United States
Environmental Protection
Agency
Robert S. Kerr Environmental
Research Laboratory
Ada OK 74820
Research and Development
EPA-600/S2-84-108 July 1984
c/ERA Project Summary
Laboratory Assessment of
Potential Hydrocarbon Emissions
from Land Treatment of Refinery
Oily Sludges
R.G. Wetherold, J.L. Randall, and K.R. Williams
Volatile organic emissions were
characterized when oily petroleum
sludges from refineries were incorpo-
rated in soils under controlled labora-
tory conditions. The sludges tested
included three of the five listed hazard-
ous wastes for the refining industry:
dissolved air flotation float, slop oil
emulsion solids, and API separator
sludge. The volatile components of the
sludges were first identified. Then the
effects of air temperature and humidity,
wind speed, soil type, temperature and
moisture, sludge loading and volatility,
and method of waste application were
studied. The volatile components iden-
tified in the sludge were also present in
the emissions from the soil-waste
mixtures. The quantity of emissions
was most affected by the sludge volatil-
ity, sludge loading, application method,
and atmospheric humidity; the cumula-
tive emissions at a given period of time
could be correlated with these opera-
tional variables. The emission rate or
level was not significantly affected by
soil type or soil moisture. An expression
for estimating the rate of emissions as a
function of elapsed time after applica-
tion could not be developed from the
data. Although every effort was made
to simulate actual land treatment
conditions, it was not possible to apply
these laboratory findings directly to
predict full-scale results.
This Project Summary was developed
by EPA's Robert S. Kerr Environmental
Research Laboratory. Ada, OK, to an-
nounce key findings of the research
project that is fully documented in a
separate report of the same title (see
Project Report ordering information at
back). The research effort was jointly
funded by the US EPA and the American
Petroleum Institute.
Introduction
Land treatment has been used exten-
sively by the petroleum refining industry
to attenuate oily sludges, predominantly
on company property. In the current
process of renewing land treatment
permits, there has been an increasing
interest in addressing the characteristics
and magnitude of volatile organic emis-
sions occurring in land treatment opera-
tions.
This laboratory study was performed to
assess the atmospheric emissions from
the land treatment of refinery sludges,
particularly those listed as hazardous
wastes for petroleum refining in 40 CFR
261.32 and which are routinely land
treated by the industry. The wastes
studied were API separator sludge, slop
oil emulsion solids, and dissolved air
flotation (DAF) float. The magnitude and
characteristics of the emissions and the
variables affecting them were investi-
gated using sludges and soils collected
from participating refineries.
Procedures
The volatile organic constituents of the
sludges were identified by using a
purging device, trapping the emitted
organics, and performing analyses by gas
chromatography 'mass spectrometry
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(GC/MS). A laboratory land treatment
simulator apparatus was constructed to
measure air emissions from soil/waste
mixtures while controlling and mea-
suring air velocity, humidity, and tem-
perature, and soil temperature and mois-
ture. A series of tests was conducted with
this simulator using eight soil samples
and nine sludges obtained from eight
participating refineries. Initially, nine
variables were evaluated with the
simulator (Table 1). Based on these
preliminary studies, the five variables
indicated by asterisks in Table 1 were
chosen for further intensive study. Table
2 is the experimental matrix for evaluating
these variables, where one variable was
studied while holding the four others
constant. The remaining variables in
Table 1 were held constant: air and soil
temperatures at 90°F, wind velocity 3
mph, and sludge application mode being
to the surface. Emissions measurements
consisted of total hydrocarbons as
measured by a Byron Instruments 401
Total Hydrocarbon Analyzer and indivi-
dual compound identification by collec-
tion in steel cylinders and dual detector
GC analysis using normalized toluene
response as the indicator of the compound
present.1
Results and Discussion
The sludge characteristics are presented
in Table 3 (nonspecific organic content)
and in Table 4 (specific organic compounds
identified). Fifty-two runs were made
with the land treatment simulator. Statis-
tical interpretation identified the param-
Table 1. Operational Variables Studied
with the Land Treatment Simula-
tion Apparatus
Table 3. Nonspecific Organic Composition of Sludges
*Sludge Volatility
Application Mode
"So/1 Loading
Air Temperature
Soil Temperature
*Soil Type
*Soil Moisture
*Air Humidity
Air Flow
Sludge
SL-11
SL-12
SL-13
SL-14
Type
API Sludge
DAF Float
Slop Oil
API Sludge
Oil &
Grease
(wt. %)
22
1
2
2
Volatilized
hydrocarbons"
(PPM /ml sludge)
820
70
125
103
Sum of volatilized
compounds
identified''
(ug/gm)
6,100
760
2,910
850
"A verage total hydrocarbon concentration in vapor phase over 4 hrs. nitrogen purging using 1 ml
sludge (expressed as hexane).
"Total concentration of emitted compounds identified by GC/MS (see Table 4).
Table 4. Major Organic Compounds Identified in Sludges
Sludges
SL-11
SL-12
SL-13
SL-14
Compound
Benzene
Toluene
M/P-Xylene
0-Xylene
CyBenzene
CyBenzene
Napthalene
Anthr./Phen.
C9-H.C.
(alkane)
Ciz-H.C.
(alkane)
C,i-H.C.
(alkane)
Cn-H.C.
(alkanej
(pristane)
Cig-MC.
Cso-H.C.
540
1,700
7OO
330
/, 7OO
890
230
150
13O
140
84
66
31
2
32
58
58
28
150
120
34
20
30
57
72
72
26
NM
18
98
11O
SO
4OO
40O
350
1,100
14
210
84
24
4O ^
16
5
14
30
16
160
140
64
92
36
J2O
68
68
28
14
eters having the most significant affects
on emission levels: sludge volatility,
sludge loading, and air humidity. The
emission rate or level is not significantly
affected by type of soil or its moisture
content. In general, the results showed
that the more volatile components
identified in the sludges are emitted to the
air, specifically C9 - Ci2 alkanes, xylenes.
C3-benzenes, toluene, and benzene. The
more volatile compounds were present in
Table 2.
Experimental Matrix for Evaluating Operational Variables
Sludge ID
Sludge Volatility:
Low
Medium
High
SL-12
SL-13. SL-14
SL-11
Soil ID
Soil Type:
Sludge Loadings:
Soil Moisture:
Air Relative Humidity:
D-1
D-8
D-7
Silty sand
Silty clay
Sandy Silt
5 levels (0.05 - 2.0 Ib oil/ft2 soil)
5 levels (5 - 25 wt. %)
3 levels (30 - 80%)
the emissions at relatively higher con-
centrations compared to the concentra-
tions in the sludges that were the
respective sources of the emissions. The
cumulative emissions at a given period
in time (four to seven hours after
application) can be correlated with sludge
volatility, sludge loading, and atmospheric
humidity. During the two phases of the
study, the hydrocarbon volatilization
ranges, expressed as % oil content in
sludges applied, were 0 - 3.6% after 30
minutes and 0-6% after 4 hours applied.
An expression for estimating rate of
emissions as a function of elapsed time
after sludge application could not be
developed from the data obtained.
Alt of the specific organic compounds
identified in the emissions from each of
the runs is tabulated in the report to-
gether with the measured concentra-
tions in parts per million by volume
expressed as carbon (ppmv-C).
References
1Cox, R.D. and R.D. Earp "Determination
of Trace Level-Organics in Ambient Air
-------
by High-Resolution Gas Chromatogra-
phy with Simultaneous Photoioniza-
tion and Flame lonization Detection,"
Anal. Chem. 54 (13) 2266, November,
1982.
R. G. Wetherold, J. L Randall, and K. R. Williams are with Radian Corporation.
Austin, TX 78766.
Fred M. Pfeffer is the EPA Project Officer (see below).
The complete report, entitled "Laboratory Assessment of Potential Hydrocarbon
Emissions from Land Treatment of Refinery Oily Sludges," (Order No. PB 84-
209 766; Cost: $13.00, subject to change) will be available only from:
National Technical Information Service
5285 Port Royal Road
Springfield, VA22161
Telephone: 703-487-4650
The EPA Project Officer can be contacted at:
Robert S. Kerr Environmental Research Laboratory
U.S. Environmental Protection Agency
Ada, OK 74820
U S. GOVERNMENT PRINTING OFFICE, 1984 — 759-015/7755
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United States Center for Environmental Research
Environmental Protection Information
Agency Cincinnati OH 45268
Official Business
Penalty for Private Use $300
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