My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
HYDRO20192
DRMS
>
Back File Migration
>
Hydrology
>
HYDRO20192
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
8/24/2016 8:41:33 PM
Creation date
11/20/2007 1:24:46 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999034
IBM Index Class Name
Hydrology
Doc Date
9/23/2003
Doc Name
DIMP Testing
From
ADCO Consulting
To
DMG
Media Type
D
Archive
No
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
21
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
<br />COLORADO DEPARTMENT OF PUBLIC HEALTH AND ENVIRONMENT <br />W ATER QUALITY CONTRO L DI V [S ION <br />VJATERQUALITY PROTECTION SECTION <br />GROUND-~VA.TER PSRMfT GUIDANCE <br />SUGGESTED MONiTORiNG WELL SAMPLING PROTOCOL <br />S. CzRCEL72vTIl-WATER SAMPLE CQLLECTION <br />6. FIELD SAMPLE COLLECTION AvB TESTING <br />is area[er than 11 and sodium concentration is more than 10 moles per liter Measurement of pH is <br />temperature is temperature sensitive, so the standazd buffers should be within -/- I°C of the sample solution <br />for precise determinations. Calibrate [he.equipment in strict accordance with the manufacturer's instructions. <br />If the sampling continues from one day to the next, the pH field testing equipment is to be calibrated each day <br />of its use. The correct buffer solution is to be determined based upon };.nowledge of the ground water in the <br />area. Typically the ground water is going to be around 7.0 s. u. The buffer solutions of 7.00 and 10.0 aze to <br />be used to calibrate the off equipment. The pH is [o be recorded to the neazest hundredth. Ensure that the <br />buffer solutions are stored properly and acprozimately at the [emperatu:e o: the ground water. If the <br />temperature or` the Ground water is not lmown, then a temperaure near 45 °F would sur7ce. It is suggested <br />that two probes be available for use. The probe in use should be kept wet in deionized water or according to <br />the manufacture:'; instructions. <br />'9 Specific Conductance <br />Specific conductance is to be measured for each monitoring well during the purging process. the meter is to <br />be calibrated m strict adherence to the manufacturer's instructons. The meter is to be calibrated on each day <br />that sampling is to occur. Calibration is made by using the 0.00702 N standazd solution at the ambient <br />temperature. The temperature conuol s see at 2~°C, and the ambient temperature of the srandard KCl <br />solution is recorded A value of specifc conductance is obtained and compared with values given in a graph <br />of Specific conductance at 3~°C and specitc conductance of a 0.00702 N KCI solution at various <br />temperatures. The meter is to be within five (~) percent of the grzoh. Specitc conductance meters used in <br />the feld should be banerv opera[ed, equipped with temperature comceasator and read directly in <br />micromhos/cm at 2~ °C. Tire direr*, reading meter is recerunended to save time in converting resistance <br />i <br />values co specific conductance and to msurz that the value rs read in the fie]d. <br />Temperature <br />Measurement of g-round-water temeerature is most accurate when the ambient temperature is within 20°C of <br />the ground-water temeerature. New or little-used wells may develop new producing zones during ptunpvng, <br />thereby varying die propottiou of water enre:ins ;he well from different deaths and causins either an <br />instantaneous change or con[inual drift ir, the temperature measuremen[s. Drawdown may czuse <br />
The URL can be used to link to this page
Your browser does not support the video tag.