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Basic Cooling Water Treatment principles

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Title: Basic Cooling Water Treatment principles


1
Basic Cooling Water Treatment principles
  • John Cowpar
  • Area Manager
  • GE Water and Process Technologies

2
USING WATER
3
POTENTIAL PROBLEMS
  • CORROSION
  • DEPOSITION - Fouling
  • Biofouling
  • Scaling

4
Scale Formation
  • Results in loss of heat transfer efficiency
  • Increased running costs
  • Danger of under deposit corrosion
  • Increased maintenance costs
  • Danger of bacteria
  • Health implications

5
Corrosion
  • Destruction of plant
  • increased maintenance costs
  • Fouling
  • loss of efficiency due to increased pumping costs
  • loss of heat transfer efficiency
  • Increased Biological Nutrients
  • fouling and health implications

6
Fouling
  • Loss of heat transfer efficiency
  • increase in running costs
  • Under deposit corrosion
  • increase in maintenance requirements
  • Increased biological nutrients
  • health implications
  • Blockages in system
  • increased operating costs and downtime

7
Objectives of Water Treatment
  • MINIMISE SCALE
  • MINIMISE CORROSION
  • MINIMISE FOULING
  • MINIMISE BIOFOULING
  • MAXIMUM SAFETY
  • MAXIMUM EFFICIENCY
  • NON-POLLUTING

8
WHAT CAUSES OUR PROBLEMS?
9
DISSOLVED SOLIDS
  • e.g. CALCIUM
  • MAGNESIUM
  • SODIUM
  • CHLORIDE
  • BICARBONATE
  • SULPHATE
  • SILICA
  • IRON

10
DISSOLVED GASES
  • e.g. OXYGEN
  • CARBON DIOXIDE
  • NITROGEN
  • SULPHUR DIOXIDE

11
SUSPENDED MATTER
  • DUST/DIRT
  • CONTAMINANTS e.g. OIL
  • BIOLOGICAL e.g. ALGAE, FUNGI, BACTERIA

12
TYPICAL WATER ANALYSIS CHART
13
Water Analysis

Result pH

7.7 Colour
3.00 HAZEN Turbidity
9.00 F.T.U. Solids - Suspended
5 mg/l Chloride as Cl 44
mg/l Alkalinity as CaC03
144 mg/l Ammoniacal Nitrogen as N
0.140 ug/l Iron (Total) as Fe
311 ug/l Manganese (Total) as
Mn 65 ug/l Nitrate as
N
4.0 mg/l Total Hardness as CaC03
207 mg/l Sulphate
as S04
62.3
mg/l Silica - Reactive as Si02
6.9 mg/l Sulphide as S 0.015
mg.l Carbon Dioxide - Free
2.50 mg.l Solids - Total Diss. at
180C 347 mg/l D.O.
Concentration (Field Det.)
10.7 mg/l Coliforms lt10 /100ml E.
Coli lt10 /100ml Faecal
Streptococci
lt1 /100ml Sulphite Red. Clostridia
300 /20ml
14
Hardness
  • Hardness is due to calcium and magnesium salts
    dissolved in water
  • All hardness salts are less soluble in hot water
    than in cold water (they show inverse solubility)
  • Different hardness salts have different levels of
    solubility
  • Hardness is normally reported as calcium carbonate

15
EVAPORATION
WINDAGE
MAKE UP
BLEED
M E W B
16
Useful Equations
ER/100 x Temp Drop(degF)/10
WR x 0.2/100 ( Forced Draught)
WR x 0.6/100 (Natural Draught)
BE/(C-1) -W
ME B W
17
SCALE FORMATION
  • SCALE CAN BE CONTROLLED BY
  • PRE-TREATMENT
  • CHEMICALS
  • CONCENTRATION FACTOR

18
CORROSION
  • Iron ore is found in nature and requires a large
    input of energy to convert it into steel.
  • Steel corrodes in order to get back to its
    natural (lower energy) state
  • Corrosion is an electrochemical process

19
CORROSION CAN BE CONTROLLED BY
  • REMOVAL OF OXYGEN ?
  • ADDITION OF CHEMICALS
  • CONTROL OF pH

20
Biofouling
21
What is Biofouling caused by?
  • FUNGI
  • ALGAE
  • BACTERIA

22
FOULING/BIOFOULING
  • Can be controlled by
  • Filtration
  • Control of Concentration Factor (bleed)
  • Dispersants
  • Biocides

23
Open Cooling
  • When evaporation occurs, the heat of evaporation
    is used to drive off the vapour
  • The loss of this energy results in a cooling
    effect in the water
  • Pure water is evaporated (gases may also be lost)
  • Dissolved solids remain in the water

24
Cooling Water
WATER DROPLET COOLS BY
EVAPORATION RADIATION
CONVECTION
25
Control of Concentration
  • The number of times the solids build in the
    system water is termed the concentration factor
    (CF).
  • CF is controlled by bleed
  • to increase CF - decrease bleed
  • to decrease CF - increase bleed

26
Bleed Control
  • Effect of too much or too little bleed
  • Too much bleed -
  • low concentration factor
  • waste of water
  • waste of treatment
  • Too little bleed-
  • high concentration factor
  • danger of scale and fouling
  • increased nutrient in system
  • danger of biofouling

27
x
While increasing concentration factor reduces
water use, it also increases nutrients in the
system water, encouraging growth of bacteria and
slimes. Therefore, we normally run most cooling
systems between 2 and 5
Water Use
x
x
x
x
x
1 2 3 4
5 6
Concentration Factor
28
Non-biological Fouling
  • Treated by addition of dispersants
  • dispersants (antifoulants) coat the particles and
    so keep them apart
  • The dispersed particles are then removed from the
    system water
  • either with the bleed or via a side stream filter

29
Non-biological Foulants
  • Silt
  • Rust
  • Process contamination
  • all removed by dispersant/bleed
  • Oil
  • Grease
  • a different chemical is required but the
    principle is the same

30
MICROBIOLOGY
31
Microbiology in Industrial Cooling Systems
  • Problematic Microorganisms
  • The Biofouling Process
  • Water Treatment Biocides
  • Biocide Programming
  • Monitoring and Control

32
FUNGI
  • Although yeast and some aquatic fungi are
    normally unicellular, most fungi are filamentous
    organisms
  • Fungi form solid structures which can reach a
    considerable size
  • Some wood destroying fungi exist, associated with
    deterioration of tower timber
  • Fungi require presence of organic energy source
  • Exist at between 5 to 38 C and pH 2 to 9 with an
    optimum of 5 to 6

33
ALGAE
  • Classified as plants as they grow
    by photosynthesis
  • Range in size from unicellular microscopic
    organisms to plants that can be up tp 50m in
    length

Single cells
Multi cellular
34
ALGAE
  • Algae cannot survive in the absence of air, water
    or sunlight
  • Basic difference is that algae utilise CO2 and
    water using sunlight as the energy source to
    assimilate food
  • Large quantities of polysaccharides (slime) can
    be produced during algal metabolism
  • Plug screens, restrict flow and accelerate
    corrosion
  • Provide excellent food source
  • Exist between 5 to 65 C and pH 4 to 9

35
BACTERIA
  • Universally distributed in nature
  • Great variety of micro organisms
  • Multiply by cell division
  • Slime formation
  • Pseudomonas (utilise hydrocarbon contaminants)
  • Sulphur bacteria - anaerobic sulphate reducing
    bacteria
  • Nitrogen cycle bacteria

36
FACTORS CONTRIBUTING TOMICROBIAL GROWTH
  • Rate of incoming contamination
  • Amount of nutrient present
  • pH
  • Temperature
  • Sunlight
  • Availability of oxygen/carbon dioxide
  • Water velocities

37
THE BIOFOULING PROCESS
  • Bacteria prefer to colonise surfaces
  • enables production of biofilm which acts to
    protect and entrap food sources
  • Planktonic bacteria
  • free swimming in bulk water
  • Sessile bacteria
  • attached to surfaces

38
EFFECTS OF BIOFOULING
  • Fouling of tower, distribution pipework, heat
    exchangers
  • Reduction in heat transfer efficiency
  • Lost production
  • Under deposit corrosion
  • Inactivation/interference with inhibitors

39
WATER TREATMENT BIOCIDES
  • Oxidising Biocides
  • Have the ability to oxidise organic matter eg.
    protein groups
  • Non-Oxidising Biocides
  • Prevent normal cell metabolism in any of the
    following ways
  • Alter permeability of cell wall
  • Destroy protein groups
  • Precipitate protein
  • Block metabolic enzyme reactions

40
OXIDISING BIOCIDES
  • Sodium Hypochlorite
  • Hypobromous Acid
  • Chlorine dioxide
  • Ozone
  • Hydrogen Peroxide

41
Oxidising Biocides
  • Rapid kill
  • Cost effective
  • Tolerant of contamination
  • e.g. Bromine, Chlorine Dioxide
  • Minimal environmental impact
  • e.g. Bromine, Ozone, Peroxide, Chlorine
    Dioxide
  • Ineffective against SRBs
  • Low residual toxicity
  • Counts approaching potable water standards
    possible

42
Non Oxidising Biocides
  • Screen water
  • Select alternating biocide to prevent resistant
    strains from developing
  • Effective against SRBs
  • Can protect system long after dosing.
  • Contain biodispersant
  • Higher dosage for kill possible
  • Environmentally some have rapid breakdown e.g.
    DBNPA

43
BIODISPERSANTS
  • Improves penetration of biocide within bacterial
    slime
  • Disperse released bacteria and biofilm into bulk
    water for removal by blowdown
  • Reduces ability for bacteria to attach to system
    surface
  • Improves performance of both non oxidising and
    particularly oxidising biocides

44
Physical Methods
  • Ultra Violet and Ultra Filtration
  • Only Effective At Point Of Use
  • Cannot Kill Sessile Organisms
  • Offer No Protection To Isolated Parts Of System
    (Static Areas)
  • Environmentally Acceptable.

45
Control of Concentration
  • The number of times the solids build in the
    system water is termed the concentration factor
    (CF).
  • CF is controlled by bleed
  • to increase CF - decrease bleed
  • to decrease CF - increase bleed

46
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47
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