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3 collecting laboratory data for calibration, Collecting laboratory data for calibration – Campbell Scientific CS650 and CS655 Water Content Reflectometers User Manual

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CS650 and CS655 Water Content Reflectometers

A minimum of four data points are required for derivation of a 3

rd

degree

polynomial. Data points should be spaced as evenly as practical over the

expected range of water content and include the wettest and driest expected

values.

8.3 Collecting Laboratory Data for Calibration

Water content reflectometer data needed for CS650 calibration are the CS650

permittivity reading and an independently determined volumetric water

content. From this data, the probe response to changing water content can be

described by a linear or polynomial function as described in Section 8.2, The

User-Derived Calibration Equation.

Required equipment:

1. CS650 connected to datalogger programmed to measure permittivity
2. Cylindrical sampling devices to determine sample volume for bulk

density, e.g. copper tubing of diameter ≥ 1” and length about 2”

3. Containers and scale to measure soil sample mass

4. Oven to dry samples (microwave oven can also be used)

The calibration coefficients are derived from a curve fit of known water

content and probe permittivity output. The number of data sets needed to

derive a calibration depends on the form of the calibration equation. At least

three data sets should be generated to determine whether the linear form is

valid. If a polynomial is to be used, four data sets will determine whether the

function is a quadratic or 3

rd

order polynomial. Accuracy requirements may

require additional data sets. Consider the expected range of soil water content

and include data sets from the highest and lowest expected water contents.

The measurement sensitive volume around the probe rods must be completely

occupied by the calibration soil. Only soil should be in the region within

10 cm (4 inches) of the rod surface. The probe rods can be buried in a tray of

soil that is dry or nearly dry. The soil will be homogeneous around the probe

rods if it is poured around the rods while dry. Also, a 20 cm diameter PVC

pipe with length about 35 cm can be closed at one end and used as the

container.

It is important that the bulk density of the soil used for calibration be similar to

the bulk density of the undisturbed soil. Using dry soil without compaction will

give a typical bulk density, 1.1 - 1.4 g cm

-3

. This is especially important when

bulk density is greater than 1.55 g cm

-3

. Compaction of the calibration soil to

similar bulk density at the field site is necessary for an accurate calibration.

The typically used method for packing a container of soil to uniform bulk

density is to roughly separate the soil into three or more equal portions and add

one portion to the container with compaction. Evenly place the first loose soil

layer in the bottom of the container. Compact by tamping the surface to a level

in the container that is correct for the target bulk density. Repeat for the

remaining layers. Prior to placing successive layers, scarify (loosen) the top of

the existing compacted layer.

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