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81a,(DMDR
To: D, L Cravener, Jr„ D/064
From: B, L, Tuffly, D/99l°359N . V, Sutton, D/991~35 9
Subject: The Fluoride Water Pollution Question
INTRODUCTION
RM ll83
18 August 1965
Since the Nomad Program in 19599 Rocketdyne has conducted a strict surveillance
program on the fluoride contamination in the catch ponds and reservoirs at Santa
Susan , Working cooperatively with the State authorities , maximum values for
propellant exhaust products in property surface drainage were establishe& In
addition9 standard methods of chemical analysis for these pollutants in water
were agreed upon When the chemical analysis results exceeded given limits, the
catch (or skim) ponds were chemically treated to reduce the contamination to an
acceptable value
The demise of the Nomad program relieved Rocketdyne of the fluorideacontaminationo
The interest in operational high energy systems , however, has reintroduced the
fluoride contamination questiono As of this writing, three areas handle fluorine,,
vino, the activity at PRA is Area I; the PLOX program at Alfa in Area II, and the
Compound A facility in Area IIIo While the quantities of fluoride discharged from
these systems do not pose a problem at this time , because there exists satisfactory
and economic methods for handling the water pollution , the question has arisen that
the increased usage of fluorine may introduce new problems in discharging the
polluted water
This report discusses in detail certain problems relating to the fluoride pollution
and attempts to recommend procedures for water handling to cope with the antici-
pated increase in fluorine usage
II0I muim i iimnmum i iim uii iuBNA0255145 3
HDMSE00637997
To; Do L Cravener, Jro, 1)1064 Page 2
From: B0 L0 Tuffly, L Vo Sutton B1 l183
Subject: The Fluoride Water Pollution Question 18 Auguat 196 5
THE SANTA SITSANA POND SYSTEM
Area I
The Area I pond system is shown in Figure 1o Propellant product discharge from
the PRA goes into PRA 1 , which has a capacity of 25 ,000 gallonse Another ponds
PRA 2, capacity 70,000 gallons, is used when PRA1 is too contaminated to intro
duce into the Area I pond system ; the total water capacity in Area I is abou t
5 million gallonso Discharge off the property is from the Perimeter pond and
surface drainage is into the San Fernando Valley via Bell Canyon , The PRA .l and
2, CTLml , CHTL, C3$!2 panda have cement bottoms, while all the other ponds
have dirt bottomso Killing the fluoride takes place in the discharge pond
(PRA 1) and, when required, PRA 2 0
Area II
The Area II pond system is shown in Figure 20 The total water capacity of Area II
is about 8 million gallons Propellant product discharge from the Alfa 5 stand is
into the 400, 000 gallon Alfa Skim pond , The physical aspects of this pond are
noteworthy , and demonstrate how well the geological features of the area have been
utilizedo The test stands fire against a natural stone walla The water runs down
a natural rock trough into this downhill , Y shaped ponds When a kill is required,
lime is dumped into the trough and as water runs down the trough, the lime is
easily "watered " in this runways The mixture then travels on down to the pond
(about 50 feet) and mixes in very readily Discharge of the water off the property
is from the 2,2 million gallon R-2®A ponds Surface drainage from this pond is also
into Bell Canyon leading into the San Fernando Valley
II0I m u imi i imnmumi i ini i iiu m iBNA02551454
HDMSE00637998
D, L. Cravener , Jr . , D/064To : Page 3
BL, Tuffly N0 V. SuttonFrom, RM 1183
The Fluoride Water Pollution QuestionSubject : 18 August 1965
SSFL WATER SUPPLY
There are two sources of water supply at 55'L: the well water which xontains
about 008 ppm fluorides and fresh water which is fed in through pipeline from
the Metropolitan Water District ( Simi Valley) , This latter water contains from
O,3 to Oo6 pa of fluoride0 The cost of he water averages about 51,000 for 3
million 'gallons
MAXIMUM ALLOWABLE CONTAMINATION
San Fernando Valley
The surface drainage from Area I is into the San Fernando Valley where State
authorities have established the maximum permissible contamination , as listed in
Table I, These values therefore represent ; the maximum pollutants that the 1,1
million gallon Perimeter Pond can have and still be cumped ,
The surface drainage from Area II is also into the San Fernando Valley These
values, therefore, represent the max imum pollutants that the 202 million gallon
R2~-A pond can have and still be dumped 0
Simi valley
From time to time, water may drain into the Simi Valley, ~ithough thin occurs only
from some of the Atomic International pondso For purposes cf this report, and for
future planning of the North American pond system, cognizan .A should be taken of
the requirements for draining into the Valley The maximum ,11.,wable concentration
for surface drainage water is shown in Table I1 0
CURRENT METHODS FOR POLLUTANT LULLS
A plurality of propellanta are fired or lumped at Santa Susana And definite
II0I muim i iimnmum i iim uim iBNA0255145 5
HDMSE00637999
To: Do H, Cravener9 JrD/064 Page 4
From: B, L, Tuffly , N, V, Sutton RM 1183
Subject : The Fluoride Water Pollution Question 18 August 1964
methods have been established for disposal of their waste , These methods have
been in use for over 10 years and have proven extremely effective , Many of the
methods9 where applicable , are also employed at NFL ,
By razines
The hydrazine fuels are killed with hydrogen peroxide at a pH of from 8 to 11 0
The chemical equations for hydrazine are : N2H4 + H2O ----~ N2H5OH
N21150H + H2a2-- 3 N2H5OOH + 1120
N2H500H - ---~ N2H2 +2$20
N2H2 + H2O2 -- --+ N2 + H2O
The nitrogen leaves the pond as a gas , This has proved to be an excellent route
to reducing the hydrazine concentration to acceptable values, notwithstanding the
fact that the effectiveness of the procedure is pH and temperature sensitive . The
treatment is satisfactory for hydrazine , monometbyl~hydrazine and unsym~dimethyl-
hydrazine ,
RP].
Because the RP~1 floats on water , its removal is performed by skimming the pond,
In addition , repeated use of contaminated water for cooling the flame bucket reduces
the RP 1, If necessary , the RP -1 can also be burned on the surface of the pond,
Nitrates
The maximum allowable concentration for nitrogen (as nitrate ) is 50 ppm , Because
of this high tolerance, nitrates are usually killed by dilution,
II0I muimiiimnmumiiin iimimiBNA02551456
HDMSE00638000
To : D, H,, yravener, Jr,, D/064 page 5
From: B0 L, Tuffly, N, V0 Sutton JL fl83
Subject : The Fluoride Water Pollution Question 18 August 196 5
Fluoride
The detailed procedure for killing fluoride is attached The present method
^omprises introducing lime r93 per hydrated calcium oxide ) to the catch pond ,
This causes the formation of the slightly soluble salt, calcium fluoride , Any excess
fluoride in the catch pond above the allowable 105 ppm is diluted as the water from
the catch pond is introduced into the SSFL =water system ,
REQUIREMENTS T~)R A FLUORIDE KILL AT SSF L
Any technique developed for reducing fluoride in the pond systems at SSFL must
meet the following criteria ;
i.) Reduce the F ' below 105 ppm when discharged off property ,
2) Must not reduce pH of the system below 8, so that the hydrazine kill can be
effected ,
3) Must not introduce a more serious problem such as toxic heavy metals , flocculence,
etc o
4) Must cost less than equivalent amount of fresh water , $1000 for 3 million gallons,
5) Must be simple enough to be carried out routinely by non-professional personnel,
6) Must be flexible enough to be operable for a large kill as well as a small ,
EVALUATION OF PRESENT TECHNIQUE
Because there is no chemical fix for F , as there is with the hydrazine,, the present
method takes advantage of the insolubility of the salt calcium fluoride, The upper
limit for calcium, as calcium carbonate, is 500 ppm, If the pH is above 7, the
soluble calcium salts will be below this value
The price of lime is $35 a ton ; use of lime to kill the fluoride is acceptable to
the state and to Rocketdyne , Notwiths xding the fact that lime cannot reduce the
fluoride to 1,5 ppm, fresh water is avaiiable f ;;r the complete kill, In addition ,
II0I muimiiimnmumiiin i iBNA0255145]
i u I IHDMSE00638001
To : D,. H0 Cravener9 Jr ., D/064 Page 6
From ; B, L< TufflyD H0 V Sutton R 1183
Subjects The fluoride Water Pollution question 18 August 1965
because of the large quantity of waste water in the Canoga Park water system,
it is permissible to dump water containing up to 25 ppm into the Canoga Park
sewer systemo The cost is approximately $600 to haul away 70,000 gallons of
water from Santa Susan to Canoga Park,
CHEMICAL ASPECTS
Fluorine is a cryogenic oxidizer , which is an important propellant for high energy
systems , When mixed p ith oxygenD the resulting oxidizer is called FLAX , which is
hypergolic with RP-J , In addition to the advantage of hypergolicityD 3C% FLOX
also will insreas~ the payload capability of the Atlas-Centaur by 30 percents and
the Atlas =Agena by 58 percent ,
to addition to its use as a neat propellant or as an additive to oxygen , fluorine
is an ip-rtant starting material in the manufacture of eartJ~storable high energy
oxidizes , such as chlorine trifluoride , Those materials incorporating chemically
the f ]uorine atom will undoubtedly be the oxidizers of choice in advanced pre
packaged propellant systems
T ose chemical reactions involving fluorine containing propellants all lead to at
".east one common reaction product, HF This weak acid is completely soluble in
water, and dissociates into the hydrogen ion, [HI , the fluoride ion [F'] , and the
und~ssociated molecule [BP] Although the boiling point of pure HF is lowD l94 C
66 9 P. when dissolved in water , it can not be removed except by boiling the watero
Thus, by using F containing water for cooling during an engine firing , some HF would
ce removed from the water, This has been attempted , but the efficiency was too low
o be practical ,
The amount of each of the three species Fresent when HF is dissolved in water can
be changed by changing the pH, Thus at low pH (high hydrogen ion), the fluoride
II0I muimiiimnmumiiinn i iBNA02551458
I IHDMSE00638002
To: D, H, Cravener, Jr. D/064 Page 7
From : B. L, Tuffly, N, V, Sutton RM~1183
Subject : The Fluoride Water Pollution Question 18 August 1965
concentration goes down, but the HF concentration goes up, Thus the F stays
constant but the chemical form changes, At high pH, (low hydrogen ion), the
fluoride concentration goes up but the HF concentration goes down, Again, the
total F stays the same,, The reason for having a pH of above 8 in the ponds for
the present kill is to reduce the amount of HF, which does not react with the
lime, and to increase the availability of the Fu which does react with the lime
A process for removing fluoride as a gas would be desirable , because this technique
would obviate residue build up and/or expensive capital installations, However,
the chemical reactions of HF to form volatile materials usually take place at
fairly high reaction densities , i,e,, at high concentrations of HF , Thus, to
remove small amounts of fluoride from water in the form of a noxious gas is not
possible ,
Alternate methods of fluoride removal therefore are, 1) passage of the water over
a fixed fluoride absorption bed, or 2) precipitation as an insoluble salt ,
The use of a fixed bed to remove anions (fluoride ion is an anion ) is a common
industrial practice, Beds comprising ion exohmnge resins could be installed for
passage of the water over them to remove fluoride ,, However, this requires a great
deal of facility modifications, capital equipment , and a staff to operate ; in other
words ,, a water treatment plant would be necessary , Although this is the ultimate
in water treatment , the potenti , .l problems of fluoride contamination are not
ouficiently great to warrant such an expensive undertaking . However, it shoul d
be borne in mind that if excess ive firings of fluorine do begin , involving the
release of several tons a day ,, on a daily basis , serious consideration should be
given to a recovery plant
The last alternative is precipitation ~ .f the fluoride as an insoluble salt, An
examination of the literature for insoluble fluoride materials shows the following :
II0I muimiiimnmumiiiniuuBNA02551459
UHDMSE00638003
To: D„ HL Cravener , Jr,, 1)1064 Page 8
From: B, Lo Tuffly , N, V, Sutton &Mm1183
Subject : The Fluoride Water Pollution Question 18 August 1965
Solubility, ppmCaP2 ( Calcium fluoride) 16
(Magnesium fluoride) 76
PbF2 (Lead fluoride) 640
Pb C1F (Lead chlorofluoride) 370
Al F3 (Aluminum fluoride )
(Aluminum oxyfluorides )
5600
5 (eat, )
There are, of course , other inorganic fluorides which are insoluble , but these
are the most important ones , The only material less soluble than calcium fluoride
is an aluminum oxyfluoride compound, The lead salt can be immediately discarded
as a candidate because of the increased toxicity problem lead would introduce d
The aluminum oxyfluoride should be considered , although it is anticipated that
close pH control would be required, and further ; the floc might introduce serious
flow problems in transferring water from one pond to the other,
The calcium fluoride has many advantages , and these are listed below :
1) Compact precipitate
2)
3)
4)
Calcium is a natural constituent in water and is non-toxic
Cheap method , 1 calcium atom for 2 fluoride atoms )
Proven to be effective
The fact remains that no candidate methods can compete effectively with the lime
treatment, If this is true , it would ordinarily be necessary to determine if lime
would fulfill the requirement of a large kill, However, due to air pollution aspects
of he fluoride situation , limitations are in effect which restrict tankage of
fluorine at Santa Susana to 1000# (2400# for CTF and Campo i)0 Therefore , large kill
considerations are not required,
II0I muimiiimimmmiiumi iuBNA02551460
UHDMSE00638004
Toe Da H, Cravener, Jr,, D/064 Page
oQ.; B. Lo Tuffly, Ne V, Sutton RM 1183
Subject: The Fluoride Water Pollution Question 18 August 196
CONCLUSION S
10 SSFL has utilized 31,136 lbs . of fluorine (or fluorine containing
oxidizers ) at Area I during the period 1 July 1964 to 1 July 1965, Lime
treatment or hauling the contaminated water away bas solved the fluoride
contamination problem, About 20,200 ibs, of fluorine ( or fluorine con
taming oxidizers ) will be used in Area I from July 65 to July 66, Hence,
lime treatment should be effective ,
2r, SSFL has utilized 479250 lbs, of fluorine at Area II since cy
Lime . treatment of the skim pond has solved the fluoride question During
the nest six months , little or no fluorine activity is anticipated o
3, A facility at Area III which will have a maximum of 200 lbso of fluorine
(or fluorine containing materials) has an isolated pond which will not empty
into any complex SSFL water systeme Lime treatment will handle all potential
contamination problems e
4~ Past intrusion of fluoride into the ponds due to rain cannot be calculated
although it is anticipated that the majority of residual fluoride will be
washed back into the skim pond around the test stand , where the fluoride can
be killed ,
5, In the absence of a large fluorine program, the present lime treatment,
and, where deemed necessary, haulage will satisfy the present State and
Rocketdyne control of the fluoride pollution
II0I muim i iimimmm i i um iuBNA02551461
UHDMSE00638005
To: D, L Cravener, Jr -~ D/065 Pare 10
Pram : B, L- Tuffly9 N, V, Sutton RL-1183
Subject : The Fluoride Water Pollution Question 18 August 1965
RECOMMENDATIONS
It is recognized that some of the recommendations herewith made are currently
implemented ,
1. Cement al skim ponds which are recipients of the cooling water from
fluoride containing firings
2, Industrial Sngineering must be advised in advance of any fluorine
firing to provide for adequate kills .,
3 . All future fluorine programs must anticipate a pollution phase0 This
is to be coordinated with Industrial Engineering who would then coordinate
with SSFL.Chemical Analysis o
REFERENCES FOR PHYSICAL CONSTANTS
i LangeA HANDBOOK of CHEMISTRY9 9th Editions
2, Seidell9 SOLUBILITIES-Inorganic & Metal Organic Compounds , Vol, I .
5. U, S, Rubber CompanyB HANDBOOK of CfEMISTR7 and PRYSICS9 45th Edition o
II0I muimiiimimmmiiumimiiuBNA02551462
HDMSE00638006
To : D, H, Cravener9 Jr 0 9 D/065 Page 11
Fraa : B, L> Tuffly9 N . V, Sutton RM~1183
Subject : The Fluoride Water Pollution Question 18 August 196 5
CHART I
AREA I m FLUORINE CONTAINING OXIDIZERS
Period Period1 July 64 1 July 65 1 July 65 v 1 Jul 66
Pr=~llant Lbso Lbs estimated
CT? 14a300 69400
Comp ., A 19630
F2 986 19800
OF2 20 300
FLAX 149200 11,800
IIDI muimiiimimmmiiummim iBNA02551463
HDMSE00638007
Toy D Hp Cravener9 Jr,9 D/065 Page 12
Vim; Ba Lo Tuffly9 N, Va Sutton RM 1l83
Subject : The ?Fluoride Water Pollution Question 18 August 196 5
CART II
AREA II FLUORINE USAGE
079 19659Lb80
January 4, 600
Fehruazy 59260
March 89000
April 69190
May 1,000
June 49200
July 109000
August 7 8,000
47 250
Remainder of year none anticipated
A1tEA III Maximum 200 lba, weekly9
Beginning August9 1965
II0I muim i iimimmm i i umi im u iBNA02551464
HDMSE00638008
T, Y D0 H, Cravener, Jr, D/061~ Page 13
Fir Bm L. Tuf'P1y, Ya V, Sutton RM l183
Subject, THE FLUORIDE WATER POLLUTION QUESTION 18 August 1965
TABLE I
MAXIMUM ALLOWABLE CONTAMINATION
SURFACE DRAINAGE TO THE SAN FERNANDO VALLEY
maxe
Total dissolved solids 1000Total hardness (as CaCO) 500
3V( e~rsenate Method)ChlorideSultah plus chloride salinityNitrogen (as NO,)Hexa lent chroidiFluorideBoronpHTurbidityColor (p1atinumcoba1t scale)Floatable oil & greaseTotal oil and grease (including rats
and waxes , wet extraction use thud)Hydraaines
250500
50 0005lay100
5 0 5 to 1110020
None visible
25None
TABLE II
MA%IIi4UM ALLOWABLE CONTAMINATION
SURFACE DRAINAGE TO SIMI VALLEY AND PERCOLATIO N
Total dissolved solidsChlorideSulfateBoronNitrogen (as N03)FluorideHexavalent ChroeiumpHTurbidityTotal oil and grease
(including fats and waxes zitextraction method)
Floatable oil and greaseHydrasines
2000175500
None visibleNana
II0I muimiiimimmmiiummim iBNA02551465
HDMSE00638009
Tog Do H, Cravener , Jr, m D/0614 Page 11 4From s B0 L, Tuffly9 N. V o Sutton RM 1183
Subjects THE FLUORIDE WATER POLLUTION QUESTION 18 August 1965
APPENDI=
PROCEDURES FOR DECONTAMINATING WATER CONTAINING FLUORIDE ,
The fluoride content of water should be rednced ' at the test stand retaining
ponds because it is easier to precipitate the fluoride in concentrated fog
rather than after it has been diluted by passing to reclamation reservoirs .
Although the allowable fluoride concentration is limited to 1 .5 ppa for water
passing frcas he facility , it usually will not be necessary to reduce the
fluoride content to this limit at the test stand treating ponds, Current
practice is to reclaim or recirculate the water used for test stand use and
under such circumstances , substantial Quantities of fluoride in the water
should provide no deleterious effects , Tuning the heavy rain season, which
lasts about four writhe of a year, it will be necessary to pass some of the
water off property, It is desirable in this case to maintain the fluoride
content of the reclamation reservoirs to relatively low limits to minimise
the quantity of dilution water requiredo The addition of lime to the water
in sufficient concentration to completely saturate the water will usually
reduce the concentration of the fluoride to a range of 540 o The actual
concentration will depend on mangy factors including water temperature, degree
of mining , reaction time , and concentrations of otter dissolved salts, Low
temperatures and high concentrations of magnesium favor fluoride precipitation 0
moderate mixing will speed up the precipitation of fluoride by increasin g
the rate at which lime goes into solution while excessive agitation is
undesirable since it has a tendency to break up the (loos and leave finely
divided calcium fluoride in suspension .
The addition of lime to contaminated xater should be done with discretion
because from the viewpoint of test stand operation , excessive lime may be more
objectionable than fluorideo High concentration of line have a tendency to
form calcium carbonate precipitates Which contribute to the formation of
familiar "boil scale" in water pipes, The concentration of calcium in the
reclamation ponds mapr be
fn ~~ ~8d2t99 T'€ k er L98 c °k:a n
DI IBNA02551466
I IHDMSE00638010
To: D0 H Cravener9 Jr,D/064 Page 15
From: B L0 Tuffly, L. V, Sutton RM~1183
Sub .ect: The Fluoride Water Pollution Question 18 August 1965
retained to eafe operating limits by the addition of sodium carbonate, which
precipitates the calcium as calcium carbonate ; however, this represents added
expanse and increases the dissolved solid content of the water which is limited
to 1,000 ppm for water passing off property, Thus, lame should be added to the
water only when sufficient fluoride will be precipitated to justify its use d
The addition of magnesium sulphate to water after it has been treated with
lie will cause a further reduction in the fluoride concentration , The magnesium*
required for fluoride precipitation may be estimated from the following equation :
t F F <3 2tag 200 A ? _
'
Where Mg = quantity of magnesium required ppm
Fl - original fluoride concentration„ ppm
F2 = final concentration of fluoride, ppm
The use of magnesium sulphate should be limited to those cases where it is essential
to reduce the fluoride concentration to a range of 1~4 ppm, since it results in
added sulphate contamination ,
Because of the varying nature of the water and the degree of contamination that may
be tolerated, it is not practical to specify a water treatment procedure which should
be applicable for each case of water pollutiono A few general rules and decontamznat--,
ing procedures will be specified which in general, will be applicable for the
Research and Delta areas where fluorine is currently being used for test operations o
DECONTAMINATION PROCEDURES FOR TEST STAND TETAINING PONDS :
Determine the fluoride concentration of the water before taking any decontamination
steps 0
*W A= Handenbergh; Water Supply and Pu.rifzcaf on, 1952
II0I muimiiimimmmiium iBNA0255146]
I I IHDMSE00638011
r Too Do L Cravener, JrD/064 Page 16
From: Bo L0 Tuffly , N, Y, Sutton RM_-1183
Subje'°t: The Fluoride Water Pollution Question 18 August 195 5
2n If the totav fluoride content is equal to or less than 15 pp, no
decontamination steps are necessary, Allow the water to pass to the
reclamation pond
If the fluoride concentration exceeds 15 ppm, add lime (Ca(OH)2) to the
water in a quantity equivalent to the theoretical quantity required to
precipitate the fluoride, The required quantities are given in Figures 1
and 2
5
In addition to the lime required for precipitation, additional lime should
be present in the ?ond to ensure a saturated solution of lime in the water
and ensure a reass~nable rate of equilibrium attainment, The required quantity
will vary greatij with degree of agitation ; particle size of the lime, and
water temperatu.•ea As an initial treatment, it is suggested that abou t
30 pounds of L.mef1000 gals, of water be added to the pond in addition to
the theoretical quantity of lime required to precipitate the fluoride,
Moat of the unreacted lime will remain in the
bottom of the pond and will serve to saturate the water after subsequent tests
with fluorine With repetitive additions of lime for fluoride precipitation, the
the solid lime content of the pond may be sufficient, to precipitate the fluoride with
without further additions of lime., In this case, mixing of the lime and water as
speci!ied in step (4) may be sufficient, This condition may be anticipated by
1towiag the quantity of lime that has been previously added to the pond and the
quantity of fluoride precipitated
40 The water should be stirred or agitated sufficiently to cause a fairly uniform
su:pen.ion of solid lime in the water, The required mixing time will probably
be in. the range of l 53O minutes but will vary with lime concentration and
the efficiency of the mixing apparatus
TYr"s specification may be dowered if the fluorine usage rate is increased .,
II0I muimiiimnmumiiuunuBNA02551468
UHDMSE00638012
To. D, H. Cravener, Jr,, iU/064 Page l
From : B . L. Tuffly, N, V . -Sutton FX--1183
Subje t: The Fluoride Water Pollution Ruesticn 18 August 196 5
Take a sample of the Na ::er and analyze it for fluoride . If the fluoride
-cntent is eater than 12 %~pms continue stirring and alternately analyzing
w4til the fluoride content is no greater than 12 ppm ,
6 Add 2J lbs, of magnesium sulphate ( SO4;ifor each 1000 gal- of water in
the pord< Stir the water for an additional l3 minutes, This step should
reduce the, fluoride °.oncentration to a range of 2-4 ppm ,
A.1ow the waier to settle without agitation f~)r at least 2 hours „
8, glow the water to pass to the reclanaticn reservoir . The drain from the pond
scoui'i be aoove the '.evel of the lime-~:alcium fluoride slime which will collect
a th;, ;bottom of the goad ,
3 After extensive usage , the quantity of the lime-calcium fluoride mixture will
: ;come sufficient to seriously affect the capacity of the pond , When this
occurs, the pond should be dredged and the solid lime and calcium fluoride
ai.xtura hai.Ced to a dump,
*Phis step may be eliminated if the fluoride content in the reclamation
reservoir Is lass than 1,5 ppm o
AJ I/N, V. Sut :ron B, Tuff
Principal C,: :.er. iet =soup Scientist
Chemical 1,ralyc3.s Analytical Chemistry
e search P e sear-,h
Aoprnved oya
J. 3LvesmanChiChemistryResearch
BNA02551469I I
HDMSE00638013
AREA I Pollution Pond System I UZ-1000 gsl,4ot-,
11 ponds : 4,782,9000 gallons
Industrial Engineering can pump water
back from Perimeter Pond to R-1 o
O P E3.OPERT"Y ----------------
0r
Arrows indicatedownhill direction