IAEA Reference Materials

Reference Sheets

REFERENCE MATERIAL
IAEA-408
ORGANOCHLORINE COMPOUNDS, PETROLEUM HYDROCARBONS AND STEROLS
IN

SEDIMENT

Intended Use  
    This sample is intended to be used as a reference material for the determination of chlorinated compounds, petroleum hydrocarbons and sterols in sediment samples. It can also be used as a quality control material for the assessment of a laboratory's analytical work, for the validation of analytical methods and for quality assurance within a laboratory.   

Origin and preparation of the material  
    A large sample of sediment was collected from the mudflats of the Tagus estuary. This sediment was deep-frozen, freeze-dried, ground and sieved through a 150 µm stainless steel sieve.
    The sediment fraction of particle size less than 150 µm was homogenized by mixing in a rotating drum for two weeks. Then, aliquots of about 40 grams were packaged into glass bottles with aluminium screw caps and sealed with Teflon tape.
Date of Release:  
November 1999
Unit Price:  
130 €
Unit Size:  
40 g
Producer:  
Marine Environment Laboratory (MEL)
International Atomic Energy Agency 
B.P. No 800 
MC-98012 Monaco
Supplier:  
Analytical Quality Control Services 
Agency's Laboratories, Seibersdorf 
A-2444 Seibersdorf, Austria
Reference Sheet: IAEA-408(.pdf)

Analyte
Status
Concentration
[ng/g]
(Based on dry weight)
95% C. I.
[ng/g]
N *
Chlorinated pesticides
alpha- HCH
I
0.61
0.21 - 1.5
4
beta- HCH
I
0.55
0.38 - 1.7
5
gamma- HCH (Lindane)
R
0.19
0.11 - 0.2
14
HCB
R
0.41
0.3 - 0.57
25
pp’ DDE
R
1.4
0.88 - 2.0
34
pp’ DDD
I
0.87
0.56 - 1.7
30
pp’ DDT
R
0.67
0.48 - 0.98
21
op DDD
I
0.19
0.18 - 0.33
4
op DDT
I
0.38
0.09 - 3.8
3
Aldrin
I
0.41
0.2 - 2.3
11
Endrin
I
0.57
0.14 - 1.2
7
Dieldrin
R
0.3
0.3 - 0.48
13
Heptachlor
I
0.42
0.23 - 0.7
7
Heptachlor Epoxide
I
0.64
0.43 - 1.5
10
alpha- Endosulfan
I
1.6
0.3 - 6.2
3
Endosulfan Sulfate
I
1.6
0.5 - 8.2
3
alpha- Chlordane
I
0.12
0.1 - 0.34
5
gamma- Chlordane
I
0.27
0.06 - 0.48
6
Aroclor 1254
I
19
14 - 40
10
Aroclor 1260
I
10
6.8 - 25
11
Hydrocarbons
Total Aliphatics
I
120000
81000 - 160000
4
n - C 17
R
74
56 - 140
8
Pristane
R
69
50 - 130
10
n - C 18
I
90
60 - 110
7
Phytane
R
78
63 - 130
9
SUM n Alkanes (C 14 - C 34)
R
8100
4300 -12000
8
Phenanthrene
R
35
21 - 43
15
2 Methyl Phenanthrene
I
12
12 - 14
4
1 Methyl Phenanthrene
I
10
9.2 - 11
6
Anthracene
R
9.8
8.0 - 13
9
Chrysene
R
35
25 - 56
16
Fluorene
I
6.7
4.6 - 24
7
Fluoranthene
R
84
53 - 110
18
Pyrene
R
77
57 - 93
17
Benzo (b) Fluoranthene
R
46
32 - 69
8
Benzo (k) Fluoranthene
R
46
26 - 61
8
Benz (a) Anthracene
R
53
35 - 60
13
Benzo (e) Pyrene
R
55
51 - 81
8
Benzo (a) Pyrene
R
48
30 - 63
14
Naphthalene
R
27
16 - 47
13
Benzo (ghi) Perylene
R
38
20 - 52
12
Indeno (123cd) Pyrene
I
51
45 - 53
5
UVF equival. Chrysene
I
6000
4600 - 19000
6
UVF equival. ROPME oil
I
49000
35000 - 120000
4
Resolved Aliphatics
R
11000
6400 - 17000
7
Unresolved Aliphatics
I
110000
68000 - 150000
4
Total Aromatics
I
3700
1300 -11000
4
Resolved Aromatics
I
1900
240- 6800
4
Perylene
R
320
140 - 420
7
1 Methyl Naphthalene
I
7.5
4.7 - 12
4
2 Methyl Naphthalene
I
14
13 - 33
3
Dibenz (ah) Anthracene
I
11
7.8 - 14
3
Acenaphthene
I
3.3
2.0 - 17
4
Acenaphthylene
I
3.6
2.1 - 4.7
4
PCBs
PCB No 8
I
0.24
0.22 - 4.6
3
PCB No 18
I
0.74
0.13 - 1.9
6
PCB No 28
R
0.79
0.35 - 0.98
14
PCB No 31
I
0.43
0.09 - 1.5
3
PCB No 44
I
0.47
0.23 - 3.0
9
PCB No 49
I
0.35
0.22 - 0.38
4
PCB No 52
R
0.6
0.38 - 0.93
18
PCB No 87
I
0.87
0.26 - 1.1
3
PCB No 101
R
1.2
0.81 - 1.7
23
PCB No 105
R
0.57
0.44 - 0.67
9
PCB No 110
R
0.83
0.5 - 0.9
6
PCB No 118
R
1.2
0.9 - 1.6
21
PCB No 128
R
0.33
0.27 - 0.53
10
PCB No 138
R
1.6
1.1 - 2.1
22
PCB No 149
R
1.4
1.3 - 1.6
7
PCB No 153
R
1.9
0.98 - 2.1
20
PCB No 156
I
0.36
0.31 - 0.39
4
PCB No 170
R
0.47
0.34 - 0.59
8
PCB No 174
I
0.34
0.2 - 0.44
4
PCB No 177
I
0.35
0.23 - 0.43
4
PCB No 180
R
1.1
0.85 - 1.2
20
PCB No 183
I
0.32
0.26 - 0.33
3
PCB No 187
R
0.68
0.49 - 0.94
7
PCB No 194
R
0.2
0.2 - 0.23
5
PCB No 195
I
0.12
0.06 - 0.16
4
PCB No 196
I
0.22
0.17 - 0.4
3
Sterols
Coprostanol
I
1900
1700§
3
Cholesterol
I
910
670§
3
Cholestanol
I
1100
760§
3
beta- Sistosterol
I
1100
640§
3
Campesterol
I
2200
2200§
2

*
Number of accepted laboratory results which were used to calculate the recommended or information values and their respective confidence intervals about the median value.
(R/I)  Classification assigned to the property value for Analyte (Recommended/Information)
§ Standard deviation


The values listed above were established on the basis of statistically valid results submitted by laboratories which had participated in an international intercomparison exercise conducted between 1998 - 1999. The details concerning the criteria for qualification as a recommended or information value can be found in the report (IAEA/AL/121; IAEA/MEL/67), "World-wide and Regional Intercomparison for Determination of Organochlorine Compounds, Petroleum Hydrocarbons and Sterols in Sediment Sample IAEA-408" [1]. This report is available free of charge upon request.    

Homogeneity  
    The homogeneity of the material for organochlorine compounds, petroleum hydrocarbons and sterols was checked by determining the concentration of some compounds (chlorinated pesticides, petroleum hydrocarbons and sterols) in 10 replicate analyses taken at random from the bulk material. A one-way variance analysis indicated that the material could be considered homogeneous.

Dry weight determination
 
 
    The moisture content of the lyophilized sample as determined by drying to a constant weight at 105°C was found to be 3.7 %. Since the moisture content can change with the ambient humidity and temperature, it was recommended that the water content of this material always be determined in a separate sub-sample (not that taken for analysis) by drying to a constant weight (~24 hours) at 105°C. Results should always be reported on a dry weight basis. 

Instructions for use  
    The recommended sample size for analysis is 5 g for petroleum hydrocarbons and 10 g for organochlorines respectively. Analysts are reminded to take appropriate precautions in order to avoid contamination of the material during handling. The material should be stored in the dark and kept in a refrigerator.  

References: 
[1]

Last updated 30 March 2004