contaminated soil
TRANSCRIPT
-
8/2/2019 Contaminated Soil
1/8
Petroleum Product Identification in Environmental Samples:Distribution Patterns of Fuel-Specific Homologous Series
Yakov Galperin, Henry Camp
Identification of fuel-type in environmental samples (hydrocarbon fingerprinting) is one
of the major objectives of forensic investigations conducted at many of the petroleum-
contaminated sites throughout the country. Among analytical methods commonly used toidentify fugitive refined petroleum products, are those that focus on hydrocarbon group-
type analysis, such as alkanes, polynuclear aromatic hydrocarbons (PAH) and thepolycyclic alkanes, often referred to as biomarkers. These classic methods are included inthe analytical arsenal of most laboratories conducting fuel fingerprinting. Basic principles
of their application have been exhaustively examined in this column by Battelle
researchers.
Alkane distribution patters are routinely obtained using gas chromatography with flame
ionization detection (GC/FID). For petroleum products that have not undergonenoticeable biodegradation, this method provides an adequate procedure for fingerprinting
and fuel recognition based on the n-alkane homologous series. However, GC/FID issignificantly less useful for identification of other hydrocarbon groups, which is often
necessary for petroleum product fingerprinting in weathered environmental samples.Conventional analytical methods for identification of isoprenoids, PAH and biomarkers
which are commonly used in characterizing crude oil, are of limited utility for light andsome middle distillate fuels.
The serious limitations for the application of normal alkanes arises from the fact thatupon release into the environment, refined petroleum products are subject to various
weathering changes. In weathered products, most n-alkanes could be lost due to
biological degradation, whereas distribution of the more recalcitrant isoprenoids andPAH may not provide conclusive information on the source or type of fugitive fuel.
Recent investigations demonstrated that the cyclohexane homologous series of
hydrocarbons also exhibits fuel-specific distribution patterns that allow for fingerprintingof weathered fugitive fuels.
Fuel-specific distribution patterns
Crude oil contains a wide range of hydrocarbons from light gases to heavy residue. Atthe refinery, crude oil is separated by distillation into three main products: naphtha,
middle distillate and bottoms fraction. Naphtha is mainly used for motor gasoline and
processed further for octane improvement. The middle distillate can actually be
1
-
8/2/2019 Contaminated Soil
2/8
separated into two categories consisting of kerosene range products (light-end) and dieselrange products (heavy-end). The light-end products are used for specialty solvents
(mineral spirits, stoddard solvent, etc), certain jet fuels and light diesel fuels (diesel #1).
The heavy-end middle distillates are used for diesel fuels (diesel #2), some jet fuels andheating oils.
Based on the systematic studies of different commercial and military fuels, it wasdetermined that in addition to a well-known alkane pattern, cyclohexane homologous
series also exhibit characteristic distribution patterns. Examples of alkane and
alkylcyclohexane patterns for three common fuels are shown in Figures 1-3. The
alkylcyclohexane distribution in gasoline (Figure 1) exhibits an asymmetric rapidlydecreasing pattern from methylcyclohexane to heptylcyclohexane. Jet propulsion fuel Jet
A (Figure 2) is characterized by a distribution pattern in the range from
methylcyclohexane to decylcyclohexane with the maximum at butylcyclohexane. Dieselfuel exhibits alkylcyclohexane pattern from methylcyclohexane to tridecylcyclohexane
with maximum at pentylcyclohexane (Figure 3).
The range of hydrocarbons in each product is determined by its boiling range, whereas
the distribution pattern reflects its application-specific formulation. Since the composition
of modern fuels is controlled by stringent manufacturing specifications, the range anddistribution pattern of each fuel varies only slightly, depending on the composition of
crude oil feedstock and refining practices used in manufacture.
Fuel-type characterization in weathered samples
Distribution patterns shown demonstrate that alkylcyclohexane distribution patterns are
as fuel-specific as are the alkane distributions.The main advantage in utilizingalkylcyclohexane patterns for hydrocarbon fuel recognition is that alicyclic compounds
are more resistant to environmental alteration and could be detected in a sample even
when most of the alkanes are degraded. Two case studies illustrating the application ofalkylcyclohexane pattern recognition for weathered environmental samples are
summarized below.
Case 1. Shown in Figure 4 is an alkane distribution pattern in the product sample. The
product lost most of n-alkanes due to weathering in the subsurface environment. The
group of peaks identified on the chromatogram represents isoalkanes, whose distributionsuggests the presence of diesel fuel. Because of the alkane reduction, it is not apparent if
other middle distillate products are also present. However, evaluation of the
alkylcyclohexane pattern confirms that the product consists entirely of diesel fuel.
Case 2. Alkane distribution patterns of two samples collected at the same site are shown
in Figure 5. Sample A have lost most of n-alkanes and appears to represent a severely
weathered product, whereas a high abundance of n-alkanes in sample B attests to itsrelatively unaltered nature. A significant difference in the degree of product weathering
does not allow evaluating their source relationship. However, a comparison of the
alkylcyclohexane distributions (Figure 6) clearly indicates that both samples represent thesame fuel-type.
2
-
8/2/2019 Contaminated Soil
3/8
Figure 1. Gasoline alkane (a) and alkylcyclohexane (b) distribution patterns
5.00 10.0015.0020.0025.0030.0035.0040.0045.0050.0055.0060.0065.000
20000
40000
60000
80000
100000
120000
140000
160000
180000
200000
220000
240000
260000
280000
300000
320000
340000
360000
380000
400000
420000
Time
Response_
09190036.D\FID1A
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
RelativeAbundance,%
(b)
(a)
3
-
8/2/2019 Contaminated Soil
4/8
Figure 2. Jet A fuel alkane (a) and alkylcyclohexane (b) distribution patterns
5.00 10.0015.0020.0025.0030.0035.0040.0045.0050.0055.0060.0065.000
10000
20000
30000
40000
50000
60000
70000
80000
90000
100000
110000
120000
130000
140000
150000
Time
Response_
09190041.D\FID2B
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
Relative
Abundance,%
n-C9
n-C16
n-C12
(b)
(a)
4
-
8/2/2019 Contaminated Soil
5/8
Figure 3. Diesel fuel alkane (a) and alkylcyclohexane (b) distribution patterns
5.00 10.0015.0020.0025.0030.0035.0040.0045.0050.0055.0060.0065.000
10000
20000
30000
40000
50000
60000
70000
80000
90000
100000
110000
120000
Time
Response_
09190044.D\FID1A
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
RelativeAbundance,%
n-C9
n-C21
n-C14
(b)
(a)
5
-
8/2/2019 Contaminated Soil
6/8
Figure 4. Product sample alkane (a) and alkylcyclohexane (b) distribution patterns
5.00 10.00 15.00 20.00 25.00 30.00 35.00 40.000
50000
100000
150000
200000
250000
300000
350000
400000
450000
500000
550000
600000
650000
700000
Time-->
Abundance
Ion 85.00 (84.70 to 85.70): Y4504.D
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
Relative
Abundance,%
i-C18
i-C15
i-C15
Ph
Pr
(b)
(a)
6
-
8/2/2019 Contaminated Soil
7/8
Figure 5. Product samples alkane distribution patterns
20.0025.0030.0035.0040.0045.0050.0055.0060.0065.0070.0075.0080.0085.000
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
55000
60000
65000
70000
75000
80000
85000
90000
95000
100000
Time-->
bundance
Ion 85.00 (84.70 to 85.70): V4978.D
20.0025.0030.0035.0040.0045.0050.0055.0060.0065.0070.0075.0080.0085.000
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
55000
60000
65000
70000
Time-->
Abundance
Ion 85.00 (84.70 to 85.70): V4687.D
Sample A
Sample B
n-C11
7
-
8/2/2019 Contaminated Soil
8/8
Figure 6. Product samples alkylcyclohexane distribution patterns
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
RelativeAbundance,%
0
10
20
30
40
50
60
70
80
90
100
Methylcyclohexane
Ethylcyclohexane
Propylcyclohexane
Butylcyclohexane
Pentylcyclohexane
Hexylcyclohexane
Heptylcyclohexane
Octylcyclohexane
Nonylcyclohexane
Decylcyclohexane
Undecanylcyclohexane
Dodecanylcyclohexane
Tridecanylcyclohexane
RelativeAbundance,%
Sample B
Sample A
8