Document ID: EPA-HQ-OW-2002-0043-0214
Agency: epa
Document Type: Supporting & Related Material
Title: 
Posted Date: 2003-08-18T04:00Z

SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
Sampling
Period
(
for
Initial
and
Final
Sampling
Plans)
Assigned
sampling
period
for
initial
and
final
monitoring
plans.
If
Initial
Monitoring
Period,
Then
0;
ELSE
19.
Extraction
Utility
Design,

Plant
Design
Utility
Design,

Plant
Design
Total
Population
Served
Total
population
served
by
the
utility.
Sum
Wholesale
Population
and
Retail
Population.
Extraction
Utility
Monthly
Utility
Monthly
Population
Size
Category
Size
category
for
systems
based
on
total
population
served.
See
Exhibit
5
of
this
Document.
Extraction
Utility
Monthly
Utility
Monthly
Average
Percent
Solids
The
average
percent
solids
reported
by
a
utility
over
the
monitoring
period.
Average
(%
Solids)
reported
for
however
many
months
of
data
are
available.
Extraction
Plant
Monthly
Plant
Design
Geographic
Region
of
the
Plant
EPA
Region
for
the
plant.
See
Exhibit
4
of
this
Document.
Extraction
Plant
Design
Plant
Design
Hydrologic
Unit
Code
(
HUC)
Standardized
code
for
water
resource
identification.
EPA
will
define
this
algorithm.
Extraction
Plant
Design
Plant
Design
Process
Train
Name
Name
of
the
unit
process
train
where
samples
are
collected.
If
Any
Sample
Number
for
Process
Train
=
VALUE,

then
select
information
for
this
process
train.
Extraction
Plant
Design
Plant
Design
Sludge
Handling
Capacity
in
dry
tons/
day
Sludge
Handling
and
Disposal
design
capacity
in
dry
tons/
day.
See
Section
2.2.4
of
this
Document.
Extraction
Plant
Design
Plant
Design
Surface
Water
Resource
Category
Characterization
of
the
type
of
surface
water
used
for
those
plants
characterized
as
"
SW."
For
all
Source
Water
Category
=
SW;
Step
0.

Calculate
the
total
SW
Flow,
mgd
=
FS
Flow
+
RL
Flow
+
GWUDI
Flow
+
NF
Flow.
Step
1.
Calculate
the
%
of
SW
Flow
from
FS,
RL,
GWUDI,
and
NF.
Step
2.
If
FS%
>
80%,
then
"
FS;"
If
RL%
>
80%,
then
"
RL;"
If
GWUDI%
>
80%,
then
"
GWUDI;"
If
NF%
>
80%,
then
"
NF;"
ELSE
"
MIX."
Extraction
Plant
Design,

Plant
Monthly
Plant
Design,

Plant
Monthly
Water
Resource
Category
Characterization
of
the
source
type
being
used
by
plants
and
trains.
Step
1.
Calculate
%
of
total
plant
flow
from
Flow
Stream,
Res/
Lake,
GWUDI,
GW,
NonFresh,
Purchased.

Step
2.
Calculate
the
SW
Percentage
=
Sum
of
FS,
RL,

GWUDI,
NonFresh.
Step
3.
IF
SW
%>
80%,
then
"
SW;"
if
GW%
>
80%,
then
"
GW;"
If
Purchased%
>

80%,
then
"
PUR;"
ELSE
"
MIX."
Extraction
Plant
Design,

Plant
Monthly
Plant
Design,

Plant
Monthly
Chlorine
Demand
Initial
chlorine
demand
of
the
source
water.
If
(
Free
Chlorine
Residual
>=
0.2
mg/
L
and
<=
1.5
mg/
L)
and
(
Contact
Time
<=
10
min),
then
((
Total
Chlorine
Dose)
­
(
Total
Chlorine
Residual));
ELSE
Missing
Value.
Extraction
Plant
Monthly
Plant
Monthly
Distribution
System
Disinfectant
Type
Characterization
of
the
disinfectant
used
in
the
distribution
system.
If
any
Unit
Process
=
DIS
is
"
NH3,"
then
"
CLM;"
if
no
Unit
Process
=
DIS
is
"
NH3"
and
at
least
1
other
Unit
Process
has
a
dose
>
than
0,
then
CL2;
ELSE
"
Null."
Extraction
Plant
Monthly
Plant
Monthly
E­
1
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
Plant
Disinfection
Type
Categorical
descriptive
of
disinfection
practices
in
the
treatment
plant.
If
Unit
Process="
DIS"="
O3"
and
Dose
=
Nonzero,
then
O3;
If
Unit
Process
=
"
DIS"
=
"
CLX
"
and
Dose
=

Nonzero,
then
CLX;
ELSE
IF
ALL
Unit
Process
with
sequence
numbers
less
than
the
sequence
number
associated
with
the
last
unit
process
having
a
liquid
volume
greater
than
zero
=
"
DIS"
=
"
CL2"
or
"
SOY,"

then
CL2;
If
the
first
Unit
Process
=
"
DIS"
=
"
NH3,"
then
CLM;
If
the
second
Unit
Process
=
"
DIS"
="
NH3"
and
no
upstream
Unit
Process
has
a
Volume>
0,
then
"
CLM;"

If
there
is
no
sampled
process
train
or
the
influent
flow
is
null
or
if
all
of
the
disinfectant
addition
unit
processes
with
sequence
numbers
less
than
the
sequence
number
associated
with
the
last
unit
process
having
a
liquid
volume
greater
than
zero
have
doses
equal
to
zero,
then
"
Null;"
ELSE
CL2+
CLM.
Extraction
Plant
Monthly
Plant
Monthly
Process
Train
Name
Name
of
the
process
train
selected.
Select
Process
Train
if
Sampled;
If
more
than
one
train
is
sampled,
then
Select
the
Process
Train
with
the
largest
flow
at
the
time
of
sampling
for
the
first
unit
process.
If
the
flows
are
equal,
sort
the
process
train
name
alphabetically
and
select
the
first
process
trian.
Extraction
Plant
Monthly
Plant
Monthly
Overall
Plant
Baffling
Factor
Aggregated
average
baffling
factor
(
ratio
of
T10
to
T50)
across
all
unit
processes.
[
SUM(
T10)
for
all
unit
processes]
/
[
SUM(
T50)
for
all
unit
processes].
Extraction
Unit
Process
Plant
Monthly
Aluminum­
based
Coagulant
Dose
Total
applied
dose
of
aluminum­
based
metal
acid
coagulants
as
mg/
L
Aluminum.
Sum
all
Chemical
Feed
Dosages
where
the
Chemical
Feed
Name
is
"
ALUM."
Extraction
Unit
Process
­

Chem
Feed
Plant
Monthly
Iron­
based
Coagulant
Dose
Total
applied
dose
of
iron­
based
metal
acid
coagulants
as
mg/
L
iron.
Sum
all
Chemical
Feed
Dosages
where
the
Chemical
Feed
Name
=
"
IRON."
Extraction
Unit
Process
­

Chem
Feed
Plant
Monthly
Coagulant
Type
Metal­
coagulant
type
applied
at
the
plant.
If
Aluminum­
based>
0
and
Iron­
based>
0,
then
"
MIX;"

ELSE
IF
Aluminum­
based
>
0,
then
"
AL;"
ELSE
IF
Ironbased
>
0,
then
"
IRON;"
ELSE
NULL.
Extraction
Unit
Process
­

Chem
Feed
Plant
Monthly
Sludge
Solids
Production
Capacity
in
dry
ton/
day
Sludge
production
quantity
normalized
to
dry
tons/
day.
See
Section
2.2.7
of
this
Document.
Extraction
Plant
Monthly
Plant
Monthly
E­
2
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
Wastewater
Return
Treatment
Type
Overall
type
of
treatment
provided
for
the
washwater
return
supply.
If
WWR
Plain
Sed
=
WWR
Coag/
Sed
=
WWR
Filt
=

WWR
Dis
=
WWR
Other
=
"
N,"
then
"
NONE;"
ELSE
IF
ONLY
WWR
Plain
Sed
=
WWR
Coag/
Sed
=
"
Y,"
then
"
SETTLE;"
ELSE
IF
ONLY
WWR
Filt
=
"
Y,"
then
"
FILT;"
ELSE
IF
ONLY
WWR
Filt
=
"
Y"
and
WWR
Coag/
Sed
=
"
Y,"
then
"
CONV;"
ELSE
IF
ONLY
WWR
DIS
=
"
Y,"
then
"
DIS;"
ELSE
IF
ONLY
WWR
Coag/
Sed
=
"
Y"
and
WWR
Filt
=
"
Y"
and
WWR
Dis
=

"
Y,"
then
"
CONV_
DIS;"
ELSE
"
OTHER."
Extraction
Plant
Monthly
Plant
Monthly
Sample
Event
Name
Name
of
the
sample
point
represented.
Influent
Samples
=
"
INFLUENT;"
Through­
the­

Plant=
Associated
Unit
Process
Name;
Finished
Water
=
"
FINISH;"
Distribution
System
=
Location
Name.
Extraction
Sample
Event
Sample
Event
Sample
Event
Type
Type
of
location
represented
by
the
sample
point.
Influent
Samples
=
"
INFLUENT;"
Through­
the­
Plant
=
Associated
Unit
Process
Type
Code;
Finished
Water
=
"
FINISH;"
Distribution
System
=
Location
Type.
Extraction
Sample
Event
Sample
Event
Sample
Event
Identification
Unique
code
to
identify
sampling
events
in
a
plant.
Composition
of
Plant
ID,
Sample
Location,
and
Sample
Period:
III
LL
PP.
Extraction
Sample
Event
Sample
Event
Sample
Location
Sequence
Number
Numerical
sequence
of
sampling
location
represented
through­
the­
plant.
FOR
NONBLENDED
SYSTEMS:
Influent
Samples
=

0;
Through­
the­
Plant
=
Associated
Unit
Process
Sequence
Number;
Finished
Water
=
Maximum
Plant
Sequence
+
1;
Distribution
System
Samples:
DSE
=

FW+
1;
Avg1
=
FW+
2;
Avg2
=
FW+
3;
Max
=
FW+
4;

SDS=
FW+
5;
First
Customer=
FW+
6;
FOR
BLENDED
SYSTEMS
ONLY:
Entry
Point
=
200;

Distribution
System
Samples
(
for
m
plants):

DSE(
i)=
EP
+
1
thru
EP
+
m;
Avg(
i)
=
DSE(
max)
+
1
thru
DSE(
max)
+
2*
m;
Max(
i)
=
Avg(
max)
+
1
thru
Avg(
max)
+
m;
SDS(
i)
=
Max(
max)
+
1
thru
Max(
max)

+
m;
First
Customer(
i)
=
SDS(
max)
+
1
thru
SDS(
max)

+
m.
Extraction
Sample
Event
Sample
Event
Sample
Quarter
Assigned
quarter
in
which
samples
are
collected.
If
Sample
Period
<=
3,
then
1;
ELSE
IF
Sample
Period
<=
6,
then
2;
ELSE
IF
Sample
Period
<=
9,.
then
3;
ELSE
IF
Sample
Period
<=
12,
then
4;
ELSE
IF
Sample
Period
<=
15,
then
5;
ELSE
6.
Extraction
Sample
Event
Sample
Event
E­
3
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
Total
HAA5
Sample
Value
Total
concentration
of
the
following
five
haloacetic
acid
species:
monochloroacetic
acid
(
MCAA),
dichloroacetic
acid
(
DCAA),

trichloroacetic
acid
(
TCAA),
monobromoacetic
acid
(
MBAA),
dibromoacetic
acid
(
DBAA).
Step1.
Transform
all
below
detection
results
to
the
MRL
place­
holder
(
e.
g.,
­
999).
Step
2.
Sum
concentrations
(
ug/
L)
of
MCAA,
DCAA,
TCAA,
MBAA,
DBAA
with
data
below
MRL
being
set
equal
to
zero.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
Total
HAA6
Sample
Value
Total
concentration
of
the
following
six
haloacetic
acid
species:
HAA5
+

bromochloroacetic
acid
(
BCAA).
Step1.
Transform
all
below
detection
results
to
the
MRL
place­
holder
(
e.
g.,
­
999).
Step
2.
Sum
concentrations
(
ug/
L)
of
MCAA,
DCAA,
TCAA,
MBAA,
DBAA,

BCAA
with
data
below
MRL
being
set
equal
to
zero.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
Total
HAA9
Sample
Value
Total
concentration
of
the
following
nine
haloacetic
acid
species:
HAA6
+

bromodichloroacetic
acid
(
BDCAA),

dibromochloroacetic
acid
(
DBCAA),

tribromoacetic
acid
(
TBAA).
Step1.
Transform
all
below
detection
results
to
the
MRL
place­
holder
(
e.
g.,
­
999).
Step
2.
Sum
concentrations
(
ug/
L)
of
MCAA,
DCAA,
TCAA,
MBAA,
DBAA,

BCAA,
BDCAA,
DBCAA,
TBAA
with
data
below
MRL
being
set
equal
to
zero.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
Total
Haloacetonitriles
(
HAN4)
Total
concentraction
for
the
following
haloacetonitriles:
dichloroacetonitrile
(
DCNA),

trichloroacetonitrile
(
TCAN),

bromochloroacetonitrile
(
BCAN),

dibromoacetonitrile
(
DBAN).
Step1.
Transform
all
below
detection
results
to
the
MRL
place­
holder
(
e.
g.,
­
999).
Step
2.
Sum
concentrations
(
ug/
L)
of
DCAN,
TCAN,
BCAN,
DBAN
with
data
below
MRL
being
set
equal
to
zero.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
Total
THM
Sample
Value
Total
concentration
of
all
trihalomethane
species
in
sample:
chloroform
(
TCM),

bromodichloromethane
(
BDCM),

dibromochloromethane
(
DBCM),
bromoform
(
TBM).
Step1.
Transform
all
below
detection
results
to
the
MRL
place­
holder
(
e.
g.,
­
999).
Step
2.
Sum
concentrations
(
ug/
L)
of
TCM,
BDCM,
DBCM,
TBM
with
data
below
MRL
being
set
equal
to
zero.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
Chlorine
Dioxide
Residual
Value
Chlorine
dioxide
residual
concentration
corrected
for
an
assigned
MRL
condition.
If
Value
=
0.1
and
the
analyte
comment
<>
"
Null"
or
if
Value
=
0,
then
Value
=­
333;
ELSE
Value
=
Value.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Expert
Chlorine
Dioxide
Residual
Value
Chlorine
dioxide
residual
concentration
corrected
for
the
sample­
specific
detection
limit.
If
Chlorine
Dioxide
Residual
Value
is
­
333,
then
expert
value
determined
manually
replace
the
­
333
with
either
­

999
if
result
is
BDL
or
measured
value
noted
in
comment;
Else,
the
Total
CL2
Residual
Value
remains
the
same.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Free
CL2
Residual
Value
Free
CL2
residual
concentration
corrected
for
an
assigned
MRL
condition.
If
Value
=
0.1
and
the
analyte
comment
<>
"
Null"
or
if
Value
=
0,
then
Value
=­
333;
ELSE
Value
=
Value.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Expert
Free
CL2
Residual
Value
Free
CL2
residual
concentration
corrected
for
the
sample­
specific
detection
limit.
If
Free
CL2
Value
is
­
333,
then
expert
value
determined
manually
replace
the
­
333
with
either
­
999
if
result
is
BDL
or
measured
value
noted
in
comment;
Else,
the
Total
CL2
Residual
Value
remains
the
same.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
E­
4
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
NH3
Sample
Value
NH3
sample
concentration
corrected
for
an
assigned
MRL
condition.
If
Value
=
0.1
and
the
analyte
comment
<>
"
Null"
or
if
Value
=
0,
then
Value
=­
333;
ELSE
Value
=
Value.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Expert
NH3
Sample
Value
NH3
sample
concentration
corrected
for
the
sample­
specific
detection
limit.
If
Ammonia
Sample
Value
is
­
333,
then
expert
value
determined
manually
replace
the
­
333
with
either
­
999
if
result
is
BDL
or
measured
value
noted
in
comment;
Else,

the
Total
CL2
Residual
Value
remains
the
same.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Ozone
Residual
Value
Ozone
residual
concentration
corrected
for
an
assigned
MRL
condition.
If
Value
=
0.1
and
the
analyte
comment
<>
"
Null"
or
if
Value
=
0,
then
Value
=­
333;
ELSE
Value
=
Value.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Expert
Ozone
Residual
Value
Ozone
residual
concentration
corrected
for
the
sample­
specific
detection
limit.
If
Ozone
Residual
Value
is
­
333,
then
expert
value
determined
manually
replace
the
­
333
with
either
­
999
if
result
is
BDL
or
measured
value
noted
in
comment;
Else,

the
Total
CL2
Residual
Value
remains
the
same.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Total
CL2
Residual
Value
Total
CL2
residual
concentration
corrected
for
an
assigned
MRL
condition.
If
Value
=
0.1
and
the
analyte
comment
<>
"
Null"
or
if
Value
=
0,
then
Value
=­
333;
ELSE
Value
=
Value.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Expert
Total
CL2
Residual
Value
Total
CL2
residual
concentration
corrected
for
the
sample­
specific
detection
limit.
If
Total
CL2
Residual
Value
is
­
333,
then
expert
value
determined
manually
replace
the
­
333
with
either
­
999
if
result
is
BDL
or
measured
value
noted
in
comment;
Else,

the
Total
CL2
Residual
Value
remains
the
same.
Extraction
Sample
Event
­

Residuals
Sample
Event
­

Residuals
Sample/
Analyte
Comment
Flag
Identification
flag
for
any
utility
Sample/
Analyte
level
comments.
If
any
sample
or
analyte
has
an
associated
comment
field,
then
1;
ELSE
blank.
Extraction
Sample
Event
Entities
­
Associated
Sample
Event
Entities
­
Associated
Sample/
Analyte
QA
Flag
Identification
flag
for
any
Utility
Sample/
Analyte
Level
QA
Codes
as
"
Q."
If
any
sample
or
analyte
has
an
associated
"
Q"
value
in
the
Utility
Sample
QA
Field,
then
1;
ELSE
blank.
Extraction
Sample
Event
Entities
­
Associated
Sample
Event
Entities
­
Associated
Average
TOC
Sample
Value
Monthly
average
level
of
total
organic
carbon
based
on
duplicate
samples.
Step
1.
Transform
all
below
detection
results
to
numeric
values
equal
to
the
MRL.
Step
2.
Average
the
transformed
values
of
the
duplicate
sample
results.
Step
3.
If
the
average=
MRL,
then
extract
as
a
­
999
value;

ELSE
extract
average
value.
Extraction
Sample
Event
­

WQPs
Sample
Event
­

WQPs
Average
TOX
Sample
Value
Monthly
average
level
of
total
halogenated
organics
based
on
duplicate
samples.
Step
1.
Transform
all
below
detection
results
to
numeric
values
equal
to
the
MRL.
Step
2.
Average
the
transformed
values
of
the
duplicate
sample
results.
Step
3.
If
the
average=
MRL,
then
extract
as
a
­
999
value;

ELSE
extract
average
value.
Extraction
Sample
Event
­

DBPs
Sample
Event
­

DBPs
E­
5
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Calculated
Attribute
Definition
Calculation
Who
Calculates
Where
Calculated
Where
Stored
Average
UV254
Sample
Value
Monthly
average
level
of
UV254
based
on
duplicate
samples.
Step
1.
Transform
all
below
detection
results
to
numeric
values
equal
to
the
MRL.
Step
2.
Average
the
transformed
values
of
the
duplicate
sample
results.
Step
3.
If
the
average=
MRL,
then
extract
as
a
­
999
value;

ELSE
extract
average
value.
Extaction
Sample
Event
­

WQPs
Sample
Event
­

WQPs
Normalization
of
Disinfectant
Additions
Conversion
of
disinfectant
addition
information
into
a
standardized
format.
Normalization
is
performed
according
to
Appendix
F
for
Disinfectant
Chemical
Name,
Dose
Rate,
and
Measurement
Formula.
Extraction
Unit
Process
Unit
Process
Liquid
Volume
Normalize
Liquid
Volume
to
from
cubic
feet
to
gallons
for
ozone
unit
processes.
Multiply
Liquid
Volume
(
gal)
by
7.48
gal/
cuft.
Extraction
Unit
Process
Unit
Process
T10
(
min)
for
ozone
chambers
Estimated
effective
contact
time
for
disinfection,

in
minutes,
for
ozone
chambers.
If
Ozone
Gas
Split
=
0,
then
(
T50
*
0.7);
Else
(
T50
*

0.1).
Extraction
Unit
Process
­
O3
Chamber
Unit
Process
T50
(
min)
for
unit
processes
where
missing
Theoretical
detention
time
for
unit
processes
in
minutes.
If
T50
=
"
Missing,"
then
Unit
Process
Liquid
Volume/(
Flow,
mgd*
694.44,
gpm/
mgd);
ELSE
T50
=

VALUE.
Extraction
Unit
Process
Unit
Process
Normalization
of
Chemical
Feeds
Conversion
of
chemical
feed
information
into
a
standardized
format.
Normalization
is
performed
according
to
Appendix
G
for
Chemical
Feed
Name,
Dose
Rate,
and
Chemical
Formula.
Extraction
Unit
Process
­

Chem
Feed
Unit
Process
­

Chem
Feed
Total
Applied
Ozone
Dose
Total
ozone
dose
applied
within
an
ozone
contactor.
Sum
all
ozone
dosages
for
disinfection
addition
unit
processes
with
sequence
numbers
less
than
the
maximum
sequence
number
of
the
chambers
included
in
the
ozone
contactor
basin
but
less
than
than
the
maximum
sequence
number
for
chambers
in
the
prior
ozone
contactor.
Extraction
O3
Contactor
O3
Contactor
Number
of
Ozone
Chambers
Total
number
of
ozone
contact
chambers
in
a
contact
basin.
Find
the
maximum
and
minimum
sequence
number
for
the
ozone
contact
basin.
Calculate
the
sum
of
chambers
by
[(
MAX
Seq)
­
(
Min
Seq)
+
1].
Extraction
Unit
Process
­
O3
Contactor
Unit
Process
­
O3
Contactor
E­
6
SDC­
0002­
007­
HB­
2011B
April
21,
2000
CHM
NAME
CHEMICAL
FORMULA
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
CACL
CACL
CACL
0.992
mg/
L
CL2
CL2
CL2
#
Cl2/
MGDx8.34
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
100%
Cl2
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
Chlorine
Gas
CL2
1
mg/
L
CL2
CL2
CL2
Cl
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
CL2
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
CL­
2
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
Cl2
(
g)
CL2
1
mg/
L
CL2
CL2
CL2
Cl2
(
gas)
CL2
1
mg/
L
CL2
CL2
CL2
Cl2(
g)
CL2
1
mg/
L
CL2
CL2
CL2
Free
Chlorine
CL2
SOY
1
1
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CL2
MGDx8.34xPPM=
Lbs
of
CL2/
Day
CL2
SOY
1
1
mg/
L
CL2
CL2
SOY
CL2
HOCl
CL2
SOY
1.35
1.35
mg/
L
CL2
mg/
L
CL2
CL2
SOY
CLO2
Cl02
CLO2
CDA
1
1
mg/
L
ClO2
mg/
L
ClO2
CLO2
CLO2
CLO2
ClO2
CLO2
CDA
1
1
mg/
L
ClO2
mg/
L
ClO2
CLO2
CLO2
CLO2
NaClO2
/
Cl2
CLO2
1
mg/
L
CLO2
CLO2
NH3A
MGDx8.34xPPM=
Mg/
Lx.
25=
PPD/
NH3
NH3
NH3A
NH3S
0.834
0.834
0.834
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3A
NH3
NH3
NH3A
NH3S
0.834
0.834
0.834
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3A
NH3
(
anhydrous)
NH3
NH3A
0.834
0.834
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3A
NH3A
NH3
NH3A
0.834
0.834
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
25%
NH4OH
NH3
NH3A
NH3S
0.412
0.412
0.412
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3H
Aqua
Ammonia
NH3
NH3A
NH3S
0.412
0.412
0.412
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3H
NH3(
OH)
NH3
NH3A
0.412
0.412
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
NH30H
NH3
NH3A
0.412
0.412
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
NH3OH
NH3
NH3A
0.412
0.412
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
NH4(
OH)
NH3
NH3A
0.412
0.412
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
NH4OH
NH3
NH3A
0.412
0.412
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3H
NH3H
NH3
NH3A
NH3S
0.778
0.778
0.778
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3H
NH4+
NH3
NH3A
NH3S
0.778
0.778
0.778
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3H
N
NH3
NH3A
NH3S
1
1
1
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3H
NH3­
N
NH3
NH3A
NH3S
1
1
1
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
NH3S
(
NH4)
2SO4
NH3
NH3A
NH3S
0.212
0.212
0.212
mg/
L
N
mg/
L
N
mg/
L
N
NH3_
N
NH3_
N
NH3_
N
O3
03
O3
1
mg/
L
O3
O3
O3
O3
O3
1
mg/
L
O3
O3
SOY
NA0CL
SOY
CL2
0.952
0.952
mg/
L
CL2
mg/
L
CL2
SOY
SOY
SOY
NaClO
SOY
CL2
0.952
0.952
mg/
L
CL2
mg/
L
CL2
SOY
SOY
SOY
NaOCl
SOY
CL2
0.952
0.952
mg/
L
CL2
mg/
L
CL2
SOY
SOY
SOY
NaOCl
@
13%
solution
SOY
CL2
0.952
0.952
mg/
L
CL2
mg/
L
CL2
SOY
SOY
SOY
sodium
hypoclorite
SOY
CL2
0.952
0.952
mg/
L
CL2
mg/
L
CL2
SOY
SOY
SOY
NaOCl
as
Cl2
SOY
CL2
1
1
mg/
L
CL2
mg/
L
CL2
SOY
SOY
CL2
Lbs.
1
CL2
MG/
L
1
Where
more
than
one
alternative
chemical
name
is
shown,
the
chemical
formula
could
apply
to
multiple
types
of
chemicals.
Therefore,
the
normalization
is
performed
based
on
the
chemical
name
identified
by
the
utility
as
shown
in
the
table
below.

Alternative
Chemicals
Multiplication
Factor
Normalized
Chemical
Formula
Normalized
Chemical
Name
F­
7
SDC­
0002­
007­
HB­
2011B
April
21,
2000
CHM
NAME
CHEMICAL
FORMULA
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
ALT1
ALT2
ALT3
Where
more
than
one
alternative
chemical
name
is
shown,
the
chemical
formula
could
apply
to
multiple
types
of
chemicals.
Therefore,
the
normalization
is
performed
based
on
the
chemical
name
identified
by
the
utility
as
shown
in
the
table
below.

Alternative
Chemicals
Multiplication
Factor
Normalized
Chemical
Formula
Normalized
Chemical
Name
CLO2
MGDx8.34xppmx.
511x3785/
1440
1
F­
8
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Number
Chem
Formula
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
1
A12(
SO4)
3.49.6H2O
ALUM
OTH
0.046
0.046
mg/
L
Al
mg/
L
Al
ALUM
ALUM
2
Al2(
SO4)
3:
49.6H2O
ALUM
OTH
0.046
0.046
mg/
L
Al
mg/
L
Al
ALUM
ALUM
3
Al2(
SO4)
3.18H2O
ALUM
OTH
0.081
0.081
mg/
L
Al
mg/
L
Al
ALUM
ALUM
4
Al2(
S04)
3­
16H20
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
5
Al2(
SO4)
3
.
16
H2O
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
6
Al2(
SO4)
3*
16H2O
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
7
Al2(
SO4)
3.16H2O
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
8
Al2(
SO4)
3­
16H2O
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
9
AL2S04:
16H20
ALUM
OTH
0.086
0.086
mg/
L
Al
mg/
L
Al
ALUM
ALUM
10
AL2(
SO4)
3*
14
H2O
+
POLYMER
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
11
(
Al)
2(
SO4)
3.14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
12
(
Al2SO4)
3*
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
13
(
Al2SO4)
3.14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
14
Al2
(
SO4)
3
.
14
H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
15
AL2(
S04)
3.14H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
16
Al2(
S04)
3.14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
17
Al2(
SO4)
3
14
H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
18
Al2(
SO4)
3
*
14
H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
19
AL2(
SO4)
3
.
14H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
20
Al2(
SO4)
3
.
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
21
al2(
so4)
3
.14h2o
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
22
AL2(
SO4)
3
14H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
23
Al2(
SO4)
3
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
24
Al2(
SO4)
3
14H2O
Aqueous
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
25
Al2(
so4)
3
x
14
(
H2O)
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
26
AL2(
SO4)
3(
14
H2O)
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
27
AL2(
SO4)
3*
14
H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
28
Al2(
SO4)
3*
14H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
29
Al2(
SO4)
3*
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
30
Al2(
SO4)
3*
H2O
(
14
H2O)
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
31
AL2(
SO4)
3.14H20
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
32
Al2(
SO4)
3.14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
33
Al2(
SO4)
3.14H2O
48.5%
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
34
Al2(
SO4)
3.14H2O
48.5%
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
35
Al2(
SO4)
3­
14(
H2O)
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
36
Al2(
SO4)
3­
14(
H2O)
+
Floc
Agent
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
37
AL2(
SO4)
3­
14.3H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
38
Al2(
SO4)
3­
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
39
Al2SO4*
14H2O
ALUM
OTH
0.091
0.091
mg/
L
Al
mg/
L
Al
ALUM
ALUM
40
Al2(
SO4)
3­
4H2O
ALUM
OTH
0.13
0.13
mg/
L
Al
mg/
L
Al
ALUM
ALUM
41
Al2(
SO4)
x
H2O
ALUM
OTH
0.15
0.15
mg/
L
Al
mg/
L
Al
ALUM
ALUM
42
AL2(
SO4)
3*
H20
+
POLYMER
ALUM
OTH
0.15
0.15
mg/
L
Al
mg/
L
Al
ALUM
ALUM
43
Al2(
SO)
4
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
44
AL2(
SO4)
3
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
45
Al2(
SO4)
3
(
dry
wt
per
gal)
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
46
AL2S04
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
47
AL2SO4
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
48
ALSO4
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
49
ALUM
ALUM
OTH
0.16
0.16
mg/
L
Al
mg/
L
Al
ALUM
ALUM
50
8%
AL203
ALUM
OTH
0.63
0.63
mg/
L
Al
mg/
L
Al
ALUM
ALUM
51
Al2O3
ALUM
OTH
0.63
0.63
mg/
L
Al
mg/
L
Al
ALUM
ALUM
52
Al
ALUM
OTH
1
1
mg/
L
Al
mg/
L
Al
ALUM
ALUM
1
CaCO3
CAOH
CAO
OTH
0.74
0.74
0.74
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
2
CaOH2
as
mg/
L
CaCO3
CAOH
CAO
OTH
0.74
0.74
0.74
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
3
Ca
OH2
CAOH
CAO
OTH
1
1
1
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
4
Ca(
OH)
2
CAOH
CAO
OTH
1
1
1
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
5
CaOH
CAOH
CAO
OTH
1
1
1
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
6
CaOH2
CAOH
CAO
OTH
1
1
1
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
7
as
CaO
CAOH
CAO
OTH
1.32
1.32
1.32
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
8
CaO
CAOH
CAO
OTH
1.32
1.32
1.32
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
9
CaO
QuickLime
CAOH
CAO
OTH
1.32
1.32
1.32
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
10
Lime
CAOH
CAO
OTH
1.32
1.32
1.32
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
mg/
L
Ca(
OH)
2
CAOH
CAOH
CAOH
Where
more
than
one
alternative
chemical
name
is
shown,
the
chemical
formula
could
apply
to
multiple
types
of
chemicals.
Therefore,
the
normalization
is
performed
based
on
the
chemical
name
identified
by
the
utility
as
shown
in
the
table
below.

Chemical
Name
Alternatives
Multiplication
Factors
for
Normalization
Normalized
Units
Normalized
Chemical
Names
G­
9
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Number
Chem
Formula
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
Where
more
than
one
alternative
chemical
name
is
shown,
the
chemical
formula
could
apply
to
multiple
types
of
chemicals.
Therefore,
the
normalization
is
performed
based
on
the
chemical
name
identified
by
the
utility
as
shown
in
the
table
below.

Chemical
Name
Alternatives
Multiplication
Factors
for
Normalization
Normalized
Units
Normalized
Chemical
Names
1
CL2
OTH
1
mg/
L
CL2
CL2
1
CO2
CO2
OTH
1
1
mg/
L
CO2
mg/
L
CO2
CO2
CO2
1
CuSO4*
5H2O
OTH
0.64
0.64
mg/
L
Cu(
SO4)
mg/
L
Cu(
SO4)
CUS
2
CuSO
OTH
1
1
mg/
L
Cu(
SO4)
mg/
L
Cu(
SO4)
CUS
3
CuSO4
OTH
1
1
mg/
L
Cu(
SO4)
mg/
L
Cu(
SO4)
CUS
1
42%
FeCl3.6H2O
FEC
OTH
0.21
0.21
mg/
L
Fe
mg/
L
Fe
IRON
IRON
2
FeCl2*
6H2O
FEC
OTH
0.21
0.21
mg/
L
Fe
mg/
L
Fe
IRON
IRON
3
FeCl3.6H20
FEC
OTH
0.21
0.21
mg/
L
Fe
mg/
L
Fe
IRON
IRON
4
FeCl3.6H2O
FEC
OTH
0.21
0.21
mg/
L
Fe
mg/
L
Fe
IRON
IRON
5
Cl2Fe
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
6
Fe
Cl3
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
7
FEC
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
8
FEC
dry
wt.
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
9
FeCl
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
10
FECL2
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
11
FeCl3
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
12
FeCl3
30
%
Solu
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
13
FeCl3,
@
40%
solution
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
14
FeCl3,
32­
45%
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
15
Ferric
Chloride
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
16
Ferric
Chloride
­
dry
wt
FEC
OTH
0.34
0.34
mg/
L
Fe
mg/
L
Fe
IRON
IRON
17
Fe
FEC
FES
FOS
OTH
1
1
1
1
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
IRON
IRON
IRON
IRON
18
FE3
FEC
FES
FOS
OTH
1
1
1
1
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
IRON
IRON
IRON
IRON
1
Fe5(
SO4)
7OH
60%
Solution
FES
OTH
0.29
0.29
mg/
L
Fe
mg/
L
Fe
IRON
IRON
2
Fe5(
SO4)
7OH,
60%
Solution
FES
OTH
0.29
0.29
mg/
L
Fe
mg/
L
Fe
IRON
IRON
3
Fe2(
SO4)
3.9H2O
FES
OTH
0.20
0.20
mg/
L
Fe
mg/
L
Fe
IRON
IRON
4
(
FE2SO4)
3
FES
OTH
0.28
0.28
mg/
L
Fe
mg/
L
Fe
IRON
IRON
5
Fe2(
SO4)
3
FES
OTH
0.28
0.28
mg/
L
Fe
mg/
L
Fe
IRON
IRON
6
FES
FES
OTH
0.28
0.28
mg/
L
Fe
mg/
L
Fe
IRON
IRON
7
FeSO4.7H2O
FES
FOS
OTH
0.20
0.20
0.20
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
IRON
IRON
IRON
8
FESO4
FES
FOS
OTH
0.37
0.37
0.37
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
IRON
IRON
IRON
9
FOS
FES
FOS
OTH
0.37
0.37
0.37
mg/
L
Fe
mg/
L
Fe
mg/
L
Fe
IRON
IRON
IRON
1
HCl
OTH
1
mg/
L
HCl
HCL
1
23%
H2SiF6
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
2
23%
H2SiF6
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
3
F2H2Si
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
4
H2
Si
F6
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
5
h2fs6
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
6
H2SiF6
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
7
H2SiF6
(
25%
solution)
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
8
H2SiF6
25%
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
9
H2SiF6,
23%
solution
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
10
H2SiF76
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
11
HFS
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
12
HSF
HFS
OTH
0.79
0.79
mg/
L
F
mg/
L
F
HFS
HFS
13
24%
as
H2SiF6
as
F
HFS
OTH
1
1
mg/
L
F
mg/
L
F
HFS
HFS
14
as
F
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
15
F
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
16
F­
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
17
Fl
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
18
Fl­
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
19
Fluoride
HFS
SOF
OTH
1
1
1
mg/
L
F
mg/
L
F
mg/
L
F
HFS
SOF
HFS
20
H2SiF6
(
25%
soln)
ppm
as
F
HFS
OTH
1
1
mg/
L
F
mg/
L
F
HFS
HFS
1
H2O2
OTH
1
mg/
L
H2O2
HPX
2
Peroxide
OTH
1
mg/
L
H2O2
HPX
1
NH3
OTH
0.82
mg/
L
N
NH3
1
ActiCarb
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
2
C
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
3
Calgon
­
WPH
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
4
Carbon
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
5
CARBON
93%
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
6
Norit
Americas
Hydrodarco
B
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
G­
10
SDC­
0002­
007­
HB­
2011B
April
21,
2000
Number
Chem
Formula
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
ALT1
ALT2
ALT3
ALT4
Where
more
than
one
alternative
chemical
name
is
shown,
the
chemical
formula
could
apply
to
multiple
types
of
chemicals.
Therefore,
the
normalization
is
performed
based
on
the
chemical
name
identified
by
the
utility
as
shown
in
the
table
below.

Chemical
Name
Alternatives
Multiplication
Factors
for
Normalization
Normalized
Units
Normalized
Chemical
Names
7
PAC
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
8
PAC
(
Calgon)
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
9
PAC,
3
parts
per
million
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
10
PAC,
3.5
parts
per
billion
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
11
pac,
5
parts
per
Billion
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
12
PAC,
7
parts
per
billion
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
13
PPC
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
14
TS
PAC
OTH
1
1
mg/
L
C
mg/
L
C
PAC
PAC
1
50%
KOH
PHX
OTH
1
1
mg/
L
KOH
mg/
L
KOH
KOH
KOH
1
KMn04
PPM
OTH
1
1
mg/
L
KMnO4
mg/
L
KMnO4
PPM
PPM
2
KMnO4
PPM
OTH
1
1
mg/
L
KMnO4
mg/
L
KMnO4
PPM
PPM
3
KMnO4
powder
PPM
OTH
1
1
mg/
L
KMnO4
mg/
L
KMnO5
PPM
PPM
4
PPM
PPM
OTH
1
1
mg/
L
KMnO4
mg/
L
KMnO6
PPM
PPM
1
SO2
OTH
1
mg/
L
SO2
SO2
1
Na2(
CO3)
SOC
OTH
0.57
0.57
mg/
L
CO3
mg/
L
CO3
SOC
SOC
2
Na2C03
SOC
OTH
0.57
0.57
mg/
L
CO3
mg/
L
CO3
SOC
SOC
3
NA2CO3
SOC
OTH
0.57
0.57
mg/
L
CO3
mg/
L
CO3
SOC
SOC
4
NaCO3
SOC
OTH
0.57
0.57
mg/
L
CO3
mg/
L
CO3
SOC
SOC
5
soc
SOC
OTH
0.57
0.57
mg/
L
CO3
mg/
L
CO3
SOC
SOC
1
NaF
SOF
OTH
0.45
0.45
mg/
L
F
mg/
L
F
SOF
SOF
2
Na2SiF5
SOF
OTH
0.61
0.61
mg/
L
F
mg/
L
F
SOF
SOF
3
Na2SiF6
SOF
OTH
0.61
0.61
mg/
L
F
mg/
L
F
SOF
SOF
4
NaSiF6
SOF
OTH
0.61
0.61
mg/
L
F
mg/
L
F
SOF
SOF
5
SOF
SOF
OTH
1
1
mg/
L
F
mg/
L
F
SOF
SOF
1
25%
NaOH
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
2
50%
NaOH
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
3
NaHO
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
4
NaOH
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
5
NaOH
(
50%)
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
6
NaOH
­
50%
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
7
NAOH
(
50%)
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
8
NaOH(
20%)
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
9
NAOH,
50%
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
10
SOH
SOH
OTH
1
1
mg/
L
NaOH
mg/
L
NaOH
SOH
SOH
1
NaOCl
OTH
0.95
mg/
L
CL2
SOY
1
H2S04
SUA
OTH
1
1
mg/
L
H2(
SO4)
mg/
L
H2(
SO4)
SUA
SUA
2
H2SO4
SUA
OTH
1
1
mg/
L
H2(
SO4)
mg/
L
H2(
SO4)
SUA
SUA
3
SUA
SUA
OTH
1
1
mg/
L
H2(
SO4)
mg/
L
H2(
SO4)
SUA
SUA
1
This
table
converts
all
metal
coagulants
into
the
mg/
L
of
metal
(
Aluminum
or
Iron)
added
regardless
of
coagulant
type.
This
is
done
to
minimize
the
number
of
normalization
calculations
required.

NOTE:
For
the
following
units,
assume
the
proper
units
are
provided
in
the
normalized
units
appropriate
to
the
chemical
name
indicated.

Lbs.

mg/
l
MGD
x
PPM
x
8.34
=
Lbs/
Day
Mgdx8.34xppm/
wtx3785/
1440
none
NONE
GIVEN
not
known
ppm
on
dry
wt
basis
(
33%)

PPM,
1
part
per
million
product
proprietary
Stuff
visual
as
Product
PPM
(
WT/
WT)
G­
11