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Phytoremediation
Cleaning the Soil with Flowers
by Shanon Trueman
According to the International Phytotechnology Society website,
phytotechnology is defined as the science of using plants to solve
environmental problems such as pollution, reforestation, biofuels, and
landfilling.
Phytoremediation, a subcategory of phytotechnology, uses plants to
absorb pollutants from soils or from water.
The pollutants involved can include heavy metals, defined as any elements considered
as a metal that may cause pollution or an environmental problem, and that
cannot be further degraded.
A high accumulation of heavy metals in a soil or water can be
considered toxic to plants or animals.
Why Use Phytoremediation?
Other methodologies used to remediate soils polluted with heavy metals
can cost $1 million US per acre, whereas phytoremediation was estimated to cost
between 45 cents and $1.69 US per square foot, lowering the cost per acre to
the tens of thousands of dollars.
How Does Phytoremediation Work?
Not every plant species can be used for phytoremediation.
A plant that is able to take up more metals than normal plants is
called a hyperaccumulator.
Hyperaccumulators can absorb more heavy metals than is present in the
soil in which they are growing.
All plants need some heavy metals in small amounts; iron, copper, and
manganese are just a few of the heavy metals which are essential to plant
function.
Also, there are plants that can tolerate a high amount of metals in
their system, even more than they need for normal growth, instead of exhibiting
toxicity symptoms.
For example, a species of Thlaspi has a protein called a "metal
tolerance protein".
Zinc is heavily taken up by Thlaspi due to
the activation of a systemic zinc deficiency response.
In other words, the metal tolerance protein tells the plant that it
needs more zinc because it "needs more", even if it doesn't, so it
takes more up!
Specialized metal transporters within
a plant can assist in the uptake of heavy metals also.
The transporters, which are specific to the heavy metal to which it
binds, are proteins which assist in the transport, detoxification, and
sequestration of heavy metals within plants.
Microbes in the rhizosphere cling to the surface of plant roots, and
some remediating microbes are able to break down organic materials such
as petroleum and take heavy metals up and out
of the soil.
This benefits the microbes as well as the plant, as the process can
provide a template and a food source for microbes that can degrade organic
pollutants.
The plants subsequently release root exudates, enzymes, and organic
carbon for the microbes to feed upon.
History Of Phytoremediation
The "godfather" of phytoremediation and the study of
hyperaccumulator plants may very well be R. R. Brooks of New Zealand.
One of the first papers involving an unusually high level of heavy
metal uptake in plants in a polluted ecosystem was written by Reeves and Brooks in
1983.
They found that the concentration of lead in Thlaspi located in a mining area was easily the
highest ever recorded for any flowering plant.
Professor Brooks' work on heavy metal hyperaccumulation by plants led
to questions as to how this knowledge could be used to clean polluted soils.
The first article on phytoremediation was written by scientists at
Rutgers University about the use of specially-selected and engineered
metal-accumulating plants used to clean polluted soils.
In 1993, a United States patent was
filed by a company called Phytotech. Titled "Phytoremediation of
Metals," the patent disclosed a method to remove metal ions from soil
using plants.
Several species of plants, including radish and mustard, were
genetically engineered to express a protein called metallothionein.
The plant protein binds heavy metals and removes them so that plant
toxicity does not occur.
Due to this technology, genetically engineered plants, including Arabidopsis, tobacco, canola, and rice have been
modified to remediate areas contaminated with mercury.
External Factors Affecting Phytoremediation
The main factor affecting a plant's ability to hyperaccumulate heavy
metals is age.
Young roots grow faster and take up nutrients at a higher rate than
older roots, and age may also affect how the chemical contaminant moves
throughout the plant.
Naturally, the microbial populations in the root area affect the
uptake of metals.
Transpiration rates, due to sun/shade exposure and seasonal changes,
can affect plant uptake of heavy metals as well.
Plant Species Used For Phytoremediation
Over 500 plant species are
reported to have hyperaccumulation properties.
Natural hyperaccumulators include Iberis intermedia and Thlaspi spp.
Different plants accumulate different metals; for example, Brassica juncea accumulates copper, selenium, and
nickel, whereas Arabidopsis halleri accumulates
cadmium and Lemna gibba accumulates
arsenic.
Plants used in engineered wetlands include
sedges, rushes, reeds, and cattails because they are flood tolerant and are
able to uptake pollutants. Genetically engineered plants, including Arabidopsis, tobacco, canola, and rice, have been modified
to remediate areas contaminated with mercury.
How are plants tested for their hyperaccumulative abilities?
Plant tissue cultures are used frequently in
phytoremediation research, due to their ability to predict plant response and
to save time and money.
Marketability Of Phytoremediation
Phytoremediation is popular in theory due to its low establishment
cost and relative simplicity.
In the 1990's, there were several companies working with
phytoremediation, including Phytotech, PhytoWorks, and Earthcare.
Other large companies such as Chevron and DuPont were also developing
phytoremediation technologies.
However, little work has been performed recently by the companies, and
several of the smaller companies have gone out of business.
Problems with the technology include the fact that plant roots cannot
reach far enough into the soil core to accumulate some pollutants, and the
disposal of the plants after hyperaccumulation has taken place.
The plants cannot be plowed back into the soil, consumed by humans or
animals, or put into a landfill.
Dr. Brooks led pioneering work on the extraction of metals from
hyperaccumulator plants. This process is called phytomining and involves the
smelting of metals from the plants.
Shanon Trueman
Associate or adjunct professor of biology,
botany, and microbiology (past and present) at New England schools including
Quinnipiac University, Goodwin College, and Springfield Technical Community
College, among others
Plant research analyst for Nerac and Earthgro
for over 15 years
A published writer whose work has appeared in
a number of scientific journals including for the University of Massachusettes,
Amherst
Experience
Shanon Trueman is a former writer for
ThoughtCo who developed articles covering topics of biology and botany over the
course of five months. After graduate with a master's degree from Amherst,
Shanon was the director of research quality assurance for Earthgro and an
analyst for Nerac for over 14 years before she started teaching. Throughout her
professional career, Sharon has published in multiple scientific journals and
has held associate or adjunct professor positions at a number of New England
colleges and Universities including Goodwin College, Manchester Community
College, Springfield Technical Community College, and Quinnipiac University.
Education
Shanon received a master's degree in
microbiology and plant pathology at the University of Massachusetts, Amherst
and a bachelor's degree in agronomy from the University of Connecticut.
Awards and Publications
"The Effect of Fungal Disease on Basil
Plants" for UMass Amherst
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