This kit has been designed to comply with MDHS method 52/3 obtainable from the Health &
Safety Executive for the testing of Chromic Acid Mist.
We strongly recommend reading MDHS 52/3 prior to commencing any sampling.
Synopsis of the method
Using either a ‘seven hole head’ or - more recently - the ‘IOM sampler’ to hold an alkali treated filter
paper, an air sample is taken at 2 litres per minute over the time period of one hour.
This can be positioned over a tank with the optional clamp.
After sampling, the filter paper is removed from the sampling head and using the chemical kit and
comparator, an analysis and quantification can be made of the Chromic Acid Mist levels.
Getting started
Refer to your air sampling pump manual for detailed descriptions on setting the pump sampling
flow rate and time period. Most pumps can be started and stopped manually. The flow rate must
be set using an external calibration device such as a rotameter or other such calibrator. This must
be done with the filter sampling head assembled and inline.
For convenience we recommend an SKC Universal Deluxe air sampling pump which can be set to
automatically stop after one hour.
This manual contains all the information required to process the filter with the chemical kit that you
have purchased.
Page 2 www.skcltd.com
Page 5
Introduction
CAUTION!
Observe precautions when handling treated filters, and chemicals provided, as they may
cause harm to health.
We recommend only using stainless steel forceps/tweezers to handle alkali treated
filters.
Safety Data Sheets are provided at the rear of this manual.
www.skcltd.com Page 3
Page 6
Sampling
Tips and advice on setting up a sampling train (the sample pump with a filter) can be found in the
SKC Step by Step guide.
The process of loading a filter paper and calibrating this sampling train is similar to the set up
required for inhalable dust sampling using an IOM sampler.
If you do not have this guide, a free copy can be downloaded from the SKC website at -
www.skcltd.com
Loading the filter paper
The IOM comprises a two piece cassette and
the filter is loaded into the cassette which is
then placed inside the sampler.
The front cover of the sampler is then
screwed onto the thread of the body.
Diagram showing the positioning of the filter
paper within an IOM Sampler.
Note that the filter is cream/ white in
colour.
A blue paper if present is a separator
only and is not used in sampling.
Page 4 www.skcltd.com
front
cover
filter
cassette
front
body
cassette
grid
Page 7
Sampling
Calibration
Assuming an IOM head, SKC
Universal pump, and rotameter for
calibration.
The IOM head with filter is clipped/
held down onto the foam seal on top
of the rotameter ensuring a good seal
with no leaks. With the toolkit the
flow is adjusted by turning the flow
adjustment screw.
This is located to the bottom left side
of the universal sampler and marked
‘flow adjust’. Adjust to to 2L/min.
As the screw is turned the float or ball
should move up or down inside the
rotameter tube.
For other types of sampler or calibrator,
or for more indepth directions, refer to
the equipment manuals.
www.skcltd.com Page 5
Page 8
Analysis
The chemicals
The kit contains the following chemicals:
•1,5Diphenylcarbazide0.125gvial10off
•Sulphuricacid0.25M,500ml 1off
•Acetone 250ml 1off
•De-ionisedwater 500ml 1off
Use only 25 mm alkali-treated filter membranes prepared in accordance with MDHS 52/3.
1,5 diphenylcarbazide solution 0.25% w/v is obtained by transferring the contents of one vial
(0.125 g) to the 60 ml plastic bottle labelled Diphenylcarbazide 0.25% w/v.
Using rhe 25 ml measuring cylinder, transfer 25 ml acetone to the bottle and swirl until the powder
has dissolved. Measure 25 ml deionised water and add to the bottle. Replace the cap tightly and
mix thoroughly.
Protect from light.
There is sufficient reagent for 25 determinations of hexavalent chromium.
Page 6 www.skcltd.com
Page 9
Analysis
The apparatus
The kit comprises:
1 off Alkali treated filter membranes (pack of 24)
10 off 1,5 Diphenylcarbazide 0.125g vial
1 off Sulphuric Acid 500ml
1 off Acetone 250ml
1 off De-ionised Water 500ml
3 off Plastic beaker
1 off Glass measuring cylinder 25ml
1 off Glass measuring cylinder 10ml
1 off Glass measuring cylinder 5ml
1 off Plastic bottle labeled 60ml
5 off Comparator moulded cell and cap 10ml
1 off Wash bottle 250ml
1 off Forceps
1 off Lovibond comparator with CrVI disc 26620
1 off Handbook with health and safety data
A holding clamp to position the filter head above the facility tank is available as an optional extra.
www.skcltd.com Page 7
Page 10
Analysis
The comparator
The Lovibond 2000 comparator fitted with chromium VI comparator disc 26620 covers the range
0-0.1 mg chromium VI per cubic metre of air in steps of:
This is suitable for the measurement of 120 litres of sample drawn at 2 litre/minute for 60 minutes.
Removing the filter paper for analysis
1. Transfer your sampling system to clean, non hazardous area to perform the analysis.
2. Remove filter using forceps, taking care not to cause damage, and place filter into 50 ml plastic
beaker.
3. Using 10 ml measuring cylinder, add 8 ml 0.25M sulphuric acid to the beaker.
4. Wait 10 minutes for dissolution of any hexavalent to take place, swirling solution occasionally.
5. Using 5 ml measuring cylinder add 2 ml diphenylcarbazide solution to beaker and swirl to mix.
Allow to stand 10 minutes.
6. Transfer one new unused filter membrane to a clean 50 ml plastic beaker using forceps and
repeat steps 2 - 4 above.
7. Fill a comparator cell to 10 ml mark with ‘sample’ solution and place in right hand compartment
of Lovibond comparator. Place a second cell containing deionised water in left hand
compartment.
Page 8 www.skcltd.com
Page 11
Analysis
8. Check that comparator colour standards disc Chromium 66200 is inserted. Hold comparator
against good north daylight (not fluorescent lighting) and rotate comparator disc until match
with ‘sample’ solution is obtained.
9. The value appearing in the window of the comparator is the amount of hexavalent chromium
in milligrams per cubic metre (mg/m3) of air based on a sample volume of 120 litres. Note this
value.
10. Repeat steps 6 and 7 above using the solution from step 5. Note the reading for reference.
In ideal conditions there should be no reading from this solution as it was made with a clean
unused filter. If a reading is obtained this highlights a problem with procedures:
11. check on the purity of reagents and filters
12. check for contamination caused by unclean apparatus
13. Record results (see page 10).
14. Clean all apparatus between measurements and at the end of testing. The filter head should
be cleaned to avoid cross-contamination between samples.
www.skcltd.com Page 9
Page 12
Administration and Next Steps
Record keeping
Ensure all results obtained from sampling are adequately recorded!
This data must be kept for a period of time as defined in H.S.E. guidance, so it is vital to maintain
these in an easy-retrieve format.
Each sample position should clearly be identified for record purposes and the results of the analysis
recorded.
Record facility identity, date of sampling, the identity of the person carrying out the test and the
sampling position, and in accordance with guidelines laid out in MDHS 52/3 and by the H.S.E.
Results
Any result higher than normal or in excess of the maximum limit should be investigated to determine
the reason.
If in doubt of how to proceed or if you are concerned about the results obtained, consult the Health
& Safety Executive for guidance.
Refer to MDHS 52/3 and EH40 for further advice and exposure limit values.
Page 10 www.skcltd.com
Page 13
Supplies
For supplies and for further advice please contact SKC customer services at: