler is run at 40 gpm. The heat exchanger has a
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specified capacity of 200,000 BTU/hr. Operations staff indicated the heat exchanger had historically been
able to maintain the digester at the correct temperature up until the last two years.
The existing propane boiler is nearing the end of its useful life and is no longer manufactured by Weil-
McLain. The dual-fuel capabilities of the existing boiler are not operational due to maintenance difficulties.
An equivalent sized dual-fuel boiler can be installed which can be fired by either digester gas or natural
gas (which is currently being installed at the WWTP). This system will allow the boiler to utilize digester
gas when the heating demand is less in the summer and natural gas in the winter when heating demand
is greater. The relatively low gas production rates of the digester is insufficient to supply the higher
heating demand of the digester and facility buildings in the colder winter months. The digester gas is
estimated to reduce the natural gas demand for heating by 264,000 standard cubic feet (scf), which is
approximately $2,200 based on a per thousand scf cost of $8.29. The annual estimated cost to operate
the dual-fuel boiler is $12,000.
A mixed fuel boiler is estimated to cost $222,000 to purchase and install but would utilize the digester gas
year-round as the boiler has the ability to blend the natural gas and digester gas. The cost of natural gas
offset of utilizing the boiler gas all-year round is only enough to decrease the simple payback to 34 years
which is longer than the life of the equipment.
A replacement heat exchanger is estimated to cost approximately $79,000 for purchase and installation,
the Engineer’s Opinion of Probable Cost can be found in Appendix A. A review of the energy costs,
energy savings, and simple payback of the dual-fuel boiler are outlined in Table 6.
Table 6 – Anaerobic Digester Heating System Energy Savings Estimates
Digester Heating
System
Annual
Natural Gas
Savings
(thousand scf)
Annual
Natural Gas
Needs
(thousand scf)
Annual
Energy
Savings*
($)
Budget
Estimate ŧ
($)
Simple
Payback
(years)
Dual-Fuel Boiler System
with Auxiliaries 264 1,700 $2,200 $145,000 79
Mixed Fuel Boiler System 793 1,700 $6,600 $222,000 34
* Electricity cost estimates are based on total per kWh cost of $0.10. Natural Gas cost based on $8.29/thousand scf. ŧ Budget estimates are a simple estimate of equipment purchase and installation. Engineer’s Opinion of Probable Cost can be found
in Appendix A.
The replacement of the existing boiler with either the dual-fuel boiler or mixed fuel boiler and replacement
heat exchanger will provide improved heating capabilities of the primary anaerobic digester. The simple
payback period exceeds the expected life of the equipment, however due to the existing equipment being
in disrepair and no longer operating to manufacturer specifications, the upgrade to new equipment is
recommended. Boiler choice will largely depend on the broader sludge processing and handling
upgrades, if the digester process is abandoned in preference for shipment to a regional biosolids
processing facility, a boiler with digester gas utilization capabilities will be unnecessary.
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4 SCREENING EVALUATION – NON-ENERGY TASK
The Ulster WWTP does not have influent screening as part of the wastewater treatment process.
Currently, large solids are processed by a Muffin Monster grinder in the influent building before the flow
reaches the influent pumps. Even with the grinder, operators have reported many occurrences of rags
and flushable wipes wrapping around the pump impellers which reduces pump capacity and creates
maintenance activities for staff. Installing a mechanical screening mechanism upstream of the pumps
would improve the daily and long-term operational efficiency of the pumps, as well as likely extend their
useful life. Rags also plug the RBC media and accumulate in the digesters.
The influent channel passes through the headworks building 23.5 ft below grade. The influent channel is
two feet wide and splits into primary and bypass channels which are each one foot 10-inches wide. The
outer edges of each channel are flush with the building walls and are separated by a four foot 4-inch wide
concrete “island” floor. The available space in the influent building is very constrained. Most of the
existing wall space is occupied by stairwells, HVAC ducts, piping, and electrical equipment and conduits.
Likely, any screening solution will require 1) adjustment to the existing equipment in the building, 2)
mounting in a vertical or near vertical orientation, and 3) taking the channel orientation against the
building wall into consideration.
Typical screening operations capture rags and debris on the upstream side of an angled screen, a
rotating rake clears the screen by lifting the captured solids to grade and depositing the screened
materials into a container or washer/compactor. Due to the space constraints of the building, this
traditional process will be difficult to achieve. Several alternative design options were reviewed for
feasibility. The options include: 1) installation of a mechanically raked bar-screen in a new structure
upstream of the Administration Building, 2) installation of a vertically mounted micro-strainer with
washer/compactor, and 3) a mechanical bar screen with a washer/compactor placed on the headworks
floor that will lift the screenings to grade after compaction.
Arcadis reviewed several screening systems to assess the feasibility of each option. Option #1, installing
the mechanically raked screen in a new structure upstream of the existing Administration building, will
require the construction of a 400 sq. ft. addition onto the south-west side of the Administration Building
where the existing raw sewage comes into the Administration Building. This building addition is estimated
to cost $420,000. The building addition would facilitate the installation of an angled mechanically raked
bar screen mounted away from the building walls, eliminating the design concerns relating to the influent
channel and building orientations stated previously.
Option #2, installing a micro-strainer with built-in compaction, will have a high solids removal rate, and
can be mounted in the existing channel. Typical micro-strainers with compactors are installed at an
inclined angle, but to accommodate the constraints of the building, a micro-strainer with a vertical
configuration is proposed. Compacted screenings will be conveyed to grade via a compaction tube. This
option will likely require relocation of existing HVAC ducts within the building. Due to the channel wall
being flush with the building wall, the slide rail, a mechanism used to lift the micro-strainer out of the
channel for routine maintenance, cannot be installed. The maintenance on the submerged mechanicals
are recommended to be performed every 6 to 12 months and will require the installation of a structural
beam and hoisting system to raise the micro-strainer out of the channel. The micro-strainer is expected to
have approximately 5-feet of space above it available for installation of a hoist and beam assembly.
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Option #3, installing a mechanically raked bar screen combined with a washer/compactor which conveys
the compacted screenings to grade, was also considered. The compacted conveyance will be a vertical
distance of approximately 19 ft from the building floor up to grade. This is a relatively long distance to
convey compacted screenings. The design of the new washer/compactor technology is specifically
created to facilitate a long vertical conveyance of the screenings. The mechanically raked bar screen
made by Duperon is unique in that it does not contain any mechanicals that are mounted in the channel
and thus does not need to be lifted out of the channel for maintenance. This allows it to be mounted in the
channel against the building wall without concern for lift equipment.
Table 7 below outlines expected costs of equipment for each screening option.
Table 7 - Influent Screening Operations and Budget Estimates
Screening System
(Option #)
Annual Energy
Costs*
($)
Estimated
Budget ŧ
($)
20-Year Total
Cost
($)
Conventional Screening,
Washer/Compactor (#1) $5,200 $450,000 $555,000
Micro-strainer (#2) $2,000 $189,000 $228,000
Screening and
Washer/Compactor (#3) $1,300 $260,000 $286,000
* Energy cost estimates are based on total per kWh cost of $0.10 ŧ Budget estimates are a simple estimate of equipment purchase and installation. Appurtenant work and equipment not included.
Engineer’s Opinion of Probable Cost can be found in Appendix A.
5 ANAEROBIC DIGESTERS EVALUATION – NON-ENERGY
TASKS
The primary anaerobic digester receives 7,000 gallons per day of thickened primary sludge and
unthickened secondary sludge. The sludge enters the primary digester with a solids content of
approximately 2.4%. The optimum temperature for mesophilic anaerobic digestion is 98oF.
Based on volatile solids content of thickened primary sludge, secondary sludge, and digested sludge, the
volatile solids reduction is 53%, which is slightly lower than the desired 55%. Approximately 6,600 cubic
feet of digester gas are generated per day. Anaerobic digester gas generated in the digestion system is
flared. Previously, the existing boiler could be fueled with digester gas, but due to maintenance issues,
that is no longer feasible. The digesters produce approximately 10 cubic feet of gas per pound of volatile
solids reduced (ft3/lbVSR). This is less than the typical 12 to 18 ft3/lbVSR as stated in Wastewater
Engineering Treatment and Reuse (Metcalf & Eddy, 2012).
The solids retention time (SRT) of the primary anaerobic digester was calculated to be 5.3 days based on
recorded sludge flow rates and digester tank utilization. Metcalf & Eddy recommends a minimum design
SRT for an anaerobic digester operating at 98 oF of 10 days, therefore the digester is operating below
recommended parameters and appears to have no additional capacity to accept sludge.
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5.1 Sludge Thickening
Currently, primary sludge is pumped to the gravity thickener which increases the solids content to
approximately 2.7%. Sludge from the secondary clarifiers is not thickened before being pumped to the
digesters at a solids content of approximately 2.1%. One method to increase the SRT of the digesters is
to thicken the sludge to a higher solids content, which in turn increases the capacity of the digesters. A
gravity belt thickener could be installed prior to the anaerobic digesters to thicken both the primary and
secondary sludge. A gravity belt thickener could be installed in the garage where the existing sludge
degritter is located. If grit removal is added to the liquid stream, the sludge degritter can be removed.
A gravity belt thickener processing primary and secondary sludge, is capable of increasing the total solids
to between 5 and 7%. An increase to 5% solids increases the SRT to 10.6 days, 7% results in an SRT of
15 days. The combined primary and secondary can be mixed in the existing gravity thickener and
pumped to at a rate of approximately 30 gpm, which can be processed effectively by a 1-m gravity belt
thickener according to the sizing criterion outlined in the Design of Municipal Wastewater Treatment
Plants WEF manual No. 8. A 1-m gravity belt thickener has a budget estimate of $377,000 for equipment
purchase and installation. Thickening primary sludge may produce noxious odors and odor control should
be considered.
5.2 CHP System
A CHP unit was considered to utilize the digester gas generated by the anaerobic digestion process and
offset the reliance on natural gas to heat the digester and generate power.
The mixing and heating improvements outlined in this report are estimated to increase digester gas
production to at least 12 ft3/lbVSR. The increased digester gas volume could be used in a microturbine to
generate electricity and heat as a CHP system. The electrical efficiency of a small microturbine operating
on digester gas is 26%. At this efficiency, a power generation of 15 to 23 kW could be achieved at the
Ulster WWTP. The smallest microturbine available from Capstone is 30 kW. At this time, the smallest
digester gas treatment system is suited for a higher gas flow and would use a significant portion of the
generated power. One option is to blend natural gas with the digester gas to use in a larger 65 kW
microturbine, which has a higher electrical efficiency of 29%, and an integrated heat recovery module.
The 65 kW microturbine maximum operational capacity is 842,000 BTU/hr, the digesters are expected to
produce 200,000 BTU/hr. The difference between the supplied digester gas and maximum capacity is
subsidized with natural gas, which is an annual average volume of 5,000,000 scf per year. The annual
electricity generation of the microturbine is estimated at 149,000 kWh which is approximately 15% of the
current electricity utilization of the WWTP.
The heat recovery capability of the CHP unit is estimated at 0.24 MMBTU/hr. The digester heat
requirement is less than this production, at 0.18 MMBTU/hr, however the CHP unit would be installed in
addition to a replacement heat exchanger and replacement boiler which can operate on natural gas and
digester gas, the details of which are outlined in Section 3.5 of this report.
A review of the heat and power capabilities of the 65-kW unit and associated energy cost savings are
outlined in Table 8.
Table 8 – Anaerobic Digester Heating System Energy Savings Estimates
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CHP
Annual
Electricity
Savings
(kWh)
Annual
Natural Gas
Needs
(1000 scf)
Baseline Energy
Costs*
($)
Annual NG
Costs to
Operate CHP*
($)
Budget
Estimate ŧ
($)
65 kW CHP 149,000 5,000 $37,400 $42,000 $780,000
* Electricity cost estimates are based on total per kWh cost of $0.10. Natural Gas cost based on $8.29/thousand scf. Propane cost
based on $1.31/gallon. ŧ Budget estimates are a simple estimate of equipment purchase and installation. Engineer’s Opinion of Probable Cost can be found
in Appendix A.
Due to the low gas production volumes of the anaerobic digester tank, natural gas would need to be
purchased and blended with the digester gas to effectively utilize the capabilities of the CHP unit, with a
small offset of electricity purchase. The CHP unit will cost more on an annual basis to operate than
purchasing the equivalent electricity and propane needs (baseline), eliminating any payback potential. It
is not recommended to install a CHP unit as part of the digester heating system, as the relatively low
digester gas production of the facility does not make it a feasible option for utilization of the digester gas.
5.3 Digester Cover Replacement
The primary digester currently has a fixed steel cover, the secondary digester is equipped with a floating
steel cover. Both covers were installed during the original facility construction in the 1970’s. Due to the
age of the covers, they likely need to be replaced. Utilization of digester gas presented in earlier sections
of this report requires the secondary digester cover to be a gas holding cover. Gas holding covers can be
constructed of steel or membrane. Steel covers are estimated to have a lifespan of 30 years, membrane
covers typically have a useful life of 15 years. Table 9 outlines estimated budgetary costs of installing
new digester covers.
Table 9 - Anaerobic Digester Tank Cover Replacement Budget Estimates
Digester Tank Digester Cover Type Budget
Estimate ŧ
Primary Digester Fixed Steel $180,000
Secondary Digester Floating Steel $210,000
Secondary Digester Gas Holding - Steel $220,000
Secondary Digester Gas Holding- Membrane $370,500 ŧ Budget estimates are a simple estimate of equipment purchase and installation. Engineer’s Opinion of Probable Cost can be found
in Appendix A.
5.4 Haul Un-Stabilized Sludge
Due to the high cost of sludge digestion updates and upgrades relative to the volume of sludge produced
at the WWTP, the option of sending undigested sludge to a regional biosolids facility in Albany was
evaluated. The identified facility is expected to be fully operational by 2023.
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All recommended upgrades to the anaerobic digestion process outlined in Section 5 are expected to cost
at a minimum $2.12 million (Appendix A). The recommended anaerobic digestion upgrades include: 1)
addition of a gravity belt thickener, 2) replacement of the digester heating system (heat exchanger and
boiler), 3) replacement of the digester mixing system, and 4) replacement of the covers for the primary
and secondary digester tanks. The Ulster WWTP currently produces approximately 652 tons of digested
and dewatered sludge per year for disposal, this is expected to be relatively unaffected by the
recommended upgrades. The dewatering process relies on the addition of polymer to the digested
sludge, which comes at a cost of $10,000/year. The addition of a gravity belt thickener before the
anaerobic digesters will increase the polymer demand by 100%, increasing the annual polymer budget to
$20,000. The full upgraded anaerobic digester operations annual costs include: 1) $16,000 heating costs
for the purchase of natural gas, 2) $60,000 for sludge disposal fees at the New Paltz landfill, and 3)
$10,000 in trucking costs to the New Paltz landfill. The estimated annual operating costs of the upgraded
sludge thickening, digestion, dewatering, and disposal is $106,000.
The option of delivering undigested sludge to the Albany Regional Biosolids Facility would not be
available until 2023. In the interim, the Ulster WWTP would need to upgrade the anaerobic digestion
heating system to prevent failure and purchase natural gas for heating the digester for the two-year
period. Additionally, adjustments to the existing digestion equipment to convert into sludge handling and
holding for shipment would need to be performed when the digestion process is abandoned. The
upgrades to the anaerobic digestion heating equipment includes replacement of the heat exchanger and
boiler. To convert the digestion tanks to holding tanks an aerated mixing system and a replacement tank
cover will need to be installed. The estimated construction budget for these upgrades is $1,040,000
(Appendix A). By not digesting the sludge, the volume of sludge needing to be shipped will be greater
than that of the digestion condition, estimated at about 10,900 tons per year. The trucking distance is
greater to the Albany facility than the New Paltz landfill, which will increase the trucking costs. The Albany
Regional Biosolids Facility has provided an estimated disposal fee of $72 per thousand gallons.
The annual cost estimate of undigested sludge disposal is: 1) $18,000 for sludge disposal fees at the
Albany Regional Biosolids Facility, 2) $81,000 in trucking costs, 3) $10,000 in polymer use, and 4) $4,000
for electricity to run the holding tank mixing system. This option removes the need for heating fuel to be
used in maintaining digester tank temperature after 2023 but will need to be purchased at $16,000/year
until the biosolids facility is open. The estimated average annual operating costs of abandoning sludge
digestion process at the Ulster WWTP in favor of shipping undigested sludge to the Albany Regional
Biosolids Facility is $114,000.
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Table 10 - Sludge Handling Costs Analysis
Sludge Handling Option Budget
Estimate +
Annual
Operating
Costs*
Simple Payback
(years)
Full digester upgrade w/
continued disposal at New Paltz
Landfill
$2,120,000 $106,000 132
“Stop-Gap” upgrade w/ disposal
at Albany Regional Biosolids
Facility
$1,040,000 $114,000 N/A
* Annual operating costs estimates are based on equipment energy demands, sludge disposal fees, trucking costs, polymer
purchase. Electricity costs per kWh is $0.10. Natural Gas cost based on $8.29/thousand scf. +Principal Investment is the “all-in” cost of the upgrades including: equipment purchase and installation, electrical work, concrete,
excavation, yard piping, I&C, engineering etc.
The Albany Regional Biosolids Facility disposal option has a slightly larger annual operating cost than the
full digestion process upgrade. Due to the large capital investment for the digestion process upgrade, the
simple payback for this operation in comparison to disposing undigested sludge at the biosolids facility is
132 years. There are likely operational and future facility demands which should be considered when
selecting the appropriate solution for the WWTP.
6 RECOMMENDATIONS
Arcadis provided an evaluation of Energy Conservation Measures and other non-energy measures that
could improve the energy efficiency and the overall efficiency of operations at the Ulster WWTP.
Under Energy Conservation Measure (ECM) 1, the influent pumps were field tested and determined to be
under-performing their design curves. The existing pumps should be replaced with the proposed pumps,
which would result in a payback equal to the expected life. The proposed pumps will have the capacity to
pump the peak plant flow, in addition to providing energy savings. Grit removal systems were compared
under ECM 2 for energy efficiency and feasibility of incorporation into the treatment process. Compared
to each other, since there isn’t a current grit removal system, the vortex type has a payback of 4.5 years
and is recommended over the aerated type. Under ECM 3, the existing UV disinfection system’s energy
use was calculated and compared with estimated energy use to operate open-channel and replacement
enclosed systems. The existing UV disinfection system’s energy use underperforms all the UV
disinfection systems analyzed for feasibility. It is estimated that a replacement enclosed system will result
in the smallest total project cost but has an estimated payback of 118 years. In addition to a decrease in
energy consumption, the proposed system will improve hydraulics and reduce the number of UV lamps
used per year. ECM 4 includes a review of the digester mixing system, which is currently a pumped
mixing setup. The recommended replacement with in-kind equipment will provide the highest energy
savings and a 12-year payback. ECM 5 reviewed expected energy savings of upgrading the existing
propane boiler with a new dual-fuel boiler which can fire natural gas or digester gas. The recommended
equipment, including a new heat exchanger, will provide a payback of 61 years. Improvements will
provide a more stable operation of the digestion process.
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Additional technical reviews were performed on the feasibility of incorporating influent screening
equipment, and improvements to the anaerobic digester processes. To improve the overall plant process,
it is recommended that the facility install screening equipment upstream of the influent pump station. The
Micro-strainer (Options #2) is the screening option with the lowest capital costs reviewed in this study.
However, the frequent and involved maintenance requirements of the equipment makes the option
infeasible. The screening Option #3 is a larger capital investment but will require significantly less
maintenance and has a smaller expected annual energy cost than that of the Micro-strainer.
The digester heating system, digester tank covers, and sludge thickening systems were reviewed for
design improvements and upgrades. The digesters are currently operating outside of design conditions.
Recommended upgrades to the digester heating system including a replacement boiler and heat
exchanger and incorporation of sludge thickening prior to the digester tank will improve the operational
parameters of the digesters and bring them within the suggested operational parameter of the 10-State
Standards, bringing the additional benefit of increasing the digesters capacity to accept external sludge.
The digestion tank covers are near their end of life and should be replaced.
FIGURE
ULSTER WWTP OVERVIEW
1
RBC Units
Secondary Settling
Digester Control Building
Blower BuildingSludge
Thickening Tank
Sludge Degritter& Press Building
FIGURE
8/9/
2019
11:
56:2
2 AM
ELECTRICITY USAGE BY PROCESS TYPE
2
Headworks0.2%
Pumping12.1% Primary Treatment
0.4%
Secondary Treatment59.6%
Disinfection3.6%
Sludge Treatment10.6%
Buildings8.9%
Other4.4%
FIGURE
8/9/
2019
11:
56:2
2 AM
PROPANE USAGE BY PROCESS TYPE
3
Building Heating51%
Digester Heating49%
FIGURE
8/9/
2019
11:
56:2
2 AM
ALL ENERGY SOURCE USAGE BY PROCESS TYPE
4
Headworks0.1%
Pumping8.3%
Primary Treatment0.3%
Secondary Treatment40.7%
Disinfection2.5%
Sludge Treatment7.2%
Buildings6.1%
Other3.0%
Building Heating16.2%
Digester Heating15.6%
FIGURE
8/9/
2019
11:
56:2
2 AM
INFLUENT PUMPS DESIGN CURVE AND FIELD-TESTED CURVE
5
0
10
20
30
40
50
60
70
80
90
100
0 500 1000 1500 2000
Hea
d (ft
)
Flowrate (gpm)
Pump 1&2 - Design Curve
Pump 3 - Design Curve
Pump 1 - Test Data
Pump 2 - Test Data
Pump 3 - Test Data
System Curve - Max Head
System Curve - Min Head
DESCRIPTION QTY. UNIT TOTAL
Equipment
Pumps 4 EA $ 102,800
VFD & Controls 1 EA $ 88,600
Equipment + Installation SUBTOTAL $ 191,400
Construction
Electrical 1 EA $ 40,000
I&C 1 EA $ 22,000
$ 260,000
10% $ 26,000
25% $ 65,000
30% $ 78,000
$ 430,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostInfluent Pumping
OPINION OF PROBABLE CONSTRUCTION COST
$40,000.00
$22,000.00
SUBTOTAL
$25,700
$88,600
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
LEGAL, ADMINISTRATION, ENGINEERING
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 1/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Vortex Grit System 1 EA $ 342,000
Construction
Excavation & Disposal 60 CY $ 5,000
Cast-in-Place Concrete 45 CY $ 32,000
Equipment + Installation SUBTOTAL $ 379,000
Yard piping 1 LS $ 24,000
Electrical 1 LS $ 60,000
I&C 1 LS $ 35,000
$ 500,000
10% $ 50,000
25% $ 125,000
30% $ 150,000
$ 830,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction Cost
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
$342,000
Vortex Grit Removal
$80
$35,000
$695
$24,000
$60,000
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
SUBTOTAL
GENERAL REQUIREMENTS
The following assumptions and references were used to develop the opinion of probable 1. Opinions of probable costs are based on a conceptual level of project design.2. All unit costs are in 2019 dollars.
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
CONSTRUCTION CONTINGENCY
LEGAL, ADMINISTRATION, ENGINEERING
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 2/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
AeroDuctor 1 EA $ 284,400
Construction
Excavation & Disposal 240 CY $ 19,200
Cast-in-Place Concrete 100 CY $ 69,500
Equipment + Installation SUBTOTAL $ 373,000
Yard piping 1 LS $ 24,000
Electrical 1 LS $ 60,000
I&C 1 LS $ 35,000
$ 500,000
10% $ 50,000
25% $ 125,000
30% $ 150,000
$ 830,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostAerated Grit Removal
OPINION OF PROBABLE CONSTRUCTION COST
$80
$695
$284,400
$24,000
$60,000
$35,000
SUBTOTAL
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
LEGAL, ADMINISTRATION, ENGINEERING
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 3/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Enclosed UV Disinfection 1 LS $ 364,000
Equipment + Installation SUBTOTAL $ 364,000
Construction
Demolition of Existing UV Units 5 EA $ 5,000
Electrical 1 LS $ 36,400
I&C 1 LS $ 54,600
$ 460,000
10% $ 46,000
25% $ 115,000
30% $ 138,000
$ 760,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostEnclosed UV Disinfection
OPINION OF PROBABLE CONSTRUCTION COST
CONSTRUCTION CONTINGENCY
$364,000
$1,000
$36,400
$54,600
SUBTOTAL
GENERAL REQUIREMENTS
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
LEGAL, ADMINISTRATION, ENGINEERING
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 4/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Wedeco Open Channel UV Disinfection 1 EA $ 168,000
Construction
Excavation & Disposal 120 CY $ 9,600
Cast-in-Place Concrete 100.0 CY $ 69,500
Equipment + Installation SUBTOTAL $ 247,100
Canopy Structure 1 EA $ 55,000
Yard piping 1 LS $ 48,000
Electrical 1 LS $ 100,000
I&C 1 LS $ 40,000
$ 500,000
10% $ 50,000
25% $ 125,000
30% $ 150,000
$ 830,000
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
CONSTRUCTION CONTINGENCY
LEGAL, ADMINISTRATION, ENGINEERING
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
$168,000
$80
$695
$55,000
$48,000
SUBTOTAL
GENERAL REQUIREMENTS
$100,000
$40,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostOpen Channel UV Disinfection
OPINION OF PROBABLE CONSTRUCTION COST
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 5/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Screen 1 EA $ 273,400
Washer Compactor 1 EA $ 176,500
Equipment + Installation SUBTOTAL $ 449,900
Construction
Building Addition 400 SF $ 400,000
Building Concrete 240 CY $ 19,680
HVAC 1 EA $ 30,000
Electrical 1 EA $ 75,000
I&C 1 EA $ 45,000
$ 1,020,000
10% $ 102,000
25% $ 255,000
30% $ 306,000
$ 1,690,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostScreening & New Building (Option #1)
OPINION OF PROBABLE CONSTRUCTION COST
SUBTOTAL
$273,400
$176,500
$1,000
$82
$30,000
$75,000
$45,000
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
LEGAL, ADMINISTRATION, ENGINEERING
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 6/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Micro-strainer 1 EA $ 189,000
Equipment + Installation SUBTOTAL $ 189,000
Construction
Structural Beam 1 LS $ 15,000
Hoist 1 EA $ 8,000
HVAC 1 LS $ 19,000
Electrical 1 LS $ 19,000
I&C 1 LS $ 16,000
Demolition of Existing Equipment 1 EA $ 7,000
$ 280,000
10% $ 30,000
25% $ 70,000
30% $ 84,000
$ 470,000
$15,000
$8,000
1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
$19,000
SUBTOTAL
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:
$19,000
$16,000
$7,000
LEGAL, ADMINISTRATION, ENGINEERING
$189,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostMicro-strainer Screening (Option #2)
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 7/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Screen & Washer/Compactor 1 EA $ 260,000
Equipment + Installation SUBTOTAL $ 260,000
Construction
HVAC 1 EA $ 15,000
Electrical 1 EA $ 43,000
I&C 1 EA $ 26,000
Demolition of Existing Equipment 1 EA $ 7,000
$ 360,000
10% $ 36,000
25% $ 90,000
30% $ 108,000
$ 600,000
$26,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostDuperon Screening (Option #3)
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
$260,000
$15,000
$43,000
1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
$7,000
SUBTOTAL
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:
LEGAL, ADMINISTRATION, ENGINEERING
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 8/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Heat Exchanger 1 EA $ 79,000
Mixed Fuel Boiler 1 EA $ 222,000
Equipment + Installation SUBTOTAL $ 301,000
Construction
Electrical 1 LS $ 37,000
I&C 1 LS $ 31,000
Demolition of Existing Equipment 2 EA $ 14,000
$ 390,000
10% $ 40,000
25% $ 98,000
30% $ 117,000
$ 650,000
$79,000
$222,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostAnearobic Digester Heating
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
$37,000
$31,000
$7,000
1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
SUBTOTAL
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
LEGAL, ADMINISTRATION, ENGINEERING
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 9/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Pumped Mixing System 1 EA $ 50,000
Primary Digester Fixed Cover 1 EA $ 180,000
Secondary Digester Floating Cover 1 EA $ 210,000
Heat Exchanger 1 EA $ 79,000
Dual-Fuel Boiler 1 EA $ 142,500
Gravity Belt Thickener 1 EA $ 377,000
Equipment + Installation SUBTOTAL $ 1,038,500
Construction
Electrical 1 LS $ 95,000
I&C 1 LS $ 99,000
Demolition of Existing Equipment 6 EA $ 42,000
$ 1,280,000
10% $ 130,000
25% $ 320,000
30% $ 384,000
$ 2,120,000
LEGAL, ADMINISTRATION, ENGINEERING
$50,000
$180,000
$210,000
$99,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostAnearobic Digester Upgrades
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
$79,000
$7,000
SUBTOTAL
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
$142,500
$377,000
$95,000
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 10/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Vertical Draft Tube Mixing 1 EA $ 135,000
Heat Exchanger 1 EA $ 79,000
Natural Gas Boiler 1 EA $ 127,500
Fixed Cover 1 EA $ 180,000
Equipment + Installation SUBTOTAL $ 521,500
Construction
Electrical 1 LS $ 44,000
I&C 1 LS $ 21,000
Demolition of Existing Equipment 4 EA $ 28,000
$ 620,000
10% $ 70,000
25% $ 155,000
30% $ 186,000
$ 1,040,000
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
SUBTOTAL
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
LEGAL, ADMINISTRATION, ENGINEERING
$135,000
$79,000
$127,500
$180,000
$44,000
$21,000
$7,000
UNIT COST
Town of Ulster
FlexTech Study
Opinion of Probable Construction CostAnearobic Digester "Stop-Gap" for Regional Biosolids Disposal
OPINION OF PROBABLE CONSTRUCTION COST
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 11/12
DESCRIPTION QTY. UNIT TOTAL
Equipment
Pumped Mixing System 1 EA $ 50,000
Primary Digester Fixed Cover 1 EA $ 180,000
Secondary Digester Gasholding Cover 1 EA $ 220,000
Heat Exchanger 1 EA $ 79,000
Natural Gas Boiler 1 EA $ 127,500
CHP 1 EA $ 780,000
Gravity Belt Thickener 1 EA $ 377,000
Equipment + Installation SUBTOTAL $ 1,813,500
Construction
Electrical 1 LS $ 202,000
I&C 1 LS $ 177,000
Demolition of Existing Equipment 5 EA $ 35,000
$ 2,230,000
10% $ 230,000
25% $ 558,000
30% $ 669,000
$ 3,690,000
Town of Ulster
FlexTech Study
Opinion of Probable Construction Cost
$7,000
OPINION OF PROBABLE CONSTRUCTION COST
UNIT COST
$180,000
$177,000
$50,000
$79,000
$780,000
$377,000
$202,000
Anearobic Digesters Upgrades with CHP
2. All unit costs are in 2019 dollars.
3. All items are rounded to the nearest $1,000. All subtotals rounded to nearest $10,000.
The following assumptions and references were used to develop the opinion of probable
construction cost:1. Opinions of probable costs are based on a conceptual level of project design.
TOTAL OPINION OF PROBABLE CONSTRUCTION COST
(POINT ESTIMATE)
LEGAL, ADMINISTRATION, ENGINEERING
$220,000
$127,500
GENERAL REQUIREMENTS
CONSTRUCTION CONTINGENCY
SUBTOTAL
G:\PROJECT\02255220.0000\Cost Estimates\BOD - Opinion of Cost_Master.xlsx 12/12
Patented self cleaning semi-open channel impeller, ideal f or pumping inwaste water applications. Possible to be upgraded with Guide-pin®f or ev en better clogging resistance. Modular based design with highadaptat ion grade.
Head
433 234mm
78.6% Eff.
0
4
8
12
16
20
24
28
32
36
40
44
48
52
56
60
64
68
72
76
80
84
88
92
[ft]
0 400 800 1200 1600 2000 [US g.p.m.]
Impeller
Frequency
Motor
Rated v oltage
-
Rated power
Rated speed
Number of poles
Rated current
460 V60 Hz
20 hp
4
1755 rpm
26 A
NT 3153 MT 3~ 433
Motor #
3~
Suction Flange Diameter
NT,FT 3153 MT
* Dimension to inlet elbow flange.
* * For concrete foundation dimensions, see drawing768 50 00.
Not supplied by X ylem.
Ø8"
Ø6"
**
n9 71 6
x M 1 6 (4 x )
n13"xM16 (4x)
caleS
Dr awn
Reg no
Dat ebyChec k ed
by
DRAW ING
AUTOCAD
Denom inat ion
Dimensional drwg
7787300 3
130702DS
1:1
Ø8"/Ø6 "
13
361 2
1734
73 81
01 4
834
1458
223 4
min
.
90° (
4x)
163 4
67 8
5*
âÆ&11
16
(4x)
201 2
1334
253 4
2012
187 8
Impeller diameter 234 mmNumber of blades 2
N3153.185 21-18-4AA-D 20hp
Stator v ariant 5
Phases
Starting current 148 A
Technical specification
Note: Picture might not correspond to the current configuration.
Power f actor
Motor ef f iciency
1/1 Load3/4 Load1/2 Load
1/1 Load3/4 Load1/2 Load
0.830.770.66
87.5 %89.0 %89.0 %
5 7/8 inchCurve ISO
T - Vertical Permanent, DryInstallation:
Configuration
Impeller material Hard-Iron ™
General
Discharge Flange Diameter 5 7/8 inch
Water, pure
Standard
Last updateCreated on
8/17/2018
Created byProject IDProject
Head
Pump Efficiency
Overall Eff iciency
Pow er input P1
Shaft pow er P2
NPSH-values
433 234mm
78.6% Eff.
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
433 234mm
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
433 234mm
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
433 234mm (P2)
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
433 234mm (P1)
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
433 234mm
62.3 ft
71.3 %
63.3 %
16.9 hp
19 hp
23 ft 764.1 US g.p.m.
0
5
10
15
20
25
30
35
40
45
50
55
60
65
70
75
80
85
90
[ft]
0
20
40
60
[%]
0
5
10
15
[hp]
20
25
30
35
40
[ft]
0 200 400 600 800 1000 1200 1400 1600 1800 2000 2200 [US g.p.m.]
Motor #
60 Hz
Phases 3~
460 VNumber of poles 4
Rated power 20 hp
Starting currentRated current 26 A
Rated speed 1755 rpm
N3153.185 21-18-4AA-D 20hp
Stator variantNumber of blades 2
Power factor
NT 3153 MT 3~ 433
Suction Flange Diameter
Performance curve
Pump
Impeller diameter 93/16"
Motor
Rated voltage
148 A
Motor efficiency
1/1 Load3/4 Load1/2 Load
1/1 Load3/4 Load1/2 Load
Frequency5
0.83
87.5 %
0.770.66
89.0 %89.0 %
150 mm
Curve ISO
Discharge Flange Diameter 5 7/8 inch
Water, pure
Last updateCreated on
8/17/2018
Created byProject IDProject
Head
433 234mm
78.6% Eff.
62.3 ft
764.1 US g.p.m.0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
36
38
40
42
44
46
48
50
52
54
56
58
60
62
64
66
68
70
72
74
76
78
80
82
84
86
88
90
92
94
[ft]
0 200 400 600 800 1000 1200 1400 1600 1800 2000 2200 [US g.p.m.]
1
NT 3153 MT 3~ 433Duty Analysis
Curve ISO
Indiv idual pump Total
1 764 US g.p.m. 62.3 ft 16.9 hp 764 US g.p.m. 62.3 ft 16.9 hp 71.3 % 309 kWh/US MG 23 ft
Pumps running Specific /System Flow Head Shaft power Flow Head Shaft power Pump eff. energy NPSHre
Water, pure
Curve issue 7
Last updateCreated on
8/17/2018
Created byProject IDProject
Head
Pump Efficiency
Overall Eff iciency
Pow er input P1
Shaft pow er P2
NPSH-values
55 Hz
78.6%
50 Hz
78.6%
45 Hz
78.6%
40 Hz
78.6%
433 234mm
78.6% Eff.
55 Hz50 Hz45 Hz40 Hz 433 234mm433 234mm
55 Hz
50 Hz
45 Hz40 Hz
433 234mm (P2)433 234mm (P1)
55 Hz
50 Hz
45 Hz
40 Hz
433 234mm
0
4
8
12
16
20
24
28
32
36
40
44
48
52
56
60
64
68
72
76
80
84
88
92
[ft]
0
10
20
30
40
50
60
70
[%]
0
4
8
12
16
20
[hp]
15
20
25
30
35
40
[ft]
0 200 400 600 800 1000 1200 1400 1600 1800 2000 2200 [US g.p.m.]
NT 3153 MT 3~ 433VFD Curve
Curve ISO
Last updateCreated on
8/17/2018
Created byProject IDProject
Head
55 Hz
78.6%
50 Hz
78.6%
45 Hz
78.6%
40 Hz
78.6%
433 234mm
78.6% Eff.
62.3 ft
764.1 US g.p.m.0
4
8
12
16
20
24
28
32
36
40
44
48
52
56
60
64
68
72
76
80
84
88
92
[ft]
0 200 400 600 800 1000 1200 1400 1600 1800 2000 2200 [US g.p.m.]
1
NT 3153 MT 3~ 433VFD Analysis
Curve ISO
1 60 Hz 764 US g.p.m. 62.3 ft 16.9 hp 764 US g.p.m. 62.3 ft 16.9 hp 71.3 % 309 kWh/US MG 23 ft1 55 Hz 701 US g.p.m. 52.4 ft 13 hp 701 US g.p.m. 52.4 ft 13 hp 71.3 % 259 kWh/US MG 20.1 ft1 50 Hz 637 US g.p.m. 43.3 ft 9.79 hp 637 US g.p.m. 43.3 ft 9.79 hp 71.3 % 214 kWh/US MG 17.2 ft1 45 Hz 574 US g.p.m. 35.1 ft 7.14 hp 574 US g.p.m. 35.1 ft 7.14 hp 71.3 % 176 kWh/US MG 14.6 ft1 40 Hz 510 US g.p.m. 27.7 ft 5.01 hp 510 US g.p.m. 27.7 ft 5.01 hp 71.3 % 144 kWh/US MG 12.1 ft
Pumps running Specific /System Frequency Flow Head Shaft power Flow Head Shaft power Hyd eff. energy NPSHre
Last updateCreated on
8/17/2018
Created byProject IDProject
NT 3153 MT 3~ 433Dimensional drawing
NT,FT 3153 MT
* Dimension to inlet elbow flange.
** For concrete foundation dimensions, see drawing768 50 00.
Not supplied by Xylem.
Ø8"
Ø6"
**
n9716
xM16 (4x)
n13"xM16 (4x)
caleS
Drawn
Reg no
DatebyChecked
by
DRAWINGAUTOCAD
Denomination
Dimensional drwg
7787300 3
130702DS
1:1
Ø8"/Ø6"
13
361 2
1734
73 810
1 4
834
1458
223 4 m
in.
90° (
4x)
163 4
67 8
5*
âÆ&1116 (4x)
201 2
1334
253 4
2012
187 8
Last updateCreated on
8/17/2018
Created byProject IDProject
Version 10
0% 0.00 USD Energy
0% 0.00 USD Investment costs
0% 0.00 USD Installation & commissioning
0% 0.00 USD Operating cost
0% 0.00 USD Maintenance & repair
0% 0.00 USD Downtime
0% 0.00 USD Environmental
0% 0.00 USD Decommissioning
0% 0.00 USD Energy (1st year)
0% 0.00 USD Investment costs (1st year)
0% 0.00 USD Installation & commissioning (1st year)
0% 0.00 USD Operating cost (1st year)
0% 0.00 USD Maintenance & repair (1st year)
0% 0.00 USD Downtime (1st year)
0% 0.00 USD Environmental (1st year)
0% 0.00 USD Decommissioning (1st year)
2 %
3 %
15
0.00
0.00
NT 3153 MT 3~ 433
5600
0.00 USD
Inflation rate (rate of price increases)
Interest rate (for investment)
Total l ifetime
Annual operating time
Energy cost per kWh
Total costs
First year costs
Life cycle costs (LCC)
Disclaimer: The calculations and the results are based on user input values and general assumptions and provide only estimated costs for the input data. Xylem inc can therefore not guarantee that the estimated savings will actually occur.
USD
USD
Power input P1
Last updateCreated on
8/17/2018
Created byProject IDProject
ORIGINAL
ISSUE
LET ECN NO DATE
BY
APPV'D
Smith & Loveless, Inc.
SCALE: CODE:
CHECKED BY:
APPROVED BY:
DRAWN BY: DATE:
ANGLES
DECIMALS
FRACTIONS
ALLOWABLE
TOLERANCES
FOR
SIZE
FILE
NAME
SERIAL
NO
DWG
NO
REV
PLOT
SCALE
U/M
WT.
©
DATE:
DATE:
RECIPIENT AGREES THE INFORMATION ON THIS DRAWING AND THE EQUIPMENT DEPICTED HEREIN IS CONFIDENTIAL, PROPRIETARY AND
PROTECTED UNDER UNITED STATES AND FOREIGN INTELLECTUAL PROPERTY LAWS AND IS OWNED BY SMITH & LOVELESS, INC. UNLESS
SPECIFIC WRITTEN CONSENT IS GIVEN BY SMITH & LOVELESS, INC. YOU MAY NOT COPY, REPRODUCE, TRANSMIT, DISPLAY, DISTRIBUTE, ALTER,
OR OTHERWISE USE IN WHOLE OR IN PART ANY INFORMATION ON THIS DRAWING OR THE EQUIPMENT DEPICTED HEREIN, OR PERMIT SUCH
ACTIONS TO BE TAKEN BY A THIRD PARTY. SMITH & LOVELESS, INC. TRANSFERS NO RIGHTS IN THIS DRAWING OR THE INFORMATION AND
EQUIPMENT DEPICTED HEREIN. DIMENSIONS ARE IN INCHES UNLESS OTHERWISE NOTED.
N90-56
D N2013-52
1/2014
RGD
ACM
NTS
SBM
D. FISHER
R. DIEHM
1990,93,2002,10,14
6/19/1990
3/1991
4/1991
~
~
~
EA
67C175D.dwg
67C175 D
1:1
Smith &
Loveless, Inc.
250 GPM SECOND-STAGE PISTA
GRIT CONCENTRATOR NI-HARD
67C175/D
SHEET 1 OF 1
2'-1" [637 mm]
3 3/8" [85 mm]
10 13/16" [275 mm]
7 9/16" [192 mm]
5/8" [16 mm]
1'-0" [305 mm] DIA.
4 5/8" [117 mm]
2 5/16" [59 mm]
4" [101 mm]
3 1/2" [89 mm]
7 1/2" [191 mm]
1'-2" [356 mm]
1'-3" [381 mm]
1'-0 7/8" [327 mm]
1 1/16" [27 mm]
5 1/2" [140 mm] O.D. PLAIN END GRIT OUTLET
4 1/2" [114 mm] O.D. PLAIN END INLET
7/8" X 1 1/2" [22 mm X 38 mm] SLOT
(4 PLACES)
6" [150 mm] DIA. DRAIN OUTLET WITH ANSI 150 LB. FLANGE
REDRAWN PER REVISION D
NOTE:
1. COPYRIGHT (C) 1990, 93, 2002, 10, 14 SMITH & LOVELESS, INC.
DDDDEEEETTTTAAAAIIIILLLL AAAA
}
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LLLLEEEETTTT EEEECCCCNNNN NNNNOOOO DDDDAAAATTTTEEEE BBBBYYYYAAAAPPPPPPPPVVVV''''DDDD
SSSSmmmmiiiitttthhhh &&&& LLLLoooovvvveeeelllleeeessssssss,,,, IIIInnnncccc....
SSSSCCCCAAAALLLLEEEE:::: CCCCOOOODDDDEEEE::::
CCCCHHHHEEEECCCCKKKKEEEEDDDD BBBBYYYY::::
AAAAPPPPPPPPRRRROOOOVVVVEEEEDDDD BBBBYYYY::::
DDDDRRRRAAAAWWWWNNNN BBBBYYYY:::: DDDDAAAATTTTEEEE::::
AAAANNNNGGGGLLLLEEEESSSS
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FFFFRRRRAAAACCCCTTTTIIIIOOOONNNNSSSS
AAAALLLLLLLLOOOOWWWWAAAABBBBLLLLEEEETTTTOOOOLLLLEEEERRRRAAAANNNNCCCCEEEESSSS
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©
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NNNN2222000000009999----44448888
AAAA NNNN2222000011110000----4444
NNNN2222000011111111----7777BBBB
NNNN2222000011112222----33338888CCCC
11110000////2222000011110000FFFFMMMMNNNNCCCCGGGGMMMM
CCCCGGGGMMMMFFFFMMMMNNNN5555////2222000011111111
FFFFMMMMNNNNMMMMTTTTAAAA1111////2222000011113333
NNNNTTTTSSSS
CCCCGGGGMMMM
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FFFFMMMMNNNN
2222000000009999,,,,11110000,,,,11111111,,,,11113333
8888////2222000000009999
8888////2222000000009999
8888////2222000000009999
~~~~
~~~~
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EEEEAAAA
66667777BBBB333377779999CCCC....ddddwwwwgggg
66667777BBBB333377779999 CCCC
1111::::1111
SSSSmmmmiiiitttthhhh &&&&LLLLoooovvvveeeelllleeeessssssss,,,, IIIInnnncccc....
PPPPIIIISSSSTTTTAAAA TTTTUUUURRRRBBBBOOOO GGGGRRRRIIIITTTT WWWWAAAASSSSHHHHEEEERRRR WWWW////TTTTRRRRIIII----CCCCLLLLEEEEAAAANNNNSSSSEEEE TTTTEEEECCCCHHHHNNNNOOOOLLLLOOOOGGGGYYYY
MMMMOOOODDDDEEEELLLL 222255550000 WWWW//// CCCCOOOONNNNCCCCEEEENNNNTTTTRRRRAAAATTTTOOOORRRRSSSS
66667777BBBB333377779999////CCCC
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1111''''----2222""""
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BBBBEEEELLLLTTTT GGGGUUUUAAAARRRRDDDD
DDDDRRRRIIIIVVVVEEEE AAAASSSSSSSSEEEEMMMMBBBBLLLLYYYY
3333 HHHHPPPP,,,, 3333 PPPPHHHHAAAASSSSEEEE 222233330000////444466660000 VVVVOOOOLLLLTTTT,,,,66660000 HHHHZZZZ,,,, 1111111166660000 RRRRPPPPMMMM TTTTEEEEFFFFCCCC MMMMOOOOTTTTOOOORRRR
WWWWIIIITTTTHHHH 3333////4444"""" NNNN....PPPP....TTTT.... CCCCOOOONNNNDDDDUUUUIIIITTTT CCCCOOOONNNNNNNN....
CCCCLLLLEEEEAAAARRRRAAAANNNNCCCCEEEEHHHHEEEEIIIIGGGGHHHHTTTT
LLLLIIIIFFFFTTTTIIIINNNNGGGG LLLLOOOOOOOOPPPP((((4444 PPPPLLLLAAAACCCCEEEESSSS))))
8888"""" DDDDIIIIAAAA.... SSSSTTTTEEEEEEEELLLL PPPPLLLLAAAAIIIINNNN EEEENNNNDDDDDDDDIIIISSSSCCCCHHHHAAAARRRRGGGGEEEE PPPPIIIIPPPPEEEE
PPPPIIIISSSSTTTTAAAA}}}} GGGGRRRRIIIITTTT
CCCCOOOONNNNCCCCEEEENNNNTTTTRRRRAAAATTTTOOOORRRR((((SSSSEEEEEEEE DDDDRRRRAAAAWWWWIIIINNNNGGGG66667777CCCC111177775555))))
OOOOUUUUTTTTLLLLEEEETTTT FFFFOOOORRRR PPPPIIIISSSSTTTTAAAA}}}}
GGGGRRRRIIIITTTT CCCCOOOONNNNCCCCEEEENNNNTTTTRRRRAAAATTTTOOOORRRR
8888 1111////8888""""
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22222222°°°°
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4444 11115555////11116666""""
9999''''----0000"""" 4444''''----5555 5555////11116666""""
5555''''----0000 5555////11116666""""
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1111''''----5555 1111////4444""""
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11110000 3333////11116666""""
1111 1111////4444""""
4444""""
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1111''''----3333""""
2222''''----9999 11115555////11116666""""
3333''''----11111111""""
6666 11113333////11116666""""
EEEENNNNDDDD VVVVIIIIEEEEWWWW
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9999"""" DDDDIIIIAAAA HHHHEEEELLLLIIIICCCCOOOOIIIIDDDD SSSSCCCCRRRREEEEWWWW
TTTTRRRROOOOUUUUGGGGHHHH CCCCOOOOVVVVEEEERRRRSSSSEEEEXXXXPPPPAAAANNNNDDDDEEEEDDDD MMMMEEEETTTTAAAALLLL CCCCOOOOVVVVEEEERRRR
SSSSEEEEPPPPEEEERRRRAAAATTTTOOOORRRR PPPPLLLLAAAATTTTEEEESSSS
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4444"""" DDDDIIIIAAAA.... AAAA....SSSS....AAAA.... 111155550000 LLLLBBBB.... FFFFLLLLAAAANNNNGGGGEEEE OOOOVVVVEEEERRRRFFFFLLLLOOOOWWWW
BBBBAAAACCCCKKKK TTTTOOOO PPPPIIIISSSSTTTTAAAA}}}} IIIINNNNLLLLEEEETTTT CCCCHHHHAAAANNNNNNNNEEEELLLL
((((SSSSEEEEEEEE NNNNOOOOTTTTEEEE 3333))))
5555////8888"""" DDDDIIIIAAAA.... ((((4444 HHHHOOOOLLLLEEEESSSS))))FFFFOOOORRRR 1111////2222"""" DDDDIIIIAAAA.... AAAANNNNCCCCHHHHOOOORRRRSSSS((((NNNNOOOOTTTT BBBBYYYY SSSS&&&&LLLL))))
9999 5555////8888""""3333 5555////8888""""
qqqq
qqqq
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qqqq
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FOR
REVDWG
NO
SERIAL
NO.
FILE
NAME
PLOT
SCALE
WT.U/MSIZE
ORIGINAL
ISSUE
DRAWN BY: DATE:ALLOWABLE
TOLERANCES
FRACTIONS
DECIMALS
ANGLES
DATE:
DATE:
CHECKED BY:
APPROVED BY:
SCALE:
LET ECN NO. DATEBY
APPV'D
}
Smith &
Loveless, Inc.
Smith & Loveless, Inc.
PISTA® TURBO™ GRIT WASHER W/
TRI-CLEANSE TECHNOLOGY™ MODEL 250GENERAL ARRANGEMENT
FMN
FBO
CGM
NTS
8/2009
8/2009
8/2009
~
~
~ 67B380B.dwg
67B380 B
1:1
EA
N2009-48
A N2010-4 10/2010FMN
FT
SHEET 1 OF 1
2009, 10, 11
67B380/B
B N2011-37 3/2011FT
FMN
CODE:
RECIPIENT AGREES THE INFORMATION ON THIS DRAWING AND THE EQUIPMENT DEPICTED HEREIN IS CONFIDENTIAL, PROPRIETARY AND
PROTECTED UNDER UNITED STATES AND FOREIGN INTELLECTUAL PROPERTY LAWS AND IS OWNED BY SMITH & LOVELESS, INC. UNLESS
SPECIFIC WRITTEN CONSENT IS GIVEN BY SMITH & LOVELESS, INC., YOU MAY NOT COPY, REPRODUCE, TRANSMIT, DISPLAY, DISTRIBUTE, ALTER,
OR OTHERWISE USE IN WHOLE OR IN PART ANY INFORMATION ON THIS DRAWING OR THE EQUIPMENT DEPICTED HEREIN, OR PERMIT SUCH
ACTIONS TO BE TAKEN BY A THIRD PARTY. SMITH & LOVELESS, INC. TRANSFERS NO RIGHTS IN THIS DRAWING OR THE INFORMATION AND
EQUIPMENT DEPICTED HEREIN. DIMENSIONS ARE IN INCHES UNLESS OTHERWISE NOTED.
©
6" ELBOW
2" N.P.T. BALL VALVE & PIPING
SEE NOTE 4
1/4" N.P.T. AIR INLET
5 SCFH @ 70 PSI
1" N.P.T. WASH WATER INLET
20 GPM @ 60 PSI
ALTERNATE ORIENTATION
4" DIA. PIPING FROM
GRIT PUMP
COMPRESSION
COUPLING
(NOT BY S&L)
S&L TO HERE
8" DIA. DRAIN TO PISTA}INLET CHANNEL
6" PIPING
NOTES:
1. INTERCONNECTING PIPING AND FITTINGS ARE NOT SUPPLIED BY S&L.
2. SEE DRAWING 67C175 FOR PISTA} NI-HARD GRIT CONCENTRATOR DETAILS.
3. SEE SEPARATE DRAWING FOR GRIT WASHER MODEL 250 WITH CONCENTRATOR.
4. THE 2" DRAIN PIPE WITH BALL OR PLUG VALVE IS USED TO FACILITATE CLEAN UP AND INSPECTION.
5. THE 3" DRAIN PIPE WITH AUTOMATIC BALL VALVE IS USED TO FACILITATE ORGANIC DRAIN.
6. TO PROVENT SIPHONING, THE CENTERLINE OF THE GRIT CONCENTRATOR INLET MUST BE
AT LEAST 24" ABOVE THE MAXIMUM WATER LEVEL IN THE PISTA} CHAMBER.
7. PIPING CONNECTIONS ARE PROVIDED ON BOTH SIDES TO FACILITATE EITHER RIGHT OR LEFT HAND
CONNECTION. A BLIND FLANGE IS PROVIDED ON THE SIDE THAT IS NOT USED AS A DRAIN.
8. COPYRIGHT (C) 2009, 10, 11 SMITH & LOVELESS, INC.
6" X 45° LATERAL WYE
S&L TO HERE
GRIT WASHER
(BY S&L)
LIFTING LOOP
(4 PLACES)
3" N.P.T. BALL VALVE
WITH ELEC. ACTR.
SEE NOTE 5
(BY S&L)
4" PIPING
6" X 4" REDUCER
6" X 45° ELBOW
PISTA® GRIT CONCENTRATOR
(BY S&L)
6" DIA X 5'-0" MINIMUM
AIR VENT PIPE
S&L TO HERE
3" ELBOW & HOSE
6" TEE
(NOT BY S&L)
8'-0" MAX
4" ELBOW
ALTERNATE ORIENTATION
3'-11"
Xylem Water Solutions USA, Inc. 14125 South Bridge Circle Charlotte, NC 28273
June 19, 2019 Acadis Emily Carlson Project Name: Ulster WWTP Project Number: J16080184021 Revision Number: 2 Ms. Carlson: We are pleased to submit the following proposal for the Ulster WWTP UV opportunity based on the information provided within your inquiry. This is a revised proposal that includes a redundant UV reactor in the design. The LBX series is a closed vessel system specifically designed for water and wastewater applications. We have highlighted below the major benefits of the LBX vessels that can improve the performance of the system and increase the lifespan of the equipment:
Our system includes our latest low-pressure, high-intensity Ecoray lamps which have a guaranteed life of 14,000 hours and are a more efficient lamp with a lower power consumption requirement. In addition, from a maintenance standpoint, the Ecoray lamps are more robust and easy to remove and replace.
Latest sensor technology – germicidal UV sensor of reference sensor quality (ÖNORM approved) providing the highest accuracy in UV system monitoring and control.
Automatic wiping system that prevents fouling of the quartz sleeve with easy replacement of wipers.
The WEDECO Remote Service Support allows us to monitor and if necessary to adjust the LBX control unit from remote in the same way as directly on site. Therefore Remote Service Support improves the service quality of the LBX unit due to faster and even more cost effective technical support (e.g. maintenance, software updates or service diagnosis) through WEDECO service technicians.
WEDECO’s established and proven TotalCare Program provides our customers with proactive services all designed to minimize the cost of ownership to operate and maintain a UV system. TotalCare services can provide our customers with system health checks, efficiency audits, training and preventative maintenance contracts.
Please refer to our local representative Dave Boshart of GP Jager, (315) 632-4259 or us if you have any questions. We look forward to working with you on this exciting project. Sincerely, Julia Beilsmith Bill Mattfeld Territory Manager Senior Applications Engineer (954) 483-8563
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 4 of 11 Date: June 19, 2019 Revision no.: 2
Table of Content
1 Xylem Overview ........................................................................................................ 5
2 General Process Description .................................................................................. 7
2.1 Design ........................................................................................................................ 7 2.2 Process Description ................................................................................................... 7
3 Technical Description .............................................................................................. 8
4 Price & Scope of Supply .......................................................................................... 9
4.1 Wedeco Scope of Supply ........................................................................................... 9 4.2 Budget Price .............................................................................................................. 9
5 Commercial Terms & Conditions .......................................................................... 10
6 Attachments ............................................................................................................ 11
6.1 Brochures / Drawings / others .................................................................................. 11
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 5 of 11 Date: June 19, 2019 Revision no.: 2
1 Xylem Overview
Xylem is a leading global water technology provider, enabling customers to transport, treat, test and efficiently use water in public utility, residential and commercial building services, industrial and agricultural settings. The company does business in more than 150 countries through a number of market-leading product brands, and its people bring broad applications expertise with a strong focus on finding local solutions to the world’s most challenging water and wastewater problems.
Xylem’s treatment business offers a portfolio of products and systems designed to effectively meet the demands and challenges of treating water and wastewater. From smarter aeration to advanced filtration to chemical-free disinfection, Xylem leverages its well-known Treatment brands, Flygt, Leopold, Sanitaire, and Wedeco, to offer hundreds of solutions backed by a comprehensive, integrated portfolio of services designed to ensure we can meet our customers’ needs in a number of different industries including municipal water and wastewater, aquaculture, biogas and agriculture, food and beverages, pharmaceuticals, and mining.
Our scientists and engineers utilize their deep applications expertise and continually listen and learn from our customers’ situations to create solutions that not only use less energy and reduce life-cycle costs, but also promote the smarter use of water.
Wedeco has accepted the challenge of the 21st century. With the Wedeco brand for UV Disinfection, ozone oxidation & AOP solutions, we own the advanced technologies for chemical-free and environmentally friendly treatment of drinking water, wastewater and process water as well as further industrial treatment processes. We
constantly invest a large portion of our energy in the development of high-tech components, systems and equipment, as well as in the study of new areas of application for UV, ozone & AOP. In doing so, we have always given special attention to the increase in energy efficiency of our Products equipped with our unique UV lamps and ozone electrodes.
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 6 of 11 Date: June 19, 2019 Revision no.: 2
The special characteristics of the Wedeco Ecoray UV lamp are its special doping and the unique long-life coating. Because of these features, a constantly high UV light yield is achieved with a substantially extended lamp service life at the same time. In addition, by using this technology it is not necessary to apply liquid mercury inside the lamp. Wedeco UV lamps cannot be surpassed in economic efficiency.
In relation to expenditure of energy, the High-Intensity/Low-Pressure Technology provides a light yield three times higher than comparable UV lamps of widely used Medium Pressure Technology. A higher light yield also means a lower heat generation at the same time. Thanks to this, Wedeco UV lamps become less susceptible to varying water temperatures. Even the formation of deposits on the quartz sleeves as well as lamp aging is considerably lower than with alternative UV lamp technologies in Herford and Essen.
Xylem's Wedeco ozone systems combine maximum flexibility and reliable operating characteristics for small to large ozone capacities. The ozone generator system and control unit can be combined and supplemented with option sets that allow for various application requirements. Effizon evo 2G ozone electrodes are the core of our technology and achieve an unmatched level of reliability and energy efficiency. The electrodes are manufactured completely from inert materials, without the need for fuses or
coatings, making them highly resistant to corrosion. This means that the Wedeco ozone generators are practically maintenance free with no need for regular cleaning or replacement of the electrodes. We rely on consistently high-quality standards in all divisions of the company. Moreover, product quality and manufacturing operations are constantly monitored and optimized in continuous improvement processes. Established quality controls give Xylem and you the security of knowing that Wedeco UV, Ozone & AOP systems will always operate reliably. For more information please visit us at http://www.xylem.com/treatment/
WEDECO Effizon® evo 2G Ozone electrode
WEDECO Ecoray UV lamp
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 7 of 11 Date: June 19, 2019 Revision no.: 2
2 General Process Description
2.1 DESIGN
Design Flow Rates - Peak Design Flow 2.5 MGD
Total Suspended Solids (Maximum) 5 mg/l 5-day B.O.D. 25 mg/l Allowable Effluent Temperature Range 41-86°F UV Transmittance at 253.7 nm 65%, minimum Maximum Influent Fecal Coliforms Count 100,000 Fecal Coliforms/100 mL Effluent Disinfection Standard
- Fecal Coliforms (30 day geometric mean) <200 Fecal Coliforms/100 mL - Fecal Coliforms (7 day geometric mean) <400 Fecal Coliforms/100 mL
UV Dose
- Minimum Design UV Dose (based on calculated PSS dose)
>60 mJ/cm²
2.2 PROCESS DESCRIPTION
The proposed UV system is based on an influent quality that meets the above listed criteria and requires that all wastewater to be disinfected has undergone prior treatment through Rotating Biological Contactors (RBCs) and a final settling tank.
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 8 of 11 Date: June 19, 2019 Revision no.: 2
3 Technical Description
CONFIGURATION: LBX 850e
DESCRIPTION UNITS VALUE
Number of 316L SS vessels
Number of lamps per vessel
Number of intensity sensors per vessel
Total number of lamps
2 (1 duty, 1 standby)
32
1
64
REACTOR DIMENSIONS: Inches See attached drawing
HEADLOSS PER VESSEL (at peak flow): Inches 12.2
POWER CONSUMPTION:
Peak Flow Lamp and Ballast Power
kW
10
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 9 of 11 Date: June 19, 2019 Revision no.: 2
4 Price & Scope of Supply
4.1 WEDECO SCOPE OF SUPPLY Cylindrical 316L stainless steel reactor with integrated baffle plates 32 low pressure, high intensity WEDECO Ecoray® UV lamps per vessel One (1) Type 12, Fan-cooled, Painted Steel electrical enclosure per vessel Calibrated UV intensity monitoring system (UV sensor ÖNORM certified) Electronic UV lamp supervision system WEDECO EcoTouch Controller with Touchscreen HMI (one per vessel) Optidose Dose pacing incl. variable lamp power SCADA Communication Automatic wiping system (Electric) 39 ft (12 m) lamp cables Manufacturer’s field service on site [2 trips / 6 days] Electrical supply: 480 V, 3 phase, 60 Hz, 4 wire + ground
4.2 BUDGET PRICE
LBX Standard Equipment
Total $177,000
Ulster, Ny Lbx Budget Proposal 19.06.19 R2 Page 10 of 11 Date: June 19, 2019 Revision no.: 2
5 Commercial Terms & Conditions
Commercial Details
Submittal time: 8 weeks after approved purchase order
Delivery time: 18 weeks after approved submittals
Terms of Delivery: All prices are FCA factory with full freight allowed to the job site.
Terms of Payment:
This proposal is based upon WEDECO’s General Terms of Business. Price is based upon the following payment terms (net 30 days):
10% net 30 days upon initial submittal of mechanical/electrical drawings for approval
80% net 30 days from the date of the respective shipments of the product
5% installation of the Xylem equipment, NTE 150 days after shipment
5% start-up / training on the Xylem equipment, NTE 180 days after shipment
Warranties:
Lamp Warranty: Guaranteed 14,000 hours of operation, prorated after 9,000 hours.
System Warranty: 18 months from date of delivery or 12 months from date of substantial completion of UV equipment whichever comes first.
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THIS DRAWING AND ALL INFORMATION AND KNOWLEDGECONTAINED OR REFERRED HEREIN ARE THE CONFIDENTIAL AND PROPRIETARY PROPERTY OF SUEZ AND AS SUCH ARE INSTRUMENTS OF SERVICE FOR USE SOLELY WITH RESPECT TO THIS PROJECT. THESE INSTRUMENTS OF SERVICE SHALL NOT BE REPRODUCED, TRANSMITTED, DISCLOSED OR USED OTHERWISE, IN WHOLE OR IN PART, WITHOUT PRIOR WRITTEN AGREEMENT BY SUEZ AND MUST BE IMMEDIATELY RETURNED OR DESTROYED UPON REQUEST.
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Phone (804) 756-7600 D
REVISION DESCRIPTIONREV DATE REVISION DESCRIPTIONREVDRAWN CHECKED APP DATE PROJECT INFORMATIONAPPCHECKEDDRAWN
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SUEZ CONTRACT No. ANTS-
SHEET
MDLBFHC
01/17/17
01/17/17
01/20/17
AQUARAY 40HO VLS DISINFECTION SYSTEMCHANNEL AND LIFTING LAYOUTONE MODULE
H000194 SNA ME 252 7701 DA 001
MDL MDL BF 07/11/17
LAST SAVED : Wednesday, July 12, 2017 11:49:16 AM
8007 Discovery DriveRichmond, Virginia, 23229 USA
,
SUGGESTED CHANNEL CONCRETE LAYOUTLIFTING LAYOUT
2'-0"
APROXIMATE WEIGHT : 400 LBS (181 kG)
8'-8
"
TOTA
L M
OD
ULE
HEIG
HT 43
7'-8
1 4"
2'-6" 0"
CHANNEL WIDTH2'- 1
2 "+-1/2"
6'-0
"M
IN. C
HA
NN
EL D
EPTH
PRE
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1
Trojan Technologies is an ISO 9001: 2000 registered company that has set the standard for proven UV technology and ongoing innovation for more than 30 years. With unmatched scientific and technical expertise, and a global network of water treatment specialists, representatives and technicians, Trojan is trusted more than any other firm as the best choice for municipal UV solutions. Trojan has the largest UV installation base – over 7,000 municipal installations worldwide – and almost
one in five North American wastewater treatment plants rely on our proven, chemical-free disinfection solutions.
The TrojanUV3000Plus™ is one of the reasons why. This highly flexible system has demonstrated its effective, reliable performance around the world. It is well suited to wastewater disinfection applications with a wide range of flow rates, including challenging effluent such as combined sewer overflows, primary and tertiary wastewater reclamation and reuse.
Following a review with Plant Operators and Engineers, the proven infrastructure of the TrojanUV3000Plus™ has been refined to make it even more operator-friendly. The result is more dependable performance, simplified maintenance, and maximized UV lamp output at end-of-lamp life. It also incorporates innovative features to reduce O&M costs, including variable output electronic ballasts and Trojan’s revolutionary ActiClean™ system – the industry’s only chemical/mechanical sleeve cleaning system.
The Reference Standard in UV Proven, chemical-free disinfection from the industry leader
Short trim this panel
The PDC powers each bank of modules. Its ergonomic, angled design provides easy access to module power cables and hoses for the ActiClean™ cleaning system. The robust stainless steel enclosure is mounted across the channel, with module fuses and interlock relays visually aligned with module receptacles for fast diagnostics. Modules are individually overload protected for safety. Like all TrojanUV3000Plus™ components, the PDC can be installed outdoors and requires no shelter or HVAC.
Designed for efficient, reliable performance
2
Power Distribution Center (PDC)
UV Intensity Sensor
The UV intensity sensor continually monitors UV lamp output. The ActiClean™ system automatically cleans the sensor sleeve every time lamp sleeves are cleaned.
The SCC monitors and controls all UV functions, including dose pacing – the automatic, flow-based program that ensures proper disinfection levels while conserving power and extending lamp life. The microprocessor-based SCC is integrated onto one Power Distribution Center, and features a user-friendly, touch-screen HMI display with weatherproof cover, and Modbus Ethernet SCADA connectivity. For systems treating larger flows, or where more sophisticated control is desired, a PLC-based System Control Center is available. It features a separate wall-mount panel with colour, touch-screen HMI, Ethernet/IP SCADA connectivity, automatic slide/sluice gate control for multiple channels, and integrated Flash memory trend logging (flow, power, UVT, dose).
Electronic Ballasts
The variable-output (60 - 100% power) electronic ballast is mounted in its own TYPE 6P (IP67) rated enclosure within the module frame. Features “quick connect” electrical connections. Cooling is by convection.
AlarmsExtensive alarm reporting system ensures fast, accurate diagnosing of system process and maintenance alarms. Programmable control software can generate unique alarms for individual applications.
System Control Center (SCC)
Water Level Controller
A fixed weir, motorized weir gate, or Automatic Level Control gate (shown), is required in the channel to maintain the appropriate water level over the lamps. Trojan engineers will work with you to select the appropriate level control device for your application.
Water Level Sensor
The system includes an electrode low water level sensor for each channel. If effluent levels fall below defined parameters, an alarm will be activated.
UV Modules
UV lamps are mounted on modules installed in open channels. The lamps are enclosed in quartz sleeves, and positioned horizontally and parallel to water flow. A bank is made up of multiple modules placed in parallel. All ballast and lamp wiring runs inside the module frame.
3
2. ActiClean™ Wiper Assembly A submersible wiper drive on each UV module drives the wiper carriage assembly along the module. Attached wiper canisters surround the quartz sleeves, and are filled with ActiClean™-WW Gel. The gel uses food grade ingredients and contacts the lamp sleeves between the two wiper seals. Cleaning takes place while the lamps are submerged and while they are operating.
1. Hydraulic System Center (HSC)The HSC actuates the ActiClean™ cleaning system, and is mounted close to the channel in a stainless steel enclosure. It contains the pump, valves and ancillary equipment required to operate the cleaning system, and links to the extend/retract hoses of the module wiper drives via a manifold located on the underside of the PDC.
ActiClean™ Cleaning SystemThe system consists of two components:
Key Benefits TrojanUV3000Plus™
Increased operator, community and environmental safety. The TrojanUV3000Plus™ uses environmentally-friendly ultraviolet light – the safest
alternative for wastewater disinfection. No disinfection by-products are created, and no
chemicals must be transported, stored or handled.
Well suited to changing regulations. Trojan UV systems do not have any negative
impact on receiving waters and do not produce disinfection by-products, making them a
strategic, long-term choice as regulations become increasingly stringent.
Most efficient UV system available versus competitive low-pressure, high-output
(LPHO) or amalgam lamp-based systems.
Reduces operating costs by as much as 30% per year. Long-lasting
amalgam lamps and variable-output ballasts optimize UV output to meet wastewater
conditions and maximize system efficiency versus competitive UV systems.
Proven disinfection based on actual dose delivery testing (bioassay validation), and
over 400 TrojanUV3000Plus™ installations worldwide. Real-world, field performance data
eliminates sizing assumptions resulting from theoretical dose calculations.
Dual-action sleeve cleaning system improves performance and reduces labor costs. Automatic ActiClean™ chemical/mechanical cleaning system
maintains sleeve transmittance of at least 95%, and works online – eliminating the need to
remove modules from the channel.
Reduced installation costs. The compact TrojanUV3000Plus™ can be retrofitted
into existing chlorine contact tanks, and comes pre-tested, pre-assembled and pre-wired to
minimize installation costs.
Outdoor installation flexibility. The entire TrojanUV3000Plus™ system can be
installed outdoors, eliminating the need and costs of a building, shelter, and HVAC for ballast
cooling.
Guaranteed performance and comprehensive warranty. Trojan systems
include a Lifetime Performance Guarantee, the best lamp warranty in the industry, and use
lamps from multiple approved suppliers. Ask for details.
4
Benefits:• Cleans 50% more effectively
than mechanical wiping alone
• Improves lamp performance for more reliable dose delivery
• Elimination of fouling factor reduces equipment sizing requirements and power consumption
• Automatic, online cleaning reduces O&M costs associated with manual cleaning
• Combination of chemical and mechanical cleaning action removes deposits on quartz lamp and sensor sleeves much more effectively than mechanical wiping alone
• Innovative wiper design incorporates a small quantity of ActiClean™-WW Gel for superior, dual-action cleaning
• Cleans automatically while the lamps are disinfecting. There’s no need to shut down the system, remove or bypass lamp modules for routine cleaning
• Proven in hundreds of systems around the world, including use in plants where heavy fouling had previously prohibited the use of UV disinfection technology
• ActiClean™ can be added to an installed TrojanUV3000Plus™ not originally equipped with a cleaning system
ActiClean™-WW Gel is Safe to Handle• ActiClean™-WW Gel is comprised of food-grade ingredients
• Quick connect on cleaning system allows for easy refill of gel solution
• Lubricating action of ActiClean™-WW Gel maximizes life of wiper seals
ActiClean™ Dual-Action, Automatic Cleaning SystemChemical/mechanical cleaning system eliminates sleeve fouling
The dual-action, chemical/mechanical cleaning with the ActiClean™ system provides superior sleeve cleaning and reduces maintenance costs. Fouling and residue build-up on quartz sleeves reduces system efficiency. ActiClean™ maintains at least 95% transmittance, ensuring sleeves are clean and the system is consistently delivering accurate dosing while reducing power consumption.
5
Efficacy of Cleaning Technologies to Control Sleeve Fouling
Benefits:• Performance data is generated
from actual field testing over a range of flow rates, effluent quality, and UVTs
• Provides physical verification that system will perform as expected; ensures public and environmental safety
• Provides accurate assessment of equipment sizing needs
• The TrojanUV3000Plus™ has been thoroughly validated through real-world bioassay testing under a wide range of operating conditions
• In-field bioassay testing offers the peace of mind and improved public and environmental safety of verified dose delivery – not theoretical calculations
• The USEPA has endorsed bioassays as the standard for assessment and comparison of UV technologies
• The disinfection performance ratings for the TrojanUV3000Plus™ are proof that what you see is what you actually get
Regulatory-Endorsed Bioassay ValidationReal-world testing ensures accurate dose delivery
Amalgam Lamps Require Less EnergyRequire fewer lamps and reduce O&M costs
Benefits:• Draw less energy than competitive
high-output systems – only 250 Watts per lamp
• Stable UV output over a wide range of water temperatures
• Fewer lamps are required to deliver the required dose, which reduces O&M costs
• Can treat lower quality wastewater such as primary effluents, combined sewer overflows, and storm water
• Fewer lamps allow systems to be located in compact spaces, reducing installation costs
Trojan’s high efficiency amalgam lamps generate stable UV output in a wide range of water temperatures.
6
Field Validated Dose vs. Theoretical Dose at 65% UVT(Before Fouling & Lamp Aging Are Taken into Account)
• Trojan’s amalgam lamps produce significantly higher UV output than conventional low-output lamps
• Fast and simple lamp changeouts; replacing a 50-lamp system takes less than two hours and requires no tools
• The lamps are sealed inside heavy-duty quartz sleeves by Trojan’s multi-seal system, maintaining a watertight barrier around the internal wiring while individually isolating each lamp and the module frame
• Lamps are pre-heated for reliable startup
This shows the validated dose of an actual working system and the theoretical dose calculated using UVDIS. Note that the UVDIS 3.1 dose calculation overestimates the system performance.
Benefits:• Trojan's high efficiency, amalgam
lamps deliver the most consistent UV output
• Trojan lamps have 20% less decline in UV output after 12,000 hours of use compared to competitive UV lamps
• Validated performance assures you of reliable dose delivery and prolonged lamp life
Amalgam Lamps Maintain Maximum UV OutputTrojan lamps deliver 98% of full UV output after more than one year of use
The lamps used on the TrojanUV3000Plus™ system have been independently validated to maintain 98% of original output after 12,000 hours of operation.
Open-Channel Architecture Designed for Outdoor Installation Cost-effective to install and expand
7
1,000 2,000 3,000 4,000 5,000 6,000 7,000 8,000 9,000 10,000 11,000 12,000
Decrease in UV Lamp Output Over Time
UV
Out
put
(%)
The TrojanUV3000Plus™ system delivers flexibility and cost savings through its simple installation in existing channels and chlorine contact chambers. The system can be situated outdoors with no additional building, shelter or cooling requirements.
Benefits:• Compact, open-channel design
allows cost-effective installation in existing effluent channels and chlorine contact chambers
• System can be installed outdoors to reduce capital costs – no building, shelter or HVAC is required
• Gravity-fed design eliminates costs of pressurized vessels, piping and pumps
• Scalable architecture allows precise sizing – reduces capital and O&M costs associated with oversizing
• Modular design is readily expandable to meet new regulatory or capacity requirements
• Trojan’s thorough design approach ensures that effluent quality, upstream treatment processes, and O&M needs are addressed in system configurations
• Horizontal lamp mounting delivers optimal hydraulic performance. This arrangement induces turbulence and dispersion, maximizing wastewater exposure to UV output
Benefits:• Lamps are protected in a fully
submersible, 316 stainless steel frame
• Waterproof module frame protects cables from effluent, fouling and UV light
• Electronic ballasts are housed right in the module, reducing the system footprint, minimizing installation time and costs, and eliminating the need for separate external cabinets
• Ballast enclosures are rated TYPE 6P (IP67) – air/water tight
• Module leg and lamp connector have a hydrodynamic profile to reduce headloss
• The variable-output, electronic ballast is mounted in an enclosure integrated within the module frame
• Wiring is pre-installed and factory-tested
• Cooling ballasts by convection eliminates costs associated with air conditioning and forced-air cooling
Advanced, Self-Contained UV ModuleDramatically reduces footprint size and eliminates costs of air conditioning
Module leg and lamp connector have a hydrodynamic profile to reduce headloss and potential for debris fouling.
8
Module-mounted ballasts allow for compact installation, convection cooling, and protect wires and cables from exposure to effluent and UV light.
• TrojanUV3000Plus™ lamps are warranted for 12,000 hours
• Modular design allows for maintenance on one module without disrupting disinfection performance
• Maintenance limited to replacing lamps and cleaning solution
• Automated ActiClean™ cleaning system reduces manual labor associated with cleaning sleeves
Trojan UV lamps are easily replaced in minutes without the need for tools.
Quick connect allows for easy refill of ActiClean™-WW Gel.
Designed for Easy Maintenance
System SpecificationsSystem Characteristics TrojanUV3000Plus™
Typical Applications Wide range of wastewater treatment plants
Lamp Type High-efficiency Amalgam
Ballast Type Electronic, variable output (60 to 100% power)
Input Power Per Lamp 250 Watts
Lamp Configuration Horizontal, parallel flow
Module Configuration 4, 6 or 8 lamps per module
Level Control Device Options ALC, fixed weir or motorized weir gate
Water Level Sensor 1 electrode low water level sensor per channel
Enclosure Ratings:
Module Frame / Ballast Enclosure TYPE 6P (IP68) / TYPE 6P (IP67)
All Other Enclosures TYPE 4X (IP56)
Ballast Cooling Method Convection; no air conditioning or forced air required
Installation Location Indoor or outdoor
Sleeve Cleaning System:
ActiClean™ Cleaning System Optional Automatic Chemical/Mechanical Cleaning System
ActiClean™-WW Gel Non-corrosive, operator-friendly
Recommended Fouling Factor 1.0
System Control Center:
Controller Microprocessor or PLC-based
Analog Inputs (Typical) Flow (4-20 mA) and UVT (4-20 mA)
Discrete Outputs (Typical) Bank status, common alarms and SCADA communication
Maximum Distance from UV Channel 500 ft. (152 m)
Electrical Requirements:
Power Distribution Center 208Y/120V, 3 phase, 4 wire + GND, 60 Hz (Max. 8 modules per PDC)480Y/277V, 3 phase, 4 wire + GND, 60 Hz
380Y/220V, 3 phase, 4 wire + GND, 50/60 Hz 400Y/230V, 3 phase, 4 wire + GND, 50/60 Hz 415Y/240V, 3 phase, 4 wire + GND, 50/60 Hz
System Control Center (stand alone) 120V, single phase, 2 wire + GND, 60 Hz, 1.8 kVA220/230/240V, single phase, 2 wire + GND, 50/60 Hz, 1.8kVA
Hydraulic System Center (for ActiClean™) 208V, 3 phase, 3 wire + GND, 60 Hz 380/400/415 V, 3 phase, 3 wire + GND, 50/60 Hz
480 V, 3 phase, 3 wire + GND, 60 Hz or
2.5kVA HSC powered from PDC
Water Level Sensor 24VDC powered from PDC
Find out how your wastewater treatment plant can benefit from the TrojanUV3000Plus™ – call us today.
Head Office (Canada)3020 Gore Road London, Ontario, Canada N5V 4T7Telephone: (519) 457-3400 Fax: (519) 457-3030 www.trojanuv.com
The products described in this publication may be protected by one or more patents in The United States of America, Canada and/or other countries. For a list of patents owned by Trojan Technologies, go to www.trojanuv.com.
Printed in Canada. Copyright 2011. Trojan Technologies London, Ontario, Canada.No part of this publication may be reproduced, stored in a retrieval system, or transmitted in any form or by any means without the written permission of Trojan Technologies.MWW (0512)
Xylem Water Solutions USA, Inc. 14125 South Bridge Circle Charlotte, NC 28273
June 24, 2019 Arcadis Emily Carlson Project Name: Ulster, NY WWTP Project Number: J16080184021 Revision Number: 2 Ms. Carlson: We are pleased to submit the following proposal for the Ulster, NY WWTP UV opportunity based on the information provided within your inquiry. The TAK Smart system is an open channel process which provides many benefits that improve the performance of the system and increase the lifespan of the equipment. We would like to highlight a few key items with our proposal provided:
Industry Leading Technology - Our system includes our latest low-pressure, high-intensity ECORAY lamps that have a guaranteed life of 14,000 hours and are more efficient. These lamps are extremely robust and easy to remove and replace.
True "intensity based" dose pacing control - WEDECO is unique in the marketplace by taking into account real-time sensor readings of UV intensity, as a function of lamp output, aging and sleeve fouling. This is combined with real-time UV transmittance data to offer true dose pacing for all effluent conditions. Knowing that flows and water quality constantly vary, this system provides the end user with power savings and prevents over-dosing, allowing us to ensure that the UV system will meet permit at a wide variety of water qualities.
Even Flow Distribution - The system is equipped with a hydraulic baffle plate upstream of each channel that is used to promote even flow distribution throughout the channel, which improves disinfection by creating equal flow paths and eliminating dead zones.
Automatic Wiping System - Pneumatically driven automatic wiping system that prevents fouling of the quartz sleeve with very easy replacement of wipers.
Remotely Located Ballast Enclosures - WEDECO’s ballasts are located in a separate enclosure which allows for easy accessibility to electronics, and eliminates the risk of flooding any electronics.
TotalCare - WEDECO’s established and proven TotalCare Program provides our customers with proactive services all designed to minimize the cost of ownership to operate and maintain a UV system. TotalCare services can provide our customers with system health checks, efficiency audits, training and preventative maintenance contracts.
Please refer to our local representative Dave Boshart of GP Jager, (315) 256-3071 or us if you have any questions. We look forward to working with you on this exciting project. Sincerely, Julia Beilsmith Bill Mattfeld Territory Manager Senior Application Engineer (954) 483-8563
Ulster, NY Page 4 of 11 Date: June 24, 2019 Revision no.: 0
Table of Content
1 Xylem Overview ........................................................................................................ 5
2 General Process Description .................................................................................. 7
2.1 Design ........................................................................................................................ 7 2.2 Process Description ................................................................................................... 7
3 Technical Description .............................................................................................. 8
4 Price & Scope of Supply .......................................................................................... 9
4.1 Wedeco Scope of Supply ........................................................................................... 9 4.2 Budget Price .............................................................................................................. 9
5 Commercial Terms & Conditions .......................................................................... 10
6 Attachments ............................................................................................................ 11
6.1 Brochures / Drawings / others .................................................................................. 11
Ulster, NY Page 5 of 11 Date: June 24, 2019 Revision no.: 0
1 Xylem Overview
Xylem is a leading global water technology provider, enabling customers to transport, treat, test and efficiently use water in public utility, residential and commercial building services, industrial and agricultural settings. The company does business in more than 150 countries through a number of market-leading product brands, and its people bring broad applications expertise with a strong focus on finding local solutions to the world’s most challenging water and wastewater problems.
Xylem’s treatment business offers a portfolio of products and systems designed to effectively meet the demands and challenges of treating water and wastewater. From smarter aeration to advanced filtration to chemical-free disinfection, Xylem leverages its well-known Treatment brands, Flygt, Leopold, Sanitaire, and Wedeco, to offer hundreds of solutions backed by a comprehensive, integrated portfolio of services designed to ensure we can meet our customers’ needs in a number of different industries including municipal water and wastewater, aquaculture, biogas and agriculture, food and beverages, pharmaceuticals, and mining.
Our scientists and engineers utilize their deep applications expertise and continually listen and learn from our customers’ situations to create solutions that not only use less energy and reduce life-cycle costs, but also promote the smarter use of water.
Wedeco has accepted the challenge of the 21st century. With the Wedeco brand for UV Disinfection, ozone oxidation & AOP solutions, we own the advanced technologies for chemical-free and environmentally friendly treatment of drinking water, wastewater and process water as well as further industrial treatment processes. We
constantly invest a large portion of our energy in the development of high-tech components, systems and equipment, as well as in the study of new areas of application for UV, ozone & AOP. In doing so, we have always given special attention to the increase in energy efficiency of our Products equipped with our unique UV lamps and ozone electrodes.
Ulster, NY Page 6 of 11 Date: June 24, 2019 Revision no.: 0
The special characteristics of the Wedeco Ecoray UV lamp are its special doping and the unique long-life coating. Because of these futures, a constantly high UV light yield is achieved with a substantially extended lamp service life at the same time. In addition, by using this technology it is not necessary to apply liquid mercury inside the lamp. Wedeco UV lamps cannot be surpassed in economic efficiency.
In relation to expenditure of energy, the High-Intensity/Low-Pressure Technology provides a light yield three times higher than comparable UV lamps of widely used Medium Pressure Technology. A higher light yield also means a lower heat generation at the same time. Thanks to this, Wedeco UV lamps become less susceptible to varying water temperatures. Even the formation of deposits on the quartz sleeves as well as lamp aging is considerably lower than with alternative UV lamp technologies in Herford and Essen.
Xylem's Wedeco ozone systems combine maximum flexibility and reliable operating characteristics for small to large ozone capacities. The ozone generator system and control unit can be combined and supplemented with option sets that allow for various application requirements. Effizon evo 2G ozone electrodes are the core of our technology and achieve an unmatched level of reliability and energy efficiency. The electrodes are manufactured completely from inert materials, without the need for fuses or
coatings, making them highly resistant to corrosion. This means that the Wedeco ozone generators are practically maintenance free with no need for regular cleaning or replacement of the electrodes. We rely on consistently high-quality standards in all divisions of the company. Moreover, product quality and manufacturing operations are constantly monitored and optimized in continuous improvement processes. Established quality controls give Xylem and you the security of knowing that Wedeco UV, Ozone & AOP systems will always operate reliably. For more information please visit us at http://www.xylem.com/treatment/
WEDECO Effizon® evo 2G Ozone electrode
WEDECO Ecoray UV lamp
Ulster, NY Page 7 of 11 Date: June 24, 2019 Revision no.: 0
2 General Process Description
2.1 DESIGN
Design Flow Rates - Peak Design Flow 4.6 MGD
Total Suspended Solids (Maximum) 5 mg/l 5-day B.O.D. 25 mg/l Allowable Effluent Temperature Range 41-86°F UV Transmittance at 253.7 nm 65%, minimum Maximum Influent Fecal Coliforms Count 100,000 Fecal Coliforms/100 mL Effluent Disinfection Standard
- Fecal Coliforms (30 day geometric mean) <200 Fecal Coliforms/100 mL - Fecal Coliforms (7 day geometric mean) <400 Fecal Coliforms/100 mL
UV Dose
- Minimum Design UV Dose (based on calculated PSS dose)
>60 mJ/cm²
2.2 PROCESS DESCRIPTION
The proposed UV system is based on an influent quality that meets the above listed criteria and requires that all wastewater to be disinfected has undergone prior treatment through Rotating Biological Contactors (RBCs) and a final settling tank.
Ulster, NY Page 8 of 11 Date: June 24, 2019 Revision no.: 0
3 Technical Description
CONFIGURATION: TAK Smart 4-3x2i1
DESCRIPTION UNITS VALUE
Total Number of lamps
Number of channels
Number of banks per channel
Number of modules per bank
Number of lamps per module
48
1
2
3
8
CHANNEL DIMENSIONS:
Width along UV banks
Width along weir
Design water depth @ influent
Overall channel height & length
Inches
28.0
As shown in drawing
18.5
As shown in drawing
HEADLOSS (at peak flow):
Across baffle plate
Across UV system
Across level control
Allowable freefall
Total Headloss
Inches
2
2.6
1.2
4
9.8
POWER CONSUMPTION:
Peak Flow Lamp and Ballast Power
kW
16.49
Ulster, NY Page 9 of 11 Date: June 24, 2019 Revision no.: 0
4 Price & Scope of Supply
4.1 WEDECO SCOPE OF SUPPLY All required UV modules fully equipped with lamps and quartz sleeves Supports to install modules in concrete channel 14.8 ft (4.5 m) fully assembled quick disconnect power cabling from modules to ballast cabinet Electrical Control 48 housing the electrical equipment:
Painted Steel Type 12 w/fan cooling (<104 deg F) WEDECO EcoTouch Touchscreen HMI Power supply requirements: 480 V, 3 phase, 4 wire + ground (wye) Automatic wiping system including compressed air supply Optidose Dose Pacing UV intensity sensor (one per bank) SCADA Communication Labeling of components Inlet baffle plate Fixed finger weir Spare parts: 2 lamps, 2 quartz sleeves, 4 wiper rings, and 1 ballast Three (3) operating and maintenance manuals in English language Factory testing of all parts and equipment prior to shipment Packaging of UV equipment Recommended manufacturer’s field services on site [1 trip / 3 days]
4.2 BUDGET PRICE
TAK Smart Standard Equipment
Total $112,000
Ulster, NY Page 10 of 11 Date: June 24, 2019 Revision no.: 0
5 Commercial Terms & Conditions
Commercial Details
Submittal time: 8 weeks after approved purchase order
Delivery time: 18 weeks after approved submittals
Terms of Delivery: All prices are FCA factory with full freight allowed to the job site.
Terms of Payment:
This proposal is based upon WEDECO’s General Terms of Business. Price is based upon the following payment terms (net 30 days):
10% net 30 days upon initial submittal of mechanical/electrical drawings for approval
80% net 30 days from the date of the respective shipments of the product
5% installation of the Xylem equipment, NTE 150 days after shipment
5% start-up / training on the Xylem equipment, NTE 180 days after shipment
Warranties:
Lamp Warranty: Guaranteed 14,000 hours of operation, prorated after 9,000 hours.
System Warranty: 18 months from date of delivery or 12 months from date of substantial completion of UV equipment whichever comes first.
TAK SMART GENERAL NOTES:
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Digester Mixers - Page 3
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Digester Mixers - Page 4
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Digester Mixers - Page 5
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Digester Mixers - Page 6
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Digester Mixers - Page 7
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Digester Mixers - Page 8
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Digester Mixers - Page 9
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Digester Mixers - Page 10
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Digester Mixers - Page 11
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Digester Mixers - Page 12
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Digester Mixers - Page 13
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www.ovivowater.com 1.855.GO.OVIVO
Capable of mixing viscous fats, oils and greases
Ragless design and low cost maintenance
Significant energy savings compared to conventional mixing systems
Installation and Capital cost savings
Suitable for both new and existing tanks
EFFICIENT LOW ENERGY SLUDGE MIXING
LM™ MIXER
MUNICIPAL WATEWATERANAEROBIC DIGESTION
Proven to achieve over 90%
active tank volume! Give us a call at
1.855.GO.OVIVO to learn more.
Anaerobic Digestion is highly dependent upon effective sludge mixing. When tank content is inadequately mixed, stratification occurs and the tank volume is not properly utilized. Most wastewater treatment facilities require thorough and complete mixing to ensure uniform temperature, solids distribution and microorganism contact with incoming sludge, to increase gas production and maximize the solids destruction.
• Efficient mixing is critical; therefore, the goal is to achieve the optimal mixing efficiency with the least amount of power.
• Achieving a unique mixing pattern allows for efficient mixing while keeping the energy requirements lower (allowing for the amount saved to be used elsewhere at the plant).
• Independent full scale testing has proven the lower energy needs compared to conventional mixing systems.
ANAEROBIC DIGESTION
LESS HP, MORE SAVINGS
MAJOR ENERGY SAVINGS
LM™ MIXER
ENGINEERINGDESIGNED FOR PERFORMANCE
Drive System
Drive Support
Mixer Flange
Seal Tube
Shaft
Hydro-Disk
MAIN CONFIGURATIONS FOR THE LM™ MIXER:
• Operating Speed: 30 CPM (cycles per minute)
• Stroke Length: 12 inches, 16 inches or 20 inches
• Disk Size: 72 inches, 84 inches or 96 inches
Motor Size 1 Year 5 Years 10 Years 20 Years
10HP $4,409 $25,558 $59,258 $159,275
90HP $39,684 $230,023 $533,319 $1,433,471
Difference $35,275 $204,465 $474,061 $1,274,197
Assuming $ 0.09/kWh, 75% nameplate power and 3% appreciation per year
HOW IT WORKSUNIFORM MIXING
KEY BENEFITS
MUNICIPAL WASTEWATER | ANAEROBIC DIGESTION
The LM™ mixer is designed to mix the viscous slurries in order to achieve a homogeneous mixture in the tank while using less energy at the same time. The LM mixer offers solutions to the challenges of mixing wastewater in both thin and thick sludge applica-tions.
The frequency, stroke and size of the hydro-disk control the force and velocity of the liquid core. The LM mixer’s oscillating motion produces a flow pattern that approaches nearly isotropic (uniform) mixing and does not display the turbulence intensity or vortices of rotary mixers. Additionally, LM mixers operate by using pulsating pressure waves in conjunction with the oscillating velocity. In this type of concurrent action the oscillating pres-sure wave and velocity are coupled together to enhance mass transfer and produce a uniform mixture of the tank’s contents.
Each tank configuration is different and therefore the LM mixer is custom designed to meet a variety of mixing demands by varying the frequency, stroke and disk size. Utilizing the pow-er of Computational Fluid Dynamics (CFD), tanks can be modeled and analyzed for proper mixer sizing.
EFFICIENT MIXING TO HELP IMPROVE THE DIGESTION PROCESS
• Does not rely on induced flow to create the necessary mixing.
• Rags do not build up on disk
• Uniform mixing throughout the tank
PROVEN TECHNOLOGY
• Multiple LiCl tests performed by third parties demonstrate an active volume of 90% or greater.
INSTALLATION COST SAVINGS
• Installation of a single mixer can be completed in a day or less.
• No additional piping needed.
• No core drilling necessary
SUITABLE FOR BOTH NEW AND EXISTING TANKS
• Little to no changes are needed on existing structures
LEARN MORE!Scan to view online.
1.855.GO.OVIVO
2015 © Ovivo Inc. All rights reserved
Ovivo® ConnectSM portal is an innovative and intuitive application that allows our customers to use ‘SmartTags’ installed on our equipment (or a web URL) to access a personalized customer zone. Access your equipment documentation, find contract references, track service logs, manage spare parts, and plan your next maintenance to get the most out of your equipment.
NEED ACCESS TO YOUR O&M MANUAL? NEED SPARE PARTS? WANT THE LATEST TIPS AND NEWS ON YOUR ASSET?
GET CONNECTED!ovivo.co
LM™ MIXER
OUR EXPERTISEAnaerobic Digestion is highly dependent upon effective sludge mixing. Ovivo sludge mixers are designed to provide powerful mixing, without accumulating stringy or fibrous material. Highly efficient and featuring low maintenance requirements, they can be used for existing or new digesters. Their configuration is adpated to suit best the specific tank design and application.
ANCILLARY EQUIPMENTOvivo can supply all plant required equipment for a complete Sludge Treatment / Anaerobic Digestion plant, including but not limited to:
• Ultrastore™ Membrane Gasholder• Eimix® Mechanical Sludge Mixer• Ovivo® Anaerobic Digester Steel Cover• Sonolyzer™ Ultrasound Sludge Disintegrator
THE OVIVO DIFFERENCE 200+ YEARS OF HERITAGE • 100% FOCUSED ON WATER
GT 330 A
COMMERCIAL AND INSTITUTIONAL
88%+ Efficiency
Near Condensing Eutectic Cast Iron - Water Temperature Supply @ 86°F
Operates under large Temperature Differentials - Up to 81°F without Thermal Shock
Low NOx Compatibility
Maximum Working Pressure 90 p.s.i.
Innovative Design
For Better Fuel
Efficiency
A Symbol of Quality
Engineering For Over
Three Centuries
www.dedietrichboilers.com
EUTECTIC CAST IRON BOILERS
GT 330 AHigh Performance Low-Temperature Return Eutectic Cast Iron Boilers
Low Return Water Capability
Maximizes Energy Savings
The GT 330 A Series is a eutectic cast iron 3-pass, high efficiency, large net output, low
operating temperature, designed boiler. These boilers are specifically designed for oil / gas /
propane firing.
The GT 330 A is equipped with a simplified control panel with built-in on/off limit, high limit,
manual reset limit and temperature gauge.
The GT 330 A is a Three Pass Design with
large combustion chamber and horizontal flue
passes with fins. The heat transfer is
enhanced by the fins and eutectic cast iron
baffles. This body design assures:
Efficiency up to 88%
Low pressure drops
Low noise level
High thermal efficiency and heattransfer
Low Water Outlet Temperature down to
85°F with indoor/outdoor reset achieves
significant energy savings by reducing
stand-by fuel consumption. In addition, it’s not
necessary to maintain boiler temperature
between the two heating cycles, which further
reduces fuel consumption and achieves
excellent overall efficiency. Studies show
substantial savings over retrofit boilers and
over new competitive models.
Easy Cleaning with Hinged Door for
burner and flue access. Doors can be hinged
right or left based on your access needs.
Boiler is easily cleaned and vacuumed,
resulting in lower maintenance costs.
Eutectic Cast Iron boiler body provides
exceptional resistance to temperature
variations and thermal stress. De Dietrich’s
eutectic cast iron is 30% more flexible than
any competitive cast iron allowing safe low
temperature operation.
Four Inch Insulation featuring reinforced
fiberglass wool. De Dietrich Boilers feature
double insulation of the boiler front which
minimizes heat loss and allows reduced
stand-by consumption and improved thermal
efficiency.
Control Panel. The standard control panel
supplied is designed for heating only. The
panel is equipped with a boiler thermometer,
on/off limit, high limit and manual reset limit.
The large size permits it to be integrated
easily with third party energy management
systems.
Standard Equipment
Eutectic Cast Iron Nipples
Built-in High Limit with ManualReset
Thermocord Combustion Sealed
On/Off Limit
Temperature Indicator
ASME Relief Valve
Low Water Cut-Off
Low NOx Burners (optional)
Factory Assembly (optional)
Contact your local De Dietrichrepresentative for a list of availableburners.
Thermocord & Groove
system eliminates
gaskets - the number
one cause of boiler
maintenance
De Dietrich “eutectic”
cast iron delivers 30%
more flexibility, providing
the industry’s best
thermal shock resistance
Flexible eutectic cast
allows 85°F supply water
capability. This low
temperature operation
yields significant fuel
savings
TH!NK BOILERS... TH!NK
GT 330 AHigh Performance Low-Temperature Return Eutectic Cast Iron Boilers
Large wiring duct
leading to the control
panel
Flue nozzle with two
cleaning traps directly
accessible without
dismantling the casing
Large flue-ways with
fins and turbulators
offering high efficiency
and easy maintenance
Boiler body with
3-pass flueways
Large size combustion
chamber
Design of the front section is
adapted for the use of low
NOx burners
Front return (optional)
Hinged burner
door (right or left
hand side)
Flame observation
window
Removable turbulators
2” thick ceramic fiber
insulated cleaning door
Eutectic cast iron boiler body, thermal shock
and corrosion resistant, allowing low modulated
temperature operation and complete stop
between heating periods
Completely insulated
boiler body with four
inch thick fiberglass
wool
Hinged cleaning door
(right hand or left hand
side)
Silicon wrapped ceramic
thermocord assures flue
gas tightness
Well for sensors
Control panel designed to
enable easy wiring
connections
Setting the Benchmark for Low-Temperature
Near-Condensing Eutectic Cast Iron Boilers
Ceramic insulated burner
door 3” to 4-7/8” thick
MEA 304-06-M (City of New York)
As the Boiler Should Be!!!
®
® C US
Notes:
- Approved for direct-vent applications - use only approved venting components as listed
- Natural draft applications, approved for Type L vent [Gas-Oil] or Type B Vent [Gas only]
- All model comply with latest Canadian & USA standards
- Outputs are rounded off. 85.2% efficiency is the published efficiency (oil is +3%)
Represented By:
(2)
(1) (1)
31.5“[800mm]
46.9
”[1
192m
m]
4”[103mm]
4”[103mm]
23.39”[594mm]
5.39
”[1
37m
m]
15.2
4”[3
87m
m]
6”[153mm]
2.1”[53mm]
3.86”[98mm]
6”[153mm]
12.79”[325mm]
28.27”[718mm]
1.97”[50mm]
7.68”[195mm]
4.13”[105mm]
6.3”[160mm]
4.53
”[1
15m
m]
5.39
”[1
37m
m]
40”
[101
7mm
]
32.5
6”[8
27m
m]
29”[738mm]
51”
[129
7mm
]
5.12”[130mm]
4.13
”[1
05m
m]
6.5”[165mm]
GT 334A GT 335A GT 336A GT 337A GT 338A GT 339A
L 30 [991] 45.3 [1151] 51.6 [1311] 57.9 [1471] 64.2 [1631] 70.5 [1791]
P 19.3 [490] 25.6 [650] 31.9 [810] 31.2 [970] 44.5 [1130] 50.8 [1290]
ØR 7.1 [180] 7.1 [180] 7.1 [180] 7.9 [200] 7.9 [200] 7.9 [200]
(1) Adjustable feet: basic dimension 0, adjustment possible: 0 to 1.57” [40mm] 1. Sludge removal hole Ø Rp 2 ½” (plugged)2. Rp 1½ socket for the safety control unit3. Heating outlet (clamp + counter flange withcollar to be welded) Ø 2½” (Ø 2” option)4. Heating return (clamp + counter flange withcollar to be welded) Ø 2½” (Ø 2” option)5. Rp 1½” draining outlet (plugged)
Model
Item Unit GT 334A GT 335A GT 336A GT 337A GT 338A GT 339A
CSA - Gas InputMBH 404 598 808 1,024 1,226 1,442
Kw 118 175 237 300 359 423
CSA - #2 Fuel Oil Input US/GPH 2.8 4.15 5.6 7.1 8.5 10
CSA - Output [Gas-Oil]MBH 344 510 688 872 1,044 1,229
Kw 100.8 149.4 201.6 255.7 306.1 360.1
Cast Iron Sections # 4 5 6 7 8 9
Water Resistance
Delta T=(°F)
18 (°F) Ft Water 0.483 1.026 2.099 3.055 4.380 6.332
27 (°F) Ft Water 0.210 0.457 0.933 1.358 1.945 2.818
36 (°F) Ft Water 0.121 0.256 0.525 0.764 1.094 1.583
MAWP [Water] PSI ASME IV Rating Class 30 - (90 psi)
S3NAPanel Electrical Connection V/P/H 120/1/60
Max. Water Temp.
Safety Limit [MR](°F) 248
(°C) 120
Water operating Temp.
Range(°F) 86-185
(°C) 30-85
Gas-vent category # I, II, III or IV
Boiler-vent connection inch 7 7 7 8 8 8
Boiler weight [dry]LB 1,349 1,623 1,865 2,163 2,432 2,712
Kg 612 736 846 981 1,103 1,230
TH!NK BOILERS... TH!NK
Toll Free: (800) 943-6275www.dedietrichboilers.com
Due to ongoing and continuous product improvements, DDR Americas Inc. reserves all rights to amend and delete information provided on this product specification table.
11-26-09
Town of Ulster
Analysis of Electrical Usage UWWTP
As of March 15, 2019
Invoice Usage Demand Rate Blended Rate
($) (kWh) (kW) ($/kWh) ($/kWh)
Central Hudson 1/9/2013 2/5/2013 2855.99 92960 172.8 0.03072
Direct Energy 1/9/2013 2/5/2013 9633.32 92960 0.10363 0.13435
Central Hudson 2/5/2013 3/8/2013 2349.77 81600 169.6 0.02880
Direct Energy 2/5/2013 3/8/2013 7361.17 81600 0.09021 0.11901
Central Hudson 3/8/2013 4/5/2013 1816.62 71360 166.4 0.02546
Direct Energy 3/8/2013 4/5/2013 4674.37 71360 0.06550 0.09096
Central Hudson 4/5/2013 5/6/2013 2642.3 86880 169.6 0.03041
Direct Energy 4/5/2013 5/6/2013 5054.78 86880 0.05818 0.08859
Central Hudson 5/6/2013 6/4/2013 3092.68 102080 179.2 0.03030
Direct Energy 5/6/2013 6/4/2013 6293.17 102080 0.06165 0.09195
Central Hudson 6/4/2013 7/8/2013 2924.96 111360 190.4 0.02627
Direct Energy 6/4/2013 7/8/2013 6504.76 111360 0.05841 0.08468
Central Hudson 7/8/2013 8/6/2013 3369.67 105760 184 0.03186
Direct Energy 7/8/2013 8/6/2013 7573.3 105760 0.07161 0.10347
Central Hudson 8/6/2013 9/4/2013 3060.02 99360 174.4 0.03080
Direct Energy 8/6/2013 9/4/2013 5567.07 99360 0.05603 0.08683
Central Hudson 9/4/2013 10/3/2013 3219.13 99040 168 0.03250
Direct Energy 9/4/2013 10/3/2013 5476.72 99040 0.05530 0.08780
Central Hudson 10/3/2013 11/1/2013 3177.68 96320 166.4 0.03299
Direct Energy 10/3/2013 11/1/2013 5070.74 96320 0.05264 0.08564
Central Hudson 11/1/2013 12/5/2013 2942.11 108480 168 0.02712
Direct Energy 11/1/2013 12/5/2013 6226.36 108480 0.05740 0.08452
Central Hudson 12/5/2013 1/8/2014 3304.01 110080 171.2 0.03001
Direct Energy 12/5/2013 1/8/2014 7749.63 110080 0.07040 0.10041
Central Hudson 1/8/2014 2/7/2014 3165.16 101600 172.8 0.03115
Direct Energy 1/8/2014 2/7/2014 7152.64 101600 0.07040 0.10155
Central Hudson 2/7/2014 3/7/2014 2336.66 95840 172.8 0.02438
Direct Energy 2/7/2014 3/7/2014 6747.14 95840 0.07040 0.09478
Central Hudson 3/7/2014 4/3/2014 2489.72 91200 174.4 0.02730
Direct Energy 3/7/2014 4/3/2014 6420.48 91200 0.07040 0.09770
Central Hudson 4/3/2014 5/1/2014 2819.99 95520 172.8 0.02952
Direct Energy 4/3/2014 5/1/2014 6724.61 95520 0.07040 0.09992
Central Hudson 5/1/2014 6/2/2014 3479.23 110720 171.2 0.03142
Direct Energy 5/1/2014 6/2/2014 8645.77 110720 0.07809 0.10951
Central Hudson 6/2/2014 7/3/2014 2915.29 106080 177.6 0.02748
Direct Energy 6/2/2014 7/3/2014 8410.94 106080 0.07929 0.10677
Central Hudson 7/3/2014 8/6/2014 3479.09 122720 187.2 0.02835
Direct Energy 7/3/2014 8/6/2014 9630.38 122720 0.07847 0.10682
Central Hudson 8/6/2014 9/3/2014 2892.87 95040 169.6 0.03044
Direct Energy 8/6/2014 9/3/2014 7534.47 95040 0.07928 0.10972
Central Hudson 9/3/2014 10/7/2014 3329.61 113280 171.2 0.02939
Direct Energy 9/3/2014 10/7/2014 9018.98 113280 0.07962 0.10901
Central Hudson 10/7/2014 11/3/2014 3123.99 92000 169.6 0.03396
Direct Energy 10/7/2014 11/3/2014 7247.43 92000 0.07878 0.11273
Central Hudson 11/3/2014 12/5/2014 2495.96 72800 129.6 0.03429
Direct Energy 11/3/2014 12/5/2014 5765.85 72800 0.07920 0.11349
Central Hudson 12/5/2014 1/8/2015 1805.5 76800 131.2 0.02351
Direct Energy 12/5/2014 1/8/2015 5628.89 76800 0.07329 0.09680
LIME 2/18/2015 2/18/2015 4801.15 0 0 0.00000 0.00000
Central Hudson 1/8/2015 2/3/2015 2117.83 69280 147.2 0.03057
Direct Energy 1/8/2015 2/3/2015 5050.89 69280 0.07291 0.10347
Central Hudson 2/3/2015 3/9/2015 2740.96 89440 139.2 0.03065
Direct Energy 2/3/2015 3/9/2015 6520.48 89440 0.07290 0.10355
Central Hudson 3/9/2015 4/6/2015 1934.98 71040 129.6 0.02724
Direct Energy 3/9/2015 4/6/2015 5320.84 71040 0.07490 0.10214
Central Hudson 4/6/2015 5/7/2015 3195.33 103520 171.2 0.03087
Direct Energy 4/6/2015 5/7/2015 7789.19 103520 0.07524 0.10611
Central Hudson 5/7/2015 6/4/2015 3289.62 95200 164.8 0.03455
Direct Energy 5/7/2015 6/4/2015 7617.12 95200 0.08001 0.11457
Central Hudson 6/4/2015 7/7/2015 3189.11 113920 184 0.02799
Direct Energy 6/4/2015 7/7/2015 9075.51 113920 0.07967 0.10766
Central Hudson 7/7/2015 8/4/2015 2996.6 98400 176 0.03045
Direct Energy 7/7/2015 8/4/2015 7656.37 98400 0.07781 0.10826
Central Hudson 8/4/2015 9/1/2015 2786.96 95200 172.8 0.02927
Direct Energy 8/4/2015 9/1/2015 7484.01 95200 0.07861 0.10789
Central Hudson 9/1/2015 10/2/2015 3163.47 108320 190.4 0.02920
Direct Energy 9/1/2015 10/2/2015 8529.98 108320 0.07875 0.10795
Central Hudson 10/2/2015 11/3/2015 3140.07 114080 176 0.02753
Direct Energy 10/2/2015 11/3/2015 8969.56 114080 0.07863 0.10615
Central Hudson 11/3/2015 12/4/2015 2689.26 85600 161.6 0.03142
Direct Energy 11/3/2015 12/4/2015 6582.1 85600 0.07689 0.10831
Central Hudson 12/4/2015 1/5/2016 1941.5 70080 126.4 0.02770
Direct Energy 12/4/2015 1/5/2016 5508.29 70080 0.07860 0.10630
Central Hudson 1/5/2016 2/2/2016 1994.58 71200 142.4 0.02801
Direct Energy 1/5/2016 2/2/2016 5596.32 71200 0.07860 0.10661
Central Hudson 2/2/2016 3/3/2016 1786.2 67200 124.8 0.02658
Direct Energy 2/2/2016 3/3/2016 5281.92 67200 0.07860 0.10518
Central Hudson 3/3/2016 4/1/2016 2193.98 62400 128 0.03516
Direct Energy 3/3/2016 4/1/2016 4904.64 62400 0.07860 0.11376
Central Hudson 4/1/2016 5/3/2016 2657.37 95520 171.2 0.02782
Direct Energy 4/1/2016 5/3/2016 7507.87 95520 0.07860 0.10642
Central Hudson 5/3/2016 6/2/2016 2711.56 100640 169.6 0.02694
Direct Energy 5/3/2016 6/2/2016 7910.3 100640 0.07860 0.10554
Central Hudson 6/3/2016 7/1/2016 2490.08 98240 171.2 0.02535
Direct Energy 6/3/2016 7/1/2016 7721.66 98240 0.07860 0.10395
Central Hudson 7/2/2016 8/1/2016 2691.83 106400 171.2 0.02530
Direct Energy 7/2/2016 8/1/2016 8363.04 106400 0.07860 0.10390
Vendor Period Begin Period End
Town of Ulster
Analysis of Electrical Usage UWWTP
As of March 15, 2019
Invoice Usage Demand Rate Blended Rate
($) (kWh) (kW) ($/kWh) ($/kWh)Vendor Period Begin Period End
Central Hudson 8/2/2016 8/31/2016 2770.17 101440 171.2 0.02731
Direct Energy 8/2/2016 8/31/2016 7973.18 101440 0.07860 0.10591
Central Hudson 9/1/2016 9/30/2016 2775.53 101120 171.2 0.02745
Direct Energy 9/1/2016 9/30/2016 7948.03 101120 0.07860 0.10605
Central Hudson 10/1/2016 10/28/2016 2717.88 93440 168 0.02909
Direct Energy 10/1/2016 10/28/2016 7344.38 93440 0.07860 0.10769
Central Hudson 10/29/2016 12/1/2016 2481.27 83520 158.4 0.02971
Direct Energy 10/29/2016 12/1/2016 6564.67 83520 0.07860 0.10831
Central Hudson 12/2/2016 1/5/2017 1981.54 77120 120 0.02569
Direct Energy 12/2/2016 1/5/2017 6061.63 77120 0.07860 0.10429
Central Hudson 1/5/2017 2/8/2017 1865.47 80160 126.4 0.02327
Direct Energy 1/5/2017 2/8/2017 6300.58 80160 0.07860 0.10187
Central Hudson 2/8/2017 3/9/2017 1769.24 66560 118.4 0.02658
Direct Energy 2/8/2017 3/9/2017 5231.62 66560 0.07860 0.10518
Central Hudson 3/9/2017 5/31/2017 6840.28 254720 176 0.02685
Direct Energy 3/9/2017 5/31/2017 20020.99 254720 0.07860 0.10545
Central Hudson 5/31/2017 7/13/2017 3582.66 148480 171.2 0.02413
Direct Energy 5/31/2017 7/13/2017 12157.55 148480 0.08188 0.10601
Central Hudson 7/13/2017 8/1/2017 1539.13 63680 166.4 0.02417
Direct Energy 7/13/2017 8/1/2017 5214.12 63680 0.08188 0.10605
Central Hudson 8/1/2017 9/5/2017 4465.5 120000 337.6 0.03721
Direct Energy 8/1/2017 9/5/2017 9825.6 120000 0.08188 0.11909
Central Hudson 9/5/2017 10/3/2017 2735.03 97280 171.2 0.02812
Direct Energy 9/5/2017 10/3/2017 7965.29 97280 0.08188 0.11000
Central Hudson 10/3/2017 11/2/2017 2663.93 94720 171.2 0.02812
Direct Energy 10/3/2017 11/2/2017 7755.68 94720 0.08188 0.11000
Central Hudson 11/2/2017 12/1/2017 1973.43 66560 124.8 0.02965
Direct Energy 11/2/2017 12/1/2017 5449.94 66560 0.08188 0.11153
Central Hudson 12/1/2017 1/3/2018 1902.46 78720 129.6 0.02417
Direct Energy 12/1/2017 1/3/2018 5662.4 78720 0.07193 0.09610
Central Hudson 1/3/2018 2/1/2018 1962.33 70240 131.2 0.02794
Direct Energy 1/3/2018 2/1/2018 5054.47 70240 0.07196 0.09990
Central Hudson 2/1/2018 4/3/2018 4930.23 153120 177.6 0.03220
Direct Energy 2/1/2018 4/3/2018 11017.34 153120 0.07195 0.10415
Central Hudson 4/3/2018 5/3/2018 2880.93 97280 174.4 0.02961
Direct Energy 4/3/2018 5/3/2018 6992.49 97280 0.07188 0.10149
Central Hudson 5/3/2018 6/4/2018 2828.36 111680 176 0.02533
Direct Energy 5/3/2018 6/4/2018 8027.56 111680 0.07188 0.09721
Central Hudson 6/4/2018 7/5/2018 2489.28 107360 172.8 0.02319
Direct Energy 6/4/2018 7/5/2018 7716.76 107360 0.07188 0.09506
Central Hudson 7/5/2018 8/6/2018 3160.09 109760 177.6 0.02879
Direct Energy 7/5/2018 8/6/2018 7887.35 109760 0.07186 0.10065
Central Hudson 8/6/2018 9/5/2018 2793.25 104960 176 0.02661
Direct Energy 8/6/2018 9/5/2018 7542.42 104960 0.07186 0.09847
Central Hudson 9/5/2018 10/4/2018 2624.3 102240 182.4 0.02567
Direct Energy 9/5/2018 10/4/2018 7346.97 102240 0.07186 0.09753
Central Hudson 10/4/2018 10/31/2018 2852.26 96480 180.8 0.02956
Direct Energy 10/4/2018 10/31/2018 6933.05 96480 0.07186 0.10142
Central Hudson 10/31/2018 12/6/2018 2801.46 95040 161.6 0.02948
Direct Energy 10/31/2018 12/6/2018 6829.44 95040 0.07186 0.10134
Central Hudson 12/6/2018 1/8/2019 1524.15 76640 131.2 0.01989
Direct Energy 12/6/2018 1/8/2019 5514.88 76640 0.07196 0.09185
Central Hudson 1/8/2019 2/7/2019 2072.12 70720 134.4 0.02930
Direct Energy 1/8/2019 2/7/2019 5514.88 70720 0.07798 0.10728
Town of Ulster
Analysis of Propane Usage UWWTP
As of March 23, 2019
Delivery Invoice Rate
(gallons) ($) ($/gallon)
Heritage 1/9/2017 1154.5 $1,387.02 $1.20
Heritage 1/16/2017 729.7 $883.67 $1.21
Heritage 1/30/2107 868.1 $1,101.53 $1.27
Heritage 2/6/2017 725.7 $985.43 $1.36
Heritage 2/20/2017 1400.1 $1,738.64 $1.24
Heritage 2/27/2017 376.8 $417.08 $1.11
Heritage 3/13/2017 584.4 $625.37 $1.07
Heritage 3/27/2017 1265.1 $1,368.96 $1.08
Heritage 4/10/2017 1087.5 $1,115.56 $1.03
Heritage 4/24/2017 747 $801.98 $1.07
Heritage 5/8/2017 650 $657.61 $1.01
Heritage 5/22/2017 551 $572.32 $1.04
Heritage 6/6/2017 486.5 $500.51 $1.03
Heritage 6/20/2017 387.1 $383.38 $0.99
Heritage 7/5/2017 485.4 $469.96 $0.97
Heritage 7/18/2017 270 $273.02 $1.01
Heritage 7/26/2017 240 $251.50 $1.05
Heritage 8/8/2017 310 $347.42 $1.12
Heritage 8/22/2017 400.1 $449.63 $1.12
Heritage 8/30/2017 196.3 $220.76 $1.12
Heritage 9/11/2017 450 $534.87 $1.19
Heritage 9/27/2017 360 $455.00 $1.26
Heritage 10/17/2017 600 $818.88 $1.36
Heritage 10/31/2017 415.2 $567.66 $1.37
Heritage 11/13/2017 730 $972.58 $1.33
Heritage 11/17/2017 250 $333.08 $1.33
Heritage 11/24/2017 500 $699.45 $1.40
Heritage 11/27/2017 175.5 $249.19 $1.42
Heritage 12/4/2017 350 $501.87 $1.43
Heritage 12/5/2017 200 $286.78 $1.43
Heritage 12/10/2017 500 $718.90 $1.44
Heritage 12/19/2017 700.2 $977.13 $1.40
Heritage 12/26/2017 450 $641.93 $1.43
Heritage 12/31/2017 800 $1,170.96 $1.46
Heritage 1/10/2018 855.1 $1,292.74 $1.51
Heritage 1/23/2018 1325 $2,147.03 $1.62
Heritage 1/31/2018 500.2 $860.99 $1.72
Heritage 2/7/2018 865.6 $1,460.53 $1.69
Heritage 2/12/2018 461 $731.98 $1.59
Heritage 2/19/2018 400.1 $635.28 $1.59
Propane Supplier Delivery Date
Town of Ulster
Analysis of Propane Usage UWWTP
As of March 23, 2019
Delivery Invoice Rate
(gallons) ($) ($/gallon)Propane Supplier Delivery Date
Heritage 3/1/2018 700 $1,029.70 $1.47
KOSCO HERITAGE 3/10/2018 844.60 $1,056.00 $1.25
KOSCO HERITAGE 3/22/2018 1200.00 $1,551.96 $1.29
KOSCO HERITAGE 3/29/2018 484.80 $615.26 $1.27
KOSCO HERITAGE 4/6/2018 500 $627.45 $1.25
KOSCO HERITAGE 4/30/2018 1054 $1,273.65 $1.21
KOSCO HERITAGE 5/8/2018 266.2 $327.88 $1.23
KOSCO HERITAGE 5/15/2018 513.2 $650.53 $1.27
KOSCO HERITAGE 5/22/2018 275.3 $362.60 $1.32
KOSCO HERITAGE 6/5/2018 400.00 $522.08 $1.31
KOSCO HERITAGE 6/11/2018 250.00 $323.50 $1.29
KOSCO HERITAGE 6/18/2018 210.00 $258.51 $1.23
KOSCO HERITAGE 6/21/2018 125.00 $154.76 $1.24
KOSCO HERITAGE 7/2/2018 129.00 $155.90 $1.21
KOSCO HERITAGE 7/3/2018 194.60 $244.48 $1.26
Bottini 7/25/2018 381.7 $506.33 $1.33
Bottini 8/9/2018 302.5 $427.37 $1.41
Bottini 8/23/2018 400 $568.20 $1.42
Bottini 9/6/2018 247.3 $370.03 $1.50
Bottini 9/20/2018 424.5 $645.92 $1.52
Bottini 10/9/2018 500.2 $777.66 $1.55
Bottini 10/19/2018 380.8 $573.29 $1.51
Bottini 10/26/2018 273.9 $375.49 $1.37
Bottini 11/1/2018 247.4 $342.90 $1.39
Bottini 11/8/2018 406.7 $537.21 $1.32
Bottini 11/15/2018 425 $547.02 $1.29
Bottini 11/23/2018 650 $858.72 $1.32
Bottini 12/5/2018 804.5 $1,014.15 $1.26
Bottini 12/13/2018 750.7 $972.08 $1.29
Bottini 12/20/2018 528.8 $664.60 $1.26
Bottini 12/27/2018 551.8 $677.83 $1.23
Bottini 1/3/2019 500.9 $625.27 $1.25
Bottini 1/10/2019 641.6 $803.35 $1.25
Bottini 1/17/2019 693 $886.83 $1.28
Bottini 1/26/2019 869.1 $1,118.71 $1.29
Bottini 2/5/2019 908.7 $1,173.31 $1.29
Bottini 2/14/2019 792.4 $990.02 $1.25
Bottini 2/23/2019 812.5 $1,061.78 $1.31
Table D-1
Ulster WWTP Energy Analysis
Energy Usage, Costs, Packback Calculations of ECM Alternatives
Estimated
BudgetDemand
Operational
pattern
Operational
pattern
Total Annual
UsagePayback
Annual
Energy Costs
Percent of
Savings to
Total Fuel
Consumed
($) (HP) (hrs/day) (hrs/yr) (kWh)(kWh/
year)(%) ($) (yrs) (kWh/year) (%)
Existing N/A Details in Table D-2 161,000 N/A N/A N/A N/A 16,100$ N/A
Flygt 191,400$ Details in Table D-3 76,400 84,600 53% 8,460$ 23 $7,640 53%
Aeroductor (Aerated) 373,000$ 3 24 8,760 19,605 N/A N/A N/A N/A $1,960 N/A
PISTA grit (vortex) 379,000$ 1 24 8,760 6,535 13,070 67% 1,307$ 290 $653 67%
SpiraGrit (vortex) 267,000$ 1 24 8,760 6,535 13,070 67% 1,307$ 204 $653 67%
Existing N/A Details in Table D-4 48,500 N/A N/A N/A N/A $4,850 N/A
Suez 365,600$ Details in Table D-4 29,200 19,300 40% 1,930$ 189 $2,920 40%
Trojan 803,600$ Details in Table D-4 35,000 13,500 28% 1,350$ 595 $3,500 28%
Wedeco - TAK 247,100$ Details in Table D-4 14,100 34,400 71% 3,440$ 72 $1,410 71%
Wedeco - LBX 364,000$ Details in Table D-4 17,600 30,900 64% 3,090$ 118 $1,760 64%
Annual Savings
Pu
mp
ing
Gri
t R
emo
val
UV
Dis
infe
ctio
n
Process Equipment Type
Table D-1
Ulster WWTP Energy Analysis
Energy Usage, Costs, Packback Calculations of ECM Alternatives
Estimated
BudgetDemand
Operational
pattern
Operational
pattern
Total Annual
UsagePayback
Annual
Energy Costs
Percent of
Savings to
Total Fuel
Consumed
($) (HP) (hrs/day) (hrs/yr) (kWh)(kWh/
year)(%) ($) (yrs) (kWh/year) (%)
Annual Savings
Process Equipment Type
Existing - Pumped N/A 10 24 8,760 65,350 N/A N/A N/A N/A $6,535 N/A
Rotamix - Pumped 49,050$ 3.8 24 8,760 24,833 40,517 62% 4,052$ 12 $2,483 62%
OTI - Draft Tube 135,000$ 5 24 8,760 32,675 32,675 50% 3,267$ 41 $3,267 50%
Ovivo - Linear Motion 282,000$ 7.5 24 8,760 49,012 16,337 25% 1,634$ 173 $4,901 25%
Screen & New Building
(Option #1)450,000$ 8 24 8,760 52,280 N/A N/A N/A N/A $5,228 N/A
Micro-strainer Screen
(Option #2)189,000$ 3 24 8,760 19,605 N/A N/A N/A N/A $1,960 N/A
Duperon Screen (Option
#3)260,000$ 2 24 8,760 13,070 N/A N/A N/A N/A $1,307 N/A
Dig
este
r M
ixin
gSc
reen
s
Table D-2
Ulster WWTP Energy Analysis
Existing Pumps Energy Use Calculations
Design Flow (gpm) 690
Motor Efficiency 82%
VFD Efficiency 98%
Diurnal Flow Diurnal FlowOperational
PatternTotal Flow
Operational
Pattern -
Pump 1
Operational
Pattern -
Pump 2
Flow -
Pump 1
Flow -
Pump 2
VFD Turn
Down Rate
Brake
Horsepower
Horsepower
from Pump
Curve
Power
Demand at
Full Speed
Power
Demand -
Pump 1
Power
Demand -
Pump 2
Energy -
Pump 1
Energy -
Pump 2
Total
Pumping
Energy(gpm) (gal/day) (hrs/yr) (gal/yr) (hrs) (hrs) (gpm) (gpm) (%) (BHP) (HP) (kW) (kW) (kW) (kWh) (kWh) (kWh)
0:00 561.7 33,703 365 12,301,715 1 0 562 0 98.0% 16.67 16.7 12.44 12.14 0.00 12.14 0.00 4,430
1:00 558.7 33,521 365 12,235,294 1 0 559 0 98.0% 16.65 16.7 12.42 12.12 0.00 12.12 0.00 4,425
2:00 452.4 27,144 365 9,907,677 1 0 452 0 93.5% 15.99 16.0 11.93 10.50 0.00 10.50 0.00 3,832
3:00 443.2 26,590 365 9,705,529 1 0 443 0 93.0% 15.93 15.9 11.88 10.34 0.00 10.34 0.00 3,773
4:00 455.4 27,326 365 9,974,100 1 0 455 0 93.5% 16.02 16.0 11.95 10.52 0.00 10.52 0.00 3,839
5:00 454.8 27,287 365 9,959,658 1 0 455 0 93.5% 16.01 16.0 11.94 10.51 0.00 10.51 0.00 3,837
6:00 467.8 28,070 365 10,245,558 1 0 468 0 94.0% 16.10 16.1 12.01 10.70 0.00 10.70 0.00 3,904
7:00 477.1 28,624 365 10,447,709 1 0 477 0 94.5% 16.15 16.2 12.05 10.86 0.00 10.86 0.00 3,962
8:00 635.2 38,110 365 13,910,253 1 0 635 0 99.0% 17.17 17.2 12.81 12.78 0.00 12.78 0.00 4,666
9:00 742.8 44,566 365 16,266,745 1 1 371 371 91.0% 18.35 18.4 13.69 11.35 11.35 11.35 11.35 8,286
10:00 873.6 52,415 365 19,131,500 1 1 437 437 92.5% 19.14 19.1 14.28 12.27 12.27 12.27 12.27 8,960
11:00 860.0 51,600 365 18,834,050 1 1 430 430 92.5% 19.06 19.1 14.22 12.22 12.22 12.22 12.22 8,922
12:00 950.5 57,028 365 20,815,122 1 1 475 475 95.5% 19.44 19.4 14.50 13.37 13.37 13.37 13.37 9,762
13:00 872.7 52,360 365 19,111,283 1 1 436 436 94.5% 19.02 19.0 14.19 12.78 12.78 12.78 12.78 9,332
14:00 924.6 55,477 365 20,249,099 1 1 462 462 95.5% 19.28 19.3 14.38 13.26 13.26 13.26 13.26 9,682
15:00 851.2 51,070 365 18,640,566 1 1 426 426 93.5% 18.94 18.9 14.13 12.44 12.44 12.44 12.44 9,078
16:00 781.4 46,885 365 17,112,890 1 1 391 391 91.5% 18.59 18.6 13.87 11.64 11.64 11.64 11.64 8,497
17:00 760.8 45,650 365 16,662,381 1 1 380 380 91.0% 18.48 18.5 13.79 11.43 11.43 11.43 11.43 8,345
18:00 787.9 47,272 365 17,254,391 1 1 394 394 92.5% 18.58 18.6 13.86 11.91 11.91 11.91 11.91 8,697
19:00 823.3 49,401 365 18,031,227 1 1 412 412 93.5% 18.76 18.8 13.99 12.32 12.32 12.32 12.32 8,992
20:00 764.1 45,848 365 16,734,580 1 1 382 382 91.0% 18.50 18.5 13.80 11.44 11.44 11.44 11.44 8,354
21:00 665.9 39,954 365 14,583,122 1 0 666 0 99.0% 17.39 17.4 12.97 12.95 0.00 12.95 0.00 4,726
22:00 690.0 41,402 365 15,111,601 1 1 345 345 90.0% 18.03 18.0 13.45 10.89 10.89 10.89 10.89 7,94623:00 644.9 38,696 365 14,123,952 1 0 645 0 99.0% 17.24 17.2 12.86 12.84 0.00 12.84 0.00 4,685
TOTAL 160,934
Diurnal Flow Bin Model
Time
Pump Manufacturer Data
Table D-3
Ulster WWTP Energy Analysis
Proposed Pumps Energy Use Calculations
Design Flow (gpm) 1130
Motor Efficiency 82%
VFD Efficiency 98%
Diurnal Flow Diurnal FlowOperational
PatternTotal Flow
Operational
Pattern -
Pump 1
Operational
Pattern -
Pump 2
Flow -
Pump 1
Flow -
Pump 2
VFD Turn
Down Rate
Brake
Horsepower
Horsepower
from Pump
Curve
Power
Demand at
Full Speed
Power
Demand -
Pump 1
Power
Demand -
Pump 2
Energy -
Pump 1
Energy -
Pump 2
Total
Pumping
Energy(gpm) (gal/day) (hrs/yr) (gal/yr) (hrs) (hrs) (gpm) (gpm) (%) (BHP) (HP) (kW) (kW) (kW) (kWh) (kWh) (kWh)
0:00 561.7 33,703 365 12,301,715 1 0 562 0 72.0% 16.81 20.5 15.29 7.58 0.00 7.58 0.00 2,765
1:00 558.7 33,521 365 12,235,294 1 0 559 0 72.0% 16.80 20.5 15.28 7.57 0.00 7.57 0.00 2,763
2:00 452.4 27,144 365 9,907,677 1 0 452 0 70.0% 16.43 20.0 14.95 6.96 0.00 6.96 0.00 2,540
3:00 443.2 26,590 365 9,705,529 1 0 443 0 69.5% 16.41 20.0 14.93 6.84 0.00 6.84 0.00 2,497
4:00 455.4 27,326 365 9,974,100 1 0 455 0 70.0% 16.44 20.0 14.96 6.96 0.00 6.96 0.00 2,542
5:00 454.8 27,287 365 9,959,658 1 0 455 0 70.0% 16.44 20.0 14.96 6.96 0.00 6.96 0.00 2,542
6:00 467.8 28,070 365 10,245,558 1 0 468 0 70.5% 16.48 20.1 14.99 7.09 0.00 7.09 0.00 2,588
7:00 477.1 28,624 365 10,447,709 1 0 477 0 71.0% 16.50 20.1 15.01 7.21 0.00 7.21 0.00 2,632
8:00 635.2 38,110 365 13,910,253 1 0 635 0 73.5% 17.11 20.9 15.57 8.07 0.00 8.07 0.00 2,945
9:00 742.8 44,566 365 16,266,745 1 0 743 0 76.5% 17.58 21.4 15.99 9.05 0.00 9.05 0.00 3,304
10:00 873.6 52,415 365 19,131,500 1 0 874 0 80.0% 18.21 22.2 16.57 10.35 0.00 10.35 0.00 3,777
11:00 860.0 51,600 365 18,834,050 1 0 860 0 79.5% 18.15 22.1 16.51 10.17 0.00 10.17 0.00 3,713
12:00 950.5 57,028 365 20,815,122 1 0 950 0 83.0% 18.52 22.6 16.85 11.41 0.00 11.41 0.00 4,165
13:00 872.7 52,360 365 19,111,283 1 0 873 0 80.0% 18.20 22.2 16.56 10.34 0.00 10.34 0.00 3,775
14:00 924.6 55,477 365 20,249,099 1 0 925 0 81.5% 18.46 22.5 16.79 10.93 0.00 10.93 0.00 3,988
15:00 851.2 51,070 365 18,640,566 1 0 851 0 79.0% 18.12 22.1 16.48 10.01 0.00 10.01 0.00 3,655
16:00 781.4 46,885 365 17,112,890 1 0 781 0 77.5% 17.76 21.7 16.16 9.41 0.00 9.41 0.00 3,435
17:00 760.8 45,650 365 16,662,381 1 0 761 0 77.0% 17.66 21.5 16.07 9.23 0.00 9.23 0.00 3,367
18:00 787.9 47,272 365 17,254,391 1 0 788 0 77.5% 17.80 21.7 16.19 9.43 0.00 9.43 0.00 3,443
19:00 823.3 49,401 365 18,031,227 1 0 823 0 78.0% 18.00 22.0 16.38 9.67 0.00 9.67 0.00 3,531
20:00 764.1 45,848 365 16,734,580 1 0 764 0 77.0% 17.68 21.6 16.08 9.24 0.00 9.24 0.00 3,371
21:00 665.9 39,954 365 14,583,122 1 0 666 0 74.0% 17.26 21.0 15.70 8.26 0.00 8.26 0.00 3,015
22:00 690.0 41,402 365 15,111,601 1 0 690 0 74.5% 17.37 21.2 15.80 8.44 0.00 8.44 0.00 3,08023:00 644.9 38,696 365 14,123,952 1 0 645 0 73.5% 17.17 20.9 15.62 8.10 0.00 8.10 0.00 2,955
TOTAL 76,387
Pump Manufacturer Data
Diurnal Flow Bin Model
Time
Table D-4
Ulster WWTP Energy Analysis
UV Disfinfection Alternatives Energy Usage
Diurnal Flow Diurnal FlowOperational
PatternTotal Flow UV Power
UV Energy
UseUV Power
UV Energy
UseUV Power
UV Energy
UseUV Power
UV Energy
Use
(gpm) (gal/day) (hrs/yr) (gal/yr) (kW) (kWh) (kW) (kWh) (kW) (kWh) (kW) (kWh)
0:00 561.7 33,703 443 14,936,466 6.3 1157 6.4 1179 2.6 470 3.3 599
1:00 558.7 33,521 443 14,855,820 6.3 1156 6.4 1173 2.5 467 3.2 596
2:00 452.4 27,144 443 12,029,679 6.0 1107 5.1 938 2.0 368 2.6 483
3:00 443.2 26,590 443 11,784,235 6.0 1103 5.0 918 2.0 359 2.6 473
4:00 455.4 27,326 443 12,110,328 6.0 1108 5.1 945 2.0 370 2.6 486
5:00 454.8 27,287 443 12,092,794 6.0 1108 5.1 943 2.0 370 2.6 485
6:00 467.8 28,070 443 12,439,927 6.1 1114 5.3 972 2.1 382 2.7 499
7:00 477.1 28,624 443 12,685,374 6.1 1118 5.4 992 2.1 391 2.8 509
8:00 635.2 38,110 443 16,889,517 6.5 1191 7.3 1342 2.9 539 3.7 678
9:00 742.8 44,566 443 19,750,717 6.7 1241 8.6 1579 3.5 640 4.3 793
10:00 873.6 52,415 443 23,229,038 7.1 1301 10.2 1868 4.1 763 5.1 932
11:00 860.0 51,600 443 22,867,882 7.0 1294 10.0 1838 4.1 750 5.0 918
12:00 950.5 57,028 443 25,273,255 7.3 1336 11.1 2038 4.5 835 5.5 1014
13:00 872.7 52,360 443 23,204,491 7.1 1300 10.1 1866 4.1 762 5.1 931
14:00 924.6 55,477 443 24,586,003 7.2 1324 10.8 1981 4.4 811 5.4 987
15:00 851.2 51,070 443 22,632,957 7.0 1290 9.9 1818 4.0 742 4.9 908
16:00 781.4 46,885 443 20,778,087 6.8 1258 9.0 1664 3.7 676 4.5 834
17:00 760.8 45,650 443 20,231,090 6.8 1249 8.8 1619 3.6 657 4.4 812
18:00 787.9 47,272 443 20,949,894 6.9 1261 9.1 1679 3.7 682 4.6 841
19:00 823.3 49,401 443 21,893,112 6.9 1278 9.5 1757 3.9 716 4.8 879
20:00 764.1 45,848 443 20,318,752 6.8 1250 8.8 1626 3.6 660 4.4 815
21:00 665.9 39,954 443 17,706,500 6.5 1205 7.7 1409 3.1 568 3.9 711
22:00 690.0 41,402 443 18,348,167 6.6 1216 7.9 1463 3.2 591 4.0 736
23:00 644.9 38,696 443 17,148,986 6.5 1196 7.4 1363 3.0 548 3.7 688
990,000 10,636 438,743,071 29,162 34,971 14,118 17,609
power (kW) flow (gpm) power (kW) flow (gpm) power (kW) flow (gpm) power (kW) flow (gpm)
13.2 3333 0 0 0 0 0 0
6.6 688 15 1319 3.24 694 10 1736
40 3333 8 1736 18.4 3194
16.49 3194
m 0.0025 m 0.012 m 0.0051 m 0.0058
b 4.885 b -0.3309 b -0.3092 b 0
R21 R2
0.9994 R20.996 R2
1
Trojan Wedeco-TAK Wedeco - LBX
y=mx+b y=mx+b y=mx+b
Diurnal Flow Bin Model
TOTAL
SUEZ
y=mx+b
UV
Un
it P
ow
er-
Flo
w
Re
lati
on
ship
Time
Table D-5
Ulster WWTP Energy Analysis
Dual Fuel Boiler Energy Savings Calculation
Assumed Gas HV
(Btu/ft3)
Avg Biogas
per Day (ft3)Avg Btu/day Avg Btuh
Avg Summer;
June-Sept
(Btuh)
Avg Winter;
Oct-May (Btuh)
500 6,563.62 3,281,808 136,742 137,045 185,576
Avg Summer Month 831.25 Gal/Month
Total Summer 3,325 Gal
Total Summer 274.7 Mscf
Total Summer 284.6 MMBtu
Total Savings 4,023$
SPP (years)* 36
*Based on $145,000 ECM cost
Digester Heat Requirement
Boiler Can Support Summer Load (June - Sept)
Total Wasted Biogas from Propane Utility Estimate
Table D-6
Ulster WWTP Energy Analysis
Digester Heat Requirements
Value Unit
Digester Flow Capacity 7,500 gpdSludge Density 8.34 lb/gal
Diameter 25.0 ft
Side Depth (in air) 13.3 ftSide Depth (in earth) 7.0 ftCenter Depth 20.6 ft
Wall Area (in Earth) 550 ft2Wall Area (in air) 1,045 ft2
Floor Area 491 ft2Roof Area 491 ft2
Dry earth embanked 0.12 BTU/ft2-F-h
Floor of digester in groundwater 0.15 BTU/ft2-F-hWall exposed to air with air plus brick 0.42 BTU/ft2-F-hFloating cover with 1-1/2" insulation 0.16 BTU/ft2-F-h
Parameter Value Unit Parameter Value Unit
Air 0 deg F Air 66.95 deg F
Earth next to tank 20 deg F Earth next to tank 60 deg FInfluent Sludge 50 deg F Influent Sludge 50 deg FEarth below tank 35 deg F Earth below tank 55 deg FSludge in digester 98 deg F Sludge in digester 95 deg F
Wall (in Earth) 5,146 Btu/h Wall (in Earth) 2,309 Btu/h
Wall (in air) 42,995 Btu/h Wall (in air) 12,306 Btu/hFloor 4,639 Btu/h Floor 2,945 Btu/hRoof 7,697 Btu/h Roof 2,203 Btu/h
Total Heat Loss 60,476 Btu/h Total Heat Loss 19,764 Btu/hSludge Heat Requirement* 125,100 Btu/h Sludge Heat Requirement* 117,281 Btu/hTotal Heat Requirement 185,576 Btu/h Total Heat Requirement 137,045 Btu/h
*Heat Equation: q = U*A*(T2-T1)
Winter Heat Losses* Summer Heat Losses*
Summer Heating RequirementsWinter Heating Requirements
Primary Digester Tank Dimensions
Parameter
Heat Transfer Coefficients
Winter Temperatures Summer Temperatures
F:\PROJECT\2255065\D\STUDY.RPT\Digester heat reqmt.xls