Regional drinking water quality monitoring program: long-term monitoring of water quality in select canals, reservoirs, and treatment plants of the greater Phoenix, Arizona metropolitan area drinking water system, ongoing since 1998
Publication date: 2020-08-04
Author(s):
- Peter Fox, Arizona State University
- Morteza Abbaszadegan, Arizona State University
- Paul Westerhoff
- Milton Sommerfeld
Abstract:
Regional Drinking Water Quality Monitoring Program
==================================================
Arizona Statue University (ASU) has been working with regional water providers
(Salt River Project (SRP), Central Arizona Project (CAP)) and metropolitan
Phoenix cities since 1998 on algae-related issues affecting drinking water
supplies, treatment, and distribution. The results have improved the
understanding of taste and odor (T&O) occurrence, control, and treatment,
improved the understanding of dissolved organic and algae dynamics, and
initiated a forum to discuss and address regional water quality issues. The
monitoring benefits local Water Treatment Plants (WTPs) by optimizing ongoing
operations (i.e., reducing operating costs), improving the quality of municipal
water for consumers, facilitating long-term water quality planning, and
providing information on potentially future-regulated compounds. ASU has been
monitoring water quality in terminal reservoirs (Lake Pleasant, Saguaro Lake,
and Bartlett Lake) continuously from 1998 to the present for algae-related
constituents (taste and odors, and more recently metals from the upper
reservoirs), nutrients, and disinfection by-product precursors (i.e., total and
dissolved organic carbon and organic nitrogen). Additional monitoring has been
conducted in the SRP and CAP canal systems and in water treatment plants in
Phoenix, Tempe and Peoria. During this work the Valley has been in a prolonged
drought and recently one above average wet year, and this data provides
important baseline data for development of new or expanded WTPs and management
of existing WTPs in the future. The current work has improved the understanding
of T&O sources and treatment, but additional research and monitoring into the
future is necessary.
Reservoir monitoring is conducted once per month at Bartlett Lake, Saguaro
Lake, and Lake Pleasant, and quarterly at Roosevelt, Apache, and Canyon Lakes.
Samples are depth integrated in the epilimnion and hypolimnion. CAP will
collect samples from Lake Pleasant. SRP will collect samples from Bartlett,
Saguaro, Roosevelt, Apache, and Canyon Lakes. Field measurements for
temperature with depth will also be collected. River samples (Salt River below
Saguaro Lake @ Blue Point Bridge and Verde River at the Beeline Highway) will
be collected once per month. Samples will be analyzed for carbon (TOC/DOC),
total nitrogen, total phosphorous, arsenic, conductance and T&O compounds (MIB,
Geosmin, Cyclocitrol). The purpose of the lake sampling is to provide early
warning information on potentially large changes in water quality – due to
algae production, lake destratification, and forest fire or other runoff
events. Additional monthly sampling will be coordinated with USGS (Salt River
above Roosevelt, Verde River at Tangle) and CAP (Lake Havasu).
Canal monitoring is conducted once per month (January through June), and twice
per month as needed during periods of higher T&O production (i.e.,
July-December). Field measurements for temperature and pH will be made.
Sampling will include the CAP, Arizona, and South canals at multiple locations.
Monthly samples will be analyzed for carbon (TOC/DOC), SUVA/UV254, total
dissolved nitrogen, microbes, conductance, and T&O compounds (MIB and Geosmin).
Bi-weekly samples will be analyzed only for T&O compounds. The purpose of the
canal sampling is to identify hot-spots of T&O production and to make
recommendations to the cities/SRP/CAP to perform some type of treatment
(brushing, copper, etc.). Additional canal sampling will be scheduled to
further identify canal hot spots or to provide more frequent process control
information.
WTP raw and finished water is collected once per month (January through June),
and twice per month as needed during periods of higher T&O production (e.g.,
July-December). WTP sampling will be conducted at two Tempe WTPs, one Peoria
WTP, Glendale WTPs and other selected WTPs. Monthly samples will be analyzed
for carbon (TOC/DOC), SUVA/UV254, total dissolved nitrogen, microbes,
conductance, and T&O compounds (MIB and Geosmin). Bi-weekly samples will be
analyzed only for T&O compounds. The purpose of the WTP sampling is to provide
continued evaluation of water quality produced at the WTPs.
Keywords:
urban,
dissolved organic carbon,
chlorophyll,
nutrients,
total phosphorus,
total nitrogen,
total dissolved nitrogen,
water properties,
water quality water and fluxes,
disturbance patterns,
movement of organic matter,
movement of inorganic matter total dissolved phosphorus,
geosmin,
canal,
water treatment cap lter,
cap,
caplter,
central arizona phoenix long term ecological research,
arizona,
az,
arid land
Temporal Coverage:
1999-08-16 to 2020-07-23
Geographic Coverage:
Geographic Description: canals, water treatment plants, and reservoirs in the greater phoenix metropolitan area
Bounding Coordinates:
Longitude:-111.125 to -111.1235
Latitude:33.49 to 33.2917
Contact:
Information Manager, Central Arizona–Phoenix LTER,
Arizona State University,Global Institute of Sustainability,Tempe
caplter.data@asu.edu
Methods used in producing this dataset:
Show
Regional Water Quality Sampling
===============================
Overview
--------
Grab water samples were collected for analysis from canals and water
treatment plants in headspace-free, amber glass containers. Water
samples for metals analysis were collected in centrifuge tubes and
acidified with nitric acid for stability. Lake samples were obtained
from the epilimnion and hypolimnion by way of a Kemmerer sampler. All
samples were kept on ice in the field and stored at 4 degrees Celsius
until analyzed. Nutrient samples that could not be analyzed within 24
hours were frozen. Field measurements for dissolved oxygen, pH, and
temperature were made using a portable meter. Water clarity for lake
samples was measured using a Secchi Disk. Taste and odor compounds were
measured using solid phase micro extraction and injected onto a
GC-MS/MS. Total nutrients were obtained by way of persulfate digestion
and then analysis on a continuous flow colorimetric analyzer. Metals
data were obtained by ICP-MS.
Purpose
-------
The regional water quality sampling project began in 1999 with an EPA
order for various municipalities in the Phoenix metropolitan area to
address taste and odor issues that were plaguing the regional water
supply. The compounds of concern were identified as 2-methylisoborneol
(MIB) which causes as musty odor, and Geosmin which causes an earthy
taste. Both compounds are released by algae that grows in the reservoirs
and canals that compose the region’s surface water supply, especially
during summer when abundant sunshine and warm temperatures promote algal
blooms. Complaints from water utility users were so numerous that the
issue had to be addressed. Although these compounds do not cause any
health problems, they create foul odor and taste which causes users to
lose faith in their water utilities and question the reliability of the
treatment process. Both chemicals can be detected in concentrations as
low as 10 ng/L and during peak summer algal blooms this concentration is
regularly exceeded.
The project has been ongoing since 1999, providing valuable data to the
region’s water utilities about the water supply. The project data has
been used in a variety of other projects examining topics ranging from
disinfection by-product formation to invasive species infestation.
Initially managed by the Westerhoff Group at Arizona State University,
today the project is run by Dr. Peter Fox and Dr. Morteza Abbaszadegan.
What Parameters Do We Test?
---------------------------
As part of the Regional Water Quality Sampling Project the following
tests are performed:
- UV254 Absorbance to look for natural organic matter
- DOC (Dissolved Organic Carbon)
- E. coli and fecal coliform count
- Mycobacterium count
- TDN (Total Dissolved Nitrogen)
- MIB (Methyl Isoborneol) and Geosmin
- Turbidity and Conductivity
- ICPMS to look for trace metals. This is done during quarterly
sampling.
- Dissolved Oxygen and Temperature
Sampling Locations
------------------
Here are written descriptions of the location of each site and anything
else you should know about them:
- PIMA (AZ Canal at Pima Road) – Located at the canal crossing with
Pima Road 1 mile north of McDonald Drive on the west side of the
road near the bridge. There is a pull out near the golf course.
- 56th- (AZ Canal at 56th Street) – Located at the northeast corner of
56th St. and Indian School Road. Take the sample near the pipe.
- CENT (AZ Canal at Central Avenue) – Located at Central Avenue and
Orchid Lane (north of Northern Ave 2 miles). There is a pull off for
the bike path on the west side of the road.
- UH IN/OUT (Union Hills WTP Inlet and Treated)- Deer Valley Road and
21st St. (West of Cave Creek Road). Take In sample from Raw Water
Influent tap, take Out sample from Ent Point Distribution System
tap, both located in the operators lab in Building 9.
- AN IN/OUT (Anthem WTP Inlet and Treated) – Located at Gavilan Peak
Pkwy and King Drive (off Daisy Mountain Dr. Exit of I 17). Influent
sample taken from raw water screen. Effluent sample taken from the
permeate room.
- R3 (Waddell Canal) – Located off Carefree Highway Rt. 74 exit of I
17 west of Lake Pleasant Parkway. From Highway 74 take a left onto
Lake Pleasant Parkway and then turn right onto Old Highway 74 near
the glider school. The site is on the right hand side of the road
before the crossing.
- GR IN/OUT (Greenway WTP Inlet and Treated) – Located at 75th Avenue
and Greenway Road. Take In sample from Raw Water, take Out sample
from Filt Eff. Be sure to collect this sample by 10 AM to avoid
arriving while the system is down (they flush on Monday mornings
around 11 AM).
- GL IN/OUT (Glendale WTP Inlet and Treated) – Located at Cholla
Street and 49th Avenue. Take In sample from Raw Influent, take Out
sample from BVS, both in the operators lab.
- NP IN/OUT (Tempe North WTP Inlet and Treated) – Located at 68th
Street and Marigold Lane, take the inlet sample from the canal
flowing into the treatment plant and the effluent sample from the
blue pipe located near the canal.
- SPT IN/OUT (Tempe South WTP Inlet and Treated) – Located Off of 101
south of Guadalupe. Take the samples from the operators lab.
- CH IN/OUT (Chandler WTP Inlet and Treated) – Located off of Pecos
Road and 124th St. Take the samples from the operators lab.
- MOC (Middle of Consolidated Canal) – Located at Lindsay Road north
of Juniper Avenue. There is a pull off of Lindsay Road on the Right
Side where the canal crosses the road.
- HTC (Head of Tempe Canal) - Located east of Mesa Dr. and Brown Road.
Turn onto the canal service road and take the sample midway along
the canal.
- HOC (Head of Consolidated Canal) - Located West of Horne and north
of Brown Road. Take the sample just past the turn in the canal.
- R10 (Salt River at Blue Pt. Bridge) – This sample is taken at the
Blue Point Recreation Site on Bush Highway (east of Usery Pass Rd.)
- R11 (CAP Canal at Cross Connect)- Bush Highway and Granite Reef Dam
Road. Use your Key to open this gate.
- SOCA (South Canal below CAP Cross Connect) – Located in the Granite
Reef area at the vehicle bridge over the South Canal before crossing
the wash. You will need Jeff to unlock the gate to get access to
this site.
- R12 (AZ Canal Above CAP Cross-Connect)- Granite Reef area, just west
of waterfall area with high voltage signs at guard rail (just thru
gate). You will need Jeff to unlock the gate to get access to this
site.
- R13 (AZ Canal Below CAP Cross-Connect) - Granite Reef area, boat
launch ramp area west of R12. You will need Jeff to unlock the gate
to get access to this site.
- HWY 87 (AZ Canal at Highway 87) - Located on canal service road east
of HWY 87 at boat ramp east of val vista drive. You will need Jeff
to unlock the gate to get access to this site.
- R20- Pick up from USGS (SE-corner 52nd St. and University) monthly
- R25 (Verde River at Beeline Highway) - Verde River north of HWY 87
east of Fort McDowell Rd. Watch out for the pitbull and the cows.
- HAV/R2A/R2B/SGPS/MTO - Pick up monthly from CAP (7th St. N of
Pinnacle Peak Road)
- R6A/R6B/R9A/R9A-Dup/R9B – Pick up Monthly from GWC 673 Cold Room.
Marisa Collects these.
- ISTB4- Take a sample from the tap in the sink next to bench
- ROOS/APA/CAN- Pick up from Marisa in GWC 673 cold room (quarterly
samples)
Preparation
-----------
### Ashing Glassware/DOC Vials/Filters
Prior to use in sample analysis, any materials used for carbon and
organics procedures must be ashed to remove any trace carbon present.
This is completed by placing the materials into a furnace and heating to
600 Celsius, which burns off any carbon present. This allows us to be
certain that any carbon detected during total organic carbon analysis or
UV 254 analysis was introduced from the environment and not some other
source of contamination. Objects that should be ashed include 40 mL
vials, DOC vials for the TOC analyzer, and Glass Filters for sample
processing. To ash your materials:
1. Wrap the materials in aluminum foil. Make sure that everything is
completely covered so that it will not become contaminated after
removal from the furnace. Filters can be ashed by placing 50 or so
in an envelope made by folding aluminum foil (they do not have to be
individually placed).
2. Place wrapped materials into the furnace located in the LER. Ensure
that the door is able to close without obstruction. Close the door
and lock into place by turning the handle
3. Press the run button once. You should see a program pop up. Press
the run button again. You will hear a click. The furnace will
automatically heat to 600 Celsius and cool off. Do not open the
furnace door if the internal temperature is more than 100 Celsius.
This will result in glassware shattering due to rapid temperature
change.
4. Once materials have cooled bring them back to the lab and place them
in a safe place.
### Autoclaving Microbial Bottles
Bottles used for microbial samples must be autoclaved prior to use in
order to sterilize them. This ensures that all microbial colonies
detected during sampling are actually coming from the sample and not
just from contamination in the bottles. The autoclave is located in
ISTB4 Lab 321. To autoclave the bottles follow this procedure:
1. Check to make sure that what you are autoclaving is actually
autoclavable. Using non-autoclavable bottles will result in them
melting and possibly damaging the autoclave.
2. Loosen caps on the bottles so that they are only tightened a quarter
turn. If the caps are too tight the change in pressure in the
autoclave will result in rupturing of the bottles.
3. Place a strip of autoclave tape over the top of the bottle/cap to
ensure that the cap does not fall off the bottle. The autoclave tape
will turn black upon completion to help you verify that the proper
temperature for sterilization did actually occur.
4. Check to make sure autoclave is at proper water levels. There should
be water inside the bottom of the autoclave and the water tank
should have a level between low and high.
5. Place bottles in the basket and place inside autoclave. Secure the
lid by locking the latch.
6. Select solid mode and ensure that temperature is set for 121 C and
time is set for 15 minutes. Autoclaving takes approximately 1.5
hours.
7. Remove objects from autoclave and secure lids. Store in a place
where no one will mistakenly steal sterilized bottles.
### Preparation of Microbial Media
We need to make two types of media – Brilliance for coliform and E. coli
detection and 7H11 for mycobacterium detection. Each plate should have
15-20 mL of media in it to avoid drying out during incubation.
#### To make Brilliance media:
1. Figure out how much media you will be making. You can make up to 2
months of media at a time. Each site where microbial measurements
are taken (Pima, 56th, Cent, R3, HOC, HTC, MOC, R11, R12, R13, HWY
87, and R25) needs its own plate.
2. Measure out the required volume of water. You will need to use DI
water.
3. Pour water into a flask place on hotplate and begin heating. Add a
magnetic stirrer and mix.
4. Measure out the media (the side of the bottle has the required ratio
of media to water).
5. Add the media and cover the flask with aluminum foil.
6. Once the solution is boiling and clears up turn off the heat.
7. Cool the media down to 50 C (approximately when you can touch the
glass without burning your hand).
8. Turn on a Bunsen burner and allow it to run. Using a 25 mL
serological pipette fill each plate with 15ish mL of liquid media.
Allow media to cool on benchtop.
9. Once media is cool and has solidified place the plates in a bag and
label with your name, media type and date. Store lid side down in
the fridge until use is required.
#### To make 7H11 media:
1. Figure out how much media you will be making. You can make up to 2
months of media at a time. You will need 1 plate for every 2
sampling sites.
2. Measure out the required volume of water. You will need to use DI
water.
3. Pour water into a flask place on hotplate and begin heating. Add a
magnetic stirrer and mix.
4. Measure out the media (the side of the bottle has the required ratio
of media to water).
5. Add the media and 1 mL of 50% glyceryl solution for every 100 mL of
solution and cover the flask with aluminum foil.
6. Once the solution is boiling and clears up turn off the heat.
7. Take the solution along with another flask filled with 100 mL DI
water to the autoclave and autoclave on the 15 min liquid default
cycle.
8. Once autoclave is complete bring the solution back to the lab and
place it on a mixer. Add 10 mL of OADC growth supplement (kept in
the fridge) for every 100 mL of solution. Transfer 10 mL of
autoclaved DI water into 1 vial of Panta BBL Antibiotic (also kept
in fridge) mix and add to solution for every 100 mL of solution. Mix
thoroughly
9. Turn on a Bunsen burner and allow it to run. Using a 25 mL
serological pipette fill each plate with 15ish mL of liquid media.
Allow media to cool on benchtop.
10. Once media is cool and has solidified place the plates in a bag and
label with your name, media type and date. Store lid side down in
the fridge until use is required.
Analysis
--------
### Membrane Filtration for E. coli and Fecal Coliforms
Within 24 hours of sample collection you will need to filter the
microbial samples to quantify coliforms and E. coli. Samples should be
refrigerated from collection until membrane filtration. To perform
membrane filtration:
1. Gather required supplies for membrane filtration (forceps, Bunsen
burner and propane, Millipore membrane filters, ethyl alcohol,
lighter, autoclaved filtration cups).
2. Check the level of the pump oil and fill to the line if necessary.
3. Remove the cap from one of the vacuums on the filtration unit. Spray
with ethyl alcohol solution and light with Bunsen burner. This will
sterilize the surface.
4. Flame the forceps in the Bunsen burner. Pick up a Millipore filter
and place on the vacuum.
5. Place a filtration cup over the vacuum. Pour the sample up to 100 mL
line on the filtration cup.
6. Turn on the vacuum pump and twist the valve to open the vacuum to
filter the samples.
7. Once all of the sample has drained through the vacuum close the
valve and shut off the pump.
8. Flame the forceps, remove the filtration cup, and pick up the filter
from the vacuum. Place on top of the Brilliance media plate (hatched
side up) being careful not to trap any air bubbles under the filter.
9. Repeat the process until all samples have been filtered. Place all
plates in the incubator lid side down. Incubate 18-24 hours and
count. Coliform colonies are purple/pink while E. coli colonies are
blue. Be sure to dump the filtered water in the flask after you
perform membrane filtration as part of clean up. If you cannot count
the samples right away place them in the fridge lid side down. You
have a few days before the plates will no longer be countable.
### Membrane Filtration for Mycobacterium
Mycobacterium is the other microbe that we look for. Samples must be
filtered within 2 weeks of collection (mycobacterium is a much hardier
organism than coliforms). Samples should be refrigerated from collection
until membrane filtration. To perform membrane filtration:
1. Gather required supplies for membrane filtration (forceps, Bunsen
burner and propane, Millipore membrane filters, ethyl alcohol,
lighter, autoclaved filtration cups).
2. Check the level of the pump oil and fill to the line if necessary.
3. Remove the cap from one of the vacuums on the filtration unit. Spray
with ethyl alcohol solution and light with Bunsen burner. This will
sterilize the surface.
4. Flame the forceps in the Bunsen burner. Pick up a Millipore filter
and place on the vacuum.
5. Place a filtration cup over the vacuum. Pour the sample up to 100 mL
line on the filtration cup.
6. Turn on the vacuum pump and twist the valve to open the vacuum to
filter the samples. Drain the sample down to approximately 5 mL and
close the valve (shut off the pump).
7. Add 5 mL of 4% NaOH solution. Cover the filtration cup with aluminum
foil and let it sit for 30 minutes.
8. After 30 minutes add 5 mL of 3% HCl solution. Allow the sample to
sit for 1 minute to neutralize. Turn on the pump and drain the
remaining sample. 9. Once all of the sample has drained through the
vacuum close the valve and shut off the pump.
9. Flame the forceps, remove the filtration cup, and pick up the filter
from the vacuum. Place on top of the 7H11 media plate (hatched side
up) being careful not to trap any air bubbles under the filter.
10. Repeat the process until all samples have been filtered. Place all
plates in the incubator lid side down. Incubate for 2 weeks and
count.
Due to the expense of the 7H11 media we generally put 2 filters on each
plate. If you cannot count the samples right away place them in the
fridge lid side down. You have a few days before the plates will no
longer be countable.
### Sample Filtration for UV254/DOC
Collected samples will need to be filtered through ashed 0.45 micron
glass filters to remove particles to ensure that the only carbon
remaining is dissolved carbon (the difference between DOC – Dissolved
Organic Carbon and TOC- Total Organic Carbon). To filter these samples
follow the following procedure:
1. Make sure that you have ashed the 0.45 micron glass filters before
filtration
2. Using a gloved hand place 1 filter inside the filter tip for the 60
mL syringe.
3. Attach the filter tip to the 60 mL syringe once the plunger has been
removed.
4. Pour 20-30 mL of your sample from the 250 mL amber bottle into the
syringe, swirl and dump out to rinse the syringe.
5. Fill the 60 mL syringe all the way full of your sample. Place the
syringe over the 40 mL vial, insert the plunger and flush sample
through the filter down to the 40 mL mark on the syringe.
6. Dump the vial out to rinse it.
7. Filter the remaining 40 mL from the syringe into the 40 mL vial and
cap.
8. Move on to the next sample.
### UV254
To run UV254 follow this procedure:
1. Turn on the Hach DR 5000 by flicking the power switch back panel on
the upper left side.
2. System will perform self check
3. Select single wavelength, confirm that 254 is the wavelength
selected
4. Insert cuvette filled with nanopure and select zero
5. Dump the nanopure and fill with your sample sample then press read,
it will display the absorbance value.
6. Record the absorbance value, dump your sample and refill the cuvette
with the next sample.
7. Once all samples have been run flick the power switch to turn off
the machine.
In between samples you may spill on the cuvette. Use a kimwipe to clean
off the surface of the cuvette without scratching it. Make sure that you
are using a quartz cuvette. The plastic cuvettes will not give you
accurate results.
### DOC
Once you have filtered your samples into the 40 mL amber vials you can
run DOC (Dissolved Organic Carbon). The tool we use for this is the
Shimadzu TOC-5000A Total Organic Carbon Analyzer.
To operate the TOC-5000A complete the following procedure:
1. Turn on the gas cylinder by turning the metal valve on top of the
cylinder in a counterclockwise direction 1 turn. You should see the
indicators on the regulator turn to indicate the pressure of the
cylinder and the pressure of the gas flowing through the line. The
right indicator is the pressure of the cylinder, which should be
about 2000 psi when full. This pressure will slowly decrease over
time as you run samples until it reaches 500 psi, in which case the
cylinder pressure will be too low to continue operation and a new
cylinder will have to be ordered. The indicator on the left is the
pressure of the gas flowing through the line, which should be
adjusted to 90 psi by turning the dial on the regulator.
2. Turn on the TOC Analyzer by flipping the switch located on the
bottom rear of the left side panel of the machine. It will begin to
power on. Press F5 for the ASI Initial Option, which will begin to
start up the machine. The autosampler will begin to rotate and
toggle the needles back and forth as part of a self check. Once home
position is found the machine will be turned on. Press F1 for next.
3. Use the arrows on the control panel to select option 3 General
Conditions. Press Enter to select. Scroll down to Furnace On/Off and
press 1 to turn it to TOC mode. This will begin to heat the furnace
of the TOC Analyzer. Return to the main menu by selecting F2.
4. Scroll down to 6 Monitor to observe the conditions of the machine.
There are 5 characteristics here to ensure that the machine is
operating correctly: TC Furnace Temperature (Should be 680 C for
proper operation), Dehumidifier Temperature (Should be 0.5-2 C for
proper operation), Baseline Position (should be at the middle of the
screen near 0 on the plot), Baseline Fluctuation (should be smooth
without any waves), and Baseline Noise (should not have bumps in the
baseline). Once everything is ready it will say OK next to each
parameter and if things are not ready they will say NG. The Green
light will come on next to Ready on the front panel once the machine
is ready to run samples. You can check the carrier gas in the
machine (next to sparge gas) and adjust to 150 ml/min for proper
operation. Sparge gas should be adjusted to 90 ml/min when sparging.
You generally want to run a steady baseline for a few hours prior to
initiating a sample run.
5. Load your samples and standards into the autosampler. Number a piece
of paper with the numbers of the vials on the autosampler. Begin by
loading blanks (nanopure water) into the first 3 vials. Pour your
filtered samples from the 40 mL vials into the DOC vials and place
them in position, noting the vial number on your piece of paper. 3
Blanks should be run every 10-12 vials to validate accuracy of the
TOC analysis. Blanks should be within +/- 0.5 mg/L of 0 mg/L to
ensure accurate data.
6. Perform a final check of the machine prior to beginning your run.
Ensure that all of the samples and standards have been properly
loaded. Ensure that the lid of the autosampler is properly on.
Ensure that the nanopure rinse water and humidifier water levels are
appropriately full. Ensure that there is enough printout paper
loaded in the top of the machine. Address these issues before
beginning sample run.
7. Return to the main menu and select 9 Auto Sampler to set up your
sample run. Under Type make sure that NPOC is selected. For IS,
which means initial sample, type the number of the initial vial you
would like to run from the autosampler. For FS, which means final
sample, type the number of the final vial you would like to run from
the autosampler. Under C1 click enter to select the calibration
curve. Using CAL Curve F1 you will see the 1st Standard as 10 mg/L
in vial S4, 2nd Standard as 5 mg/L in vial S3, 3rd Standard as 1
mg/L in vial S2, and 4th Standard as 0 mg/L in vial S1. You should
select an injection volume of 53 microliters, 3 injections with a
maximum of 5, an SD of 200, and a CV of 2.0%. Sparge time should be
set to 5 minutes. Make sure shift to origin and acid addition are
both off. Press F2 to return.
8. Ensure that your sample volume is set to 53 microliters, 3
injections with a maximum of 5, 200 SD, 2.0% CV, and 2 SP (sparge
time) for your samples. Once this is complete press F1 for next.
Ensure that Rinse is turned on, 2 needle washes and 2 flow line
washes are selected. Press F2 for next. Press Start and your samples
will begin to run.
The autosampler will allow for your samples to run on their own without
any additional effort from you. Samples can be run overnight. It
generally takes between 18-24 hours to run an entire month’s worth of
samples. Once you return to see that all the samples have finished
running you can power down the machine if it has cooled. The machine
will tell you whether it is ok to power down or whether you should allow
it to stay on for 30 minutes to prevent overheating. To power down the
machine flick the power switch and turn off the gas cylinder.
### TDN
TDN is run by the Goldwater Environmental Lab.
Data Files (10) :
Tabular:
617_algae_49fa96bded7c86b3720d56a128efc5a7.csv
Description: algal characteristics (chlorophyll concentration, cell counts) and specific conductance in canals and reservoirs
Tabular:
617_algal_byproducts_d4765274e6268e53e82bfece5fabb7e3.csv
Description: concentration of algal by-products in canals and reservoirs
Tabular:
617_arsenic_18c9184205e943456921449878002c3a.csv
Description: arsenic and perchlorate concentrations in canals and reservoirs
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
Glen In: Glendale WTP Inlet
-
Glen Out: Glendale WTP Treated
-
Green In: Greenway WTP Inlet
-
Green Out: Greenway WTP Treated
-
Havasu 1: Lake Havasu Site 1
-
Havasu 2: Lake Havasu Site 2
-
HTC: Head of the Tempe Canal
-
Hwy 87: AZ Canal at Highway 87
-
NP In: Tempe North WTP Inlet
-
NP Out: Tempe North WTP Treated
-
Pima: AZ Canal at Pima Rd
-
R10: Salt River below Saguaro (Blue Point Bridge)
-
R11: CAP Canal at Cross-connect
-
R12: AZ Canal above CAP Cross-connect
-
R13: AZ Canal below CAP Cross-connect
-
R14: AZ Canal - Inlet to Squaw Peak WTP
-
R15: Squaw Peak WTP treated water
-
R16: AZ Canal - Inlet to Deer Valley WTP
-
R17: Deer Valley WTP treated water
-
R18: South Canal at Val Vista WTP
-
R19: Val Vista WTP treated water
-
R20: Verde River at Tangle
-
R21: AZ Canal - Central Avenue
-
R25: Verde River at Beeline
-
R2A: Lake Pleasant integrated sample
-
R2B: Lake Pleasant integrated sample
-
R6A: Bartlett Reservoir near outlet
-
R6B: Bartlett Reservoir near outlet
-
R9A: Saguaro Lake near inlet
-
R9A-Dup: Saguaro Lake near inlet
-
R9B: Saguaro Lake near inlet
-
SOCA: South Canal below CAP Cross-connect
-
SPT In: Tempe South WTP Inlet
-
SPT Out: Tempe South WP Treated
-
UH In: Union Hills WTP Inlet
-
UH Out: Union Hills WTP Treated
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:
-
cap: Central Arizona Project canal
-
srp: Salt River Project canal
-
tempe: Tempe, AZ area canal
|
site acronym |
site number or name
|
string |
Enumeration:
-
az canal @ 56th st.: AZ Canal at 56th Street
-
az canal @ central ave.: AZ Canal at Central Avenue
-
az canal @ deer valley: AZ Canal - Inlet to Deer Valley WTP
-
az canal @ hwy 87: AZ Canal at Highway 87
-
az canal @ pima: AZ Canal at Pima Rd
-
az canal @ squaw peak: AZ Canal - Inlet to Squaw Peak WTP
-
az canal blw cap: AZ Canal below CAP Cross-connect
-
az canal inflow: AZ Canal above CAP Cross-connect
-
bartlett-epi: Bartlett Reservoir near outlet
-
bartlett-hypo: Bartlett Reservoir near outlet
-
cap @ x con: CAP Canal at Cross-connect
-
deer valley-treated: Deer Valley WTP treated water
-
Glen In: Glendale WTP Inlet
-
Glen Out: Glendale WTP Treated
-
Green In: Greenway WTP Inlet
-
Green Out: Greenway WTP Treated
-
Havasu 1: Lake Havasu Site 1
-
Havasu 2: Lake Havasu Site 2
-
head of tempe canal: Head of Tempe Canal
-
North plant inlet: Tempe North WTP Inlet
-
north plant outlet: Tempe North WTP Treated
-
pleasant-epi: Lake Pleasant integrated sample
-
pleasant-hypo: Lake Pleasant integrated sample
-
s canal @ val vista: South Canal at Val Vista WTP
-
saguaro-epi: Saguaro Lake Epilimnion
-
saguaro-epi dup: Saguaro Lake Epilimnion Duplicate Sample
-
saguaro-hypo: Saguaro Lake Hypolimnion
-
salt blw saguaro: Salt River below Saguaro (Blue Point Bridge)
-
South canal below CAP: South Canal below CAP Cross-connect
-
SPT In: Tempe South WTP Inlet
-
SPT Out: Tempe South WTP Treated
-
squaw peak-treated: Squaw Peak WTP treated water
-
STP In: Tempe Canal - Inlet to Tempe's South Plant
-
STP Out: Tempe's South Plant treated water
-
Union Hills Inlet: Union Hills WTP Inlet
-
Union Hills Outlet: Union Hills WTP Treated
-
val vista-treated: Val Vista WTP treated water
-
val vista-treated-West: Val Vista WTP treated water - west
-
verde @ beeline: verde river at beeline highway
-
verde abv horseshoe: Verde River at Tangle
-
waddell canal: Waddell Canal
|
arsenic (ug/L) |
arsenic concentration as determined by graphite furnace
|
float |
microgramsPerLiter |
perchlorate (ug/L) |
perchlorate concentration as determined by ion chromatography
|
float |
microgramsPerLiter |
date |
sample collection date
|
date |
Format: YYYY-MM-DD |
BDL |
1 = sample with arsenic concentration below detectable limit
|
string |
Enumeration:-
1: 1 = below detectable limits
|
Tabular:
617_carbon_cc0e7f16f828061c7aa3dd325fa9f0ef.csv
Description: approximately monthly water carbon data in Phoenix-area canals and reservoirs
Tabular:
617_field_measurements_61820cda981b4135b9b2efdc641bacc2.csv
Description: water quality parameters as measured in the field in canals and reservoirs
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:
-
cap: Central Arizona Project canal
-
srp: Salt River Project canal
-
tempe: Tempe, AZ area canal
|
site acronym |
site number or name
|
string |
|
date |
sample collection date
|
date |
Format: YYYY-MM-DD |
depth (m) |
water depth where measurement was taken (0 designates just below surface)
|
float |
meter |
T (C) |
water temperature
|
float |
celsius |
DO (mg/l) |
dissolved oxygen
|
float |
milligramsPerLiter |
pH |
pH
|
float |
dimensionless |
Secchi disk (m) |
water transparency measurement as measured from side of boat
|
float |
meter |
samples collected |
types of analyses for which samples were collected
|
string |
|
comments |
comment(s) about site conditions or sampling details
|
string |
|
Tabular:
617_microbial_7a331250b6c16318285bb1d355dffc95.csv
Description: E. coli, Coliform, and Mycobacterium colony counts in canals and reservoirs
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
HOC: Head of the Consolidated canal
-
HTC: Head of the Tempe Canal
-
Hwy 87: AZ Canal at Highway 87
-
MOC: Middle of the Consolidated canal
-
Pima: AZ Canal at Pima Rd
-
R11: CAP Canal at Cross-connect
-
R12: AZ Canal above CAP Cross-connect
-
R13: AZ Canal below CAP Cross-connect
-
R21: AZ Canal - Central Avenue
-
R25: Verde River at Beeline
-
SOCA: South Canal below CAP Cross-connect
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:
-
cap: Central Arizona Project canal
-
srp: Salt River Project canal
-
tempe: Tempe, AZ area canal
|
site acronym |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
az canal @ 56th st.: AZ Canal at 56th Street
-
az canal @ central ave.: AZ Canal at Central Avenue
-
az canal @ hwy 87: AZ Canal at Highway 87
-
az canal @ pima: AZ Canal at Pima Rd
-
az canal blw cap: AZ Canal below CAP Cross-connect
-
az canal inflow: AZ Canal above CAP Cross-connect
-
cap @ x con: CAP Canal at Cross-connect
-
head of tempe canal: Head of Tempe Canal
-
Head of the Consolidated Canal: Head of the Consolidated canal
-
Middle of the Consolidated Canal: Middle of the Consolidated canal
-
South canal below CAP: South Canal below CAP Cross-connect
-
verde @ beeline: verde river at beeline highway
-
waddell canal: Waddell Canal
|
date |
sample collection date
|
date |
Format: YYYY-MM-DD |
e_coli |
number of E coli colonies per 100mL of sample
|
float |
coloniesPer100milliliter |
coliform |
number of Coliform colonies per 100mL of sample
|
float |
coloniesPer100milliliter |
mycobacterium |
number of Mycobacterium colonies per 100mL of sample
|
float |
coloniesPer100milliliter |
mycobacterium_flag |
sampling, analysis, or processing flag for Mycobacterium sample
|
string |
Enumeration:
-
CONT: Not Countable Due to Contamination
-
NCDC: Not Countable Due to Contamination
-
ND: absent/too few to count
-
TNTC: Too Numerous to Count
|
Comments |
comment(s) about site conditions or sampling details
|
string |
|
Tabular:
617_nutrients_a32dafb7546f4adc6404c987eff0ddcc.csv
Description: concentration of algal by-products in canals and reservoirs
Tabular:
617_quarterly_lake_sampling_f0737c30552c0ab276c0d93483672fcb.csv
Description: concentration of nutrients and algal by-products, and other water quality parameters measured in central-Arizona area lakes
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
APA1A: Apache Lake Site 1 Epilimnion
-
APA1B: Apache Lake Site 1 Hypolimnion
-
APA2A: Apache Lake Site 2 Epilimnion
-
APA2B: Apache Lake Site 2 Hypolimnion
-
Can1A: Canyon Lake Site 1 Epilimnion
-
Can1B: Canyon Lake Site 1 Hypolimnion
-
Can2A: Canyon Lake Site 2 Epilimnion
-
Can2B: Canyon Lake Site 2 Hypolimnion
-
Roos1A: Roosevelt Lake Site 1 Epilimnion
-
Roos1B: Roosevelt Lake Site 1 Hypolimnion
-
Roos2A: Roosevelt Lake Site 2 Epilimnion
-
Roos2B: Roosevelt Lake Site 2 Hypolimnion
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:-
srp: Salt River Project canal
|
site acronym |
site number or name
|
string |
Enumeration:
-
Apache, epi, lower: Apache Lake Site 2 Epilimnion
-
Apache, epi, upper: Apache Lake Site 1 Epilimnion
-
Apache, eppi, lower: Apache Lake Site 2 Epilimnion
-
Apache, eppi, upper: Apache Lake Site 1 Epilimnion
-
Apache, hypo, lower: Apache Lake Site 2 Hypolimnion
-
Apache, hypo, upper: Apache Lake Site 1 Hypolimnion
-
Canyon, epi, lower: Canyon Lake Site 2 Epilimnion
-
Canyon, epi, upper: Canyon Lake Site 1 Epilimnion
-
Canyon, eppi, lower: Canyon Lake Site 2 Epilimnion
-
Canyon, eppi, upper: Canyon Lake Site 1 Epilimnion
-
Canyon, hypo, lower: Canyon Lake Site 2 Hypolimnion
-
Canyon, hypo, upper: Canyon Lake Site 1 Hypolimnion
-
Roosevelt, epi, lower: Roosevelt Lake Site 2 Epilimnion
-
Roosevelt, epi, upper: Roosevelt Lake Site 1 Epilimnion
-
Roosevelt, eppi, lower: Roosevelt Lake Site 2 Epilimnion
-
Roosevelt, eppi, upper: Roosevelt Lake Site 1 Epilimnion
-
Roosevelt, hypo, lower: Roosevelt Lake Site 2 Hypolimnion
-
Roosevelt, hypo, upper: Roosevelt Lake Site 1 Hypolimnion
|
date |
sample collection
|
date |
Format: YYYY-MM-DD |
MIB (ng/L) |
2-methylisoborneol
|
float |
nanogramsPerLiter |
geosmin (ng/L) |
Geosmin
|
float |
nanogramsPerLiter |
TP (ug/L) |
total phosphorus
|
float |
microgramsPerLiter |
DOC (mg/L) |
dissolved organic carbon
|
float |
milligramsPerLiter |
UVA (cm-1) |
UV absorbance measured at 254 nanometers
|
float |
perCentimeter |
Suva(L/mg-m) |
specific ultraviolet absorbance
|
float |
literPerMilligramMeter |
Conductance (us/cm) |
specific conductance
|
float |
microsiemensPerCentimeter |
TDN (mg/L) |
total dissolved nitrogen
|
float |
milligramsPerLiter |
Tabular:
617_quarterly_metals_7f32c206f2d47401a024067c57de94b3.csv
Description: concentration of dissolved metals measured in central-Arizona area lakes and canals
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
APA1A: Apache Lake Site 1 Epilimnion
-
APA1B: Apache Lake Site 1 Hypolimnion
-
APA2A: Apache Lake Site 2 Epilimnion
-
APA2B: Apache Lake Site 2 Hypolimnion
-
Can1A: Canyon Lake Site 1 Epilimnion
-
Can1B: Canyon Lake Site 1 Hypolimnion
-
Can2A: Canyon Lake Site 2 Epilimnion
-
Can2B: Canyon Lake Site 2 Hypolimnion
-
R10: Salt River below Saguaro (Blue Point Bridge)
-
R25: Verde River at Beeline
-
R2A: Lake Pleasant integrated sample
-
Roos1A: Roosevelt Lake Site 1 Epilimnion
-
Roos1B: Roosevelt Lake Site 1 Hypolimnion
-
Roos2A: Roosevelt Lake Site 2 Epilimnion
-
Roos2B: Roosevelt Lake Site 2 Hypolimnion
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:
-
cap: Central Arizona Project canal
-
srp: Salt River Project canal
|
site acronym |
site number or name
|
string |
Enumeration:
-
Apache, eppi, lower: Apache Lake Site 2 Epilimnion
-
Apache, eppi, upper: Apache Lake Site 1 Epilimnion
-
Apache, hypo, lower: Apache Lake Site 2 Hypolimnion
-
Apache, hypo, upper: Apache Lake Site 1 Hypolimnion
-
Canyon, eppi, lower: Canyon Lake Site 2 Epilimnion
-
Canyon, eppi, upper: Canyon Lake Site 1 Epilimnion
-
Canyon, hypo, lower: Canyon Lake Site 2 Hypolimnion
-
Canyon, hypo, upper: Canyon Lake Site 1 Hypolimnion
-
pleasant-epi: Lake Pleasant integrated sample
-
Roosevelt, eppi, lower: Roosevelt Lake Site 2 Epilimnion
-
Roosevelt, eppi, upper: Roosevelt Lake Site 1 Epilimnion
-
Roosevelt, hypo, lower: Roosevelt Lake Site 2 Hypolimnion
-
Roosevelt, hypo, upper: Roosevelt Lake Site 1 Hypolimnion
-
salt blw saguaro: Salt River below Saguaro (Blue Point Bridge)
-
verde @ beeline: verde river at beeline highway
-
waddell canal: Waddell Canal
|
date |
sample collection date
|
date |
Format: YYYY-MM-DD |
7Li |
Lithium measurement by ICP-MS
|
float |
microgramsPerLiter |
9Be |
Beryllium measurement by ICP-MS
|
float |
microgramsPerLiter |
23Na |
Sodium measurement by ICP-MS
|
float |
microgramsPerLiter |
24Mg |
Magnesium measurement by ICP-MS
|
float |
microgramsPerLiter |
27Al |
Aluminum measurement by ICP-MS
|
float |
microgramsPerLiter |
39K |
Potassium measurement by ICP-MS
|
float |
microgramsPerLiter |
44Ca |
Calcium measurement by ICP-MS
|
float |
microgramsPerLiter |
51V |
Vanadium measurement by ICP-MS
|
float |
microgramsPerLiter |
52Cr |
Chromium measurement by ICP-MS
|
float |
microgramsPerLiter |
55Mn |
Manganese measurement by ICP-MS
|
float |
microgramsPerLiter |
56Fe |
Iron measurement by ICP-MS
|
float |
microgramsPerLiter |
59Co |
Cobalt measurement by ICP-MS
|
float |
microgramsPerLiter |
60Ni |
Nickel measurement by ICP-MS
|
float |
microgramsPerLiter |
65Cu |
Copper measurement by ICP-MS
|
float |
microgramsPerLiter |
66Zn |
Zinc measurement by ICP-MS
|
float |
microgramsPerLiter |
75As |
Arsenic measurement by ICP-MS
|
float |
microgramsPerLiter |
82Se |
Selenium measurement by ICP-MS
|
float |
microgramsPerLiter |
88Sr |
Strontium measurement by ICP-MS
|
float |
microgramsPerLiter |
95Mo |
Molybdenum measurement by ICP-MS
|
float |
microgramsPerLiter |
107Ag |
Silver measurement by ICP-MS
|
float |
microgramsPerLiter |
111Cd |
Cadmium measurement by ICP-MS
|
float |
microgramsPerLiter |
121Sb |
Antimony measurement by ICP-MS
|
float |
microgramsPerLiter |
138Ba |
Barium measurement by ICP-MS
|
float |
microgramsPerLiter |
202Hg |
Mercury measurement by ICP-MS
|
float |
microgramsPerLiter |
208Pb |
Lead measurement by ICP-MS
|
float |
microgramsPerLiter |
238U |
Uranium measurement by ICP-MS
|
float |
microgramsPerLiter |
Tabular:
617_sampling_locations_46042e79c58446e438b4879dac011e84.csv
Description: latitude, longitude, and elevation of select canal, lake, and river water-quality sampling locations
Column |
Description |
Type |
Units |
site number |
site number or name (A designates epilimnion, B hypolimnion)
|
string |
Enumeration:
-
HOC: Head of the Consolidated canal
-
HTC: Head of the Tempe Canal
-
MOC: Middle of the Consolidated canal
-
Pima: AZ Canal at Pima Rd
-
R1: CAP canal above Waddell Canal
-
R10: Salt River below Saguaro (Blue Point Bridge)
-
R11: CAP Canal at Cross-connect
-
R12: AZ Canal above CAP Cross-connect
-
R13: AZ Canal below CAP Cross-connect
-
R14: AZ Canal - Inlet to Squaw Peak WTP
-
R15: Squaw Peak WTP treated water
-
R16: AZ Canal - Inlet to Deer Valley WTP
-
R17: Deer Valley WTP treated water
-
R18: South Canal at Val Vista WTP
-
R19: Val Vista WTP treated water
-
R20: Verde River at Tangle
-
R21: AZ Canal - Central Avenue
-
R25: Verde River at Beeline
-
R2A: Lake Pleasant integrated sample
-
R2B: Lake Pleasant integrated sample
-
R5: Verde River btwn Horseshoe and Bartlett
-
R6A: Bartlett Reservoir near outlet
-
R6B: Bartlett Reservoir near outlet
-
R7: Verde River below Bartlett Reservoir
-
R8: Salt River inlet to Saguaro Lake
-
R9A: Saguaro Lake near inlet
-
R9B: Saguaro Lake near inlet
-
SOCA: South Canal below CAP Cross-connect
|
site location |
site location description
|
string |
|
cluster |
source water
|
string |
Enumeration:
-
cap: Central Arizona Project canal
-
reservoir: metadata_not_provided
-
srp: Salt River Project canal
-
tempe: Tempe, AZ area canal
|
site acronym |
site number or name
|
string |
Enumeration:
-
az canal- head of the consolidated canal: Head of the Consolidated canal
-
az canal - 56th st: AZ Canal at 56th Street
-
az canal - cent: AZ Canal at Central Avenue
-
az canal - middle of the consolidated canal: Middle of the Consolidated canal
-
az canal - pima: AZ Canal at Pima Rd
-
az canal - verde river @ beeline: verde river at beeline highway
-
az canal @ deer valley: AZ Canal - Inlet to Deer Valley WTP
-
az canal @ squaw peak: AZ Canal - Inlet to Squaw Peak WTP
-
az canal blw cap: AZ Canal below CAP Cross-connect
-
az canal inflow: AZ Canal above CAP Cross-connect
-
bartlett-epi: Bartlett Reservoir near outlet
-
bartlett-hypo: Bartlett Reservoir near outlet
-
cap-siphon: metadata_not_provided
-
cap @ 7th st: Cap Canal at 7th St.
-
cap @ x con: CAP Canal at Cross-connect
-
deer valley-treated: Deer Valley WTP treated water
-
pleasant-epi: Lake Pleasant integrated sample
-
pleasant-hypo: Lake Pleasant integrated sample
-
s canal @ val vista: South Canal at Val Vista WTP
-
saguaro-epi: Saguaro Lake Epilimnion
-
saguaro-hypo: Saguaro Lake Hypolimnion
-
salt abv saguaro: Salt River inlet to Saguaro Lake
-
salt blw saguaro: Salt River below Saguaro (Blue Point Bridge)
-
south tempe canals - below CAP Cross-connect: South Canal below CAP Cross-connect
-
south tempe canals - head of the tempe canal: Head of the Tempe Canal
-
squaw peak-treated: Squaw Peak WTP treated water
-
val vista-treated: Val Vista WTP treated water
-
verde abv bartlett: Verde River btwn Horseshoe and Bartlett
-
verde abv horseshoe: Verde River at Tangle
-
verde blw barlett: Verde River below Bartlett Reservoir
-
waddell canal: Waddell Canal
|
date |
GPS collection date
|
date |
Format: YYYY-MM-DD |
longitude |
longitude
|
float |
degree |
latitude |
latitude
|
float |
degree |
altitude (ft) |
altitude
|
float |
meter |