rexresearch.com
Nagamany NIRMALAKAHANDAN,
et al
Low-Energy Desalination
http://www.lcsun-news.com/news/ci_5998479
Los Cruces Sun-News
05/27/2007
Eye on Research:
Researchers develop low-cost, low-energy desalination
process
by Karl Hill
A low-cost water desalination system developed by New Mexico State
University engineers can convert saltwater to pure drinking water
on a round-the-clock basis and its energy needs are so low it
can be powered by the waste heat of an air conditioning system.
A prototype built on the NMSU campus in Las Cruces can produce
enough pure water continuously to supply a four-person household,
said Nirmala Khandan, an environmental engineering professor in
NMSU's Department of Civil Engineering.
New Mexico and other parts of the world have extensive brackish
groundwater resources that could be tapped and purified to augment
limited freshwater supplies, but traditional desalination
processes such as reverse osmosis and electrodialysis consume
significant amounts of energy.
This research project, funded by the NMSU-based New Mexico Water
Resources Research Institute, explores the feasibility of using
low-grade heat — such as solar energy or waste heat from a process
such as refrigeration or air conditioning — to run a desalination
process.
Khandan said the project builds on a process, first developed by
researchers in Florida, that makes distillation of saline water
possible at relatively low temperatures — 113 to 122 degrees
Fahrenheit rather than the 140 to 212 F required by most
distillation processes.
The system utilizes the natural effects of gravity and atmospheric
pressure to create a vacuum in which water can evaporate and
condense at near-ambient temperatures.
Two 30-foot vertical tubes — one rising from a tank of saline
water and the other from a tank of pure water — are connected by a
horizontal tube. The barometric pressure of the tall water columns
creates a vacuum in the headspace.
At normal temperatures, Khandan said, evaporation from the
pure-water side will travel to the saline side and condense as the
system seeks equilibrium. "That's nature," he said. "We want it to
go the other way."
Raising the temperature of the water in the headspace over the
saline column slightly more than that of the freshwater column
causes the flow to go in the other direction, so that pure,
distilled water collects on one side and the brine concentrate is
left behind in a separate container. A temperature increase of
only 10 to 15 degrees is needed, Khandan said.
"That's the trick of this vacuum," he said. "We don't have to boil
the water like normal distillation, so you can use low-grade heat
like solar energy or waste heat from a diesel engine or some other
source of waste heat."
Potentially a desalination system using this method could be
coupled to a home's refrigerated air conditioning system, Khandan
said.
"When you air condition a house, you are pumping the heat outside
the house, and the heat is wasted into the atmosphere," he said.
"We want to capture that heat and use it to power this
desalination system."
The 30-foot-tall NMSU prototype is powered by a solar panel.
Khandan and his research assistant, civil engineering doctoral
student Veera Gnaneswar Gude, have modified the process originally
developed by Florida researchers to incorporate a thermal energy
storage device that allows the system to operate around-the-clock,
using stored energy at night. The Institute of Energy and
Environment housed in the NMSU College of Engineering helped them
instrument the system.
Their research on the system's capabilities has been presented at
national and international conferences and their research
continues.
As with any desalination process, the system leaves behind a brine
concentrate that must be disposed of, and some potential users may
be put off by the unit's height, "but this technology could go to
commercial scale pretty quickly," Khandan said. "The overall cost
of desalination by this process can be very competitive."
The project is one of many research initiatives at NMSU aimed at
addressing the critical needs of New Mexico and the nation.
"Eye on Research" is provided by New Mexico State University. This
week's feature was written by Karl Hill of University
Communications.
Desalination Using Low-Grade Thermal
Energy
US2012085108
This invention describes a low temperature, self-sustainable
desalination process operated under natural vacuum conditions
created and maintained by barometric pressure head.
CROSS-REFERENCE TO RELATED APPLICATIONS
This application is a continuation application of U.S. patent
application Ser. No. 11/955,074 (now U.S. Pat. No. 8,080,138),
entitled “Desalination Using Low-Grade Thermal Energy”, to
Nagamany Nirmalakhandan et al, filed on Dec. 12, 2007, which
claims priority to and the benefit of U.S. Provisional Application
Ser. No. 60/950,076, entitled “Desalination using Low-Grade
Thermal Energy”, to Nagamany Nirmalakhandan et al., filed on Jul.
16, 2007, and the specifications and claims thereof are
incorporated herein by reference.
BACKGROUND OF THE INVENTION
1. Field of the Invention (Technical Field)
The present invention relates to an apparatus and method for
desalination.
2. Description of Related Art
Interest in the use of low grade heat sources and recovery of
waste heat is growing due to increasing energy costs and declining
energy sources. Examples of low grade energy sources include solar
energy and heat rejected by fossil fuel-based power plants, air
conditioning/refrigeration systems, and industrial processes. As a
consequence of the laws of thermodynamics, thermal systems have to
reject large quantities of low grade heat energy to the
environment. For example, heat rejection rate of modern combined
cycle power plants is almost equal to their output. Approaches to
utilize waste heat to produce value added products or services can
conserve limited energy sources, reduce adverse environmental
impacts, and minimize overall costs.
The present invention utilizes low grade heat to operate a new
desalination process. Traditional desalination processes such as
reverse osmosis, electrodialysis, mechanical vapor compression,
and multi-effect flash distillation require electrical energy
derived from nonrenewable sources, the cost of which has increased
by 10 times over the past 20 years. Recently, a new desalination
process has been proposed that has the potential to run solely on
low grade heat sources at around 50° C. The present invention is a
modification to that process, whereby it can run around the clock,
using a thermal energy storage (TES) system that enables waste
heat sources and renewable energy sources to be used to drive the
process with minimum reliance on grid power. TES manages variable
energy demand over time, is a continuous heat source, and has a
lower specific energy for desalination. The present invention,
unlike the process mentioned above, enables solar collectors and
photovoltaic panels to provide the energy to drive the process.
The TES system can be maintained at the desired temperature using
low grade waste heat from any available source.
BRIEF SUMMARY OF THE INVENTION
A preferred embodiment of the present invention is described
below. The embodiment is a desalination system comprising a
desalination unit, a low grade heat source for powering the
desalination unit and a thermal energy storage system for storing
the low grade heat source and maintaining a specified temperature
range. The system is able to run continuously within a specified
temperature range between approximately 40-50° C. The low-grade
heat source is at least partially supplied by an absorption
refrigeration unit which maintains the thermal energy storage
refrigeration unit at a specified temperature range. The
absorption refrigeration unit operates at a pressure range of
between approximately 1.4 to 15.75 kPa.
The desalination unit comprises an evaporation chamber, a
condenser, a heat exchanger and one or more columns. The columns
comprise a saline water column, a brine withdrawal column and a
desalinated water column. The heat input to the evaporation
chamber is provided by the thermal energy storage system.
The desalination system does not have a pump except for an initial
starting pump. In addition, the system does not have any other
moving parts.
Another embodiment of the present invention is a method of
desalinating comprising the steps of operating a desalination
unit, powering the desalination unit using a low grade heat
source, storing the low grade heat source in a thermal energy
storage unit and maintaining a specified temperature range of the
low grade heat source. The desalination unit can run continuously
and comprises desalinating saline water at a temperature range of
approximately 40-50° C. The method can also comprise supplying the
low grade heat source at least partially by an absorption
refrigeration unit. The absorption refrigeration unit can also
provide a cooling load. The thermal energy storage unit is
maintained at a specified temperature range within the absorption
refrigeration unit. Finally, the absorption refrigeration unit
operates at a pressure range of between approximately 1.4 to 15.75
kPa.
Further scope of applicability of the present invention will be
set forth in part in the detailed description to follow, taken in
conjunction with the accompanying drawings, and in part will
become apparent to those skilled in the art upon examination of
the following, or may be learned by practice of the invention. The
objects and advantages of the invention may be realized and
attained by means of the instrumentalities and combinations
particularly pointed out in the appended claims.
BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWINGS
The accompanying drawings, which are incorporated into and
form a part of the specification, illustrate one or more
embodiments of the present invention and, together with the
description, serve to explain the principles of the invention.
The drawings are only for the purpose of illustrating one or
more preferred embodiments of the invention and are not to be
construed as limiting the invention. In the drawings:
FIG. 1 is a schematic of a preferred embodiment of the
desalination system of the present invention;
FIG. 2 is a table of model parameters used in an example
simulation of mass and energy balances of a preferred
embodiment;
FIG. 3 is a chart showing heat transfers and efficiency for
the desalination system of the present invention over 24 hours;
FIG. 4 is a chart showing variations of desalinated water
temperature and saline water temperature with respect to ambient
temperature over 24 hours for the desalination system of the
present invention;
FIG. 5 is a comparison of parameters in a typical
absorption refrigeration system and in the preferred embodiment;
FIG. 6 is a chart showing ambient temperature versus
thermal energy storage temperature over 24 hours for a typical
thermal energy storage and in the preferred embodiment;
FIG. 7 is a comparison of the preferred embodiment with a
multi-stage flash distillation process;
FIG. 8 is a chart showing solar fraction and optimum solar
panel area for a typical absorption refrigeration system and in
the preferred embodiment;
FIG. 9 is a chart showing desalination rates for different
cooling loads and solar panel areas for a typical absorption
refrigeration system and in the preferred embodiment;
FIG. 10 is a chart showing the effect of withdrawal rate on
desalination efficiency and saline water temperature for the
desalination system of the present invention;
FIG. 11 is a chart showing the effect of withdrawal rate on
concentration and desalination efficiency for the desalination
system of the present invention;
FIG. 12A is a chart showing solar panel area versus
desalination rate at different withdrawals for the desalination
system of the present invention; and
FIG. 12B is a chart showing cooling load versus
desalination rate at different withdrawals for the desalination
system of the present invention.
DETAILED DESCRIPTION OF THE INVENTION
This invention concerns the feasibility of a new desalination
process utilizing low grade thermal energy. The process operates
at near-vacuum pressures created by passive means. This allows for
the process to operate at low temperatures with higher efficiency.
The process utilizes low grade thermal energy rejected by an
absorption refrigeration system (ARS). The condenser of the ARS
rejects low grade thermal energy at approximately 55° C. which is
recovered and stored in a low temperature thermal energy storage
(TES) tank. A thermal energy storage tank serves best to manage
energy demands of the desalination process by maintaining the
source temperature at approximately 50-70° C. as the energy demand
to the desalination system is dependent on the ambient
temperature.
Results of this feasibility study show that the thermal energy
rejected by an ARS of cooling capacity of approximately 3.25 kW
(0.975 tons of refrigeration) along with an additional energy
input of approximately 208 kJ/kg of desalinated water is adequate
to produce desalinated water at an average rate of approximately
4.5 kg/hr. Energy demand for this process is competitive with
well-established Multi Stage Flash distillation processes. An
integrated process model and performance curves of the proposed
approach are presented below. The effect of process parameters,
such as withdrawal rate, are also presented below.
The preferred embodiment of the desalination system of the present
invention is shown schematically in FIG. 1. The invention
comprises desalination unit 10, absorption refrigeration system
12, and thermal energy storage 14. Desalination unit 10 comprises
evaporation chamber 16, condenser 18, one or more heat exchangers
20, 22, and columns 24, 26 and 28 (e.g. between approximately
10-11 m tall, equivalent to the local barometric head). These
three columns are saline water column 24, brine withdrawal column
26, and desalinated water column 28, each with its own
constant-level holding tank, saline water tank 30, brine tank 32,
and desalinated water tank 34, respectively. The heat input to
evaporation chamber 16 is provided by thermal energy storage 14,
which is maintained at a particular temperature or range (e.g.
between approximately 50-70° C.) by absorption refrigeration
system 12, preferably powered by solar energy.
Holding tanks, saline water tank 30, brine tank 32, and
desalinated water tank 34 are installed at ground level while,
evaporation chamber 16 is installed atop three columns 24, 26, 28
at a barometric height (e.g. between approximately 10-11 m,
equivalent to the local barometric head) above the free surface in
holding tanks 30, 32, 34 to create a natural vacuum in the
headspaces of three columns 24, 26, 28. This configuration enables
the desalination process to proceed preferably without any
mechanical pumping. There are also preferably no other moving
parts needed, except for the pump used to start the system. The
temperature of the head space of the feed water column is
maintained slightly higher, approximately 45-65° C. than that of
the desalinated water column, approximately 15-35° C. Since the
head spaces are at near-vacuum level pressures, a temperature
differential (e.g. between approximately 10-25° C.) is adequate to
evaporate water from the feed water side and condense in the
desalinated water side. In this manner, saline water can be
desalinated at between approximately 40-50° C., which is in
contrast to the 60-100° C. range in traditional solar stills and
other distillation processes. Brine is withdrawn continuously from
evaporation chamber 16 flowing through tube-in-tube heat exchanger
20 preheating the saline water feed entering evaporation chamber
16.
Absorption refrigeration system 12 operates with a refrigerant
(e.g. LiBr—H2O) in a pressure range of preferably 1 to 16 kPa.
Heat energy required by generator 38 of absorption refrigeration
system 12 is preferably supplied by solar collector 36 (e.g. flat
panel) during sunlight hours and by auxiliary electric or gas
heater 40 during non-sunlight hours. Solar collector 36 maintains
generator 38 at a specified temperature or range (e.g. between
approximately 80-110° C.). Heat rejected by condenser 42 of
absorption refrigeration system 12 maintains thermal energy
storage 14 at a specified temperature or range (e.g. between
approximately 50-70° C.) to serve as the low grade heat source for
the desalination process. Evaporator 44 of absorption
refrigeration system 12 feeds the cooling load. Thus, the
preferred embodiment of the present invention performs two
functions of continuous desalination and cooling with minimal
amounts of external nonrenewable energy input.
Mass and Energy Balances
The preferred embodiment was developed based on mass and energy
balances. Thermodynamic analysis of the preferred embodiment was
performed through computer simulations using Extend, manufactured
by ImagineThat Inc., San Jose, Calif. and EES, manufactured by
F-Chart Software, Madison, Wis. simulation software.
Desalination System
An evaporator area of 5 m<2 >and a height of 0.25 m were
considered. In all calculations, the reference temperature was
assumed to be 25° C. All heat exchangers were assumed to have 80%
efficiency. The following mass and heat balance equations apply to
the different components:
Mass balance on water in the evaporation chamber:
[mathematical formula]
Mass balance on solute in the evaporation chamber:
[mathematical formula]
Heat balance for the evaporation chamber:
[mathematical formula]
Evaporation rate is expressed by (Bemporad, 1995):
[mathematical formula]
where, p(T)=e<(63.042-7139.6/(T+273)-6.2558
ln(T+273))>*10<2 >Pa
In the above equations, subscripts e, i, and w, represent
evaporator outlet, inlet, and withdrawal conditions, respectively;
f and s represent freshwater and saline water respectively. The
variables are defined as follows:
V=volume of water in the evaporation chamber [m<3>]
{dot over (V)}=volumetric flow rate [m<3>/hr]
?=density [kg/m<3>]
cp=specific heat capacity of saline water [kJ/kg-° C.]
C=solute concentration[%]
Ts=saline water temperature in the evaporator chamber [° C.]
T=temperature [° C.]
qe=evaporation rate [m<3>/s]
A=area of the evaporation chamber [m<2>]
am=an experimental coefficient [10<-7>-10<-6
>kg/m<2>-Pa-s-K<0.5>] (11)
f(C)=correlation factor for the presence of solute
concentration[%]
QIn=energy input from thermal energy storage [kJ/hr]
QL=energy losses from evaporation chamber [kJ/hr]
QE=energy used for evaporation [kJ/hr]
Energy used for evaporation is given by:
QE=3,600?fhL(TS)qe (5)
where, hL(T) is the latent heat of evaporation [kJ/kg] given by:
hL(T)=[(3146-2.36(T+273° K)]
The desalination efficiency, ?d, is defined as:
[mathematical formula]
where,
me=mass of desalinated water produced over a period of time [kg]
hL=latent heat of evaporation at saline water temperature [kJ/kg]
SQIn?t=energy provided by the thermal energy storage over a period
of time [kJ]
Expressions for density, enthalpy and pressure variations are
presented below.
Density variation with temperature and concentration is given as:
?(T,C)=?0(1-ßT?T0+ßC?C0)
where, ?T0 and ?C0 are variations from reference property values,
of density.
ßT=5.10-4 C-1, thermal expansion coefficient
ßC=8.10-3%-1, solutal expansion coefficient
Effect of concentration on specific heat is given as:
cP(C)=a2C+ß2
where,
a2=-30.10 J kg-1 0C-1
ß2=4178.4 J kg-1 0C-1
Evaporation energy is given as:
Qe=?fhfg(TS)qe[kJ/hr]
Latent heat of evaporation is given as:
hfg(T)=10<3>*[(3146-2.36(T+273° K)]J/kg
The average heat transfer from the tips of the fins is given by
(Rohsenow 1985):
Nus=cRas<b >
where Nu=Nusselt number, Ra=Rayleigh Number and b and c are
constants
b=0.29; c=0.44+0.12e; e=Dco/Dfin
This equation is valid for 2<Ras<104 and 1.36<1/e<3.73
Rayleigh number is given as (Incropera, 2002):
[mathematical formula][mathematical formula]
where
g=local acceleration due to gravity (m/sec<2>)
ß=temperature coefficient, 1/° K
a=thermal diffusivity, m<2>/s
?=kinematic viscosity, m<2>/s
Ta and Tco=temperatures of the ambient and condenser respectively,
° K
S=distance between the successive fins, m
Condenser Calculations: Average heat transfer through the cylinder
surfaces and fins is given by:
[mathematical formula][mathematical formula][mathematical
formula][mathematical formula][mathematical formula]
The rate of heat transferred from the condenser prime surface and
fins can be calculated as:
Qc=[hco,tipNAf,tip?f+hcoNAf,sides?f+hcoAb](Tco-Ta)
where
hco,tip, hco=heat transfer through the tips and base or sides
N=number of fins
Ab, Af,sides, and Af,tip=areas of base, fin sides and tip
respectively
?f=efficiency of fins
For turbulent free convection for Ra>109,
Nu=c(Ra)<0.333 >
where c=0.10
For fin efficiency (Donald Q. Kern, 1972):
f=(ro-ri)3/2(2h/kAp)1/2
?=(ri/ro)
where
ri and ro=inner and outer radius of fins respectively, m
h=heat transfer coefficient trough the fin, w/m<2>-° K
k=heat transfer coefficient trough the surface, w/m-° K
Ap=Area of the fins
?=(f, ?)
Absorption Refrigeration System
Absorption refrigeration system 12 is preferably driven by solar
energy during sunlight hours and by auxiliary electric or gas
heater 40 during non-sunlight hours, although any type of power
may be utilized. The efficiency of solar collectors is expressed
in terms of solar fraction, which is the contribution of solar
energy to the total load in terms of the fractional reduction in
the amount of extra energy that must be supplied. A storage tank
volume of approximately 0.125 m<3>/m<2 >was considered
and the optimum area of solar collectors required was found from a
solar fraction graph. The optimum number of collectors was the
lowest number of collectors for which a 100% solar fraction was
achieved at the hour maximum solar radiation. Additional energy
for heating and pumping was required for condenser 42 of
absorption refrigeration system 12 to dissipate heat at
approximately 55° C. The pumping requirements were calculated
using EES® software.
Heat balance across solar collection system:
[mathematical formula]
where,
ms=mass of water in storage tank [kg]
Cps=specific heat of water in storage tank [kJ/kg-° C.]
TS1=temperature of water in storage tank [° C.]
FR=heat removal factor [dimensionless]
Ap=area of solar panels [m<2>]
t=transmitivity of glass [dimensionless]
a=absorptivity of water [dimensionless]
IS=solar energy [kJ/hr-m<2>]
UL=heat loss coefficient [kJ/hr-m<2>-° C.]
Tgs=temperature of the water from the generator [° C.]
Ta=ambient temperature [° C.]
US=heat losses from the surface of storage tank
[kJ/hr-m<2>-° C.]
AS=surface area of storage tank [m<2>]
mR=flow rate of recycling water [kg/hr]
Cpr=specific heat of recycling water [kJ/kg-° C.]
Thermal Energy Storage:
Sensible heat thermal energy storage 14 stores heat rejected by
the absorption refrigeration system-condenser 42. The optimal
volume of thermal energy storage 14 to maintain evaporation
chamber 16 at the desired temperature differential was determined
by solving the heat balance for thermal energy storage 14 by trial
and error.
Heat balance for thermal energy storage 14:
[mathematical formula]
where,
QR=heat rejected by condenser in the absorption refrigeration
system [kJ/hr]
QL1=energy losses from the thermal energy storage surface [kJ/hr]
Cp=specific heat of the water in the TES [kJ/kg-° C.]
v=volume of the thermal energy storage [m<3>]
Results:
The model equations were solved using the fixed parameters listed
in FIG. 2 and for a particular site. Previous studies have shown
that the effect of water depth in evaporation chamber 16 did not
have any significant effect on the evaporation rate. This is in
contrast to the traditional solar stills, where the water volume
provided energy storage that is required for continued evaporation
during non-sunlight hours. Since the preferred embodiment does not
depend on solar energy for continuous operation, the effect of
water depth was not taken into account.
First, results of an example case where the model equations were
solved for the reference parameters listed in FIG. 2 are
presented. In this example case, the withdrawal rate was fixed at
approximately 2.5 kg/hr (˜50%). These results demonstrate the
effectiveness of the preferred embodiment. Then, the total energy
consumption of the preferred embodiment was analyzed and compared
to that of a multi-stage flash distillation process. Finally, the
effect of withdrawal rate on the design and performance of the
preferred embodiment is presented.
Heat Balance for Evaporation Chamber
The heat balance for evaporation chamber 16 is described by
Equation 3. FIG. 3 shows the variations in heat provided by
thermal energy storage 14, the heat consumed for evaporation, and
the heat lost over a 24-hr period for a summer day, when the
ambient temperature ranged from between approximately 25 to 37° C.
The desalination efficiency defined by Equation 6 is also
indicated in FIG. 3 by the bold line. As expected, the heat lost
by evaporation chamber 16 was higher during non-sunlight hours
than that during sunlight hours due to lower ambient temperatures
during non-sunlight hours. Under the example conditions, the
energy available for desalination was about 12,500 kJ/hr (=3.45
kW) which was the waste heat rejected by condenser 42 in
absorption refrigeration system 12. However, the net heat transfer
was dependent on the temperature gradient between the transfer
medium and the heat source. The actual mass of water that could be
evaporated in evaporation chamber 16 and hence, the desalination
efficiency, depended on the heat input from thermal energy storage
14, the ambient temperature at which the condensation took place,
and the brine withdrawal rate. Since the driving force for
evaporation is the temperature differential, between evaporation
chamber 16 and condenser 42, the heat input to evaporation chamber
16 during the day is lower than that input during the night.
During the night, both the ambient temperature and the freshwater
temperature are low, favoring a higher desalination rate, thus
resulting in higher heat input and vice versa.
The temperature variations in the saline water in evaporation
chamber 16 and the desalinated water with respect to ambient
temperature over a 24-hr period are shown in FIG. 4. The
temperature of saline water varied from between approximately 43.5
to 46° C. and the ambient temperature ranged from between
approximately 25 to 37° C. while the fresh water temperatures
ranged from between approximately 35 to 40° C. FIG. 4 shows that
thermal energy storage 14 was able to maintain the approximately
10° C. temperature differential between the saline water side and
the desalinated water side. It is noted that the ambient
temperature is an important variable because condensation occurs
at the ambient temperature, which indirectly determines the
desalination rate in this process.
Operating Conditions of Absorption Refrigeration System
Absorption refrigeration system 12 is designed for two functions:
for maintaining thermal energy storage 14 at the desired
temperature and for providing the cooling load. As such,
absorption refrigeration system 12 operates under slightly
different conditions compared to the traditional systems used for
cooling alone. Operating conditions for a typical absorption
refrigeration system used in cooling and the conditions for
absorption refrigeration system 12 are compared in FIG. 5, for the
same cooling load of approximately 3.25 kW. The notable difference
is the pressure ranges between approximately 1 and 6.3 kPa versus
about 1.4 to 15.75 kPa respectively.
Volume of Thermal Energy Storage
Winter conditions were assumed to determine the volume of thermal
energy storage 14 necessary to provide the heat energy to
evaporation chamber 16. Solving Equation 8 by trial and error so
that the temperatures at the beginning and the end of a 24-hr
period would be within approximately ±0.01° C., the volume of
thermal energy storage 14 was found to be approximately 10
m<3>. The heat demand by evaporation chamber 16 on thermal
energy storage 14 varied from between approximately 8,700 and
14,200 kJ/hr over a 24-hour period shown in FIG. 2; yet, as shown
in FIG. 6, thermal energy storage 14 volume of approximately 10
m<3 >was found to be adequate to maintain its temperature at
approximately 50° C. throughout the same period to provide the
energy needs of evaporation chamber 16.
Energy Requirements
An embodiment of the invention may require additional
non-renewable energy for the following: auxiliary heat energy for
generator 38 (=approximately 192 kJ/kg of desalinated water) plus
mechanical energy to circulate heat transfer medium between
thermal energy storage 14 and evaporation chamber 16
(=approximately 14 kJ/kg of desalinated water); to circulate the
heat transfer medium between thermal energy storage 14 and
condenser 18 (=approximately 2 kJ/kg of desalinated water); and to
pump the refrigerant in absorption refrigeration system 12
(=approximately 0.04 kJ/kg of desalinated water). Hence, the total
additional energy required to maintain thermal energy storage 14
at the desired conditions is approximately 208 kJ/kg of
desalinated water produced. In comparison, multi-stage flash
distillation process would require a heat energy of approximately
294 kJ/kg of desalinated water plus a mechanical energy of
approximately 44 kJ/kg of desalinated water, for a total of
approximately 338 kJ/kg of desalinated water. Thus, the present
invention requires about 60% of the energy required by the
multi-stage flash distillation process. A comparison between the
two processes is summarized in FIG. 7.
Solar Collector for Absorption Refrigeration System
Solar collector 36, augmented by auxiliary electric heater 40, is
sized to provide for thermal energy storage 14 and the cooling
load. The temperature of storage tank 46 of solar collector 36 is
set to a particular temperature or range (e.g. between
approximately 110-115° C.) in order to maintain generator 38
temperature at a particular temperature or range (e.g. between
approximately 100-110° C.). The energy to be provided by auxiliary
heater 40 is equal to the difference between the energy required
by generator 38 and that can be collected from solar isolation.
FIG. 8 illustrates this difference and the solar fraction, over a
24-hr period. The optimal area of the collectors can be found from
Equation 7. For the conditions described herein, solar collector
area of approximately 25 m<2 >can satisfy a cooling load of
approximately 3.25 kW, at an average desalination rate of
approximately 4.3 kg/hr. The relationships between desalination
rate, solar panel area, and cooling load are presented in FIG. 9.
Brine Withdrawal vs. System Performance
Brine withdrawal rate is the primary control variable in this
system, which has positive as well as negative impacts on the
performance of the system. At low withdrawal rates, salts build up
in evaporation chamber 16, and evaporation rates decrease as shown
by Equation 4. High salt levels also reduce the enthalpy of saline
water that can further reduce evaporation. For example, when
salinity increases by approximately 1%, evaporation is also
reduced by about the same percentage. Even though better salt
removal can be achieved with higher withdrawal rates, large
amounts of sensible heat are also removed from evaporation chamber
16, resulting in decline of evaporation chamber 16 temperature.
Simulation results presented in FIG. 10 show the decline in
evaporation chamber 16 temperature and in desalination efficiency
with increasing withdrawal rate. For example, the desalination
efficiency dropped from between approximately 90.5% and 80% when
the withdrawal rate increased from between approximately 2.5 kg/hr
and 25 kg/hr. FIG. 11 shows the salt buildup with time and the
resulting decline in desalination rate. Similar observations have
been reported previously.
Further simulations were conducted to evaluate the effect of
withdrawal rate on desalination rate, cooling load, solar
collector area, and auxiliary heat requirement. As shown in FIG.
12, cooling load and solar panel area are not sensitive to
withdrawal rate in the range of between approximately 50-200%. For
a given desalination rate, even though the cooling load at a
withdrawal rate of approximately 200% is higher than that at
approximately 100%, the auxiliary heat addition is also higher. In
addition, the solar collector area is also higher. As discussed
before, the desalination efficiency also decreases. Based on these
results, a withdrawal rate of approximately 100% is an acceptable
rate to minimize salt buildup and maintain system performance.
In summary, model simulations show that the preferred embodiment
can achieve a desalination efficiency of at least approximately
85% and higher (e.g. approximately 85-90%) at a brine withdrawal
rate of approximately 70-100% with an energy consumption of less
than approximately 250 kJ/kg (e.g. between approximately 150-300
kJ/kg) of freshwater from seawater. The energy requirements for
the preferred embodiment are less than that are required for a
multi-stage flash distillation process. Based on the results from
the example, an approximate 100% withdrawal rate could prevent
scale formation that could reduce the evaporation rate. A typical
unit with a thermal energy storage volume, the volume calculated
by solving a heat balance using trial and error (e.g. between
approximately 10-20 m<3>), can produce fresh water at
between approximately 4.5 kg/hr and provide a cooling load of
between approximately 3.25 kW with a solar panel area of between
approximately 25 m<2>. The preferred embodiment minimizes
non-renewable energy usage and may be improved further by
incorporating a double or triple-effect configuration.
Although the invention has been described in detail with
particular reference to these preferred embodiments, other
embodiments can achieve the same results. Variations and
modifications of the present invention will be obvious to those
skilled in the art and it is intended to cover in the appended
claims all such modifications and equivalents. An example of a
configuration that has been demonstrated by a prototype is
described in Example 1. The entire disclosures of all references,
applications, patents, and publications cited above are hereby
incorporated by reference.
Example 1
A prototype unit was constructed and experiments were conducted
using direct solar energy and photovoltaic energy as heat sources.
Desalination was performed on a continuous basis over 24 hours a
day for several months. This prototype comprised of columns that
were 10 m, equivalent to the local barometric head. The
temperature of the head space of the feed water column was
maintained at approximately 40-50° C., while the desalinated water
column was maintained at approximately 35-45° C. The pressure in
the evaporation chamber remained at approximately 0.085 atm. The
specific energy required by this prototype was approximately 3,370
kJ/kg of desalinated. This system was run entirely on solar energy
with direct solar heat during sunlight hours and with a 350-W DC
heater powered by batteries that were charged by the photovoltaic
panels during the day time. This example system was able to
recover potable quality water meeting United States Environmental
Protection Agency drinking water standards from the effluent of a
municipal wastewater treatment plant.