|
The
schedule of sampling, analysis, and observations shall be that given as
Table I.
I,
Lawrence P. Kolb, Assistant Executive Officer, hereby certify that the
foregoing Self-Monitoring Program:
- Has been developed
in accordance with the procedure set forth in the Regional Board's Resolution
No. 73-16 in order to obtain data and document compliance with waste
discharge requirements established in Regional Board Order No.
- Is effective on
March 15, 2000.
- Maybe reviewed
at any time subsequent to the effective date upon written notice from
the Executive Officer or request from the dischargers and revisions
will be ordered by the Executive Officer.
|
Attachments:
Table I and footnotes
Part A, August 1993
Table
I
SCHEDULE FOR SAMPLING, MEASUREMENTS,
AND ANALYSIS (1)
|
Sampling Station
|
|
A-001
|
E-001
|
E-001D
|
All
OV Station
|
All
C Station
|
|
TYPE OF SAMPLE
|
Unit
|
C-24
|
G(2)
|
C-24(2)
|
Cont
|
G
|
C-24
|
|
|
|
Flow Rate
|
mgd
|
D
|
|
|
D
|
|
|
|
|
|
BOD, 5-day,
20OC
|
mg/l
& kg/day
|
W
|
|
W
|
|
|
|
|
|
|
Chlorine Residual
& Dosage (3)
|
mg/l
& kg/day
|
|
2H
or Cont.
|
2H
or Cont.
|
|
|
|
Total Suspended
Solids
|
mg/l
& kg/day
|
2/W
|
|
2/W
|
|
|
|
|
|
|
Oil & Grease
(4)
|
mg/l
& kg/day
|
Q
|
Q
|
|
|
|
|
|
|
|
Settleable Matter
|
mg/l-hr
|
|
|
2/W
|
|
|
|
|
|
|
Turbidity
|
NTU
|
|
|
D
|
|
|
|
|
|
|
Fish Toxicity
96-hr. LC 50 (5)
|
Tu
|
|
|
2M
|
|
|
|
|
|
|
Ammonia Nitrogen
& Un-ionized Ammonia (6)
|
mg/l
& kg/day
|
|
|
2M
|
|
|
|
|
Y
|
|
pH (6)
|
pH
units
|
|
D
|
2M
|
|
|
|
|
Y
|
|
Dissolved Oxygen
(6)
|
mg/l
& % saturation
|
|
D
|
2M
|
|
|
|
|
Y
|
|
Temperature
(6)
|
OC
|
|
D
|
2M
|
|
|
|
|
Y
|
|
Coliform (Total
or Fecal)
|
MPN/100
ml
|
|
|
|
|
W
|
|
|
Y
|
|
Salinity
|
ppt
|
|
|
|
|
|
|
|
Y
|
|
Sulfides
(If DO<5.0
mg/l) Total & Dissolved
|
mg/l
|
|
D
|
|
|
|
|
|
|
|
All Applicable
Standard Observations
|
|
|
D
|
|
|
|
|
E
|
Y
|
|
Daily Rainfall
|
|
|
|
|
|
|
|
|
D
|
|
Dewatered Sludge
|
|
(7)
|
|
Arsenic
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Cadmium
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Chromium (Hexavalent)
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Chromium (Trivalent)
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Copper
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Lead
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
Table I (Continued)
SCHEDULE FOR SAMPLING, MEASUREMENTS,
AND ANALYSIS (1)
|
Sampling Station
|
|
A-001
|
E-001
|
E-001D
|
All
OV Station
|
All
C Station
|
|
TYPE OF SAMPLE
|
Unit
|
C-24
|
G(2)
|
C-24(2)
|
Cont
|
G
|
C-24
|
O
|
O
|
|
Mercury
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Nickel
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Selenium
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Silver
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Zinc
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Cyanide
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Phenolic Compounds
(non-chlorinated)
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Chlorinated
Phenolics
|
mg/l
|
|
|
Q
(8)
|
|
|
|
|
|
|
Endosulfan
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Endrin
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
HCH*
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Radioactivity
|
|
|
|
Y
(8)
|
|
|
|
|
|
|
Acrolein
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Antimony
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Bis(2-chloroethoxy)
methane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Bis (2-chloroisopropyl)
ether
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Chlorobenzene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Di-n-butyl phthalate
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Dichlorobenzenes
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,1-dichloroethylene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Diethyl phthalate
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Dimethyl phthalate
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
4,6-dinitro-2-methylphenol
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
2,4-dinitrophenol
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Ethylbenzene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Fluoranthene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Hexachlorocyclopentadiene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Isophorone
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Nitrobenzene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Thallium
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Toluene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,1,2,2-tetrachloroethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Tributyltin
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,1,1-trichloroethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,1,2-trichloroethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
Table I (Continued)
SCHEDULE FOR SAMPLING, MEASUREMENTS,
AND ANALYSIS (1)
|
Sampling Station
|
|
A-001
|
E-001
|
E-001D
|
All
OV Station
|
All
C Station
|
|
TYPE OF SAMPLE
|
Unit
|
C-24
|
G(2)
|
C-24(2)
|
Cont
|
G
|
C-24
|
O
|
O
|
|
Acrylonitrile
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Aldrin
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Benzene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Benzidine
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Beryllium
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Bis(2-chloroethyl)
ether
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Bis(2-ethylhexyl)
phthalate
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Carbon Tetrachloride
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Chlordane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Chloroform
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
DDT
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,4-dichlorobenzene
|
|
|
|
Y
(8)
|
|
|
|
|
|
|
3,3-dichlorobenzidine
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,2-dichloroethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Dichloromethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,3-dichloropropene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Dieldrin
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
2,4-dinitrotoluene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
1,2-diphenylhydrazine
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Halomethanes
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Heptachlor
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Hexachlorobenzene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Hexachlorobutadiene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Hexachloroethane
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
N-nitrosodimethylamine
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
N-nitrosodiphenylamine
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
PAHs
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
PCBs
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
TCDD equivalents
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Tetrachloroethylene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Toxaphene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Trichloroethylene
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
2,4,6-trichlorophenol
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
|
Vinyl chloride
|
mg/l
|
|
|
Y
(8)
|
|
|
|
|
|
LEGEND FOR TABLE
|
TYPE
OF SAMPLES
|
TYPE
OF STATIONS
|
|
G
|
=
|
Grab sample
|
A
|
=
|
Treatment facility
influent stations
|
|
C-24
|
=
|
Composite sample
24-hr
|
E
|
=
|
Waste effluent
stations
|
|
Cont.
|
=
|
Continuous sampling
|
C
|
=
|
Receiving water
stations
|
|
O
|
=
|
Observation
|
P
|
=
|
Treatment facilities
perimeter stations
|
|
|
|
OV
|
=
|
Overflows and
bypasses
|
|
FREQUENCY
OF SAMPLING
|
|
E
|
=
|
Each occurrence
|
2/H
|
=
|
Twice per hour
|
2H
|
=
|
Every 2 hours
|
|
H
|
=
|
Once each hour
|
2/W
|
=
|
2 days per week
|
2D
|
=
|
Every 2 days
|
|
D
|
=
|
Once each day
|
5/W
|
=
|
5 days per week
|
2W
|
=
|
Every 2 weeks
|
|
W
|
=
|
Once each week
|
2/M
|
=
|
2 days per month
|
2M
|
=
|
Every 2 months
|
|
M
|
=
|
Once each month
|
Y
|
=
|
Once a year
|
|
|
|
|
2/Y
|
=
|
Once in March
and once in September
|
|
Cont.
|
=
|
Continuous
|
|
Q
|
=
|
Quarterly, once
in March, June September and December
|
FOOTNOTES
- During any day
when bypassing occurs from any treatment unit(s) in the plant or from
the outfall, the monitoring program for the effluent and any near shore
discharge shall include the following in addition to the above schedule
for sampling, measurement and analyses:
- Composite sample
for BOD and Total Suspended Solids (Influent and Effluent, for the
duration of the bypass or 24 hours, whichever is shorter.)
- Grab samples
for Total Coliform, Settleable Matter, Oil and Grease, and Chlorine
Residual (continuous or every two hours.)
- Continuous monitoring
of flow.
- Grab samples shall
be taken on day(s) of composite sampling.
- Data shall be reported
using forms provided or approved equivalent. Chlorine residual analyzers
shall be calibrated against grab samples as frequently as necessary
to maintain accurate control and reliable operation. If an effluent
violation is detected, grab samples shall be taken every 30 minutes
until compliance is achieved.
- In the event that
sampling for oil and grease once every two weeks or less frequently
shows an apparent violation of the waste discharge permit monthly average
limitation (considering the result of one or two day’s sampling as a
monthly average), then the sampling frequency shall be increased to
weekly so that a true monthly average can be computed and compliance
can be determined.
- Fish toxicity shall
be determined using 96-hour static renewal fish bioassays with one of
the following test species: three-spined stickleback, rainbow trout
or fathead minnow.
- Dissolved oxygen,
pH, and temperature shall be tested for on the same composite sample(s)
used for the bioassay(s) at the start of the bioassay(s) and at intervals
of 24, 48, 72, and 96 hours after starting the bioassay(s). Ammonia
nitrogen and unionized ammonia shall be tested for on the same composite
sample(s) used for the bioassay(s) at the start of the bioassay test(s).
The method of calculating unionized ammonia shall be indicated.
- Daily records shall
be kept of the quantity and solids contents of dewatered sludge disposed
of and the location of disposal.
- If any samples
are in violation of effluent limitations or in exceedence of the performance
goals, sampling shall be increased for that parameter to weekly until
compliance or the performance goal is demonstrated in two successive
samples.
|