Ecological implications of motor oil pollution: Earthworm survival and
soil health
Kavitha Ramadass
a, b
, Mallavarapu Megharaj
a, b, *
, Kadiyala Venkateswarlu
a, c
,
Ravi Naidu
a, b
a
Centre for Environmental Risk Assessment and Remediation, University of South Australia, Mawson Lakes, SA 5095, Australia
b
Cooperative Research Centre for Contamination and Remediation of the Environment (CRC CARE), Australia
c
Sri Krishnadevaraya University, Anantapur 515055, India
article info
Article history:
Received 7 September 2014
Received in revised form
20 February 2015
Accepted 24 February 2015
Available online 9 March 2015
Keywords:
Used motor oil
Nontarget effects
Earthworm survival
Hydrocarbon accumulation
Soil health
abstract
The nontarget effects of fresh and used motor oil were studied in a soil test system involving such criteria
as earthworm survival, response of soil dehydrogenase and urease, and nitrification. When earthworms
were exposed to motor oil-contaminated soil for 4 weeks, the observed median lethal concentrations
(LC
50
) were 40.33 and 3.88 g kg
1
soil for fresh and used oil, respectively. Only fresh motor oil application
increased earthworms' body weight even at the higher dose of 19 g kg
1
soil. Gas chromatography/mass
spectrometry revealed that used motor oil contained more of aromatic hydrocarbons and heavy metals
than fresh oil. This disparity in the chemical composition might be the factor responsible for the sig-
nificant toxicity of used motor oil towards earthworms. Activities of soil dehydrogenase and urease were
significantly enhanced in presence of both the motor oils, while there was a significant inhibition in
nitrification by the used motor oil even at a low concentration of 0.2 g kg
1
soil. This study clearly
demonstrated that earthworm survival and nitrification could serve as suitable indices to assess motor
oil pollution in soil.
© 2015 Elsevier Ltd. All rights reserved.
1. Introduction
Lubricants in the form of motor oil or engine oil are consumed
largely in automobiles to protect the internal combustion engines.
Generally, motor oil consists of 90% petroleum fractions and 10%
additives. Different brands of engine oils have different additives
that belong to several groups such as antioxidants, detergents, anti-
wear agents, dispersants, corrosion inhibitors and viscosity index
improvers (Caines and Haycock, 2004). The internal combustion
engine acts like an oxidator and the hydrocarbons in the engine oil
are partially oxidized when contacted with oxygen at elevated
temperatures for long periods. Metals like iron (Fe), copper (Cu),
lead (Pb), nickel (Ni), etc. used in the manufacture of the engine are
effective oxidation catalysts and increases the rate of oxidation of
the engine oil. The oxidation process produces acidic bodies within
the motor oil which are corrosive to typical Cu, Pb, and cadmium
(Cd) engine bearings. Furthermore, oxidation products contribute
to the formation of sludges within the motor oil and an overall
breakdown of viscosity characteristics of the lubricant.
Used motor oil contains minute quantities of gasoline or diesel,
additives, nitrogen and sulphur compounds, a broad range of aro-
matic and aliphatic hydrocarbons with chain lengths ranging from
C
15
to C
50
, and metals that arise from normal wear of engine
components and from heating and oxidation of lubricating oil
(Vazquez-Duhalt, 1989; Dominguez-Rosado, and Pichtel, 2003;
Singh et al., 2006). Thus, US EPA (2001) defined used motor oil as
“any petroleum-based or synthetic oil that has been used for
vehicle lubrication and as a result of normal use, motor oil becomes
contaminated with various impurities such as dirt, water, chemicals
or metals from vehicle engine”. Once degraded motor oil escapes
the engine, it has the potential to pollute waterways in the form of
runoff and soil. The US Environmental Protection Agency (EPA)
reported that 1.0 gallon of used motor oil can contaminate 1.0
million gallons of fresh water. If used motor oil reaches sewage
treatment plants, even small concentrations of 50e100 ppm can
foul the water treatment process.
One litre of used motor oil can pollute up to 3784 m
2
of soil,
making it non-productive for farming or plant growth for up to
* Corresponding Author. Centre for Environmental Risk Assessment and Reme-
diation, University of South Australia, X Building, Room X1-14, Mawson Lakes
Campus, Mawson Lakes, South Australia, SA 5095, Australia. Tel.: þ61 8 8302 5044
(W); fax: þ61 8 8302 3057.
E-mail address: Megharaj.Mallavarapu@unisa.edu.au (M. Megharaj).
Contents lists available at ScienceDirect
Soil Biology & Biochemistry
journal homepage: www.elsevier.com/locate/soilbio
http://dx.doi.org/10.1016/j.soilbio.2015.02.026
0038-0717/© 2015 Elsevier Ltd. All rights reserved.
Soil Biology & Biochemistry 85 (2015) 72e81