United States
             Environmental Protection
             Agency
Office of Research and
Development
Washington DC 20460
EPA/625/R-96/008
September 1996
             Technology Transfer
&EPA     Capsule Report

             Evaporation  Process

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Technology  Transfer	EPA/625/R-96/008
Capsule   Report


Evaporation  Process
 September 1996
   Center for Environmental Research Information
   National Risk Management Research Laboratory
      Office of Research and Development
      U.S. Environmental Protection Agency
            Cincinnati OH 45268
                                 Printed on Recycled Paper

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Contents
                                     Process Description 	3

                                     Applications	 3

                                     Equipment	 4

                                     Operation and Maintenance	6

                                     Failure Analysis	 6

                                     References	  10
Introduction
  A failure analysis has been  com-
pleted  for the evaporation process.
The focus was on process failures
that result in  releases of liquids and
vapors to the environment. The re-
port includes  the following:
  •   A description of evaporation
      and coverage of process  prin-
      ciples.
  •   Applications of evaporation for
      treatment of effluent waters
      from the metal finishing indus-

  •   Descriptions of equipment and
      operating and  maintenance
      procedures.
  •   Failure analysis that includes
      types of failures and causes.
  •   Key questions that can  be  used
      in  software development
  •   A bibliography on evaporation
      applications in the metal fin-
      ishing  industry.

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Evaporation  Process       Process  Description
                                       In the evaporation process, waste-
                                     waters from metal finishing processes
                                     are heated until a water vapor is
                                     formed. This vapor is continuously re-
                                     moved and condensed as an over-
                                     head product. In this manner, clean
                                     water is recovered and the solutes
                                     contained  in the original wastewater
                                     are concentrated. The solutes may
                                     be contaminants, or useful  chemicals
                                     or reagents, such as copper, nickel,
                                     or chromium compounds, which are
                                     recycled for further  use. The batch
                                     evaporation process, based  on the
                                     use of steam as the energy source, is
                                     illustrated in Figure 1.
                                       If the evaporation process is prop-
                                     erly designed and operated, the clean
                                     condensate generally contains no
                                     more than 10-20 ppm contamination
                                     from wastes containing up to several
                                     percent of dissolved solutes. By us-
                                     ing mechanical  vapor  recompression
                                     (MVR) or  multiple stages, evapora-
                                     tion can be made energy efficient;
                                     however, the initial capital investment
                                     tends to be higher to include these
                                     options.
  Evaporation is an established tech-
nology. There is little risk and it has a
low capital cost. Using the proper pro-
cess configuration, evaporation can
achieve a high degree of water re-
moval. However, water removal is
normally limited by the ability to pump
the  solution.  When  wastewaters con-
tain volatile organics with boiling points
that coincide with that for water, prod-
uct condensate  can  be  contaminated
with organics. Removing these  organ-
ics  requires further treatment, con-
sisting of a carbon bed or other
polishing process. Other obstacles
occur at evaporation  temperatures
with foaming, scaling, fouling, and cor-
rosion all possible. Finally, pretreat-
ment chemicals may be  needed to
reduce scaling and fouling.
Applications
   Due to its reliability and econom-
 ics, evaporation has proven to be one
 of the  better processes for treatment
 of wastewaters (dragout) from the
 metal finishing industry. Evaporators
 are inexpensive to purchase, install,
 and operate, making them a powerful
                                                Steam
                                                                                          Condenser
                                                                                     "^^ Clean
                                                                                           water
                                                                                         Condensate
                                                                  Concentrated
                                                                  solution
                                           DD-388
                                      Figure 1.    Jacketed batch  evaporator.

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tool for reduction in the cost of water
treatment. The greatest  problem is
the control of contaminants in the con-
centrated solution. However,  pro-
cesses are  available  to  remove
contaminants, allowing  evaporative
recovery to be used on many metal
finishing waters.
   Process solutions that have been
successfully treated using evapora-
tive techniques include  zinc, cadmium,
copper,  nickel, and  chromium  plating
baths, and phosphoric  acid from  alu-
minum bright wastewaters. Even
though these waters become contami-
nated by excessive drag-in, dropped
work, impure makeup water, or by
chemical reaction  resulting from  pro-
cess operation, these impurities can
be controlled, reduced  or  removed
without excessive equipment costs
(Spearot,  1987; Yates, 1986;  Brown,
1984).
   Applications for evaporators in  other
industries  include  concentration  of li-
quors in the  paper industry and re-
covery of potable water from salt water
and brines. Evaporation is also  used
to recover water from various types
of wastewaters including  cooling tower
blowdown, ion exchange regeneran!
wastes, boiler blowdown, and indus-
trial  rinsewaters.
     Water
     (drag out)
 Equipment
   Evaporation may be accomplished
 operating at a vacuum or at atmo-
 spheric pressure.  Atmospheric evapo-
 rators are  used when components in
 the wastewater are thermally stable.
 Vacuum conditions reduce boiling
 temperatures and  prevent  decompo-
 sitions. Decompositions  can readily
 occur in zinc and cadmium cyanide
 solutions.

 Evaporation  Using a
 Packed  Column
   Atmospheric evaporators  may con-
 sist of a packed tower with a heated
 feed mixture fed to the top of the
 tower and air (or hot air) fed to the
 bottom of the tower. In this process,
 as the hot air contacts the water,
 evaporation takes place, thereby con-
 centrating the wastewater (see  Fig-
 ure 2).   The  wastewater is
 concentrated and recycled to the  pro-
 cess. Because contaminants are con-
 centrated by this  process,  special
 attention may be required for their
 removal.
               Air/water
               (vented or
               condensed)
                                                Packed
                                                column
                      Heater


     DD-641

Figure 2.     Evaporation using a packed column.
               Concentrated
           stream
                recycled  for
               lurther use)
Packaged  Evaporators
  Packaged evaporators, which are
available from a number of suppliers,
are used in both atmospheric and
vacuum operations (Lavis, 1994).
Most purchases for packaged evapo-
rators are for film evaporators, with
forced-circulation  evaporators ranking
next. Film evaporators are normally
used to concentrate solutions  up  to
the  point where the  solubility limits  of
the solutes are reached and signifi-
cant amounts of suspended solids
develop. Forced  circulation  evapora-
tors are designed to  handle solutions
containing suspended solids (Worral,
1988).  A number of  good  references
are available on how to select and
design  evaporators (Lavis, 1994;
Worral, 1988; Mehra, 1986;  and APV
Crepaco, 3rd Ed.). Both  film and
forced circulation evaporators are de-
scribed below.

Film Evaporators
  In film evaporators, the process liq-
uid  is distributed as a film on the heat
transfer surface  (see Figure 3). The
process liquid occupies only a thin
film on the tube wall, resulting  in low
liquid holdup.  Film  evaporators are
limited to low viscosity fluids, because
at high viscosities the film is thick-
ened and  results in  low  heat-transfer
coefficient. The practical upper limit
of viscosity for film evaporators is 1 00-
500 centipoise (Dedert Corp, 1994).
  The amount of heat transferred from
the heating medium to the wastewa-
ter depends on the temperature dif-
ference between the process fluid and
heating  medium, area of heat trans-
fer surface, and the heat transfer co-
efficient.
  Q = UADt                  (1)
where
  Q =   amount of heat transferred
         to aqueous wastewater from
         heating medium, Btu/hr.
  U  = overall heat transfer coeffi-
         cient, Btu/hr/sq ft/°F.
  A  = area of heat transfer sur-
         face, sq ft.
   Dt =  t,-tp,°F.
  t.  = temperature of heat source,
         °F.
  L  = temperature of  process, "F.
  For a given heat load and tempera-
ture difference, Equation (1) may be
used to estimate the required heat
transfer  area of the evaporator. Heat-
transfer coefficients for film evapora-

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               Steam
   Clean  water
   condensate
   (for recycle)
           Wastewater
           (dragout)
                           Concen-
                           trated
                           solution
                           (for
                           recycle)
 DD-435
Figure 3.     Falling  film  evaporator.
Recirculation pump
tors are based on operating experi-
ence or pilot plant testing. Assuming
that the heat source is condensing
steam, overall heat transfer coeffi-
cients range from 500 Btu/h/sq ft/°F
when  processing  water-like  materials
to 100 Btu/h/sq ft/°F for high viscosity
fluids.
   Film evaporators come in rising or
falling film configurations. In the fall-
ing film  evaporator,  liquor is supplied
at the top of the evaporator and is
distributed  to  the tubesheet by
nozzles. The liquor then falls down-
ward  by gravity  along the tube wall.
Steam supplied on the outside of the
tube  in  a  shell-and-tube  configuration
causes evaporation of the film; then
vapors pass along the center of the
tube while the film progresses down
the tube wall. As the liquid-vapor mix-
ture  enters the  main body of  the
evaporator, liquid falls to the bottom
while vapors rise. Following entrain-
ment separation,  vapors  exit  the
evaporator. Liquid is discharged as  a
    concentrate from the bottom  of the
    evaporator body.

    Forced Circulation
    Evaporators
       Solutions containing significant
    amounts of suspended solids are bet-
    ter handled  in a forced-circulation
    evaporator. In this type of evaporator,
    process liquid circulates through the
    heat exchanger at  a very high rate.
    As the process liquid is heated, boil-
    ing  is suppressed by back pressure
    created by the static head of the pip-
    ing at the heat exchanger exit.  As the
    liquid  leaves  the heat exchanger, the
    pressure is reduced, and the liquid
    flashes in the  evaporator body. In the
    evaporator body, vapor is removed
    and concentrated liquid  is recirculated.
    The elements of the forced  circula-
    tion evaporator are illustrated  in Fig-
    ure 4.
      High velocities  in the heat ex-
    changer  increase  the  heat-transfer
    coefficient and reduce fouling  but in-
crease the pressure drop. Design con-
siderations  for  forced circulation
evaporators  include  balancing heat
exchanger  requirements  versus pump-
ing requirements.  Heat exchangers for
forced circulation evaporators are usu-
ally of the shell-and-tube design with
the process fluid nearly always on
the tube side. Plate heat exchangers
offer higher heat transfer coefficients
than the shell-and-tube exchangers,
and a more compact design, but they
are more expensive.

Energy  Savings
  Because evaporation is an  energy
intensive process, it is important to
explore  ways for energy conserva-
tion.  Common ways to save energy
in  evaporation include using  mechani-
cal vapor  recompression (MVR) and
multiple stages.  While both options
increase capital  costs, energy sav-
ings  may justify the expenditure when
energy is expensive or at remote sites,
where thermal energy may be spar-
ingly  available.

Mechanical Vapor
Recompression
   Energy for evaporation may be re-
duced by 95% using MVR, though
aa'ding the necessary compressor
adds to  mechanical  complexity.
Evaporators  equipped  with MVR  are
commonly used  in the food industry
(Iverson,  1980  and Centec Corp.,
1980). In MVR, the vapor leaving  the
evaporator is compressed to the pres-
sure that corresponds to the satura-
tion  temperature required on the
steam side of the heat exchanger. In
most cases, steam is not required
once the system is running. MVR was
popular in the early 1980s when  en-
ergy  was costly, but lower energy
costs have made new installations
less  common. The falling film evapo-
rator  equipped with MVR is illustrated
in  Figure 5.

Multiple Stages
   In multiple-stage evaporation,  the
water vapor from one stage is used
as the heating medium for another
stage operating at lower  pressure.
Multiple-stage evaporation is com-
monly used for  recovery of potable
water from seawater (Darwish et al.,
1989). Most of the separation takes
place in the first stage, but as many
as six or eight stages have been used

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           Vapor
  Heat exchanger
       C
I
                          Compressor
                               Liquor

Forced
circulation
evaporator
             Clean water
             (for recycle)
 DD-664
                                                      Wastewater
                                                      (dragout)
           i—O—
                 /—\     Recycle
                 Pump
                    Concentrated  solution
                    (for recycle)
Figure 4.     Forced circulation evaporator with mechanical vapor recompres-
            sion.
in one system. To illustrate energy
savings, three stages require slightly
less than half the energy than a single-
stage  operation. The process is illus-
trated  in Figure  6 for three stages.
  The lower steam requirement of the
multiple-staged  evaporator is accom-
panied by a higher equipment cost.
The available  temperature  difference
at any single  heat exchanger is con-
siderably lower than that available in
a single-stage evaporator. Thus the
total heat transfer surface area  is
greater. In addition, the multiple-stage
evaporator requires more  vessels,
pumps and piping. As in other  pro-
cesses, the trade-off between capital
and operating costs is the  key con-
sideration.

 Operation And
Maintenance
  Pretreatment  chemicals may be re-
quired for the  evaporation  process,
                    depending on the  characteristics of
                    the wastewater. Chemicals are used
                    to prevent corrosion and fouling of
                    the evaporator. Other operations in-
                    clude  adding  acids  to  reduce alkalin-
                    ity, removing  carbon  dioxide to
                    enhance performance, adjusting pH
                    to control precipitation, and removing
                    oxygen  to reduce corrosion. Should
                    precipitation occur, calcium sulfate (or
                    other crystals) are needed, solids and
                    scales deposit on the crystals rather
                    than  on  heat  transfer surfaces.  Mate-
                    rials  of construction must be selected
                    to minimize corrosion and provide long
                    equipment life.
                       For moderate fouling, film  evapora-
                    tors are acceptable if cleaned often.
                    All film  evaporators have a  minimum
                    liquid wetting rate, to assure that the
                    surface  gets  coated.  If the  required
                    rate  is above the product flow rate,
                    one must recirculate material back to
                    the heat exchanger to maintain the
                    minimum wetting rate.
Failure Analysis

High  Probability

Seals
  Seal or o-ring failures may occur in
the  evaporator feed pump, chemical
feed pumps, or the air compressor,
which delivers instrument air to in-
struments and control  valves.  Pos-
sible causes of seal failures  include
overheating and mechanical stress.
Visual inspection will confirm spray-
ing or leaking of wastewater at the
pumps or compressor.

Valves and Pipe Fittings
  This type of failure is more preva-
lent in older plants than in newer ones.
Generally, leaks in evaporator sys-
tems are likely to be small because
evaporators operate at  low pressures
(atmospheric and vacuum). Causes
for this failure include mechanical
stress,  improper  maintenance  proce-
dures,  and  freezing  during  cold
weather.

Miscellaneous Spills During
Daily Operations
  Spills  of pretreatment  chemicals  and
wastewaters can  occur when  tanks
are replenished. They  may also  oc-
cur when the system is shut down for
maintenance.  In evaporation  systems,
pretreatment chemicals  include  acids,
bases, and phosphates.

Relief Valves (Vapor)
  Tanks are equipped  with vapor re-
lief valves to maintain a constant tank
pressure. These valves will  release
contaminated vapors to the atmo-
sphere as tank levels (and tank pres-
sures) increase. These releases are
small but they occur frequently.

 Evaporator  Failures
  An evaporator can fail for a num-
ber of reasons but failures are  due
mostly to foaming or entrainment.
When foaming occurs,  wastewater
foam fills the body of the evaporator
and ultimately  contaminates the clean
condensate.  Foaming  is caused by
the presence of surface active agents,
though  such agents are often difficult
to detect and  measure. With entrain-
ment, wastewater drops are physi-
cally carried overhead  by the flowing

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          Compressor
                                                                                Clean water condensate
                                                                                (for recycle)
                                                        Concentrated
                                                        wastewater
                                                                                 Concentrated solution
                                                                                 (for recycle)
   DD-658
                             Recirculation  pump
Figure 5.     Falling film evaporator with  mechanical vapor recompression.
vapor with the condensate being con-
taminated by the wastewater drops.
Entrainment is caused by operating
at vapor rates higher than design ca-
pacity.

Moderate Probability

Relief Valves (Liquid)
   Relief valves are  included in evapo-
ration systems to  protect piping and
filings from  overpressure, they are
less numerous and less likely to fail
than  in reverse osmosis because
evaporators are operated at low pres-
sures (atmospheric  and vacuum).

Tank Overflows
  Tank overflows can  result in a sig-
nificant release of wastewater or
chemicals to the environment. They
occur mostly during  startups and shut-
downs.

Low Probability

Tank Ruptures
  A tank can rupture, possibly be-
cause of mechanical failure or freeze
damage. Though this type of failure
is rare, a rupture can result in the
release of large quantity of wastewa-
ter or chemicals to the environment.

Piping Ruptures
   Possible causes of rupture include
mechanical stress, freezing, and im-
proper maintenance  procedures.  Sig-
nificant leaks are possible with this
type  of failure.
  The types and causes of failure
and associated questions for subse-
quent software development are  pre-
sented in Table 1.

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             Boiler
             steam
                          First
                          stage
Second
stage
Third
stage
Condenser
                               Vapor
          Condensate
        Vapor
                                                                              Vapor
                          Cooling
                          water
                                             Liquor
                                                                                  Wastewater
    i
                                                                        i.
                                                                                                B
                          Concentrated
                          wastewater
                                             Clean
                                             water
        DD-364
Figure 6.     Three-stage evaporation  process.

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Table 1. Failure Analyses for Evaporation System

       Failure                    Cause(s)
                                              Questions for Software Development
                                                  High Probability
Seals
Valves and pipe fittings
Miscellaneous  spills
during daily  operations
 Relief valves  (vapor)



 Evaporator  failures
- Overheating
- Mechanical stress
-Abrasive wear
- Mechanical stress
- Improper maintenance  procedures
- Freezing

-Spills during filling  of tanks (due to
 faulty gages and equipment and
 mistakes by operators). Spills can
 include wastewater and
 pretreatment acids and bases.
- Faulty maintenance procedures

- Increases  in tank  levels
-Changes in ambient temperature
 • Foaming
 • Entrainment (operating at above
  design  capacity)
What is the expected quantity of leaks through seals
(gallons)? What is the disposition  of these leaks  (i.e.
Do they go to a capture system, process sewer,  or
are they lost directly to the environment?

What is the expected quantity of leaks through
valves and pipe fittings (gallons)? What is the
disposition of these  leaks?

What is the expected quantity of leaks from spills
(gallons)? (Base on  plant experience  and
operating records). What is the disposition  of these
spills?
What is the expected quantity of leaks through vapor
relief valves (standard cubic feet/hour)? What is the
disposition of these  leaks?

What is the expected quantity of leaks through
evaporators (gallons)? What is the  disposition of
these leaks?
                                                Moderate Probability
 Relief valves (liquid)
 Tank  overflows
- Overpressures during startups,
  upsets, and  shutdowns (for
  evaporators  operating at  pressures
  of atmospheric and  above)
-Key  control valves failing  in
  closed  position

- Plugging of  valves,  piping, and
  membrane modules due to buildup
  of solids. Hollow-fiber and spiral
  membrane modules are most
  susceptible to fouling.

-Occur mostly during unstable
  conditions (during startups and
  shutdowns).  Overflows can
  include wastewater  and
  pretreatment acids and bases.
What is the expected quantity of leaks through liquid
relief valves (gallons)? What is the disposition of
these  leaks?
What is the expected quantity of tank overflows
(gallons)?  (Base on plant experience and records).
What is the disposition  of these overflows?
                                                   Low Probability
 Tank  ruptures
 Piping ruptures
 DD-840
   Mechanical  failures
   Freezing
   Mechanical failures
   Freezing
 What is the expected quantity of releases due to tank
 failures (gallons)? (Be sure to include the concentrated
 waste if it is stored onsite). What is the disposition of
 these  releases?

 What is the expected quantity of losses due to pipe
 ruptures (gallons)? What is the  disposition of these
 losses?

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References
  APV Crepaco, Inc., Chicago, IL,
      Evaporator Handbook,  3rd  Edi-
      tion, EHB-1189.

  Brown, C., "Recovery of Phospho-
      ric Acid by Ion  Exchange and
      Evaporation," 71 st AES Annual
      Technical Conference  Proceed-
      ings, New York,  NY, July, 1984,
      American Electroplaters' Soc.
      Inc., Winter Park, FL  (1984).

  Centec Corporation, "Energy Sav-
      ing Potential  of Mechanical
      Vapor  Recompression,"  Tech-
      nology review sponsored by In-
      dustrial Organizations in the
      Food Industry and U.S. Dept.
      of Energy/Office of Industrial
      Programs, April 1980.

  Darwish, M. A. et al., "Technical
      and Economical Comparison
    Between Large Capacity MSF
    and RO Desalting Plants," De-
    salination, 76:281-304, (1989).

Dedert Corp., Olympia Fields, IL,
    "A  New Evaporator  Gives
    Sweet  Performance,"  Chemical
    Engineering,  May  1994.

Iverson, C. H., G. E. Coury, and
    J.  H.  Fischer, "Evaporation
    by  Mechanical  Vapor  Re-
    compression," Final Report
    #BSDF-38-4Q-80,   Beet
    Sugar Development  Foun-
    dation, September,  1979-
    October31, 1980.

Lavis, G.,   "Evaporators How To
    Make  The  Right Choice,"
    Chemical Engineering,  April
    1994,  p92.

Mehra, D.  K., "Selecting Evapora-
    tors,"  Chemical  Engineering,
    February 3,  1986.
Spearot, R. M., "Evaporative  Re-
    covery," Plating and  Surface
    Finishing,  February, 1987, pp
    22-29.

Worrall, P., "Tips  For  Evaporator
    Selection," CPI Equipment Re-
    potter,  May/June 1988.

Worrall, P., "Sorting Out Evapora-
    tor Types And Designs," CPI
    Equipment Reporter,  March/
    April, 1988.

Yates,  B.,  "Atmospheric Evapora-
    tors: Recovery with Atmo-
    spheric Evaporators Shows
    Major Benefits - Particularly for
    Nickel and Chromium Plating
    Lines,"  Plating  and Surface Fin-
    ishing, 73:4, April 1986, pp 30-
    32.
  &U& GOVERNMENT PRINTING OFFICE: 1994.75MOV41053

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