5. Potential Environmental
Impacts of Tyre Leachate
The literature reviewed on the environmental impact of tyre leachate
is summarised in Sections 5.1 and 5.2. It should be noted, however,
the review was not an in-depth analysis of the literature.
5.1 Recent Laboratory Research
Recent laboratory research on tyre leachate reviewed in this study
is briefly summarised in Table 5.1.
Table 5.1: Summary of reviewed laboratory
research on tyre leachate
View
summary of reviewed laboratory research on tyre leachate (large table)
In the laboratory tyre leachate is often generated by inundating a
tyre sample (plug, shred, chip, or crumb) with water. There are limitations
when comparing the results of the reviewed laboratory studies as different
makes of tyres were used and different compounds were measured; however
the following general observations can be made about the tyre leachate
generated in the laboratory:
- it may be toxic to some fish species (eg rainbow trout but not minnow),
bacteria, invertebrates and green algae
- levels of aluminium and manganese are likely to be elevated, especially
where steel is exposed
- levels of mercury and lead may be elevated; however most studies
reported negligible levels
- levels of zinc and organic compounds are likely to be dependent
on individual circumstances as a wide range of levels have been reported
in the studies reviewed
- levels of other substances are likely to below United States Drinking
Water Standards
- levels of leachate compounds (metals and organic compounds) are
likely to increase with time of inundation, increase proportionally
with amount of tyre and decrease proportionally with size of tyre
exposed to inundation.
5.2 Recent Field Trials
Recent field trials on tyre leachate reviewed in this study are briefly
summarised in Table 5.2.
Table 5.2: Summary of reviewed field
trials on tyre leachate
View
summary of reviewed field trials on tyre leachate (large table)
In field trials tyre leachate is generated by water percolating through
the tyre sample (whole tyre, shred or chip). There are limitations when
comparing the results of the reviewed field trials as different makes
of tyres were used and different compounds were measured; however the
following general observations can be made about the nature of tyre
leachate generated in the field:
- levels of manganese and iron are likely to be elevated in groundwater,
especially when steel is exposed
- levels of aluminium, zinc and organic compounds may be elevated
in groundwater; however the majority of studies reported negligible
levels
- level of cadmium and lead may be elevated in soil; however no studies
reviewed reported elevated levels in groundwater
- levels of other substances measured are likely to be below United
States Drinking Water Standards
- level of leachate compounds in groundwater are likely to decrease
down gradient of the tyre site.
5.3 General Observations
The potential environmental impacts of tyre leachate are contamination
of soil, surface water and groundwater on the site and surrounding area.
Based on the reviewed literature and previous MWH experience in site
contamination, factors that may affect the rate of leaching and/or the
concentration of tyre leachate compounds in soil, surface water and
groundwater include:
- tyre size: leaching from whole tyres
is likely to be slower than leaching from tyre chips or shreds - this
is because of the differences in the surface area to volume ratio
- amount of exposed steel: if steel is
exposed, say in tyre chips, there is likely to be faster leaching
of manganese and iron than from whole tyres where the steel is not
exposed
- chemical environment: leaching of metals
is likely to be more rapid under acidic conditions while leaching
of organic compounds is likely to be more rapid under basic conditions
- permeability of soil: leaching is likely
to be faster when soils are permeable
- distance to groundwater table: the greater
the vertical distance to the groundwater table, the less likely the
contamination of groundwater
- distance from tyre storage site: the
further the downstream distance from the tyre storage site, the lower
the contaminant concentration in the soil and groundwater
- contact time with water: the longer the
tyres are in contact with water, the greater the risk of groundwater
contamination
- vertical water flow through soil: the
greater the water flow through the soil (eg, from rainfall), the greater
the dilution of contaminants
- horizontal groundwater flow: the greater
the groundwater flow, the greater the spread of the contaminant plume
- leached compounds at site: levels of
manganese and iron are likely to be elevated in groundwater when steel
is exposed. Levels of aluminium, zinc and organic compounds may be
elevated in groundwater. Levels of zinc, cadmium and lead may be elevated
in soil.
Specific and general mitigation measures to address the environmental
risks associated with tyre leachate are outlined in
Section
8.8.